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TS ie 8 a i ee ee ee ee ee a SS > : : — ik i a rem eee ene PFE == = ; = EE PS a ES De ar ee ae MCCS 3 ar SIT ~ Ae ee ee ee E See rer rene ee emp et Pen tee ee Ee Ae Re) ee aes a ee we ee ee ee SE OF See SR PPS PPE PI Sate AS TE ~ Se RS a eee eR ge ep ge ee tegen aes nnn rte a Le we Rta eS St ree ee pe ee > pee none ee SAP ei hare Rome ary ie A PPE : <== --—- “98 oe >- setae ssf SSeS os = = - oe + ne = a ae Z —=Ts a Se Ee - nee f } | Sy fa ih tt ei nN i sti ne fd ‘ TD ’ va . ah fil wf 4 \' ie ey : we 4? ‘ ' 1 r i 7) nibs Hh i Hei Pe. Yeon te aK hy ; A » 7 A 7 P Fi i mt the Ah Ai AA Nd me f Sh vba Hi Digitized by the Internet Archive in 2010 with funding from University of Toronto yt i. y j ‘ eey) i yar iv - i fit Ve se | oma VWW.a Anal Man hs A J ‘ 4) “ti ie J ie , } wilt) Ny We ity, De et iN eal y. University of California Publications in AGRICULTURAL SCIENCES VOLUME III 1917-1919 EDITORS CHARLES B. LIPMAN ERNEST B. BABCOCK JOHN W. GILMORE UNIVERSITY OF CALIFORNIA PRESS b . BERKELEY, CALIFORNIA ¢ : : \ ) se : Taer iL ee aKhh ery, é : 7.\ ! > ys, oe / - Z io) oO Z ° ~ No. Ve) CONTENTS PAGE New Grasses tor Calrornia, by P. B, Kennedy... 2.scccceccsssssovesenaneses ] Optimum Moisture Conditions for Young Lemon Trees on a Loam OE NE SED ey hat ch Mi Oe A OY 000) | ec 25 Some Abnormal Water Relations in Citrus Trees of the Arid South- west and Their Possible Significance, by Robert W. Hodgson.......... 37 Bei LPomgrouIoner, DY LIODAIG BYiC@ la... nic. 0-snosnsecsnssesinennecasseadenesmeres 55 Toxie and Antagonistic Effects of Salt on Wine Yeast (Sacchar- GMNUCCS: CIDSOUA CURT, WY ii. MAGE. ino orc. ce cscncnnsesantaccrrecsvosaztnvacnenconesiecn 63 Changes in the Chemical Composition of Grapes during Ripening, eet eOLEb bl Wee ce hteme, BIN EL; DAV 1. oca ue ciescenincnsrunceiends 103 A New Method of Extracting the Soil Solution (A Preliminary Coimmunication), by Charles 5. Taapman ... ... a . é <—s == —_-= 1917 | Mitra: YVowxie and Antagonistic Effects of Salts on Wine Yeast 75 NaCl shows a directly opposite reaction with yeast from that found by Lipman"! with soil bacteria. Both Loeb and Ostwald found NaCl to be toxie for animals, but less so than we have found with yeast. The toxicity of NaCl to animals may be compared with the toxicity of NaCl, to yeast. Loeb* found it impossible to develop embryos in the egg of Fundulus at .625M NaCl. Osterhout* *® found that a .375M solution of sodium chloride is fairly toxie to marine plants. Young plants of a fresh-water alga, Vaucheria sessilis, could not live at a .094M concentration of sodium chloride, and even a concentration of .0001M NaCl was found to be toxic. Magowan has shown that sodium chloride is very toxic to wheat seedlings and down to .02M the root hairs did not grow at all. The relation of yeast to plants is thus to a certain extent shown by similar physiological behavior. It may be noted here that the experiments with yeasts have been conducted on the same general principle followed by previous investi- gators with animals, plants, and bacteria. The number of yeast cells was taken as the measure of multiplication or activity and was de- termined by a microscopical count of each flask every forty-eight hours. It must be admitted that experimental errors may occur in counting, but as the numbers were taken from the average results of two sets of duplicates it does not interfere with the validity of the final result, as the range of variation between the results of these two sets of duplicates was only between 0 and 10 per cent calculated from the mean variation. SERIES V—EFFECT OF THE TOXICITY OF SALTS ON THE MICROSCOPICAL APPEARANCE OF YEAST CELLS It is generally known that all salts at certain concentrations are more or less toxic to living organisms. Yeast shows its physiological condition in relation to various salts in characteristic ways. It is evident from the above experiments that in this respect it occupies a place between the animal and the plant kingdoms. Although yeast grows normally in a physiologically balanced solution, for which grape juice answers in every way, the addition of a small amount of a favorable salt, as potassium chloride, may stimulate the growth a great deal. This is of some practical zalue to zymologists. Yeast is affected very remarkably by the toxicity of salts at dif- ferent concentrations. In the extreme concentrations it apparently 76 University of California Publications in Agricultural Sciences | Vol. 3 dissolves. This occurs in the cultures having 2.2M KCl, 1.2M, MgCL, .7™M CaCl, and .2M NaCl respectively. At lower concentrations there is a degenerated condition, various shapes occurring, as shown in figure C. Such diseased cells show a heavy black membrane, especially in the ease of CaCl, and NaCl, with transparent cell-illusions or black spots within the cells. Moreover, they vary in size. This variation in size occurs also with KCl and MgCl,, but in these cases the yeast cells are larger than with CaCl, and NaCl. In all instances, as the concentration of salt increases beyond the favorable degree of con- centration the cells become smaller and smaller until finally, in the extreme concentrations, they dissolve. Table 5 (a, b, c, d) and the curves in figure 5 (a, b) show the effect on the size of yeast cells in different salt solutions. TABLE 5a—EFFECT OF KCL ON S1zE oF YEAST CELLS (S. ellipsoideus) Av. length Av. volume Concentration and breadth of yeast cells of salt yeast cells calculated from (M.KCl) in Mu. length and breadth .00 4.7 x 4.6 77 001 5.4 x 5.4 122 OL 6.7 x 6.7 232 1 6.7 x 6.7 232 2 6.7 x 6.7 232 4 6.6 x 6.6 223 6 6.6 x 6.6 223 8 5.8 x 5.8 151 1.0 5.8 x 5.8 151 1.2 5.8 x 5.8 151 1.4 5.8 x 5.8 -151 1.6 4.9x 4.9 91 1.8 4.9 x 4.9 91 2.0 3.83.3 28 2.2 3.3 x 3.3 28 TaBLE 5b—Errect oF MGCL, oN Size or YEAST CELLS (S. ellipsoideus) Av. length Av. volume Concentration and breadth of yeast cells of salt yeast cells calculated from (M.MgCle) in Mu. length and breadth .00 4.5 x 4.5 71 .001 5.1.x 5.1 103 O01 6.2 x 6.2 185 1 6.2 x 6.2 185 2 5.0 x 5.0 98 4 5.1x5.1 103 6 5.0 x 5.0 98 8 4.9x 4.9 91 1.0 4.4 x 4.4 66 1.2 3.3 x 3.3 28 1917 | Mitra: Toxie and Antagonistic Effects of Salts on Wine Yeast 77 TABLE 5c—EFFECT OF CACL, ON Size or YEAST CELLS (S. ellipsoideus) Avy. length Av. volume Concentration and breadth of of yeast cells of salt yeast cells calculated from (M.OaCl.) in Mu. length and breadth .00 4.7 x 4.4 70 O01 : 4.6 x 4.6 75 O1 4.1 x 4.1 53 wl 3.3 X 3.3 28 2 3.3 X3.3 28 3 2.8 x 2.8 bts j 4 2.8 x 2.8 17 3) 2.8 x 2.8 17 6 2.6 x 2.6 14 - 2.6 x 2.6 14 TABLE 5d—Errect or NACL ON Size or YEAST CELLS (S. ellipsoides) Av. length Av. volume ber ei and breadth of of yeast cells of salt ot yeast cells calculated from (M.NaCl) in Mu. length and breadth .00 5.1 x 4.8 91 O01 5.0 x 4.4 75 OL 4.4 x 3.3 37 oil 4:1xX3.3 34 2 2.6 x 2.6 14 Average volume of each cell Concentration of salt Fig. 5a.—Curves showing the average relative volumes of yeast cells in various concentrations of CaCl, and MgCl,. The ordinates represent the average volume of the yeast cells and the abscissae, the concentrations of KCl and MgCl, used. The ordinate at 0 represents the volume in blank cultures. 78 University of California Publications in Agricultural Sciences [ Vol. 3 Da gi i 5 ide a ee Hf ms o 2 2 s o ~~ ° Z 3 a= ° > © 20 x he o > < peda ole Er SAS Se Concentration of salt Fig. 5b.—Curves showing the average relative sizes in volumes of yeast cells in various concentrations of KCl and MgCl,. The ordinates represent the volume of the yeast cells and the abscissae, the concentrations of the salts used. The ordinate at 0 represents the volume in blank cultures. Fig. 5c.—Appearance of yeast cells in extreme concentrations of salts. Normal yeast cells in 1, 2 and 3, diseased yeast cells from extreme concen- trations of KCl and MgCl, in 4 and 5; (white) and diseased yeast cells from extreme concentrations of CaCl, and NaCl in 6, 7 and 8 (black or shadowy) (X5000). 1917 | Mitra: Toxie and Antagonistic Effects of Salts on Wine Yeast 79 The measurements given are the average of five counts in each ease. The volumes from which the curves have been drawn in figure 5 (a, b) have been calculated, for purposes of comparison, as though the cells were cylindrical. Both from table 5 (a, b, c, d) and the curves in figure 5 (a, b) it is evident that KCl and MgCl, favor growth in size up to the most favorable concentration, beyond which the cells decrease in size until the extreme concentration is reached, where they dissolve. Both NaCl and CaCl, limit the growth even in minute concentrations, thus show- ing their extreme toxicity to yeast cells. Yeast cells seem to have remarkable resistant power. Many of them with cell wall thickened to a heavy membrane have been found in extreme concentrations. Perhaps this heavy membrane is formed to resist the osmotic pressure outside the cell. Besides some of the cells in these extreme concentrations are in normal condition and are even budding, thus showing the power of adaptability of yeast cells to new conditions. After they have become habituated to the presence of toxic salts, they grow normally and reproduce. It is probably owing to fhe adaptability of yeast to different conditions that the same yeast, S. ellipsoideus, collected from various sources, shows dis- similar physiological characters. Besides in many cases I have observed that the diseased yeast cells in extreme toxicity of KCl and MgCl, form a white membrane with normal cell contents, while those of CaCl, and NaCl form a rather dark cell membrane with shadowy cell contents. A similar case to that of Loeb*** may be cited here. In his experiments with sea urchin eggs he found two distinct phases rie of cytolysis which he terms ‘‘black cytolysis’’ and ‘‘ white eytolysis.”’ With regard to the effect of the salts on the size of the yeast cells, NaCl is the most and KCi the least toxic, while CaCl, and MgCl, stand midway. The effect is parallel with that of the multiplication of cells. An experiment was carried on with a second culture of 8. ellip- soideus collected from another source by Cruess and named no. 60. This experiment was also made in duplicate. With this yeast potas- sium chloride and magnesium chloride gave the same results as with no. 66, but NaCl and CaCl, showed a marked difference and CaCl, was the most toxic of all. 4M NaCl gave an appreciable number of yeast cells, while even .3M CaCl, stopped the growth altogether. Further, the number of yeast cells was much lower than that of yeast no. 66. Evidently yeast no. 60 was less vigorous than the other, though other- wise there was no fundamental difference between them. 80 University of California Publications in Agricultural Sciences [ Vol. 3 B. EXPERIMENTS WitH COMBINATIONS OF SALTS—ANTAGONISTIC EFFECTS The toxic effects of the single salts KCl, MgCl,, CaCl, and NaCl upon a wine yeast, NS. ellipsoideus, have been shown in the first part of this paper. The results of the study indicate that the reactions of yeast differ from those of plants, animals or bacteria. This second part of the paper gives the results of an investigation to ascertain the effects of various binary combinations of the salts named upon the Same yeast. From the four salts, six combinations of two salts each are possible. All of these were tested. Judging from analogous work of other investigators with animals, plants and bacteria, it was expected that these salts would exhibit mutually antagonistic action, i.e., that the toxicity of one salt would be reduced by the presence of another and that the total effect of two salts together would be less than the sum of their individual effects: In some eases definite antagonistic effects were found. In others antagonism was not so well defined. In a few instances there was no antagonism shown. In the discussion of results, considerable space has been given to the findings of other investigators because it was considered important to point out how the effects on other organisms compare with those on yeast. A few words on the development of the idea of antagonism in binary combinations of salts will be of value as an introduction to the data in this paper. Considerable work on the antagonistic effects of salts has been done by Ringer, Locke, Howell, Loeb, Osterhout, Overton, Ostwald, Loew, Lipman and others. That the poisonous effect of one salt is reduced by the addition of another salt has been known for a long time, especially among animal physiologists. In this matter we owe a great deal of our knowledge to Loeb, whose investigations brought forth a large number of unexpected results. It was he who first developed the theory that the valences of metallic ions have consid- erable influence on their toxie and antagonistic effects, and that mono- valent cations may be antagonized by bivalent, trivalent or tetravalent but not by monovalent cations. His results show some parallelism to the work of Linder and Picton.* This general statement does not apply in all cases to plants, animals and bacteria, experimented upon by various other investigators. Neither does it apply always to yeast. * Hober and Gordon, Beitr. zur chem. physiol., vol. 5, p. 432, 1904, cited by Osterhout.” 1917] Mitra: Towxie and Antagonistic Effects of Salts on Wine Yeast 81 The experiments with binary salts were made in the same general way as those with simple salts, but with slight modifications of tech- nique. The flasks were arranged as before in duplicate, but in com- bining the salts in different molecular concentrations the method followed differed from those of previous investigators. Of the two salts to be tested for antagonism, one was weighed from the minimum concentration to that of extreme toxicity according to the molecular concentration, and the other was weighed and added to the former in the reverse way in the corresponding flasks. The flasks containing the extreme concentration of each salt did not receive any addition of the other salt. Aside from this, the methods of in- oculation, incubation, and microscopical counting were the same as those described for the single salts. Duplicates were made in all cases and two blanks were used in each series, as checks on the growth of the yeast in the treated flasks. The same yeast, S. cllipsoideus, no. 66, was employed in these experiments as in the ones with simple salts. The results given are therefore the average of duplicate experi- ments. SERIES VI—ANTAGONISM BETWEEN MAGNESIUM CHLORIDE AND CALCIUM CHLORIDE In this series MgCl, and CaCl, were combined in various mole- cular concentrations. A series of 16 Erlenmyer flasks was arranged in dupheate with two blank cultures. First, amounts of MgCl, cor- responding to from 0M to 2.2M were weighed and put in the flasks, as was done with the single salts. The CaCl, also was weighed ac- cording to its molecular concentration and put in the same flasks in reverse order, leaving the extreme concentrations of each salt free from the addition of the other. Thus the first two flasks received .72M CaCl, without any addition of MgCl,; the second received .66M CaCl, and .001 MgCl,; the third .60M CaCl, and .01M MgCl,, and so on to the last couple, which contained only 1.2M MgCl, and no addition of CaCl,. The remaining flasks were combined in different molecular concentrations, as shown in table 1. Two blanks were taken to which no salt was added. In order to facilitate the plotting of the curves, the different combinations of salts have been indicated by letters A, B, C, D, ete. A represents the blank cultures, while the other letters represent the different molecular combinations shown in the table below: 82 University of California Publications in Agricultural Sciences | Vol. 3 TABLE 6—ANTAGONISTIC ErPFECT BETWEEN MGCL, AND CaCL, MgCl. vs. No. CaCls M. Cone, 48 hrs. 96 hrs. 144 hrs. 192 hrs. 240 hrs. A 00 x .0O 1,954,000 6,290,000 10,556,000 14,108,000 16,944,000 B Rt ch) nese: Sen Sees Oe RnR eN ee CAMNNLOE I ooaioryi SEE one Ml wee REO De oe te C St ROO Cate «= echoes) Sseanineees 226,000 452,000 dD 1 x .60 452,000 2,034,000 3,842,000 4,520,000 5,650,000 E ll x.48 8,362,000 20,860,000 23,120,000 24,730,000 26,842,000 1) 2 X.36 10,548,000 26,024,000 29,706,000 30,856,000 31,960,000 G 4 x.18 9,718,000 28,996,000 32,284,000 33,974,000 36,120,000 H 6 x .06 8,804,000 25,286,000 30,256,000 31,865,000 32,556,000 8 ~x.01 452,000 4,972,000 8,289,000 10,298,000 12,684,000 P TO. 088. 226,000 1,130,000 2,260,000 3,129,000 Se Oo oe eee. | eecaacunepipuins” | __eaxseutudekpesrin. s Usuceiiedbastedatasnel alleen nanan 36 34 32 30 28 26 24 Millions of yeast cells — A MgCls a: ie fan een en OS SSESE Ee BEE! Bei ee i \i Loves E CECT NCHA NCA RoE Concentration of salts CaCle Fig. 6—Curves of yeast growth showing antagonism between MgCl, and Cael... abscissae, the concentration of the salts in combination. represent the number of yeast cells in blank cultures. The ordinates represent the number of yeast cells in millions and the The ordinates at A Me : : (PIs 8) 1917] Mitra: Toxie and Antagonistic Lffects of Salts on Wine Yeast 83 From both table 6 and the curves in figure 6 it is evident that there is a distinct antagonism between these two salts. For example, in the experiments with simple salts MgCl, alone at .8M concentration allowed the growth of yeast cells up to only 814 millions, but in com- bination with .01M CaCl, the growth was increased up to 1214 millions, ie., 50 per cent increase. Similarly, .6M CaCl, alone allowed an increase to about one millions, and, with the addition of .01 MgCl,, an inerease to 514 millions, showing 514 times more growth. The highest number in MgCl, alone was 2614 millions at .1M, and in CaCl, alone 19 millions at .01M concentration. In this binary combination the highest number was obtained at G, the point where 4M MgCl, and 18M CaCl, were combined with a ratio of about 2:1. For purposes of comparison let us now consider the results obtained in similar experiments with these four salts on plants, animals, and bacteria. (a) Plants—Kearney and Cameron® found a distinct antagonism between Mg and Ca ions for higher plants. In their experiments with leguminous plants Lupinus albus and Medicago sativa they found that, for a combination of these two salts, the plants show about five times as much tolerance as for the salts separately. The plants also dis- played a remarkable degree of tolerance when MgSO, was used in- stead of MgCl,, thus showing in addition the relative difference be- tween different anions of fhe same salt. Loew and his pupils,'® ** in their experiments with lower plants (Spirogyra), have found a strong antagonism between Mg and Ca ions. (b) Animals.—Loeb? with sea urchins (blastulae and gastrulae) found that a mixture of MgCl, (10/8n) and CaCl, (10/8n) will allow them to swim for about forty-eight hours, while each of the salts singly at the same concentration is extremely poisonous and kills the animals. The same investigator’? working with a jellyfish (Polyor- chis) has shown that the addition of a small quantity of CaCl, to a mixture of NaCl and MgCl, favors the normal, rhythmical contrac- tions, while MgCl, alone stops them altogether. Contrary to the above results, Loeb’ in his experiments with frogs has found that a combination of Mg and Ca ions completely inhibits the rhythmical muscular contractions. This has been corroborated by Anne Moore,‘ in her experiments with the contraction of the lymph hearts of frogs. Lillie’ has found that the ciliary movement of the larvae of 84 University of California Publications in Agricultural Sciences | Vol. 3 Arenicola goes on normally for a time in a mixture of MgCl, and CaCl, with the ratio of 4:1 at 10/8n concentration, though either of the two salts used alone would stop it entirely. Matthews,'? in his work with the development of embryos in the eggs of Fundulus, found a distinct antagonism between Mg and Ca. Meltzer and Auer*! have shown with rabbits and a monkey that the poisonous action of MgCl, in subcutaneous injection is similarly diminished by the injection of CaCl,. They found also a strong antagonism between the nitrates, acetates and sulfates of these two salts respectively. (c) Bacteria—Lipman,** ** with a soil bacterium, Bacillus sub- tilis, found little or no antagonism between the two salts, but, on the contrary, the addition of one salt to the other was found to be more toxic than either of the two salts used alone. All of the above mentioned experiments, except those of the three eases of Lipman, Loeb, and Anne Moore, are in agreement with the antagonistic effects between Mg and Ca ions that occur with yeast. In addition, it may be noted here that the antagonistic effect between MgCl, and CaCl, with yeast has been found to be the strongest of all the combinations. This corroborates the opinion advanced by Loew that there is a strong antagonism between calcium and magnesium both with plants and animals.'® SERIES VII—ANTAGONISM BETWEEN POTASSIUM CHLORIDE AND CALCIUM CHLORIDE In this series the experiments were carried on in the same way as with MgCl, and CaCl,. Table 7 and the curves in figure 7 show there is a distinct antagonism between the two salts. In this case marked antagonism was found on the side of CaCl,, but little or none on the side of KCl. For example, the combination of .001M KCl with .66M CaCl, allowed the yeast to grow up to 61% millions, while in CaCl, at .6 alone the yeast was found to increase only up to about one million. Thus there was 614 times as much growth where the KCl was present. But, on the other hand, the combination of .001M CaCl, to 2.0M KCI did not accelerate the growth. This unexpected result may be accounted for by the fact that the higher concentrations of KCl being very high in comparison to the small concentrations of CaCl, the latter was not sufficient to reduce the toxicity of the KCl at such a high concentration. It is also very probable that a concen- 1917} Mitra: Toxie and Antagonistic Effects of Salts on Wine Yeast 85 tration of 2.0M KCl exerts a strong osmotie effect and that the toxicity is due to osmotic influences rather than to the usual toxicity of the ion itself. If this were true we would expect little antagonism from other salts. Loeb’? in his experiments with a jellyfish (Gonionemus) met with a similar difficulty. In this ease the KCl concentration was so high that a small coneentration of NaCl did not remove the toxicity, and so the combination inhibited the contraction of the animal, while the same concentrations used in the ease of another kind of fish, Mundulus, allowed the development of embryos in the eggs. He has pointed out the fact that in the embryos of Pundulus the solutions in which cleay- age proceeds normally interferes seriously with the heartbeat of Coni- onemus, if the proportion of KCl exceeds a certain limit. In this instance we find proof of the fact that in the same organism eell- division and muscular contractility are influenced by entirely different combinations of ions, and therefore these vital activities must depend on widely different chemical constitutions. However, the highest growth in the case of yeast was obtained at H, where .6M KCl and .36M CaCl, have been combined, a ratio of about 2:1. In the case of KCl alone the highest growth was obtained at .2M concentration, allowing growth up to 3014 millions per ¢c.e. CaCl, allowed growth up to 19 millions at .01M concentration. TABLE 7—ANTAGONISTIC EFFECTS BETWEEN KCL AND CACr, KOl_ vs. 48 hrs. 144 hrs. No. CaClo M. Conc. 96 hrs. 192 hrs. 240 hrs. A .00 x.00 2,101,000 8,589,000 13,908,000 16,896,000 17,520,000 B gad ay i late OID thi NGI gh Ne ie Re RRA nk ete: Pie Ors SEE ad | eee Ue esGG |) he Se 226,000 2,034,000 3,985,000 6,722,000 D 4.01 x.60 452,000 4,972,000 13,315,000 18,604,000 22,720,000 E 1 x.54 4,020,000 10,328,000 20,245,000 23,266,000 25,120,000 F 2 x.48 5,558,000 12,840,000 22,190,000 26,880,000 29,380,000 G 4 x.42 3,034,000 12,840,000 26,852,000 19,126,000 32,285,000 H 6 x.36 1,017,000 8,398,000 13,645,000 28,904,000 34,500,000 I 8 xX.30 226,000 4,256,000 10,250,000 14,966,000 18,732,000 AGE 2 Bie 2” ree ai 2.965,000 6,126,000 9,551,000 16,159,000 lage | Te ee | a ee 1,130,000 3,986,000 ~—-5,410,000 ~—7,119,000 L BAe ee 452,000 2,550,000 2,712,000 4,438,000 es Wb RRS a | ae eee as RS ee eer 904,000 1,130,000 3,906,000 N fil SURG 8 RE Ieee, 2 Ros Wee ae pene pea ne 452,000 904,000 2,652,000 Be OR FSCS yc Sh aalaale a wekievccs mp “meet 226,000 1,130,000 i Bee ae | ocean | CO aeeGMRRESRSTCE . aimciannereytndaee ) epee 86 University of California Publications in Agricultural Sciences | Vol. 3 A a PCY ca Zoe OE BES HBP a a FO, ND ECC Acre py ye is | | AN COPECO Millions of yeast cells (ae See ML | IAT NAL Te oo KCl Concentration of salts CaCle Fig. 7—Curves of yeast growth showing antagonism between KCl and CaCl. The ordinates represent the number of yeast cells in millions and the abscissae, the concentration of salts in combination. The ordinate at A represents the number of yeast cells in blank cultures. For comparison with these results, a number of cases dealing with plants, animals and bacteria may be cited below: (a) Plants——Osterhout”? has shown that for higher plants a com- bination of 100 ¢.c. KCl and 5 ¢.e. CaCl, at the concentration of .12M is best suited for the highest development of roots. Benecke’® has shown that for lower plants (Spirogyra) the harmful effect of the K ion is very distinctly antagonized by the addition of the Ca ion at a certain definite concentration. 1917] Mitra: Toxic and Antagonistic Effects of Salts on Wine Yeast 87 (b) Animals.—In regard to the development of embryos in the eggs of Fundulus, Loeb’ has met with a marked antagonism between the two salts, using 75 ¢.c. of KCl (5/8n) and 25 ¢.e. of CaCl, (10/8n). This combination allowed the development of a number of embryos, while in the same concentration of KCl alone no development was shown. He also obtained a similar result with the muscular contrac- tion of a jellyfish (Polyorchis),’ thus showing an antagonistic effect between the two salts. The same investigator* in his experiments with the hydromedusa Gonionemus has shown that the combination of K ion (5/8n) and Ca ion (10/8n) is poisonous to the animals. Anne Moore’ obtained a similar result in her experiments on the contraction of the lymph heart of frogs. Meltzer and Auer*! have shown that with rabbits and a monkey in subcutaneous injection there is a limited antagonism between the two salts. Matthews" with Fundulus met with a similar result. He found that at the dilution of M/1600 CaCl, to 6/8n KCl the develop- ment of embryos in the eggs was found to be the best. Lillie’ found that with the larvae of Arenicola the ciliary activity went on when he used 97.5 e.e. CaCl, (10/8n) and 2.5 ¢.e. KCl (5/8n), showing an antagonism between the two salts. (c) Bacteria.—Lipman*® has shown that for Bacillus subtilis the highest production of ammonia is found at the point where 100 c.c. KCl and 5 «.e. CaCl, at the concentration of .35M is used, thus showing a distinct antagonism between the two salts. His work has a striking similarity to that of Osterhout on wheat. Summarizing the antagonism between K and Ca, it may be said that the toxicity of high concentrations of Ca is greatly reduced by the presence of K, but that the toxicity of high concentrations of K is not appreciably reduced by small amounts of Ca. The optimum ratio of KCl to CaCl, was about 2:1 for yeast. SERIES VIII—ANTAGONISM BETWEEN MAGNESIUM CHLORIDE AND SODIUM CHLORIDE The experiments in this series were carried on in the same way as the others. Both table 8 and the curves in figure 8 show that there is a distinct antagonism between these two salts. The highest growth in this case was found at G, the point where .4M MgCl, and .06M NaCl were combined, a ratio of about 6:1. As already shown, when used singly MgCl, allows the highest growth at .1M, 1.e., 2614 millions, 338 University of California Publications in Agricultural Sciences TABLE 8—ANTAGONISTIC EFFECTS BETWEEN MGCL, AND NACL MgCl. vs. No. NaCl M. Cone 48 hrs. 96 hrs. 144 hrs. A 00 x .0U 3,100,000 7,644,000 13,686,000 B J.) MR ah Bue ere te: s 2b aay Bova e Peete ance. eke Ste te C SCS 36 TD eecceeee | Oacccceenaes . gemetaabcuaien D Ol x .160 226,000 452,000 452,000 E » Pee gk 3,250,000 6,212,000 11,201,000 F 2 x .096 5,424,000 10,396,000 16,368,000 G 4 x .064 2,260,000 12,656,000 20,696,000 H 6 x.032 1,582,000 8,684,000 14,956,000 I SOP 904,000 3,102,000 6,358,000 J OQ “30 DOL. 904,000 1,872,000 |e ys iis Sie sya ee mene a Baie Se een SNe oy 30 2c Se a BP else HGR “ CONE 192 hrs. 15,203,000 226,000 678,000 14,258,000 21,690,000 25,882,000 17,009,000 10,605,000 3,896,000 : ‘ bane! (mia e a S 18 3S 2 16 : PCN 2 14 = S 12 10 8 6 ; rah SEN 2 van an ae A G H J K MgCle Concentration of salts NaCl Fig. 8.—Curves of yeast growth showing antagonism between MgCl, and NaCl. The ordinates represent the number of yeast cells in millions and the The ordinate at A repre- abscissae, the concentration of salts in combination. sents the number of yeast cells in blank cultures. [ Vol. 3 240 hrs. 17,009,000 226,000 1,130,000 17,255,000 25,793,000 28,890,000 21,583,000 15,430,000 4,276,000 1917 | Mitra: Toxic and Antagonistic Effects of Salts on Wine Yeast 89 and NaCl at .001M, 1.e., 18 millions. But in combination the two salts permit the highest growth of 29 millions per ¢.c. at .4M and .06M respectively. The antagonism between these two salts in the case of yeast is found very distinctly at both ends of the curves. For example, .1M NaCl alone shows a growth of seareely more than one million, while in combination with .1M MgCl, it shows over 17 millions, or 17 times as much. On the other hand, .8M MgCl, alone allowed a growth of about 81% millions, while in combination with .01M NaCl the growth was increased to about 1514 millions, or about twice as much. In comparison with these results, a number of cases dealing with the effects of combinations of MgCl, and NaCl on plants, animals and bacteria are cited below. (a) Plants——Osterhout® found a distinct antagonism between the two salts with the growth of a fungus (Botrytis cinerea). He found that 15.M NaCl alone was very toxic, but that when this concentration of NaCl was combined with .4 M MgCl, the toxicity was much re- duced. He also found with wheat that neither NaCl nor MgCl, at 12M alone allowed root development, but in a combination in the proportion of 100 ¢.c. NaCl to 75 ¢.c. MgCl, the root developed very well. The same investigator obtained a negative result with green algae.?° Kearney and Cameron® with Lupinus albus and Medicago sativa have shown that the addition of MgCl, to NaCl raised the tolerance of these plants to the latter 3-10 times. (b) Animals.—Loeb” with Fundulus has found that in a mixture of 98 ec. 5/8n NaCl and 2 «ec. 10/8n MgCl, all the eggs develop embryos, while the same salts alone at the same concentration are extremely toxic. Even an equal proportion of the two salts in the same concentration allowed about 75 per cent of the embryos to de- velop. He also found a similar antagonism with a sea urchin (Ar- bacia) and a jellyfish (Polyorchis). Lillie® found that with the larvae of Arenicola the ciliary move- ment continued for a time when he added 10 ec. MgCl, (10/8n) to 90 ec. NaCl (5/8n), while the same concentrations of NaCl alone would stop it immediately. Matthews with Fundulus found an an- tagonism between the two salts. Ostwald,!? however, with fresh-water Grammarus obtained con- trary results. In this case a combination of the two salts was found 90 University of California Publications in Agricultural Sciences [ Vol. 3 to be more toxie than NaCl alone, isotonic with sea water (2.7 per cent NaCl in sea water or about .4M NaCl). (c) Bacteria—Lipman** with Bacillus subtilis obtained a result similar to that of Osterhout. A mixture of the same concentration of MgCl, and NaCl (.35M) in the ratios of 10:1 gave the maximum production of ammonia. ‘To summarize the results of these experiments, it may be said that there is a distinct antagonism between MgCl, and NaCl, which is evident on both ends of the curves in figure 8. In this case the yeast agrees with the observations on plants, animals and bacteria except in the two instances cited above in regard to fresh-water Grammarus and green algae. SERIES IX—ANTAGONISM BETWEEN POTASSIUM CHLORIDE AND SODIUM CHLORIDE In this series the flasks were arranged as before. It has been pointed out by Loeb that two salts with ions of like valence, especially in the case of monovalent ions, do not antagonize the toxicity of each other, but rather show a moderately increased toxicity when com- bined. This is evident with yeast, as is shown by table 9 and the curves in figure 9. The highest growth in this ease was found at F, where .2M KCl and .12M NaCl have been combined, having a ratio of about 2:1. KCl alone at .2M concentration allows the growth about 114 times that found in this combination. Thus the antag- onism of NaCl for KCl is found to be negative. But, on the other hand, there is a distinct antagonism of KCl for NaCl. For example, NaCl alone at .17M concentration hardly allowed any growth, but in combination with .01M KCl the growth was accelerated up to about 15 millions, thus showing a distinct antagonism. The reason of this unexpected negative result on the side of KCl is perhaps the same that I have suggested in the ease of KCl and CaCl, in Series IT. For comparison with these results, a number of cases dealing with plants, animals and bacteria are cited below: (a) Plants—Osterhout?? with wheat (Early Genésee) has found a sight antagonism between K and Na ions. But in his work" on a green alga he obtained a negative result using 3/8M concentration of two salts in combination. (b) Animals—Loeb* with Fundulus found a shght antagonism between the K and the Na ion in relation to the development of em- 1917] Mitra: TABLE 9—ANTAGONISTIC KCl vs. No. NaCl M. Cone A 0 x .00 B .00 x.208 C .00O1 x .192 D Us Kahlo BE tL «160 F 2 X.144 t 4 x<.128 H 6» |x%..242 I 8 x.096 Po! (Ae “3 080 K 1.2 ~x.064 my - 14-- x.046 M 1.6 x .032 No 2.8% O10 in 0? M001 P) > 2. <200 = = = = o no rx a oo Millions of yeast cells oo 48 hrs. 1,954,000 2,678,000 5,424,000 2,938,000 2,260,000 678,000 226,000 96 hrs. 6,290,000 226,000 7,184,000 10,786,000 12,339,000 7,838,000 6,780,000 5,650,000 4,156,000 2,906,000 1,130,000 452,000 % Sig a Sees Jf ON Hele SAV UNG ace 144 hrs. 10,556,000 1,808,000 9,256,000 14,690,000 15,942,000 11,526,000 8,678,000 7,205,000 5,882,000 4,900,000 3,390,000 1,130,000 226,000 Concentration of salts Toxic and Antagonistic Effects of Salts on Wine Yeast EFFECTS BETWEEN KCL AND NACL 192 hrs. 14,108,000 6,780,000 12,176,000 16,922,000 18,206,000 15,830,000 12,687,000 10,256,000 8,120,000 7,750,000 4,968,000 2,260,000 1,130,000 452,000 91 240 hrs. 16,944,000 7,888,000 14,952,000 18,566,000 21,250,000 17,248,000 13,266,000 12,984,000 9,886,000 8,205,000 6,983,000 4,452,000 2,960,000 904,000 Fig. 9—Curves of yeast growth showing antagonism between KCl and Nacl. abscissae, the concentration of salts in combination. sents the number of cells in blank cultures. The ordinates represent the number of yeast cells in millions and the The ordinate at A repre- 92 University of California Publications in Agricultural Sciences | Vol. 3 bryos in the eggs. He also found a similar result with sea-urchins, Hydromedusa gonionemus, and a jellyfish, Polyorchis. Lillie’ found that with the larvae of Arenicola the cilary move- ment goes on in a solution containing 20 parts of NaCl (5/8n) and 8 parts of KCl (5/8n), while each salt used alone stops the movement altogether. Ostwald"? with fresh-water Gammarus has shown that there is a distinct antagonism between K and Na ions in regard to the duration of life of that animal. Matthews": has found that it takes twice as much KCl to neutralize the toxicity of NaCl in the case of the devel- opment of embryos in the eggs of Fundulus. This is rather similar to the case of yeast, where it takes .2M KCl to neutralize the toxicity of .14M NaCl to allow the highest growth. (c) Bacteria—Lipman* with Bacillus subtilis has found that none of the combinations of these two salts gives as favorable conditions for growth as is found with each salt alone at the same concentration, thus showing non-antagonism between the two salts. To summarize the results in this experiment, it may be said that with yeast, like valences prevent the antagonistic effects, contrary to what was found by Lipman with soil bacteria, but in accordance with the results of Osterhout with wheat, Loeb with FPundulus, and other investigators with other organisms. The yeast agrees in this case with all the above-mentioned cases except with that of green algae tested by Osterhout and that of Bacillus subtilis by Lipman. SERIES X—ANTAGONISM BETWEEN POTASSIUM CHLORIDE AND MAGNESIUM CHLORIDE The experiments in this series were conducted like the others. The highest growth in this case was found at H, the point where .6M KCl and .5M MgCl, were combined in a ratio of about 1:1. In the case of simple salts KCl alone at .2M concentration allowed the highest growth up to about 3014 millions and MgCl, at .1M about 2614 millions. KCl alone at .6M and MgCl, at .5M permitted the growth of yeast more than is found in this combination at H. But this indicates a mild antagonism, because the toxic effect was less than the sum of the separate toxic effects of the two salts used alone. Distinct antag- onism to the effects of MgCl, is shown by KCl, but not the converse. For example, .8M MgCl, alone allows the yeast to grow only to 8 millions, while in the combination with .1M KCl the growth has 1917} Mitra: Toxie and Antagonistic Effects of Salts on Wine Yeast 93 been increased to 1114 millions. On the other hand, the smaller con- centrations of MgCl, with higher concentrations of KCl did not show any antagonism. The reason for this unexpected result 1s perhaps that previously mentioned in the case of KCl vs. CaCl, in Series VII. TABLE 10—ANTAGONISTIC EFFECTS BETWEEN KCL AND MGCL, KCl vs. No. MgCle M. Conc. 48 hrs. 96 hrs. 144 hrs. 192 hrs. 240 hrs. A 00 x .00 2,356,000 ~—- 9,701,000 += 12,170,000 + 14,890,000 ‘17,526,000 B POEM are, ce tee de en ee Ae ke ee A) ewe niccatananeniiye * | wcemensanenapaibe Bat amegey i 2a FS 226,000 1,130,000 = 2,260,000 ~—-3,845,000 Bi; 208 x49 226,000 1,356,000 6,780,000 10,070,000 11,560,000 E 1 x .8 1,130,000 6,780,000 —- 7,408,000 += 10,975,000 12,180,000 F 2 x .7 1,356,000 7,458,000 11,578,000 13,449,000 14,328,000 G 4 x 6 2,486,000 4,838,000 7,006,000 14,690,000 15,500,000 BY oe eS 904,000 3,816,000 5,296,000 12,850,000 16,280,000 I a xa 678,000 2,612,000 4,852,000 8,286,000 9,856,000 Bt ele 8 452,000 2,260,000 3,706,000 5,463,000 —-5,902,000 Kk 18° x 2 452,000 2,040,000 3,295,000 4,895,000 —+5,240,000 as cK! 678,000 1,926,000 2,940,000 3,656,000 —-4,864,000 M 16 x 05 226,000 904,000 3,050,000 3,006,000 4,628,000 Ree OOS | eg 226,000 2,260,000 2,990,000 3,862,000 MRO MASE CHIT Why cs ize” Sy Ge ede 2,226,000 1,130,000 ge eee ee a es Emenee oth ee eT eee ay We ee ae a a Ba eo ae mn a | aki iM ee oro NCOP We NE NOSSO SERRE NZ ESN J K L M N O P Millions of veast cells ~ KCl Concentration of salts MgCl. Fig. 10.—Curves of yeast growth showing antagonism between KCl and MgCl,. The ordinates represent the number of yeast cells in millions and the abscissae, the concentration of salts in combination. The ordinate at A repre- sents the number of cells in blank cultures. v4 University of California Publications in Agricultural Sciences [ Vol. 3 For comparison with these results a few cases may be cited as follows: (a) Plants——Osterhout*® with wheat (Early Genésee) has shown that the root develops better in a solution having 100 ¢.c. KCl and 7.5 ee. MgCl, at .12M concentration than in KCl alone. He also found with a marine alga,*? Enteromorpha hopkirku, that both salts are polsonous when used alone, but a combination in the proportion of 100 ¢.c. MgCl, and 40 ¢.c. KCl allows considerable growth. He found a similar antagonism with liverworts.” (b) Animals.—Matthews" found with Fundulus that in order to permit development of the embryos in the eggs at the concentration of 33/48n KCl at least about M/160 MgCl, is needed. He also found that a solution of 6/8n KCl requires M/80 MgCl, to give the best result. (c) Bacterta.—Lillie® has shown that a combination of 10/8n MgCl, and 5/8n KCl allows the ciliary activity of the larvae of Arenicola, which is stopped when one salt is used alone. To summarize, it may be said that a distinct antagonism was found by Osterhout with higher and lower plants and by Matthews and Lilhe with animals. With yeast a slight antagonism is found, which is shown on the curves in figure 10 on the side of MgCl.. SERIES XI—ANTAGONISM BETWEEN CALCIUM CHLORIDE AND SODIUM CHLORIDE The plan of this series of experiments was the same of that of the others. In the ease of simple salts both CaCl, and NaCl were found to be very toxic, and it may be owing to this extreme toxicity that the combinations of the two salts showed increased toxicity. Both from table 11 and the curves in figure 11 it is evident that this toxicity is very marked. The highest growth was found at E, where .1M CaCl, and .12M NaCl have been combined in the ratio of 1:1. But even here the number of yeast cells went up only to 8 millions, which is far below the highest growth obtained when the salts were used alone. However, CaCl, shows slight antagonism to the toxicity of NaCl, for example, .1M NaCl, alone allows the growth only to one million, while in combination with .1M CaCl it reached more than 8 millions. On the whole, however, both from the table and the curves it is evident that the combinations of the two salts are more toxic than the single salts. 1917 | Mitra: Towic and Antagonistic Effects of Salts on Wine Yeast 9 TABLE 11—ANTAGONISTIC EFFECTS BETWEEN CACL, AND NACL CaCle vs. No. NaCl M. Cone 48 hrs. 96 hrs. 144 hrs. 192 hrs. 240 hrs. A 00 x 00 2,356,000 9,381,000 12,172,000 14,890,000 17,108,000 B AS 0 OR a er ee ee ool vanarakh ! erductsascsduvensp ||” cuwsdyweandosoyses CG .001x.18 226,000 226,000 226,000 904,000 1,130,000 D .01 x.16 226,000 1,582,000 3,390,000 = 4,682,000 ~—-55,842,000 Moet 13 226,000 1,808,000 —- 5,650,000 ~—- 7,910,000 8,290,000 a SSS Rees vo 1,356,000 3,482,000 = 4,520,000 ~—- 7,042,000 re Bee OG) Soca 226,000 1,130,000 5,650,000 6,820,000 PH 3% .08.> > Anneka 226,000 3,390,000 4,526,000 I SPE cco EN Ad ie eee aL GREE (0. bidpiancdaeniein 452,000 J ee INES 9 = Senet it 9 rs ee RE eects | \GSeccaymaninninaedc’| 9 “debpatuninosedaies cp WO: UG >: SARI a AR cue tll SB PAS sali GEA 8 «y's, SCR ee Millions of yeast cells | Zia cele es eae ger A B C D E FE G CaCle Fig. 11—Curves of yeast growth showing effects of NaCl on CaCl,. The ordinates represent the number of yeast cells in millions and the abscissae, the concentration of salts in combination. The ordinate at A represents the number of yeast cells in blank cultures. For comparison with other organisms the following cases are cited: (a) Plants —Osterhout® with wheat found a distinct antagonism between the two salts. He obtained a similar result with green algae in which he used 100 e.c. NaCl and 10 ec. CaCl, at the concentration of 3/8M. Kearney and Cameron,’ with leguminous plants, found that a combination of the two salts increased the tolerance of the plants for CaCl, three times. 96 University of California Publications in Agricultural Sciences | Vol. 3 (b) Animals——Loeb'! with Hydromedusa Gonionemus has shown that a combination of 10/8n CaCl, and 5/8n NaCl is harmless to animals. He also found a distinct antagonism with a_ jellyfish, Polyorchis, using 50 ¢.c. NaCl and 1 ¢.¢. CaCl,, which allowed the animal to swim, while NaCl alone was poisonous. The same investi- gator found a distinct antagonism between these two salts working with the development of embryos in the eggs of the Fundulus. Anne Moore’ with the contraction of the lymph heart of frogs and Lingle* with that of the turtle’s heart noted similar phenomena, thus corrob- orating the work of Loeb. Lillie’ working with the larvae of Arenicola has found a distinct antagonism between Ca and Na ions. MacCallum'* found the same with his experiments on cathartics. Meltzer and Auer?! found a distinctly antagonistic effect with animals in subeutaneous injections. Ostwald'* wth fresh-water Gram- marus found a strong antagonism between NaCl and CaCl, in regard to the duration of life of that animal. Finally, Matthews"? has shown that there is a slight antagonism between the two salts in the develop- ment of embryos in the eggs of Fundulus. (c) Bacteria—Lipman* with Bacillus subtilis found a marked lack of antagonism between the two salts. In his case any combi- nation of the two salts at .35M concentration was found to be more poisonous than a single salt. All these experiments except that of Lipman show that there is antagonism between CaCl, and NaCl. The yeast agrees very mark- edly with Bacillus subtilis in showing little or no antagonism between the two salts, CaCl, and NaCl,. 1917 } Mitra: Toxic and Antagonistic Effects of Salts on Wine Yeast 97 RELATIVE ANTAGONISMS OF VARIOUS COMBINATIONS the are Table 12 is intended to show the relative antagonisms of various combinations. The data used in constructing the table the final counts in each flask. The average of the counts in all the check flasks is taken as the basis from which to estimate the influence of the various salts and of their combinations. The caleulation is made as follows: Yeast growth in check flasks = 17 (millions). Yeast growth with single salt no. 1—=a. Yeast growth with single salt no. 2=b. Yeast growth with combination no, 1 + 2=ce. Toxicity — expected = (17 — a) + (17— Db). Toxicity — observed = 17 —c. Antagonism of combinations* = (17 —a) + (17 — b) —.(17 — ¢). _, Antagonism = 17 + c—a—bD. TABLE 12—RANGE OF ANTAGONISM OF THE BINARY COMBINATIONS CALCULATED From THE LAST MICROSCOPICAL CoUNT* No. MgCle X CaCle KCl X CaCle MgCle X NaCl KCl X NaCl KCl X MgCle CaCle X NaCl At 17,000,000 17,000,000 17,000,000 17,000,000 17,000,000 17,000,000 oto Ue Ue Rs ERR URI eee fer 1 > A cD Ac ae es 2000000, La cele 5,000,000 4,000,000 na... D 4,000,000 17,000,000 —.....20.... 8,000,000 10,000,000 4,000,000 E 27,000,000 17,000,000 8,000,000 9,000,000 ~— 9,000,000 +~—- 7,000,000 F 24,000,000 + ~—18,000,000 25,000,000 8,000,000 + ~=—- 7,000,000 ~—- 7,000,000 G 20,000,000 30,000,000 27,000,000 + ~—- 7,000,000 +~=—16,000,000 6,000,000 H 21,000,000 31,000,000 + 14,000,000 7,000,000 9,000,000 ............... I 7,000,000 8,000,000 11,000,000 10,000,000 22. 2. J 21,000,000 °1,000:000 © “Zion. pod Ft0geoDI0 2. . het Ethan a Rai nA TN ac Lit 2) em SE a. Oke Re. eho ae Be, ee Oe Se A Re. os eee ee a SE RS PS ae: ware lie Re SE) Ss ae oe 1s ERG Ee any Ad APE ELE 5) oS rn ee ees he ee ake et ie ee eee a + Millions on average. * These results are shown graphically by the curves in figure 12. * This defines ‘antagonism’ as the difference between the expected and the observed toxicity. The curves have been drawn to show the antagonism of the com- binations and not the actual growth of the yeast as has been shown in the previous curves. 98 University of California Publications in Agricultural Sciences Vol. 3 y g 32 30 KCI & CaCl MgCle, & Cal 28 mame Mell. < NaCl weeee eee EC) St Maou 26 KCl &* NaCl CaCl. x NaCl 24 Millions of yeast cells = ACR PAE VAALLLAALEL LLL VASE TTT Combinations of Salts A Fig. 12.—Curves showing range of antagonism of binary combinations of salts. The ordinates represent the average number of yeast cells in millions and the abscissae, the concentration of salts in combinations. The ordinate at A represents the average number of cells in blank cultures. — i 1917] Mitra: Toxie and Antagonistic Effects of Salts on Wine Yeast 99 SUMMARY PART A—TOXIC EFFECTS OF SINGLE SALTS 1. Each of the four single salts—KCl, MgCl,, CaCl,, and NaCl— is more or less toxie to the yeast, Saccharomyces ellipsoideus, at certain concentration. KCl is the least toxie and NaCl the most for the yeast (no. 66) used. 2. The lower concentrations of each salt stimulate the growth of yeast. The highest number of yeast cells in microscopical count was found at .2M KCl, .1M MgCl, .01M CaCl,, and .001M NaCl, KCl being the most favorable and NaCl the least. Beyond the favorable concentrations the various salts are toxic to yeast. 3. The concentrations of salts that inhibited the growth of yeast cells were found at 2.2M KCl, 1.2M MgCl, .7M CaCl,, and .2M NaCl. 4. The results of the experiments are quite different from those found with either bacteria, the higher plants or animals. The yeast stands in this respect midway between plants and animals and swings to either direction according to the environment. 5. The salts used had a marked effect on the size and appearance of the yeast. Taking decrease in size as a criterion, the salts affected the yeast toxically in the same relative ways as indicated by the rate of multiplication of the cells. PART B—ANTAGONISTIC EFFECTS OF COMBINATIONS OF SALTS 1. As shown by growth of yeast, the variation in antagonism be- tween the four single salts in all possible combinations may be ar- ranged in order as follows: . MgCl, vs. CaCl, (most) . KCl vs. CaCl, . MgCl, vs. NaCl . KCl vs. NaCl . KCl vs. MgCl, . CaCl, vs. NaCl (least) aor WD 2. The effect of binary salts with yeast, whether positively or nega- tively antagonistic in comparison to animals, plants and soil bacteria, may be tabulated as follows: 100 University of California Publications in Agricultural Sciences [ Vol. 3 Binary salts Yeast Animals Plants Soil bacteria 1. MgCl, vs, CaCl, of + and — -f- —— 2. KCl vs, CaCl + and — + and— + + 3. MgCl, vs. NaCl } + and — + and — + 4. KCl vs. NaCl + and — + + and — + and — 5. KCl vs. MgCl, + and— + ee DM freee ie ok 6. CaCl, vs. NaCl + and — of} + —_ + = strong antagonism. + = mild antagonism. —- = strong increase of toxicity. — = slight increase of toxicity. 3. In regard to the effects of valences of ions the following results have been obtained with yeast : (a) That divalent ions may antagonize monovalent ions is evident from the combinations of MgCl, vs. NaCl and CaCl, vs. NaCl. Ngative results were ob- tained from the combinations of KCl vs. CaCl, and KCl vs. MgC). (b) That a divalent ion may be antagonized by a divalent ion is evident from the combination of MgCl, vs. CaCl.. (c) That monovalent ions may antagonize divalent ions is shown in the combinations of KCl vs. CaCl.; MgCl, vs. NaCl and KCl vs. MgCl.. (d) That a monovalent ion may antagonize a monovalent ion, though not very markedly, has been found in the combination of KCl vs. NaCl. 1917 | Mitra: Toxic and Antagonistic Effects of Salts on Wine Yeast 101 LITERATURE CITED PART A—TOXIC EFFECTS OF SINGLE SALTS 11900. Loeb, J. On the different effects of ions upon myogenic and neuro- genic rhythmical contractions and upon embryonic and muscular tissues, Am. Jour. Physiol., vol. 3, pp. 883-396. 21900.—On the ion proteid compounds and their réle in the mechanics of life phenomena, Am. Jour. Phyiol., vol. 3, pp. 327-338. 8 1902.—Studies on the physiological effects of the valency and possibly the electrical charges on ions, Am. Jour. Physiol., vol. 6, pp. 411-433. 41905. Ostwald, W. Studies on the toxicity of sea-water for fresh-water animals: (Grammarus Pulex De Geer), Publ. Univ. Calif. Physiol., vol. 2, pp. 163-191. ; 51905. Loeb, J. On fertilization, artificial parthenogenesis and Cytolysis of the sea urchin egg, Univ. Calif. Publ. Physiol., vol. 2, no. 8, pp. 73-81. 61906. Osterhout, W. J. V. On the importance of physiologically balanced solutions for plants, Bot. Gaz., vol. 42, pp. 127-134. 7 1907.—On the importance of physiologically balanced solutions for plants, Bot. Gaz., vol. 44, pp. 259-272. 8 1909.—On the similarity of behavior of sodium and potassium, Bot. Gaz., vol. 48, pp. 98-106. 9 1906.—Extreme toxicity of NaCl and its prevention by other salts, Jour. Biol. Chem., vol. 1, pp. 363-369. 101908. Magowan, F. W. The Toxic Effects of certain common salts of the soil on plants, Bot. Gaz., vol. 45, pp. 45-49. 111909. Lipman, C. B. Toxic and antagonistic effects of salts as related to ammonification by Bacillus subtilis, Bot. Gaz., vol. 48, pp. 105-125. 121912. Bokurny, T. The effects produced by metallic salts on yeasts and other fungi, Centrbl. Bakt., 2. Abt. Bd. 35, no. 6-10, pp. 118-197. 131913. Loeb, J. Artificial Parthenogenesis and Fertilization, pp. 173-190. PART B—ANTAGONISTIC EFFECTS OF COMBINATIONS OF SALTS 11900. Loeb, J. On the different effects of ions, Am. Jour. Physiol., vol. 3, p. 383. Complete entry to be found in Part A. 21900. Loeb, J. On the ion proteid compounds, Am. Jour. Physiol., vol. 3, p. 327. Complete title in Part A. 31900. Loeb, J. Ueber die Bedeutung der Ca and K ionen fiir die Herzthat- igkeit, Pfluger’s Archiv, vol. 80, pp. 229-232. 41900. Lingle, D. J. In action of certain ions, Am. Jour. Physiol., vol. 4, p. 265-282. 51900. Osterhout, W. J. V. Die Schiitzwirkung des Natriums fiir Pflanzen, Jahrb. Wiss. Bot., vol. 46, p. 121-136. 61901. Lillie, R. On the differences in the effects of, ete., Am. Jour. Physiol., vol. 5, pp. 56-85. 71901. Moore, A. Effects of ions on the contraction of, etc., Am. Jour. Physiol., vol. 5, pp. 86-94. 81902. Kearney & Cameron. Some mutual relations between alkali soils and vegetation, U. 8. Dept. Agr. Report, no. 71. 91902. Loeb, J. Studies on the physiological effects, Am. Jour. Physiol., vol. 6, p. 411. Complete title in Part A. 101903. Loew, O. The physiological réle of mineral- nutrients in plants, U. S. Dept. Agr. B. P. I., Bull. 45. 111904. Matthews, A. P. Toxie and antagonistic effects of salts, Jour. Am. Physiol., vol. 12, pp. 419-443. 121905. Loeb, J. Studies in general physiology, vol. 2, pp. 518, 572, 584. 131905. Ostwald, W. Studies on the toxicity of sea-water, Publ. Univ. Calif. Physiol., vol. 2, pp. 163-191. 102 University of California Publications in Agricultural Sciences [ Vol. 3 141905. MacCallum, J. B. The action of purgatives in a crustacean, Bull. Univ. Calif. Physiol., vol. 2, no. 6, pp. 65-70, 15 1906. Loeb, J. The stimulating and inhibitory effects of Mg and Ca., Jour, Biol. Chem., vol. 1, p. 427-436. 161906. Osterhout, W. J. V. On the importance of physiologically balanced solutions for plants, Bot. Gaz., vol. 42, pp. 127-134. 17 1906. Extreme toxicity of NaCl and its prevention by other salts, Jour. Biol. Chem., vol. 1, pp. 363-369. 181907. Loew & Azo. On the physiologically balanced solutions, Bull. Agric. Univ. Tokyo, vol. 7, no. 3. 191907, Benecke, W. Uber die Giftwirkung verscheidener Salze auf Spy- rogyra und ihre Entgiftung durch Calciumsalze, Ber. deutsch. botanisch. Ges., vol. 25, pp. 322-337. 201908. Osterhout, W. J. V. Antagonism of Mg and K on plants, Bot. Gaz., vol. 45, pp. 117-129. 21 Meltzer & Auer. The antagonistic action of calcium, Am. Jour. Physiol., vol. 21, pp. 400-419. 221909. Osterhout, W. J. V. On the similarity of behavior of Na and K, Bot. Gaz., vol. 48, pp. 98-104. 231909. Lipman, C. B. Toxie and antagonistic effects of salts, Bot. Gaz., vol. 48, p. 105. Complete title in Part A. 241910. Lipman, C. B. On the lack of antagonism, Bot. Gaz., vol. 49, pp. 41-50. 251910. Lipman, C. B. On physiologically balanced solutions for bacteria, Bot. Gaz., vol. 49, pp. 207-215. UNIVERSITY OF CALIFORNIA PUBLICATIONS /[ IN AGRICULTURAL SCIENCES Vol. 3, No. 6, pp. 103-130 . March 9, 1918 CHANGES IN THE CHEMICAL COMPOSITION OF GRAPES DURING RIPENING BY F. T. BIOLETTI, W. V. CRUESS, anp H. DAVI The investigations reported in this paper were undertaken to determine the changes in chemical composition of vinifera varieties of grapes in California during the growing and ripening stages. A survey of the literature indicated that, although the subject had been quite fully investigated in Europe with vinifera varieties and in America with the native varieties, very little had been published upon the ripening of vinifera varieties under California Conditions. A great many analyses of different varieties of grapes have been made by chemists of the University of California Experiment Station, nota- bly by G. E. Colby, and are reported in the publications of this station.* A paper by G. E. Colby? gives data upon the nitrogen content of a number of varieties of ripe vinifera grapes. Most of the analyses, however, do not show the changes in composition during ripening. Of the more recent European investigations* some deal with the changes in general composition, others are confined to a discussion of a single component, such as sugar, or coloring matter, or acid principles. The changes in composition of American varieties of grapes during ripening have been studied quite thoroughly by W. B. Alwood?* and his associates. These investigations gave particular attention to the 1 Hilgard, E. W., The composition and classification of grapes, musts, and wines. Rept. of Viticultural Work, Univ. Calif. Exper. Sta. Rep., 1887-93, pp. 3-360. 2 Colby, G. E., On the quantities of nitrogenous matters contained in Cali- fornia musts and wines. Ibid., pp. 422-446. 3 Kelhofer, W., The grape in the various stages of maturity; trans. by L. Zardetti. Gior. Vin. Ital., vol. 34 (1908), no. 30, pp. 475-477. Barberon, G., and Changeant, F., Investigations on the development and 104 University of California Publications in Agricultural Sciences [ Vol. 3 increase in sugar content and changes in acidity during the period in which the grapes were under observation. Alwood and other mem- bers of the Bureau of Chemistry, United States Department of Agri- culture, have also published a number of reportst on the general composition of American varieties of grapes as affected by season, locality, ete. The most notable changes taking place during ripening were found by the European and American investigators mentioned above to be: (1) increase in total sugar ; (2) decrease in ratio of glucose to fructose ; (3) decrease in total acid; (4) increase in ratio of cream of tartar to total acid due to decrease in total acid ; (5) decrease in tannin; and (6) increase in coloring matter. The cream of tartar and protein change very little in percentage during ripening, although, according to the composition of varieties of grapes in Abraon-Durso. Ann. Soc. Agr Sci. et Ind., Lyon (8), vol. 1 (1903), pp. 97-159. Laborde, J., The transformation of the coloring matter of grapes during ripening. C. R. Acad. Sei. (1908), vol. 17, pp. 753-755. Martinand, V., On the occurrence of sucrose and saccharose in different parts of the grape. C. R. Acad. Sei. (1907), vol. 24, pp. 1376-79. Roos, L., and Hughes, E., The sugar of the grape during ripening. Ann, Falsif. (1910), vol. III, p. 395. Bouffard, A., Observations in regard to the proportion of sugar during ripen- ing. Ann. Falsif. (1910), vol. III, pp. 394-5. Zeissig, Investigations on the process of ripening on one-year-old grape wood. Ber. k. Lehranst. Wien, Obst-u. Garten-bau (1902), pp. 59-64. Koressi, F., Biological investigations of the ripening of the wood of the grape. Rev. Gen. Bot., vol. 13 (1901), no. 149, pp. 193-211; no. 150, pp. 251-264; no. 151, pp. 307-325. Brunet, R., Analysis and composition of the grape during ripening. Rev. de Viticulture, vol. 37, pp. 15-20. Garina, C., Variations in the principal acids of grape juice during the process of maturing. Canina. Ann. R. acad. d’agricultura di Torino, vol. 57 (1914), p- 233. Cf. Ann. Chim. applicata, vol. 5 (1914), pp. 65-6. See also Ann. r. acad. d’agr. di Torino, vol. 57, pp. 233-90. Baragolia, W. I., and Godet, C., Analytical chemical investigations on the ripening of grapes and the formation of wine from them. Landw. Jahrb., vol. 47 (1914), pp. 249-302. Riviére, G., and Bailhache, G., Accumulation of sugar and decrease of acid in grapes. Chem. Abs. Jour. (1912), p. 1022; Jour. Soe. Nat. Hort. France (4), pp. 125-7; Bot. Cent., 1912, pp. 117, 431. Pantanelli, Enzyme in must of overripe grapes. Chem. Abs. Jour., vol. VI (1912), p. 2447. + Alwood, W. B., Hartmann, J. B., Eoff, J. R., and Sherwood, 8. F., Develop- ment of sugar and acid in grapes during ripening. U.S. Dept. Agric. Bull. 335, April 11, 1916. —— The occurrence of sucrose in grapes. Jour. Indust., vol. IT, Eng. Chem. (1910), pp. 481-82. —— Sugar and acid content of American native grapes. 8th Inter. Cong. Appl. Chem. (1912), Sect. VIa—XIv, pp. 33, 34. —— Enological Studies: the chemical composition of American grapes grown in Ohio, New York, and Virginia. U.S. Dept. Agric. Bur. Chem. Bull. 145, 1911. Crystallization of cream of tartar in the fruit of grapes. U.S. Dept. Agric. Jour. Agric. Research (1914), pp. 513, 514. Alwood, W. B., Hartmann, B. G., Eoff, J. R., Sherwood, 8S. F., Carrero, J. O., and Harding, T. J., The chemical composition of American grapes grown in the central and eastern states. U.S. Dept. Agric.( 1916) Bull. 452. a 1918 | Bioletti-Cruess -Davi: Chemical Composition of Grapes 105 investigations referred to, there is a slight increase in both of these constituents. In the investigations reported in the present paper, particular attention was given to increase in total solids and sugar, decrease in total acid, and changes in protein and cream of tartar in the must or juice of the grapes. The ripening of the leaves was traced by noting the changes in starch, sugar, acid, and protein content. Sampling —During 1914 and 1915 samples of fruit were taken from the time the grapes had reached full size but were still hard and green until they had become overripe. During 1916 the first samples were taken shortly after the berries had set and before the seeds had formed. The last samples were taken when the grapes had become overripe. Samples of leaves were also taken in 1916 on the same dates that samplings of the grapes were made. The samples were taken at intervals of approximately one week. They were in all cases taken from the experimental vineyard at Davis.° Five-pound samples of grapes were used. The grapes were picked from the first crop, except in 1914, when a comparison of the ripening of first and second crops was made. An ordinary five-pound grape basket was filled with leaves at each sampling. The samples of grapes and leaves were shipped from the vineyard to the laboratory at Berkeley, where the grapes were placed in an Enterprise fruit crusher and pressed. The juice was sterilized in bottles at 212° F. The leaves were ground in an Enterprise food chopper and sterilized at 212° F in wide mouth, air tight bottles. The samples were then reserved for chemical examination. In 1914 it was found that there was considerable irregularity in the variation of samples from week to week. For example, instead of an increase of total solids during the periods between samplings, a slight decrease was found in a few samples. During the 1915 season it was therefore considered of interest to note what effect certain factors might have upon the composition of samples taken on the same date. 1. Effect of Age of Vine. The entire first crop from three large old vines and from three small young vines, all of the Muscat variety, was picked, crushed, and pressed.- Analyses of the juices were made with the following results: _ 8 The authors wish to express their appreciation of the assistance of F. C. Flossfeder, of the University Farm at Davis, who gathered most of the samples reported upon in this paper. LOG University of California Publications in Agricultural Sciences | Vol. 3 TABLE 1—EFPFECT OF AGE OF VINE ON BALLING AND ACID OF Must oF Muscat GRAPES Vine Balling Acid po | ST, ee a ae ie 24.7 .67 EE RRR 8 oo Tae he SAT 27.7 49 Ria WOO seco oes 27.6 .67 ERGO, MONE irc ce tae yecee ete 22.0 88 ENOTES By Ok cantons 23.5 .75 NO AE ot 23.6 76 PVerere. OTA) fin cccccccteone 26.7 61 Average, large .............----.-.-. 23.0 381 TOI os So. a cteacoies 3.7 —.20 The results show rather strikingly that young vines ripen their fruit earlier than do mature vines. This fact makes it essential that samples, to be comparative, must be taken from vines of the same age. 2. Comparison of Grapes from North and South Sides of Vines. The whole first crop from three large Museat vines was picked. The bunches from the north and south sides of each vine were kept sep- arate. They were crushed, pressed, and analyzed for Balling and acid content. TABLE 2—COMPARISON OF BALLING AND ACID OF JUICE FROM GRAPES PICKED FROM NorRTH AND SoutTH SIDES OF VINES Vine and side of vine Balling Acid ie er Se ne ee er 21.3 92 1 A) eer Rated Cer ee eke 22.7 84 , 2) | SSeS Sas Se ee es ieee. 7 DOS 23.5 81 es ee ER Pe ae eae eee 23.5 80 ol [eae ae Ee OEP ERR SON 23.1 81 SRR rs Ses ot ere a ee 24.1 Ay fe Avyerare, N side ..-...-<...5 22.63 85 Avyorage, 8: side 2053.55.63 23.43 .78 UMOTBONG 3. 6 80 —.07 The tests indicate that grapes located on the south side of the vine ripen more rapidly than those on the north side. This difference is apparently due to the fact that the south side of the vine receives more heat than the north side. 3. Effect of Location of Bunch on Cane. Grapes of first crop, from canes showing two bunches each, were picked and the bunches from near the bases of the canes kept separate from those near the tip of the cane. They were crushed, pressed, and analyzed for Balling and acid. 1918 | Bioletti—Cruess—Davi: Chemical Composition of Grapes 107 TABLE 3—Errecr OF LOCATION OF BUNCH ON CANE Nearest base of cane Nearest tip of cane Vine ‘Balling Acid Dalling Acid MEUBGNG, TIO, 15 COMO Zo beccrsacieesnmn 25.1 73 23.7 83 Muscat, no. 1, cane 2 .................. 25.6 19 24.8 80 Muscat, mo. 2, Cane: Te .ucncsasihsens 25. 85 24.6 87 Muscat, no. 2, Cane B. ..ccsccascs->-s- 25.2 .78 24.7 85 Muscat, MO. BS, GARO 1. coiccscis.ccss. 23.0 79 22.6 82 Muscat, no. 3, cane 2 .................. 24.5 13 23. By i Museat, no. 4, cane 1 ..................- 24.2 90 25.2 90 Muscat, no. 4, cane 2 ................... 24.5 68 23.8 83 CL OELY 5 CGING Lc. ckain tis. ceniaatetenae 21.2 67 21.2 80 TOMSEY, OTIS 2. soso secthtencineseactocenatie 23.0 63 22.4 .76 PUENTE CONG Le cticiienscncteciese 23.3 61 22.3 62 SUILARINA, CONG (2) access ec ieicseeten 22.5 61 23.0 63 OTL UPON Ris GILG: Bio cc an obi aceanoneae 23.2 Rif. 21.6 70 SOU AA I ORTUG etewvtansn te Roose 21.1 90 20.0 1.20 POlOMING, | COIS si. ee BO Aa teak Ou ine PF BLOMING) COME! B02. epic nf nese ASE a Saale EOE) wn, . acasun NCUA TN eet cat hie pha ons 24.9 75 23.1 81 The data indicate that bunches at the base of the cane ripen in most cases more rapidly than those near the tip, although this relation does not always hold and may be reversed in some instances. 4. Variation in Balling Degree of Must from Bunches of Similar Appearance and Size from Same Vineyard and Gathered on Same Date. A five-pound basket of grapes of first crop and selected for similarity of color, size of bunch, and general appearance was picked from each of a number of vines in the same vineyard. Vines of similar size and appearance were chosen. Several varieties were rep- resented in the experiment. Tests of Balling degree only were made. TABLE 4—VARIATION IN BALLING IN Must FroM GRAPES OF SAME VARIETY PICKED H'ROM DIFFERENT VINES OF SIMILAR APPEARANCE Vine Mean Maximum Variety number Balling Balling variation Cornichon 3 eds | ee een Cornichon 6 Pye eee eee Cornichon 9 if Sep 9) SE eee Cornichon 11 Wepre were ass, Cornichon____....... 16.1 14.9 1.9 Emperor 10 (Uo) gS «Se ia ose Emperor 1 eR aor Emperor 13 PELE gl | acs See ee ners Emperor 14 Lg |. as Emperor 17 15.0 14.4 ° 3.5 Malaga 5 Ua Ss Malaga 6 id hl <3 es 108 Variety Malaga Malaga Malaga Museat iuuscat Muscat Muscat Museat Palomino Palomino Palomino Palomino Palomino Sultanina Sultanina Sultanina Sultanina Sultanina Tokay Tokay Tokay Tokay Tokay TABLE 4—(Continued) Vine number 7 i] 11 Pedro Zumbon Pedro Zumbon Pedro Zumbon Pedro Zumbon Emperor Emperor Emperor Emperor Emperor Cornichon Cornichon Cornichon Cornichon Cornichon Malaga Malaga Malaga Malaga Mean variation, six ripest varieties Mean variation, six least ripe varieties * 7 4 Pedro Zumbon 6 3 5 Balling 19.7 18.5 19.2 21.7 21.1 20.9 21.5 21.7 19.5 21.0 21.2 20.7 18.8 22.5 21.5 18.7 22.0 22.6 19.8 19.3 18.7 20.7 19.5 21.5 21.2 20.6 18.5 19.8 18.1 15.8 16.2 16.8 16.3 17.3 16.3 17.9 17.8 18.0 18.3 20.4 20.0 20.1 Average variation, whole series * Adjacent vines. Mean Balling University of California Publications in Agricultural Sciences Maximum Variation waeeee [ Vol. 3 1918 | Bioletti-Cruess-Davi: Chemical Composition of Grapes 109 The data illustrate the difficulty of selecting five-pound lots of the same variety that will represent average samples. 5. Effect of Location of Berries on the Bunch. All of the bunches of the first crop were taken from two Muscat vines. The bunches were cut into top and bottom halves. These lots were crushed sep- arately, pressed, and the juices analyzed. TABLE 5—Errect or LOCATION OF BERRIES ON BUNCH Sample Balling Acid Vine no. 1, stem: 6nd of. Sunel i027 k i ..s..:. 23.6 .76 Vine no. 1, apical-end of ‘bunen: ....2....2....4...... 22.7 87 Vine no. 2,:stem end of bunch <.:-..i ern. 21.3 92 Vine no. 2, apical end of biumeli ........2-............... 21.3 93 The results show that considerable variation in composition of the berries may exist within the same bunch. 6. Effect of Thoroughness of Pressing. About ten pounds of Mus- eat grapes were crushed and lightly pressed. The pulp and skins left from this pressing were then thoroughly crushed and pressed a second time. The juices from the two lots were analyzed separately. TABLE 6—EFFECT OF THOROUGHNESS OF PRESSING Sample Balling Acid PIESE: PTOGRIND -..c sd cee ee 22.8 .78 Second pressing .................... 22.8 .79 There was practically no difference between the juices from lightly and thoroughly pressed grapes of the same lot. The data from the above six tests indicate that it is a very difficult matter to select grapes that will represent a fair average sample of the grapes to be studied. The size and age of the vine, the side of the vines, the location of the bunch on the cane, and individual vines, all affect the composition of the juice from the grapes very materially, and these factors should be taken into account when samples are taken. Preservation of Samples and Preparation for Analysis —In 1914 the samples of juice were preserved with HgCl,, 1:1000. In 1915 and 1916 the samples were sterilized at 100° C. Before analysis the bottles were heated to 100° C for an hour to dissolve any cream of tartar which might have separated. The juices were filtered before analysis. Con- siderable coagulation of dissolved solids took place during sterilization. L110 University of California Publications in Agricultural Sciences | Vol. 3 Methods of Analysis —The samples were analyzed by the methods in use in the Agricultural Chemistry Laboratory and the Nutrition Laboratory of this station. A brief description of the methods follows: 1. Total Solids. The juice was filtered clear and cooled below 15° C, The specific gravity was determined by a pycnometer at 15°5 C. The corresponding total solids, or extract, was found from Windisch’s tables in Leach’s Food Analysis, page 697. This table gives the extract as ‘‘grams per 100 grams’’; that is, per cent by weight. To caleulate the corresponding grams per 100 e.c., the per cent by weight was multiplied by the specific gravity. This gives a figure not very much greater than grams per 100 grams in juices of low specific gravity, but gives a figure as much as 2 per cent greater where the total solids are much above 20 per cent. The two methods of reporting total solids has in the past led to much unnecessary confusion. It is therefore urged that the reader bear in mind the distinction between the two methods when reading the discussions in this paper or examining the curves. 2. Sugar. The sample was filtered; an aliquot was treated with lead acetate; diluted to mark; filtered; lead removed with anhydrous Na,CO,, and the sugar determined in an aliquot by the gravimetrie method, using Soxhlet’s modification of Fehling’s solution. The Cu,O was weighed directly after drying at 100° C. The corresponding sugar as invert sugar was obtained from Munson and Walker’s table in Leach’s Food Analysis. The grams of invert sugar per 100 ee. found in this way was divided by the specific gravity of the must to obtain the corresponding grams per 100 grams of juice. 3. Total acid was determined by titration of a 10 ¢.c. sample with N/10 NaOH, using phenolphthalein as an indicator, and is reported as tartarie acid, grams per 100 e.e. 4. Cream of tartar was estimated by a method suggested by Pro- fessor D. R. Hoagland of the Division of Agricultural Chemistry. Ten e.c. of the juice was incinerated at a low heat in a muffle furnace until well carbonized, but not to a white ash. (Excessive heating results in loss of K by volatilization.) The K,CO, formed by inein- eration was leached out with hot water and a known excess of N/10 HCl added. This was titrated back with N/10 NaOH, using methyl orange as an indicator. The K,CO, is obtained by difference and ealeulated back to cream of tartar, assuming that all of the K,CO, is formed by the oxidation of cream of tartar, KH(C,H,O,). It is 1918 | Bioletti-Cruess-Davi: Chemical Composition of Grapes 111 reported as grams KH(C,H,O,) per 100 ¢.¢., and also as tartaric acid, 5. Free Tartarie Acid was obtained by difference between total acid and eream of tartar calculated as tartaric acid. It is reported as grams per 100 e@.e. 6. Protein in the juice was determined by the usual KJeldahl- Gunning method upon a 10 ¢.e. sample. It is reported as grams per 100 @.e. 7. Moisture in the leaves was determined by drying the sample at 100° C. 8. Sugar in the leaves was estimated by leaching the dried sample with cold water and determining sugar by the gravimetric Fehling method in the filtrate. 9. Stareh in the leaves was determined by hydrolysis of the dried ground sample with dilute HCl at 100° C., followed by filtration and the usual gravimetric Fehling method for juice described above. 10. Protein in the leaves was determined by the Kjeldahl-Gunning method on .5 gram samples. 11. Acid in the leaves was estimated by leaching in hot water and titrating in the presence of the leaves, using litmus paper as indicator. Analyses of Musts from Grape-Ripening Samples, 1914, 1915, 1916. The data from the analyses have been assembled in the following tables. Owing to the size of the tables, abbreviations have been necessary for the headings of the columns. EXPLANATIONS OF HEADINGS OF TABLES . Sp. gr.= Specific gravity at 15°5 C. . T.S.G.= Total solids in grams per 100 grams. . T.S.C.= Total solids in grams per 100 e.e. . S.G.=Sugar in grams per 100 c¢.c. . S.I.=Sugar in grams per 100 grams. . Tl. A.= Total acid in grams per 100 e.c. . C.T.—=Cream of tartar in grams per 100 ce. 8. C.T. T.—=Cream of tartar as tartaric acid, grams per 100 c.e. 9. T. A.= Total free acid as tartaric obtained by subtracting cream of tartar as tartaric from total acid as tartaric. 10. P.= Protein, grams per 100 e.¢. 11. 8S. =Sum of sugar, cream of tartar, tartaric acid, and protein in grams per 100 e.e. 12. T.S.—S.= Total solids (T.S. C.) —S (preceding column). aon fP WD He ~] 112 Malaga First crop: Variety and date Aug. Aug Aug. Aug. Aug. Aug. Sept. Oct. 19 26 26 26 26 31 23 5 University of California Publications in Agricultural Sciences : Sp. gr. 1.0396 1.0413 1.0595 1.0613 1.0694 1.0732 1.0736 1.0965 Second crop: Aug. Aug. Sept. Sept. Sept. Oct. Tokay First crop: Aug. Aug. Aug. Aug. Sept. Sept. Sept. Oct. Oct. 10 31 14 23 9 — 14 1.0213 1.0495 1.0532 1.0670 1.0869 1.0930 1.0454 1.0624 1.0682 1.0849 1.0865 1.0912 1.0937 1.0991 1.1000 Second crop: Aug. Sept. Sept. Oct. 19 14 23 14 Cornichon Variety and date Aug. Sept. Sept. Sept. Sept. Oct. Oct. Oct. 1.0657 1.0701 1.0769 1.0911 ‘ABLE 7—GRAPE RIPENING TeEstTs, 1914 T.8.G. 8.0. 10.25 10.65 10.69 11.13 15.42 16.33 15.87 16.84 18.01 19.25 19.00 20.39 19.10 20.50 25.12 27.54 5.51 5.62 12.82 13.45 13.78 14.51 17.43 18.60 22.59 24.55 24.20 26.45 11.75 12.28 16.08 17.08 17.69 18.90 22.09 23.97 22.49 24.44 23.72 25.88 24.38 26.66 25.80 28.36 26.04 28.64 17.04 18.16 18.19 19.47 19.95 21.48 23.70 25.86 TABLE 8—GRAPE RIPENING TESTS, 1915 2 3 7.6.6, 72. 8. C. 8.38 8.65 13.31 13.99 17.85 19.08 18.76 20.12 19.13 20.54 20.28 21.86 21.91 23.76 22.70 24.68 (Grapes from Davis) 4 5 &¢. B.r. Ti 7.32 7.04 2.78 .35 7.84 7.53 2.65 .36 13.37 12.62 .77 .48 14.31 13.50 1.46 .31 16.59 15.52 1.00 .36 17.65 16.45 .87 .55 17.83 16.60 .74 .38 24.89 22.70 .72 .50 2.07 2.03 3.22 .23 958 9.13 2.51 .40 11.89 11.30 2.07 .37 15.29 14.33 1.54 .50 22.04 20.19 1.07 .45 23.90 21.87 .94 .48 8.73 8.35 2.63 .46 14.28 13.44 1.56 .45 15.94 14.92 1.32 .45 21.87 20.16 .63 .59 22.21 20.44 .77 «43 23.44 2148 .59 .64 24.15 22.08 .58 .49 25.55 23.25 .45 .54 25.78 23.44 .52 .58 15.03 14.10. 1.91 .50 16.68 15.59 1.29 .52 19.22 17.85 1.01 .48 23.43 21.47 .69 .60 (Grapes from Davis) 4 5 6 7 8 AG yo ka a OU es ee 23 25 .28 28 30 29 27 ol 3.99 3.86 3.05 .58 10.70 10.18 1.62 .61 15.94 1491 97 .70 16.97 15.83 .94 .71 18.31 17.05 .87 .75 19.41 18.02 .71 -.73 20.40 18.81 .78 .68 21.06 19.87 .75.. .78 6 7 8 wo Ce Cts 13 14 19 12 14 22 15 .20 09 16 15 20 18 19 9 yap 2.65 2.51 2.45 1.38 1.14 40 .60 44 30 24 29 1.70 21 82 45 9 Te 2.82 1.37 69 66 61 42 .62 44 [ Vol. 3 10.53 10.96 14.98 16.29 18.19 19.30 19.32 26.48 5.60 12.61 14.49 17.43 23.79 25.54 11.96 16.38 17.80 23.26 23.56 24.93 25.33 26.78 27.23 16.55 18.64 20.92 24.88 1.10 1.33 1.58 1.41 61 83 56 98 12 T.S. 8. 88 89 1.32 1.32 21 82 1.40 1.94 1918] Emperor Variety and date Aug. 19 Sept. 1 Sept. 7 Sept. 15 Sept 22 Sept. 29 i a | Oct. Oct. Malaga Aug. Aug. Zu Sept. 1 Sept. 7 Sept. 15 Sept. 22 Sept. § Oct. 7 Oct. Muscat — Aug. Aug. Sept. Sept. Sept. Sept. Sept. st. . 7 bo ane oo wo Ww e& © bo Aug. 19 Aug. 25 Sept. 1 Sept. 7 Sept. 15 Sept. 22 Sultana Aug. Aug. 25 Sept. Sept. Sept. 2 Sept. won 1 Sp. gr. 1.0420 1.0479 1.0560 1.0632 1.0652 1.0672 1.0744 1.0765 1.0792 1.0546 1.0651 1.0678 1.0719 1.0758 1.0760 1.0812 1.0838 1.0970 1.0615 1.0744 1.0805 1.0827 1.0917 1.0954 1.1048 1.1079 Pedro Zumbon 1.0555 1.0588 1.0642 1.0693 1.0708 1.0912 1.0673 1.0746 1.0815 1.0893 1.0902 1.0922 Bioletti-Cruess—Davi: Chemical Composition of Grapes 2 of CO = IC 10.87 12.40 14.51 16.37 16.9] 17.43 19.31 19.86 20.57 14.14 16.86 17.59 18.66 19.68 19.81 21.20 21.78 25.25 15.94 19.31 20.91 21.47 23.85 24.14 27.30 28.12 14.38 15.24 16.64 17.98 18.37 23.72 17.80 19.37 21.17 23.22 23.39 23.99 TABLE 8—(Continued) 5 5. I. 6.68 9.37 10.87 14.00 14.51 15.34 16.59 17.06 18.36 11.82 13.64 15.69 15.86 16.89 17.09 17.09 19.40 22.41 13.12 16.72 18.05 18.83 21.52 22.40 24.45 25.53 11.33 13.01 14.67 15.48 16.97 21.10 16.64 16.71 18.73 21.13 21.19 22.01 6 7 Gules. iet > Os 2.00 1.89 1.70 1.40 93 91 79 .79 15 2.05 1.66 1.38 1.29 1.21 1.18 Loy 1.07 9 1.70 1.21 76 38 40 A7 Oo 48 A8 58 9 .63 8 i ie 15 wa & CI 9 T.A. 2.18 1.73 1.57 1.18 14 12 56 6 Ad 1.90 1.48 1.20 AEF 1.56 1.30 92 .60 1.04 63 113 11 12 5. . 2. A.8; 9.90 1.43 12.57 42 14.00 1.32 17.48; .0t 17.23 78 18.23 3 19.47 1.28 20.15 1.23 21.59 + «61 15.48 57 17.3 9 19.28 .50 19.25 .25 20.45 .72 20.67 «65 20.65 2.27 23.22 .39 26.55 1.15 16.54 .38 20.16 .59 21.30 1.29 22.20 1.05 25.38 .66 26.53 .09 28.89 1.27 29.96 1.19 14.51 .67 15.73.41 16.93 .78 18.41 .82 19.72 .05 24.72 1.16 17.84 1.16 20.01 81 22.22 .68 24.40 .89 25.02 .48 25.50 .70 Ll4 Sultanina Variety and date Aug. Aug. Sept. Sept. Sept. Sept. Sept. Tokay Aug. Aug. 2! Sept. Sept. Sept. Sept. Sept. 2 Oct. Oct. Oct. Burger 19 Variety and date June June June § July July - July July 2 Aug. Aug. Aug. Aug. Aug. Sept. Sept. Sept. Sept. 12 12 20 26 Cornichon June June June July July July July Aug. 12 19 27 University of California Publications in Agricultural Sciences 1 Sp. gr. 1.0673 1.0743 1.0771 1.0892 1.0927 1.0984 1.1049 1.0598 1.0676 1.0757 1.0781 1.0785 1.0798 1.0823 1.0830 1.0851 1.0895 1 Sp. gr. 1.0212 1.0195 1.0220 1.0220 1.0200 1.0205 1.0225 1.0258 1.0330 1.0391 1.0422 1.0529 ° 1.0645 1.0717 1.0765 1.0808 1.0202 1.0200 1.0193 1.0201 1.0206 1.0225 1.0242 1.0373 v.84. 7.8.0. 17.46 18.64 19.26 20.69 20.02 21.56 $3.20 235.97 24.12 26.36 25.62 28.14 $7.33 30.20 15.50 16.43 17.54 18.73 19.65 21.14 20.28 21.86 20.39 21.99 20.73 23.38 21.38 23.14 21.57 23.36 22.12 24.00 23.28 25.36 2 3 T.S.G. T. S.C. 5.48 5.59 5.04 5.88 5.69 5.82 5.69 5.82 5.17 5.27 5.30 5.41 5.82 5.95 6.67 6.84 8.53 8.83 10:13. 30:5 10.92 11.38 13.70 14.42 16.73 17.81 18.61 19.94 19.86 21.37 20.99 22.68 5.22 5.32 RUT 5.27 4.99 5.08 5.19 5.29 5.32 5.43 5.82 5.95 6.25 6.40 9.65 10.00 TABLE 8—( Continued) 4 8. G. 15.87 18.30 18.98 22.42 23.62 25.71 27.41 14.41 15.63 18.17 19.11 19.26 20.17 20.76 20.87 21.53 22.91 5 8. I. 14.87 17.03 17.62 20.58 21.62 23.41 24.81 13,60 14.64 16.89 17.73 17.86 18.68 19.18 19.27 19.84 21.03 6 7 iy A Sa » A. 127 .44 119 .47 85 .49 72 .80 79 .76 60.58 o4 «51 1.74 .41 1.24 .39 384 47 19 = 45 74 48 o9 .51 85 .58 69 .63 65 .69 66 .72 3 Oo F.t. AS 19 20 oo B0 23 20 23 25 28 29 TABLE 9—GRAPE RIPENING TESTS, 1916 1.28 1.63 5.00 1.55 1.28 1.28 1.05 1.15 2.19 3.46 6.13 6.27 10.42 15.43 17.36 18.73 19.99 93 88 86 89 87 1.30 1.66 5.19 6 (i 8 Th. 2. 0. 2. 6. YF. 2.95 .55 .22 2.88 51 .21 2.94 .33 .13 2.98 .49 .20 3.32 57 .23 3.13 55 .22 2.93 .48 .19 2.71 83° 425 2.67 8&7 .35 2.41 95 .38 2.10 98 .39 115 1.03 .41 1.01 1.07 .43 95 . .98 .39 87 1.06 .42 81 1.01 .40 S15 64 26 2.96 .62 .25 2.89. .39 .16 2.88 .44 .18 3.27 54 .22 acy 00 \~ eee 2.94 .54 .22 2.87 .59 .24 9 ¥. A. 1.09 1.00 65 40 bo po bo “I a — 10 | Vol, 3 11 12 6, 2232.8 17.82 82 20.14 ~=.55 20.54 1.02 24.24 1.03 25.22 1.14 27.11 1.03 28.68 1.52 16.69 = 26 17.80 .93 19.74 1.40 20.54 1.32 20.69 1.30 21.43 95 22.24 .90 22.36 1.00 22.96 1.04 24.37 .99 11 12 Ss. Tass D.27 836d 4.51 1.37 4.87 .95 4.86 96 4.97 .30 4.86 55 4.71 1.24 5.68 1.16 7.12 1.21 9.57 .94 9.59 1.89 12.70 1.72 17.79 .02 19.72 22 20.86 .51 22.24 44 4.78 54 4.63 .64 4.54 44 4.55 .74 4.99 44 5.30 — .65 5.26 .14 8.97 1.03 1918 | Variety Bioletti—Cruess—Davi ’ “ as tas ee 9.70 11,28 16.47 17.77 18.01 19.65 20.41 21.52 65 1.06 06 10 90 1.14 .94 83 TABLE 9—( Continued) 3 A 5 6 7 1s Oper eee: (ee Hoe Olt. 10.06 5.28 5.48 2.79 11.71 630 6.57 . 2.75 17.51 12.19 12.96 1.85 18.97 14.75 15.61 1.16 19.25 15.03 16.07 .93 21.09 16.37 17.60 .87 22.00 17.52 18.88 .84 23.30 18.52 20.03 .72 5.39 91 93 2.93 5.24 .70 12_-3t 5.54. 1.383 --1.36 3.33 5.54 1.63 1.66 3.32 ‘5.14 1.33 1.36 3.60 6.65 2.55 2.61 3.40 8.22 3.56 3.67 2.67 13,20) S78) * LOITO4 Pe 16.58 12.72 13.53 1.60 2200 16.81 18:15. 1.16 25.82 20.20 22.04 .82 27.75 21.87 22.99 .65 29.36 23.28 24.74 .60 31.85 25.95 27.83 .56 32.72 26.43 29.39 .68 32.89 26.68 29.70 .56 8 Led ey 26 43 43 44 36 46 37 2 ) 4 ) 2.6 -~ 27 9 d itay 9.53 2.32 1.42 vB mY 4) TABLE 10—CATAWBA GRAPE RIPENING TESTS : Chemical Composition of Grapes 58 115 11 12 8 Tr, A. 8 10.48 1.23 16.02 1.49 18.06 .91 18.12 1.13 19.97 1.12 20.85 1.15 22.10 1.20 16.12 46 20.38 1.70 24.04 1.78 25.94 1.81 (Table from U.S. Dept. Agric. Bulletin 335, by W. B. Alwood) and date Sp. gr. Aug. 7 1.0875 Aug. 16 1.0434 Aug. 23 1.0635 Aug. 30 1.0685 Sept. 5 1.0694 Sept. 12 1.0757 Sept. 20 1.0786 Sept. 26 1.0828 Muscat June 12 1.0203 _ June 19 1.0199 June 27 1.0210 July 7 1.0210 July 10 1.0195 July 19 1.0251 July 27 1.0308 Aug. 3 1.0488 Aug. 7 1.0582 Aug. 16 1.0803 Aug. 23 1.0910 Aug. 30 1.0972 Sept. 5 1.1023 Sept. 12 1.1101 Sept. 20 1.1122 Sept. 26 1.1133 Catawba 1912: Variety and date Sept. 4 Sept. 9 Sept. 12 Sept. 17 Sept. 24 Oct. 1 Oct. 7 Oct. 16 Oct. 23 Oct. 29 Nov. 4 Nov. 8 il Sp. gr. 1.0329 1.0419 1.0515 1.0537 1.0569 1.0614 1.0663 1.0725 1.0716 1.0769 1.0790 1.0755 2 1. 8. G. 8.51 10.84 13.34 13.91 14.74 15.92 17.20 18.82 18.58 19.97 20.52 19.60 3 J hig — RN 8.84 11.29 14.03 14.66 15.58 16.89 18.54 20.18 19.90 21.50 22.14 21.07 5 BerG: 3.72 6.96 9.78 10.95 11.96 13.48 14.71 16.46 16.09 17.75 18.08 17.61 6 db ae: 3.68 3.02 2.48 2.12 1.74 1.63 1.53 1.34 1.28 1.22 1.28 1.09 ff 8 9 O72 OT es Daye oo 6 0 41 16 5 46 18 8 45 18 13 53 5 | 20 04 22 27 61 24 33 61 24 42 59 24 47 7 23 53 71 28 59 Je ' wb , Oe 116 University of California Publications in Agricultural Sciences | Vol, 3 Curves of Total Solids, Sugar, Total Acid, Free Acid, and Cream of Tartar.—In order to present the data in a form in which they may be readily studied, graphs have been constructed using time in days as abseissae and the above constituents expressed in grams per 100 ¢.¢. as ordinates. The curves represent the data for 1914, 1915, and 1916. For comparison, curves of the changes in composition of Catawba grapes reported by W. B. Alwood in the United States Department of Agriculture Bulletin 335 have been included. The acid principles have been plotted to a scale five times as great as that used for total solids and sugar in order that the variations in acidity might be more apparent. Discussion of Graphs of Total Solids, Sugar, Total Acid, Cream of Tartar, and Free Acid.—(1) Total Solids and Sugar. The data are more complete for 1916 than for 1914 or 1915, and include the period during which the berries are growing to full size as well as the ripen- ing period itself, during which the rapid increase in sugar occurs. The curves for 1916, therefore, are of more interest than those for 1914 and 1915. In the case of the Burger variety, total solids and sugar remained constant for approximately forty days after the tests were started. There was then a slight rise in these components for a period of about ten days. From that point on the rise in total solids and sugar was very rapid and fairly uniform. The behavior of the Corniehon was very similar. The Museat began ripening about ten days earler than the Burger and Cornichon, and proceeded much more rapidly up to about the ninetieth day after the experiment was started. There was then a slowing up in the increase in total solids and sugar corresponding to the period of over-ripeness. This slower increase in total solids is also evident in the curves for Emperor, Muscat, Sultana, and Tokay for the 1915 season, and would undoubtedly show in all eases if the observations were continued sufficiently. The effect of the season upon the rate of ripening is shown by a comparison of the Cornichon and Museat varieties for 1915 and 1916. All varieties ripened more slowly in 1915 than in 1916, resulting in steeper curves for 1916. However, owing to the fact that sampling was started later in 1914 and 1915 than in 1916, the curves for the former two years show only the changes taking place during the latter half of the ripening period. No very close comparisons therefore can be made of the three years. The Catawba reported by Alwood, and for which curves appear 117 SICH . SEN ECCT NG TEA NCI CCIE Bioletti-Cruess—Davi: Chemical Composition of Grapes Y aw 1918] de I ri fe ALN EREINSRO GOAN PSEC SCCM PCT CCN TI He aa AN CULE CULLENINT ES TIVE (N DIFYS TIME /N as Fig. 1—Malaga first and second crops, 1914. [Vol. 3 Agricultural Sciences University of California Publications in 118 MELT TT | SAN ETAT He AAT LTE TT aN UL yt EW | HOPnE IRIOE Hn Seca Vd il TIME /N DAYS 1914. Fig. 2—Tokay first and second crops, 1918 | Bioletti-Cruess—Davi: Chemical Composition of Grapes 119 = TIME IN DAYS Bile i lf | Lt | MF Bb, 5 Fig. 3—Cornichon and Emperor, 1915. TIME IN DAYS [| Vol. 3 University of California Publications in Agricultural Sciences L20 SUT BERBER ARSC HARE EEE IE-HIE al Aga TUTTI ENCURRR ERG Baan ELLA RAAT EEF G DOE ai See MTU TLE SAT AMT GT BCCHMMENVRRE HIE GRGRNK N/A TELIA BuaAN UIT IATn aa : TIME IN ORY: S TIME iN DAYS Fig. 4—Malaga and Muscat, 1915. 121 Bioletti—Cruess—Davi: Chemical Composition of Grapes 1918] “Las UNE 4 7/ME /N nae 5. Fig. 5—Pedro Zumbon and Sultana, 191 | Vol. 3 University of California Publications in Agricultural Sciences i | ani dee atiint ani aa TIME IN DAFYS Tefal Sol Fig. 6—Sultanina and Tokay, 1915. Bioletti-Cruess-Davi: Chemical Composition of Grapes 1918] 4M IN OATS ' TIAL INI a al | a We PEUMMNEL-ABARIG Hr | ee y aaa ChhtAAAAY APERIRK A aid Ho Fig. 7—Burger and Cornichon, 1916. 124 University of California Publications in Agricultural Sciences [ Vol. 3 lo 4, 0 a TIME IN DAYS Fig. 8—Muscat, 1916. a ee eC ee to eee a TIME /N DFFYS Fig. 9—Catawba (U.S. Dept. Agric. Bull. 335). 1918 | Bioletti-Cruess—Davi: Chemical Composition of Grapes 125 in figure 9, ripened more slowly than the Vinifera varieties. For example, during a period of fifty days, the total solids increased only 4 per cent. It can not be said from the data at hand whether this slow ripening is due to the conditions under which the grapes were grown or to the variety. By reference to figures 1 and 2 it may be seen that the general form of the ripening curves is the same for the first and for second crop. In one ease, the Malaga, the curves are almost identical for the period common to both, 1.e., from 10.6 Bal. to 26.3 Bal., showing an equal rate of ripening. In the other, the Tokay, the curve of the second crop, from 18.2 Bal. to 24.6 Bal., is much flatter than that of the first, indicating a rate of ripening with the latter of about two and a half times that of the former. This difference can be accounted for by the cooler weather during the time the second crop Tokay was ripening, which was about ten days later than in the case of the second crop Malaga. The slower ripening is probably due both to the direct effect of the cool weather and to the decreased activity of the leaves at lower temperatures. (2) Changes in Total Acid, Cream of Tartar, and Free Acid. Owing to the fact that the analyses were started in 1914 and 1915 after ripening had commenced, the curves for these years show a decrease in acid throughout the period of the tests. In 1916, however, a rise in total acid occurred during the growing stage, as shown by a rise in the curve during the first thirty days of the experiment. Although this rise is not very large, it is quite definite, and occurs in all three varieties tested. The rise was most positive in the case of the Muscat grape, and amounted to .67 per cent acid as tartaric. From the point of maximum acidity, the total decreases slowly until the period of rapid ripening sets in. The total acid then decreases very rapidly for a time and more or less in proportion to the increase in total solids and sugar. As the grapes near maturity, the rate of de- erease of total acid becomes less and the total remains practically constant after the grapes have reached maturity. The cream of tartar in general increases very slightly during the periods of growth and ripening. The inerease in total acid during the first stages of growth is due to increase in the free acid. Since the cream of tartar remains almost constant throughout the ripening period, the curve of the free acid is practically parallel with that of the total acid. As the grapes approach maturity, the cream of tartar calculated as 126 University of California Publications in Agricultural Sciences [ Vol. 3 tartaric acid approaches the total acid, and in one case, (Musct, 1916), actually became equal to the total acid, indicating that in this instance no free acid remained. Second crop grapes were found to be higher, in free acid than first crop grapes of the same total solids and sugar content. The Catawba grape grown under eastern conditions (fig. 9) exhibits rela- tively high free acid. Alwood® has found this free acidity in eastern grapes to be due largely to malic acid. No attempt was made in the analyses of the California samples to identify the various acids making up the free acidity which was calculated as tartaric acid. Mean Differences Between Total Solids and Sugar.—The following table contains figures representing the differences between total solids and sugar at the various percentages of total solids indicated at the tops of the columns. The data represent a range of total solids from 5 per cent to 30 per cent. The figures were taken from the data reported in tables 7 to 9, and represent several varieties of grapes. Only a few determinations of total solids and sugar were available for the lower concentrations (5 per cent to 15 per cent), and therefore the figures for this range may not represent averages so accurately as the figures above 15 per cent total solids. Between 5 per cent and 11 per cent solids, the average difference between total solids and sugar remains practically constant. From 11 per cent to 17 per cent total solids, the mean difference decreases quite rapidly. From 17 per cent to 30 per cent, the difference remains fairly constant. The variations noted after 17 per cent total solids Lit ia BS Pee, Sey Fig. 10—Mean differences between total solids and sugar between 5 per cent and 30 per cent total solids. 6U. 8S. Dept. Agric. Bull. 335. 127 Bioletti-Crucss- Davi: Chemical Composition of Grapes 1918} (Figures in columns re 5 6 7 42 4.7 49 42 45 .. £4; 30) ~ an Samples: 3 3 1 Average: 4,26 4.33 4.5 4.3 9 10 4.6 4.4 4.6 4.2 vaen | Si4 2 5) 4.6 4.3 11 4.1 4.9 4.9 4.66 present difference be 12 9Q oO. 4.0 3.9 9 oO. 13 o 3.2 2.9 Go 14 3.2 3.0 3.8 3.0 15 2.3 3.2 3.8 i) 3.1 16 2.4 2.8 2.88 17 2.6 3.0 3.3 2.7 2.3 2.7 3.0 2.2 9.69 2.84 2.85 2.69 2.73 tween total solids and sugar for 18 2.2 3.3 3.3 2.7 19 2.6 2.3 3.3 2.3 3.1 2.7 2.6 2.9 3.2 TABLE 11—MEAN DIFFERENCES BETWEEN TOTAL 20 1.5 2.7 3.2 2.7 3.1 2.4 2.4 2.8 3.0 II 21 lid 3.1 2.3 2.0 2.9 2.4 2.3 29 2.9 2.5 2.9 4.0 12 various juices of total soli 22 2.0 3.6 2.5 2.6 2.8 2.6 2.8 10 2.76 2.62 2.43 ds content indic Le) SoLIDS AND SUGAR 10 25 26 2.5 2.9 2.6 2.8 2:5. 2.7 2.9 2.5 2.4 2.2 Mle 2.4 3.4 9 5 2.37 2.62 ated at tops of columns) 27 28 29 29 29 2.8 25 2.6 2.8 2.55 2.4 2.8 Babs | Sar Stare 5 3 3 2.68 2.50 2.8 30 » 9 3.1 2.96 128 University of California Publications in Agricultural Sciences [Vol. 3 was reached are probably within the experimental error. The large difference between the total solids and sugar noted during the first stages of ripening is no doubt due to the high acid content of the unripe grapes. ‘The fact that the difference remains fairly constant after the grapes have become mature is to be expected, because the cream of tartar, total acid, and protein remain fairly constant as maturity is approached and during the periods of maturity and over- ripeness. Stil CNET UENCEEENEL EL Q d 9 9 Fig. 11—Variation in non-coagulable protein content for three varieties, 1916. Protein.—The total nitrogen content of the various samples was multiplied by 6.25 to convert it into its protein equivalent. Owing to the fact that the samples were sterilized by heat and filtered before analysis, the figures represent only the protein not coagulated by heat. The curves show that there is a slow increase in protein content during growth and ripening and the greatest increase occurs during the period of most rapid increase of sugar and most rapid decrease of acid. The increase amounted to about .2 per cent in the case of the Museat and .6 per cent in the ease of the Cornichon. The increase seems to be quite definite, although the protein curves are not so regular as those of total solids, sugar, and total acid. 1918 | Bioletti-Cruess—Davi:; Chemical Composition of Grapes 129 SUMMARY OF CHANGES IN Must oF GRAPES DuRING GROWTH AND RIPENING OF BERRIES 1. Votal Solids.—The total solids remain fairly constant during the period of growth, corresponding to the period between setting of the berries and the time at which the berries have reached almost full size but are still hard and green. From this point on, there is a rapid increase in total solids due to increase in sugar. After the period usually considered as full maturity is reached, the increase in total solids is slow. The question may be raised as to whether this last increase is due to an actual synthesis and secretion of sugar or other solids, or simply to evaporation of water. The fact that there is no change in the curve of the acid decrease at this time indicates that the same processes are continuing and that the increased Balling degree represents an actual increase of solids. This view is fortified by observations regarding the increase of weight of solids during the ripening of raisin grapes. It has been shown that the weight of dried grapes shows a continuous increase up to the highest degree observed, 28.75 Balling.’ 2. Sugar.—The total sugar during the growth period comprises only a small amount of the total solids. During ripening, the sugar rapidly inereases and then constitutes a much greater proportion. During ripening, the sugar curve follows the total solids curve closely. It is more or less the mirror image of the total acid curve multiplied by five, i.e., Increases as the acid decreases. 3. Total Acid and Free Acid.—During the early stages of the crowth of the berries, the acidity increases owing to an increase of free acid. This is a fact that the authors have not found mentioned in the literature. During ripening, the total and free acid rapidly decrease. After maturity is reached, the decrease is very slow. 4. Cream of Tartar—tThere is a very slow, but usually fairly defi- nite, increase in cream of tartar during ripening. This increase is very much less than the decrease in free acid, and therefore can not account for any great part of this decrease. 7 Bioletti, Frederic T., Relation of the maturity of the grapes to the quantity and quality of the raisins. Proc. Inter. Cong. of Viticulture, San Francisco, 1915, pp. 307-314. 130 University of California Publications in Agricultural Sciences [ Vol. 3 5. Protein—The protein not coagulated by heat increased defi- nitely during growth and ripening, although the increase was not so regular nor so marked as the increase in sugar or the decrease in total acid. 6. Difference Between Total Solids and Sugar.—This factor re- mained constant for the lower percentages of total solids, decreased during the rapid ripening stage, and remained constant through maturity and over-ripeness. UNIVERSITY OF CALIFORNIA PUBLICATIONS (>| IN AGRICULTURAL SCIENCES Vol. 3, No. 7, pp. 131-134 March 15, 1918 A NEW METHOD OF EXTRACTING THE SOIL SOLUTION (A Prelininary Commumeation) BY CHAS. B. LIPMAN While studying, in 1914, some of the data obtained by Quincke in measuring the forces by which thin water films are held by tiny particles of solid matter, there occurred to the writer a new possibility for a method of extracting the soil solution from soils with optimum moisture contents. By making a simple calculation, I found that if Quincke’s figures were correct, particles of .005 mm. in diameter had the power of holding very thin films of water with a force equivalent to about 300,000 lbs. to the square inch. I argued, therefore, that since particles of .005 mm. diameter constitute the ‘‘clay’’ fraction in some mechanical analysis systems and since a large part of soil material may consist of much larger particles, that it should be possible to bring to bear on soils by pressure apparatus already in existence enough force to separate soil particles from some water, even when soils contained relatively small quantities of moisture. It appeared to me, moreover, that the large machines used in engineering laboratories for testing the strength of materials should be admirably adapted to the task of expressing water from soil if suitable containers for the soil are employed. With this idea as a basis, I started, in the year above mentioned, to experiment first on peat soils with a letter press of the old fashioned sort and found that water could be obtained with it from peat containing 40% of moisture. I then proceeded to have made a special perforated brass plate for the bottom of an iron casing about 12 inches long and about 6 inches in diameter. A quan- tity of clay adobe soil with optimum moisture content was placed in 132 University of California Publications in Agricultural Sciences [Vol.3 the tube, a plate placed over it and pressure applied in a machine of a capacity of 200,000 lbs. to the square inch. About 25 ¢.¢. of liquid were thus obtained from eight pounds of soil. The result of this ex- periment was unsatisfactory, owing to the small amount of lquid obtained from a soil with an optimum moisture content. I determined, therefore, to use a tube with a much smaller diameter (1 to 2 inches), so that the pressure exerted by the machine could be concentrated on as small a surface as possible and thus rendered more efficient. When such a tube was made, other difficulties were encountered. A few months later, these were surmounted and revised forms of appa- ratus were thus prepared from time to time as other duties permitted. No form of these was satisfactory even though I had demonstrated that small amounts of the soil solution could be obtained with some of them. During the last few months, however, I have had the privi- lege of the counsel of Mr. C. T. Wiskocil of the Department of Civil Engineering of this university, who has designed a new form of pressure tube for my purposes. Such a tube was made up and we have tried it out, recently, on several occasions with gratifying results. In the ease of a very fine sandy soil containing an optimum moisture percentage (about 15% by weight), nearly two-thirds of the moisture was expressed from samples of 300 to 400 grams of moist soil. In the ease of a clay loam soil, we were not so successful, but from two or three samples of about 300 grams each of such a soil containing about 20% of moisture (by weight), we obtained enough of the soil solution to make conductivity measurements and, if needed, quanti- tative analyses. Certain difficulties were encountered in pressing the clay loam soil, which did not obtain in the ease of the fine sand, but these were also surmounted by another suggestion originating with Mr. Wiskocil. Even now we find that our apparatus needs to be changed, or a new one must be made to stand pressure in excess of 50,000 Ibs. to the square inch, so that greater efficiency in pressing clay loams and clays may be attained. The detailed description of our apparatus, and of the results of conductivity measurements and analyses of the solutions obtained are reserved for description in another paper in which due eredit will be given Mr. Wiskocil and Dr. D. D. Waynick for invaluable assistance rendered in connection with these matters. My principal object now is to direct the attention of my colleagues in soil investigations to the fact that, after nearly four years of desul- tory effort, I have succeeded in demonstrating that direct pressure ——— 1918 | Lipman: A New Method of Extracting the Soil Solution 133 can be used successfully for purposes of obtaining the soil solution as it exists in relatively thin films around the soil particles. The pro- y. With further improve- ments in apparatus which we are now planning, the method should supplant all other methods known today, including even the Morgan procedure.'| None of the other methods are really satisfactory and even that of Morgan is laborious and slow, and introduces the factor of oil, which complicates and renders it extremely time-consuming and untidy. Within recent months, I have noted in the lterature that attempts have been made by Ramann, Marz, and Bauer? and by Van Zyl® to use direct pressure as I have done. The original papers detailing the work of these investigations are not available to me, however, and I am almost entirely in the dark as to the details of the method and, in one ease, of the magnitude of the pressures em- ployed. The maximum pressure thus far exerted in my method has been approximately 53,000 Ibs. to the square inch, whereas Ramann and his associates with a hydraulic press seem to have used only about 1500 lbs. per square inch. Moreover, if the abstract of their paper which is available to me has interpreted the authors correctly, their method is only applicable to soils made up of very fine particles or containing much organic matter. My experience has always been that the coarsest soils are always the easiest to manage in expressing water from them. Indeed, until recently, the fine grained soils, as above intimated, gave me considerable trouble, because they would ereep out of the container in fine ribbons, while the pressure was being applied. Mr. Wiskocil’s suggestion of a thin casing of sand for the fine grained loam or clay loam has obviated that difficulty, how- ever. I judge from my experience, moreover, that Ramann and his coworkers must have used very wet soil or they could not possibly have secured solutions from them at the low pressure mentioned. The abstract of Van Zyl’s paper says nothing about the pressure used by him and: the manner in which it was applied. The statement is that the soil can be ‘‘squeezed.’’ Other comparisons of my method with the comparable ones just discussed will be given in a later paper. Finally, it may not be superfluous to emphasize the importance to all soil studies of the proper use of the method which I have described above. It allows of the direct determination of the concentration of cedure is rapid, clean, and of high efficiency c¢ 1 Soil Science, vol. 3, p. 531 (1917). 2 Int. Mitteil. Bodenkunde, vol. 6, p. 27 (1916), cited from Chem. Abst., vol. 11, no. 22, p. 3078 (1917). 8 Jour. Landw., vol. 64, p. 201 (1916), cited from E. 8. R., vol. 36, p. 720. 134 University of California Publications in Agricultural Sciences | Vol. 3 the soil solution, and of the amounts of each of the solutes contained therein. It renders possible, further, such studies as will clarify our vision with regard to the relations, if any, which obtain between the soil solution and soil extracts as ordinarily made. It permits us for the first time, so far as | am aware, to obtain quickly and directly large portions of the soil solution as it exists naturally under field conditions when crops are growing, and thus to correlate these solu- tions in all their qualities with the conditions of the growing crop. it may doubtless be the means of throwing much light on the methods for making nutrient solutions for growing plants, and probably also on many obseure problems in plant physiological pathology. Indeed, the possibilities are many in which the method which I have described for obtaining the soil solution can be used to the very great advantage of soil and plant studies. Transmitted March 8, 1918. Pa UNIVERSITY OF CALIFORNIA PUBLICATIONS IN AGRICULTURAL SCIENCES Vol. 3, No. 8, pp. 135-242, plates 13-24 July 12, 1918 THE CHEMICAL COMPOSITION OF THE PLANT AS FURTHER PROOF OF THE CLOSE RELA- TION BETWEEN ANTAGONISM AND CELL PERMEABILITY BY DEAN DAVID WAYNICK CONTENTS PAGE LES CU TFC) bel See ee aie ae ae Fc, eS SES Ve Ao. es ONCE ee ae tert SRR Te en Be 135 MIORUEOR. UNG TNVeSul AOI 80) 2 OA) FN LoTR ee ids Sled) ota ok a ch easteleseaien 137 eric (00 DEC VPOUS I VERUI SA CROUS 5. 5c ce beget Sai eh se snc oo etd agers 137 ET Gat BOS EN Datta e PAO MOUs ener. 22. 320nt 250.) Se eS ne Ce ew 140 EE 0 i Seacrest PNR alien so ESE” 5 5 sad eat ae mene am 144 See CreI ME LIPOUPMMCEN OL CG PU RIe GS 6 Oia 0 a me eel eee pa ao oat cewnda unde evatioaanaite 154 Beuereal Sovicow OF Oxpérimental regults 2.7 iss el 155 Seamitno wien Salts OF tle: Wen y Teele cee rs acs nenenn iene ae 156 Possible effects of variations in the concentrations of the solutions on the EDT aC ea ale BT dy Rh Pik ae tai A oO 160 Consideration of a possible Calcium-Magnesium ratio ................2--.22.--2-------------- 160 EE UOC ME CE ET eae Ore eC. ToS 2 none eee oe 162 SN alee a a dg hat re a dana Soin 164 INTRODUCTION A solution of a single salt at certain concentrations is toxic to plants grown in it. The addition of a second salt usually permits of growth superior to that in a solution of a single salt alone even though the added salt is toxic when used by itself. A third salt added may permit of a still further increase over the growth in the two salt solu- tion. Other salts added will increase or decrease growth, depending upon the salt used. Qualitative relationships only have been consid- ered. When we adjust the quantitative relationships of the various salts present, having at the same time due regard for their qualitative 136 University of California Publications in Agricultural Sciences | Vol. 3 nature, we get as a result a solution in which the plant grows and functions normally. Such a solution has been termed by Loeb, ‘‘ phy- siologically balanced.’’ It is evident that if growth is better in a two salt solution the toxic effects of the solution due to a single salt must be lessened by the presence of the second salt. We may refer to either as the second salt since either may be toxie alone. On the addition of a third salt the increase in growth over that obtained in the two salt solution points to a still further lessening of the toxie properties of the various salts present taken singly. This action of one or more salts in limiting or preventing entirely the toxic effects of one or more other salts, is termed antagonism. Sea water may be taken as an example of a physiologically balanced solution or a solution in which the mutual antagonism between the constituents of the solution is such as to allow of normal growth of numerous organisms. The fact of the existence of antagonism has been proven by a number of investigators working in plant and animal physiology, but the mechanism of antagonistic action is by no means clear. Since salts are very largely ionized in the nutrient solutions usually em- ployed, it is probable that antagonism has to do with ions. Further, antagonism will probably take place between the ions present in, or between, the ionic constituents of the solution, and the hving mem- branes in contact with the solution. Loeb!' first advanced the theory that one ion may prevent the entrance of another ion into living cells and that in this property lies the reason for antagonistic action. On the basis of this hypothesis, penetration precedes the manifestations of toxic effects and where penetration does not occur, due to antagonistic action, there are no toxie effects evident. Used in this way, the term penetration means simply the entrance of ions in greater number than would normally oeeur were the plant cells in their natural environ- ment. Experimental evidence as to the correctness of this hypothesis has been furnished by Loeb? in a very interesting series of experi- ments. Osterhout® has applied the electrical conductivity method to the measurement of the penetration of ions into plant tissue, while recently Brooks has confirmed Osterhout’s results (1) by deter- mining: the diffusion of ions through tissue,t (2) by exosmosis,® and (3) by the change in the curvature of tissue.® 1 Amer. Jour. Physiol., vol. 6 (1902), p. 411. 2 Science, n.s., vol. 36, no. 932, p. 637. 8 Ibid., vol. 35, no. 890, p. 112. 4Proec. Nat. Acad., Sci., vol. 2 (1916), p. 569. 5 Amer. Jour. Bot., vol. 3 (1916),. p. 483. 1918 | Waynick: Antagonism and Cell Permeability 137 It is evident that these methods are limited in their application and give no idea of the quantitative relationships existing between the ions actually entering the cells. They do show, however, that the permeability of the plant tissue may be greatly altered by salt action and that solutions which permit of normal growth also preserve normal permeability as regards the ions present in the solution. OBJECT OF THE INVESTIGATION In a preliminary paper’ the results obtained from chemical analy- ses of plants grown in toxie and antagonistic solutions have been reported. These results were of interest and the general method em- ployed seemed to be worthy of a more extended application in the determination of ions absorbed by plants from solutions, of known composition and coneentration. From a consideration of the data in the paper referred to above, it was felt that the results obtained in a more extensive investigation would be of importance: (1) from the standpoint of the effect of various salts upon the permeability of the cell tissue of growing plants; (2) from that of the effects of vari- ous salts upon the nutrition of plants as evidenced by growth; (3) from that of a possible correlation of growth with the absorption of ions; and (4) from the standpoint of the quantitative relationships existing between certain ions of the solution and the same ionic rela- tionships in the plant. The various phases of the problem as outlined above will be con- sidered in the discussion of the experimental results following. REVIEW OF PREvious INVESTIGATIONS It is not intended that the following review of the previous work done in this field of plant physiology be exhaustive. Robertson® has reviewed the lterature dealing with antagonistic salt action very completely up to a recent date. Brenchley® and Lipman and Gericke’® have referred to all the important work done with regard to the effects of the salts of the heavy metals upon plants. The present review therefore touches only the work bearing directly upon the 6 Ibid., p. 562. | 7 Contribution to the causes of antagonism between ions. (Univ. Calif., Master’s thesis, 1915.) 8 Ergeb. Physiol. Jahrb., vol. 10 (1910), p. 216. ’ 9Tnorganie plant poisons and stimulants. New York, Putnam, 1915 (Cam- bridge agricultural monographs). 10 Univ. Calif. Publ. Agr. Sei., vol. 1 (1917), p. 495. 138 University of California Publications in Agricultural Sciences [ Vol. 3 present problem or work so recent as not to be included in the papers cited above. A large share of the contribution to the experimental evidence in regard to antagonism between salts as regards plants we owe to Oster- hout. In a series of papers he has shown that any salt may be toxic to plants when used alone in solution at certain concentrations and further that the addition of a second salt may, in proper concentra- tion, modify or eliminate entirely the toxic effect of the first salt. He has shown further that acids, alkalies, and various organic compounds may likewise be toxic to plants and that their toxic effects may be modified by the presence of a variety of compounds, depending upon the toxic substance employed. By measuring the resistance of cylin- ders of Laminaria in solutions of one salt and in solutions containing two or more salts, he has brought forward much evidence as to the penetration of ions into plant cells. While this method has yielded very valuable results both as to the rate of entrance of ions and also the total number of ions penetrating, it does net yield results which give us a knowledge of the relative amounts of the various ions which penetrate the tissue when the qualitative as well as the quantitative relationships of the nutrient solution are varied. Osterhout has shown, however, that penetration is more rapid, and the degree of permeability is greatly increased, in unbalanced solutions and further that as the permeability of the plant tissue more nearly approaches normal the growth of the plant is also more nearly normal. Szues'! has used Cucurbita pepo as an indicator by immersing the young seedlings in various solutions for varying periods of time and counting those still able to show geotropic movement when placed in a horizontal position in a moist chamber. He found a marked antagon- ism between copper sulphate and aluminum chloride and concludes from his experiments that antagonism consists in the mutual hin- drance of similarly charged ions in entering the cell. He states further that the rate of absorption of equally charged ions is of great importance. His chemical methods are open to question, for in the experiments reported the test for copper used was that of boiling the roots and testing the resulting solution for copper with hydrogen sulphide. By analyzing the solution in which pea seedlings had grown, Pan- telli?? has determined ion absorption. The growing period was short. 11 Jahrb. Wiss. Bot. (Pringheim), vol. 52, no. 1 (1912), p. 85. 12 Ibid., p. 211. 1918 } Waynick: Antagonism and Cell Permeability 139 He found a rapid absorption of zinc, manganese, iron, and aluminum, but the total amounts taken up were small. He gives other evidence of the selective absorption of various other ions from solutions, but these results are of not direct application here. It is of interest to note, however, that he found a direct relation between time and ion absorption. His most important conclusion, which bears directly upon the problem in hand, is that strong narcosis was associated with the penetration of ions in large numbers. Schreiner and Skinner,'® using a similar method, have determined the amounts of phosphoric acid, nitrates, and potassium remaining in a solution in which plants had been grown. Various ratios of these three ions were employed, the total concentration being 80 parts per million. They found widely varying amounts of these three ions removed from the solution, and further there seemed to be a possible difference of 20 to 30 per cent in the removal of any one without an apparent effect upon the growth of the plants. Under the condi- tions reported by them increased growth was correlated with increased absorption. By means of conductivity measurements of solutions in which pea seedlings were growing, True and Bartlett** ' *° have determined the rate of absorption and of excretion of electrolytes. Their work was done with one, two and three salt solutions. In general they found a greater absorption when a mixture of salts was present than when single salts were used. Further, the absorption relationships of salts with a common kation seem to be similar. For example, from solutions of low concentrations, potassium chloride, potassium sul- phate, and potassium nitrate are not removed, but on the other hand there is an excretion of electrolytes by the plant. In direct contrast, calcium nitrate and calcium sulphate are removed from their solu- tions in every concentration employed and no exeretion of electro- lytes from the plants could be detected. It seems probable that the low concentration employed by them acted as a limiting factor in some cases. In a recent paper Breazeale’*’ has shown that the presence of sodium carbonate, and sodium sulphate, when used in concentrations of 1000 parts per million in nutrient solutions, decreased the absorp- 13 Bot. Gaz., vol. 50 (1910), p. 1. 14 Amer. Jour. Bot., vol. 2 (1915), p. 255. 15 [bid., p. 311. 16 Tbid., vol. 3 (1915), p. 47. 17 Jour. Agr. Research, vol. 7 (1916), p. 407. 140 University of California Publications in Agricultural Sciences | Vol. 3 tion of potassium and phosphoric acid as much as 70 per cent below that of the control cultures. The work of Gile*® is of interest in this connection. From ash analyses obtained in investigating the cause of chlorosis in pineapples, he found a direct relationship between the absorption of lime and that of iron; that is, when the absorption of lime was high but little iron was taken up. In soil studies Gile and Ageton’® found no direct relation between the lime content of plants and varying amounts of lime and magnesia in the soil. A few investigations have been made on the absorption of specific elements from solution, but these need only be mentioned in the present connection. Maquenne*® found that mercuric chloride causes marked increase in permeability of the protoplasm, although it is not necessarily absorbed itself in any considerable quantities. Marsh*? correlates the amount of barium chloride present in the soil with that found in the plant. Colin and De Rufz*? always found absorbed barium localized in the roots. A large number of analyses of plants grown under various condi- tions have been reported, but the environmental factors have varied so greatly as to render the results obtained of little value in the present study. From this review it is evident that no quantitative study of the elements actually absorbed from the nutrient solutions, balanced and unbalanced, has been made with the idea in mind of a correlation between the absorption of the various ions with their antagonistic or toxic effects in solution cultures. MertTHODS Barley was used as the plant indicator. The seeds were obtained from the University Farm at Davis and were of a pure strain of the Beldi variety. The method of sprouting the seeds, while simple, has not been noted elsewhere and has given such excellent results, both to the writer and to others, that it seems worthy of mention here in detail. A piece of oilcloth about 12x18 inches was covered with sev- eral thicknesses of paper toweling and the whole thoroughly wetted. 18 Porto Rico Exp. Sta. Bull., 11 (1911). 19 Tbid., Bull. 16 (1914). 20 O.-R. Acad. Sci. (Paris), vol. 123 (1896), p. 898. 21 Bot. Gaz., vol. 54 (1912), p. 250. 22 C.-R. Acad. Sci. (Paris), vol. 150 (1910), p. 1074. 1918 } Waynick: Antagonism and Cell Permeability 14] Selected seeds were distributed over the toweling so that about two hundred were placed on an area of the size indicated above. Another layer, made up of several sheets of toweling, was then laid on the seeds and the whole thoroughly soaked with water. The water was allowed to evaporate gradually until the paper was but slightly moist to the touch and the water relation then maintained constant until the seedlings were transferred to the solutions. If the paper is kept too moist the growth of molds is often very abundant, but with a low moisture content no trouble was experienced from this source. By the time the roots were a quarter of an inch long, the upper layer of paper was supported two or three inches above the seedlings. This procedure permits of a straight growth of the shoots, which is of con- siderable importance in placing the seedlings in the corks. The seed- lings were transferred when the shoots were about an inch and a half in length. The paper in which the roots are grown, tears apart readily without injuring them in any way, the oilcloth not permitting their downward penetration. There is no contact with metal containers at any time, the apparatus required is practically nothing, the time period is short—about six days under greenhouse conditions—and strong seedlings are obtained which can be transferred to any contain- ers without injury. The containers used were quart jars of the Mason type, each holding approximately 950 ¢.c. of solution. The inside of each jar, as well as that of the bottles for the stock solutions, was coated with a layer of paraffin so that the solutions were never in contact with the glass. The outside of the jar was covered with black paper to exclude light, the black surface facing the glass. Flat corks, having a diam- eter of three and a half inches, were used to support the seedlings. Each cork had seven holes, one in tlie center through which distilled water was added to maintain the volume of the solution as nearly constant as possible, and six equally spaced, one and a quarter inches from the center, for holding the seedlings. After the holes were made the corks were soaked in boiling paraffin. To introduce the seedlings the corks were turned upside down, supported by the rim of the jar, and the shoots stuck through the holes prepared for them and held in place by a small piece of cotton. On turning the corks over the seedlings were in their proper position without being in the least injured, for there was no necessity for touching the roots at any stage since the plant was always picked up by the seed coat. The method suggested by Tottingham** was tried, 142 University of California Publications in Agricultural Sciences | Vol. 3 but the one outlined above proved very satisfactory and much simpler. The basic nutrient solution used throughout was Shive’s three salt nutrient** containing the following salts in the given partial molecular concentrations: or yt oe eee 0180 M. Ce (RO re Sa i ae 0052 M. Mano, Co ek ae ne 0150 M. The stock solution was made up to twice the strength indicated above and diluted as necessary by the addition of added salt solution, or distilled water, or both. In the case of the chlorides used, viz., calcium, magnesium and potassium, normal or twice normal solutions were prepared and standardized by titrating against a standard silver nitrate solution. Normal solutions of magnesium and potassium sulphate were stand- ardized by weighing the barium sulphate precipitate. Solutions of copper, zine, iron, and mercury salts were prepared in concentrations of 1000 parts per million by weighing out the carefully dried salts. The final volume of solution required for the duplicate jars was approximately two thousand ecubie centimenters. Starting with a thousand of the nutrient solution, various volumes of the standard solutions were added so that when the total volume was made up to two liters with distilled water, the concentrations of the various salts would be those reported in the accompanying tables. The growing period was six weeks. The duplicate cultures were grown in specially constructed mouse-proof cages each holding ninety jars. The tops of the cages were open and the sides made of coarse wire screening. The different parts of the cages were equally well lighted, as shown by the nearly equal growth of the controls in dif- ferent parts of the cages. When necessary the plants were supported by cords strung across from side to side of the cages. The solutions were not changed during the growing period, but the volumes were kept as nearly constant as possible by adding dis- tilled water. There are objections to this method, as there are objec- tions to the method of using water cultures at all. The growth was found to be very satisfactory and compares favorably with the growth 23 Physiol. Researches, no. 4 (1915), p. 174. 24 Amer. Jour. Bot., vol. 2 (1915), p. 157. 1918 } Waynick: Antagonism and Cell Permeability 143 obtained by other investigators in comparable periods of time. A further discussion of this point will be taken up below. At the expiration of the six weeks growing period the plants were removed from the corks, the roots rinsed thoroughly with dis- tilled water, placed between layers of paper toweling, dried in the oven at 100°-105°C, roots and tops separated, weighed, and placed in envelopes ready for analysis. For analysis the roots from dupli- eate cultures were combined unless the dry weight was sufficient to allow of separate analysis. Total ash was determined after direct ignition of the dry material in a muffle at a low red heat until no trace of carbon remained. The ash was then taken up in dilute hydrochloric acid and evaporated to dryness to remove possible contamination with silica. Iron was precipitated as the hydroxide with ammonia and titrated with = potassium permanganate after reduction with zine and sulphurie acid. This determination was made because of the relation Gile has shown to exist between calcium and iron absorption by plants. Calcium was precipitated as oxalate and titrated with = potassium perman- ganate. The double precipitation of the oxalate assured freedom from magnesium contamination. Magnesium was precipitated by ammonium phosphate and weighed as the pyrophosphate. Potassium, where determined, was precipitated and weighed as the chloroplati- nate. Copper was determined colorometrically by using the ferro- eyanide method. The amount of material available precluded the possibility of a more complete analysis than was made if any degree of accuracy was desired. For example, in Series vu, the weight of the ash varied from 12 to 233 milligrams in the ease of the roots and from 32 to 183 milligrams in the case of the tops. While these varia- tions are not extreme, they are fairly representative. The values of these elements actually determined cannot be taken as absolute in every case because of the limited amounts of material available, but the significant differences are so great as to make a small variation in this regard of minor importance. The strength of all solutions is uniformly expressed in terms of molecular concentrations since this mode of expression has been quite generally used in experimental work reported by different investigators. Under experimental results twenty-six series are reported. A series, as used in the present work, may be defined as a number of 144 University of California Publications in Agricultural Sciences | Vol. 3 duplicate cultures containing one salt in varying concentrations in each, or one salt constant and varying concentrations of a second salt. In some instances both salts varied but only in concentration, the same ratios being maintained. These are few. The number of con- centrations reported vary from three to fourteen in a series, depend- ing upon the salt used. Before two salts were taken together, the effects of each separately upon the plants were determined. Usually this meant only the establishment of the toxic limits of the salts em- ployed when used in the nutrient solution. Several series of this kind are not reported here, as no analytical work was done upon them. Calcium and magnesium salts were used to a large extent because of the fact that their kations can be determined with less experi- mental error than most other nutrient salts where the small amounts of material dealt with here are considered; also it was of interest to determine whether or not there is a lime-magnesia ratio for plants grown under carefully controlled conditions. Copper, zinc, iron, and mercury salts were used because of the fact that their toxic and antag- onistie effects have not been previously determined as regards absorp- tion. Potassium chloride was the only monovalent salt used. A longer growing period than has usually been employed was con- sidered important. McGowan,”° in conducting experiments in pure solutions of sodium, potassium and ealecium chlorides, found growth better in the first two at the end of six days, but far superior in a solution of calcium chloride in twenty-five days. In a qualitative way the same relationships were observed in the present investigation. It seems reasonable to assume that the results obtained in six weeks with plants are more nearly representative of the true effect of various solutions than those obtained in two or three day periods or even in three week periods. But it is not assumed that the results herein reported are the same as those which might be obtained were the plants grown to maturity. It is hoped that more data may be pre- sented shortly on this point. In the following section, in which the experimental results are given, the time factor and the basic nutrient solutions are constants. EXPERIMENTAL DATA All analyses are reported as percentages of the dry weights of the plants. To make the results obtained as clear as possible, graphs and photographs have been used throughout as well as the tables giving the actual percentage composition of the plants. 25 Bot. Gaz., vol. 45 (1908), p. 45. 1918] Waynick: Antagonism and Cell Permeability 145 The relationships of calcium to magnesium salts are reported in the first seven tables. For a review of the more important literature bearing directly upon the relationships of the salts to these two ele- ments reference is made to MeCool,*° who has considered these in some detail, and to a recent critical survey of the lime-magnesia ratio hypothesis by Lipman.** As is evident from table 1, calcium chloride does not become toxic until present in concentration of over .24 M. Up to and including this concentration the growth seems to be but little affected by the increasing concentrations of the salt added. The percentage of cal- cium in the plants shows no direct increase with increasing concen- tration of calcium chloride in the solution. The lowest percentage of calcium given occurs in a concentration of .20 M. calcium chloride. In table 2 there is a close parallelism between the growth of roots and tops. Two low points on the dry weight graph are evident, the first occurring at cultures 4 and 5 and the second from 7 to 11. At these low points we have a high percentage of magnesium in both roots and tops, but of calcium only in the second low point. Calcium is low where growth is good in cultures 2 and 3. But the most inter- esting feature is the decreased absorption of both elements at cul- ture 6, where there is a distinct increase in dry weight. [ron was not present in sufficient concentration to allow of titration until cul- ture 11 is reached. It may be stated here that the iron determined is limited to that in the seed as a maximum, for it was purposely ex- eluded from the solutions except where its toxic or antagonistic action was under observation. In many instances the titration of this residual iron is of interest. Table 3 is a record of one of the most interesting and significant series reported. The root growth was so limited in nearly every cul- ture that no attempt was made to segregate roots from tops for sep- arate determinations except where the total dry weight was so greatly increased as in cultures 6 and 11. In the first place we have double maxima of growth, the first in culture 6 and the second in 11. The total dry weight at culture 11 is twice that at 6, but the dry weight in culture 6 amounts to a 35 per cent increase over that in culture 7. A direct inverse relationship is shown between -total growth and ab- sorption at these two high points; the maximum growth in culture 11 is accompanied by the lowest absorption of calcium and magnesium. The percentage of magnesium is low in culture 6, but that of calcium 26 Cornell Univ. Agr. Exp. Sta. Mem. 2 (1913), p. 127. 27 Plant world, vol. 19 (1916), p. 83. 146 University of California Publications in Agricultural Sciences | Vol. 3 is higher than in the cultures of slightly higher or lower concentra- tions. No explanation of the narrow ratio between these two ele- ments at this point can be offered. It is of interest to note the very ereat increase in the amounts of calcium and magnesium found in the plants grown in concentrations of .20 M. calcium chloride alone. While magnesium chloride is constant throughout the series, the amount of magnesium does not increase proportionately to that of calcium. A still higher concentration of magnesium chloride was used in the series reported in table 4. The percentage of magnesium found in the roots is very high and would indicate that it was not entirely removed from the roots by washing. In general the percentages of calcium and magnesium found are high, the calcium content increas- ing as the concentration of calcium chloride present in the culture, but not proportionately. Magnesium is lower at the greater dry weights for the tops, the decrease amounting to 50 per cent in the case of culture 6. Magnesium sulphate was used alone in the series reported in table 5. The decrease in growth is nearly proportional to the increase in concentration of the added salt. In this series we have a very marked decrease in the percentages of calcium and magnesium present in the roots without any evident effect upon the growth of the plants, especially that of the tops. Here again, however, we have increased absorption of calcium as the percentage of magnesium increases, even though the concentration of the former in the nutrient solution is constant. It is of interest to note that the percentages of both ele- ments in the tops throughout this series are low and vary but little, regardless of the increasing concentration of the nutrient solution. Very marked antagonism between calcium chloride and magnesium sulphate is shown in table 6. The dry weight of the plants grown in a solution of magnesium sulphate .18 M. concentration was .29 gram, but when .04 M. concentration of calcium chloride was added the aver- age dry weight was 1.20 grams and in a concentration of .18 M. magnesium sulphate and .24 M. ealecium chloride the average dry weight was .98 gram. Between these two concentrations of calcium chloride the dry weights recorded are uniformly high. Correlated with the rapid decrease in growth, in concentrations of .24 M. of cal- cium chloride, is the marked increase in the percentage of both calcium and magnesium found in the plants. The graphs representing the amounts of these elements found crosses the growth graph coincident 1918 | Waynick: Antagonism and Cell Permeability 147 with its sharp decline. The low percentage of magnesium is of interest since the concentration of the culture solution was uniformly high with respect to this ion. It is striking that there is a marked decrease in the growth of roots at the concentration which gave the best growth of tops, and further that the percentage of calcium in the tops and magnesium in the roots parallel this decrease in the growth of the roots. A comparison of the results obtained with magnesium sulphate as against those with magnesium chloride is reserved for later discussion. In table 7 we have an opportunity to compare indirectly anion effects, or possibly the effects of combinations of the same kation with different anions. From preliminary results it seemed advisable to use .15 M. magnesium sulphate in this series instead of .18 M. as used in the preceding series, so that the concentration of magnesium ion is not equivalent in the two series. A solution containing magnesium sulphate .15 M. plus calcium nitrate .08 M. proved highly toxic, while a solution containing calcium chloride of the same concentration as the nitrate in the above solution supported normal growth. It is possible that the difference is due to the toxic action of the nitrate ion on the plant directly. Tottingham has shown that the total ionization of a nutrient solution was decreased 10 per cent below the theoretical by the addition of calcium nitrate in low concentrations. It is pos- sible that the ionization of some other salt is repressed so that there is an actual lack of some ion necessary for growth. The percentage of calcium found was not high enough in any case to account for the toxic effects shown. Magnesium was found in extremely large amounts, 9.20 per cent in the case of culture 6, the largest percentage recorded in any culture studied. Unfortunately the series in which the toxic effects of calcium nitrate alone were studied was lost, so it cannot be reported here. Potassium chloride was the only monovalent salt studied, and the results are given in tables 8 and 9. The growth shown in the various concentrations of potassium chloride used was approximately the same as that found when magnesium sulphate was used alone. The increase in the percentage of ash, as far as the tops are concerned in table 8 is very striking. The percentage of calcium found in the tops and of magnesium found in the roots remains practically constant throughout. The amount of potassium absorbed increases as the con- centration of potassium chloride in the solution increases and in- versely as the growth of the plants. The toxic effects due to the 148 University of California Publications in Agricultural Sciences | Vol. 3 addition of potassium chloride to the solution are much more evident in the tops than in the roots with respect to the increasing concen- trations of potassium chloride. Using a constant concentration of potassium chloride of .18 M., which is an increase of .02 M. over the highest concentration of that salt reported in table 8, against varying concentrations of magnesium sulphate, the results reported in table 9 were obtained. There is a marked increase in total ash as the concentration of the nutrient solu- tion with respect to magnesium sulphate increases. Parallel with this increase is the higher percentage of potassium. The growth decreases inversely. Antagonism between the two salts is evident where the lower concentrations of magnesium sulphate were used. In cultures 2 and 4 of this series, we have a marked increase in growth over that of culture 3. Absorption is markedly lower at the two high points than at the intermediate concentration, where the solution is evidently more toxic. The least growth obtained in the series was recorded in culture 7, which shows the highest absorption of all the elements determined. In the two higher concentrations of magnesium sulphate used the growth was increased somewhat while the percentage of cal- clum, magnesium, and potassium in the plants decreased markedly. It seems worthy of note that the amount of iron in the ash was not sufficient to allow of titration at any concentration employed in the series. This series very well illustrates the point which has been brought out a number of times before of the relationship between absorption and growth. Here we have five cultures in the one series of which this relationship is evident. The relations are not absolute in every instance, but there can be no doubt whatever of the tendeney toward decreased absorption as growth increases, or that antagonism between ions results in decreased absorption of at least some of the ions present in the nutrient solution. We turn now to a consideration of the effects of a few of the salts of the heavy metals upon growth and absorption. In table 10 the effects of adding various concentrations of aluminum chloride are shown. Growth is decreased in every concentration of the salt used. The high percentage of magnesium is marked in both roots and tops. On the other hand, the percentage of calcium is increased relatively little. The percentage of iron found was practically constant and in total quantity is in marked contrast to the last series considered in which the amount was so small that it could not be determined. In a solution of .20 M. ealeium chloride, the results with the vary- 1918 | Waynick: Antagonism and Cell Permeability 149 ing concentrations of aluminum chloride are shown in table 11. In general the toxie effects of the two salts seem to be additive, that is, the growth in this series in which two salts are present together is less than in the preceding series where aluminum chloride was used alone. The decrease is not great from the standpoint of total weight, but proportionately is very considerable, amounting to from 33 per eent to 100 per cent in the various concentrations employed. The percentage of magnesium in the two series is about the same. The amount of ealeium absorbed, on the other hand, is increased over 300 per cent and remains constant throughout. The total absorption with respect to calcium and magnesium, at least, is uniformly high. This fact is reflected in the increase in the percentage of ash over that of the control. In the next series all factors are the same except that magnesium chloride was used instead of calcium chloride, there being no difference whatever in partial or total concentration. The antag- onism shown between magnesium chloride and aluminum chloride in culture 4 is very marked, and correlated with the increased growth is the marked decrease in the percentage of both magnesium and cal- cium found in tops and roots. The percentage of magnesium found in the plants is not proportional to the concentration in the solution as was true with calcium chloride. An interesting case of the in- creased absorption of one element with a decrease in the other is well illustrated in the case of culture 6 of this series. Such a relationship has been noted previously, but is apparently of no direct importance from the standpoint of growth. Ferric chloride, a second trivalent salt, was used in the nutrient solution in the concentration shown in table 13. In the concentration employed, growth is nearly normal and absorption is very nearly the same as with plants in the control cultures, except in the case of cal- cium. The decrease in some instances in the percentage of calcium found, as iron increases in the nutrient solution, is notable, and will be referred to later in connection with the action of ferric and zine sulphates. The effects of adding .20 M. calcium chloride, together with vari- ous concentrations of ferric chloride, are given in table 14. The growth of roots and top parallel each other closely. Marked toxic effects are evident in certain combinations as in cultures 3 and 7. The percentage of calcium found in both roots and tops is high in plants grown in the same cultures. The magnesium present in the tops shows the same relationships as the calcium, although the 150 University of California Publications in Agricultural Sciences Vol. 3 y amount absorbed varies but little from that of the control. In the roots magnesium is present in large amount when growth is low in culture 2, but in succeeding cultures the percentage found falls off sharply and remains abnormally low without any relation to growth or concentration of the solution. The percentage of iron is high in cultures 6 and 7, in which the weight of the plants was small. Substituting magnesium chloride in equivalent concentration for the calcium chloride used in the preceding series, the results are of a very different order from those in table 15. The absolute growth of the tops is greater than in series 14. Root growth does not parallel the growth of the tops. The toxicity of the solution is searcely evident at some concentrations while markedly increased at others. Absorp- tion, with the exception of the magnesium in the roots, is usually low, amounting to about that of the control, but the percentages of calcium and magnesium found bear no apparent relation to the differences in erowth. Iron, however, shows the inverse relation already noted in many other series with calcium and magnesium, that is, high percent- age present when growth is low, and vice versa. The toxic and antag- onistie effects as well may be due in this instance to the ferric ion, but this statement is by no means indisputable. In several tables following, the effects of copper salts are given. Previously copper salts have been shown to be highly toxie to plants as well as to a wide variety of vegetative forms. That they may also be stimulating has been shown recently by Forbes** using solution cultures, and by Lipman and Gericke” in soil cultures. The reader is referred to the latter paper for an extensive review of the subject. The results with copper chloride are reported in table 16. Growth, especially that of the roots, was limited in every concentration re- ported. In fact, the growth of the roots was so limited that their weights are not given. There is a suggestion of antagonistic action between the nutrient solution and copper chloride in cultures 3 and 5. The percentage of magnesium found is high where growth is low. The same is not true of calcium, the percentage of which is low and decreases as growth decreases to a certain extent. A trace of copper was found in every case and appreciable amounts had penetrated the plant tissue at the two higher concentrations. When ferric chloride is added together with copper chloride marked antagonism is shown. Table 17 will make this effect evident. In this series, as in 28 Univ. Calif. Publ. Agr. Sei., vol. 1 (1917), p. 395. 29 Tbid., p. 495. 1918 | Waynick: Antagonism and Cell Permeability 151 several following, the concentrations of both salts added increase, that is, both increasing but bearing the same ratio between the two. There is an increase of approximately 100 per cent in the dry weight of culture 2 over cultures 1 and 3. The low absorption of culture 2 as related to 1 and 38 is evident. There is a marked decrease in the percentages of calcium and magnesium found in the plants grown in culture 5, in which the dry weight of the plants was also low. At this second point, however, iron and copper were found in larger amounts than at any other concentration used. As in the previous series the percentage of calcium in the tops does not seem to parallel that in the roots or of magnesium in either roots or tops. Kearney and Cameron,® and Ostwald*’, for a discus- sion of the various factors which may be of importance in this con- nection. The recent work of Clowes** and Fenn*® is important and some very striking similarities between the action of toxic and antagonistic solutions on oil emulsions and on gelatine on the one hand, and plant cells on the other, have been reported by these investigators. 46 Porto Rico Exp. Sta., Bull. 12 (1912). 47 Jour. Agr. Research, vol. 6 (1916), p. 589. 48 Plant World, vol. 19 (1916), p. 331. 49 Bot. Gaz., vol. 33 (1902), p. 26. 50 Archiv. ges. Physiol., vol. 88 (1902), p. 68. 51 Science, n.s., vol. 35 (1912), p. 112. 52 Flora, vol. 75 (1892), p. 368. 53 Zeitschr. Hygiene u. Infektionskrankheiten, vol. 25 (1897), p. 1. 54 Bull. Torr. Bot. Club, vol. 30 (1903), p. 390. 55 U. S. Dept. Agr., Bull. 231, 1912. 56 U. S. Dept. Agr., Bull. 71, 1902. 57 Archiv. ges. Physiol., vol. 120 (1907), p. 19. 58 Jour. Phys. Chem., vol. 20 (1916), p. 407. 59 Proce. Nat. Acad. Sci., vol. 2 (1916), p. 539. 1918 | Waynick: Antagonism and Cell Permeability 163 To define normal permeability is very difficult. There seems to be a comparatively wide range of concentration of salts over which the amount of any element taken up may vary without affecting the growth of the plant to any considerable extent. There is lkewise a wide range over which the ratio of any one element to any other may change without being detrimental to plant growth. The latter point has been discussed above in connection with a possible optimum calcium-magnesium ratio for plants. The first point referred to has been very well treated by Gile and Ageton,®® so that further reference need not be given here. For the work in hand the percentage composition of the plants grown in the control cultures seemed to be the most logical criterion of normal permeability available. There are variations between the controls as regards composition, but they are relatively small. On the other hand, the percentages of magnesium, for instance, range from .02 per cent to 9.21 per cent, depending upon the solution used. The percentages of calcium differ over a wide range as well. From the data presented there can be no doubt whatever that the composi- tion of the plant, as regards inorganic constituents at least, may be altered enormously by variations in the surrounding solution. That portion of the root system in any plant which functions as a semipermeable membrane is obviously of greatest importance in a study of the present kind. The actual area of the membrane which is in contact with the solution must be known in every case before it ean be said that the permeability of one root system is greater than that of another. The actual area of the plasma membrane cannot be measured directly because, in the first place, we have no means of determining just how much of the root is involved, and secondly, the area concerned may be changing continually. Length of the roots and their number and length together as well as green weight and dry weight have been taken as criteria of the existence of antagonism. In the present paper the dry weight has been taken as proportional to the area of the plasma membrane through which salts may enter the plant. It cannot be stated defi- nitely that the two are proportional. They have only been so con- sidered since the dry weight of the plant was the most logical criterion to employ. The reservation must always be made that the two may not be directly proportional, even though they are treated as being so. That the permeability of the plasma membrane of the plant cells 60 Porto Rico Agr. Exp. Sta. Bull. 16, 1914. 164 University of California Publications in Agricultural Sciences | Vol. 3 is changed by the nature and balance of the solution surrounding the roots there can be no doubt from the data already given. That a number of ions are capable of acting in a very similar manner to one another as regards permeability is also evident from the present work. Further, the same salt may act differently at different concentrations, preserving nearly normal permeability at some and allowing the pene- tration of large numbers of ions at others. As previously stated, the total balance of the solution is of vital importance in the preservation of normal permeability, which is in turn correlated with normal crowth. In connection with the salts of the heavy metals, the amounts of the kation of cupric and ferric salts which had penetrated the plant tissue were determined in a number of instances. The percentages found were low. Further, whenever these salts proved toxic, the amounts of calcium and magnesium found in the plants were high; high enough in fact to account for the toxic effect alone. In many instances the percentages of those two elements found were as high in toxie solutions of copper, iron, or zine salts as when toxic concentra- tions of calcium or magnesium chlorides were used. We might, therefore, in the light of our present knowledge, be justified in attrib- uting the decreased growth of the plants to the abnormally high ab- sorption of calcium and magnesium and the consequent reactions taking place within the plant cells. The permeability of the mem- brane must be altered to allow of the presence of these ions in large numbers. The toxic effects due to the presence of large amounts of calcium or magnesium salts might be evident if we could inject solu- tions of these salts into the plant without altering the permeability of the plasma membrane. But from the present data it seems that the alteration in the permeability of the membrane is the essential consideration. It is probable also that the toxicity of any solution is accompanied by the increased permeability of the plant tissue to all inorganic salts which are normally found in plants. There may be exceptions as noted already for iron and calcium, but in general this relation holds from the data now at hand. | Ruprecht® has localized the effects of aluminum salts in the few layers of cells surrounding the root hairs and attributes the death of the plants grown in solutions of aluminum salts to starvation incident upon the inability of the plant to obtain nutrient salts for normal 61 Mass. Exp. Sta. Bull. 161 (1915), p. 125. 1918 | Waynick: Antagonism and Cell Permeability 165 metabolism. Forbes** has likewise localized the effects of copper salts, when present in toxie concentrations, and concludes that the toxic effect of copper is due to the combination of metal with protein at the growing tips of the roots. From the experimental results given in the present paper, it is evident that the presence of the salts of each element in toxic concen- tration results in an increased permeability of the plant tissues to calcium and magnesium at least. Ruprecht’s view that plants starve for lack of nutrient salts when grown in toxic solutions is untenable, in the hght of the above discussion. The results of both investigators are significant in indicating the localization of the effect of the two metals studied in the extreme outer portion of the roots, in which the plasma membrane is located. The results obtained by Loeb with Fundulus eggs, by Osterhout with Laminaria, using electrical conductivity methods, and by Brooks employing microscopical methods with various plant tissues, all point to the preservation of normal permeability as the result of antago- nistic salt action. The results reported by these investigators using widely different methods have been confirmed in the present work by the use of a more direct and more nearly quantitative method than any hitherto employed. It must be recognized, however, that a picture of but one stage in the growth of the plant has been given and that only a portion of the inorganic constituents have been determined. The results reported are essentially those of a static system and must be so considered in comparing them with results obtained by the use of other methods referred to above. SUMMARY In the present paper results are given showing the effect of vari- ous salt solutions upon the chemical composition of plants, with spe- cial reference to a correlation between toxic and antagonistic effects and composition. A uniform nutrient solution was used throughout. The cultures were arranged in series in which the concentration of one salt was kept constant while the concentration of a second salt varied over a wide range. In several series the concentration of both varied, but the ratio between the two remained constant. The ana- lytical data cover the percentages of calcium and magnesium found in the plants grown in every culture, together with determinations 62 Univ. Cal. Publ. Agr. Sci., vol. 1 (1917), p. 395. 166 University of California Publications in Agricultural Sciences | Vol. 3 of potassium, iron and copper in certain series. With these facts in mind the results of the investigation may be briefly stated as follows: The composition of the plants grown in different solutions varied widely. Normal growth, i.e., approximately that of the controls, was always accompanied by approximately equal percentages of calcium and magnesium in the plants. In nearly all cases in which the growth of the plants was decreased to a marked extent, the amounts of. the two elements referred to above were increased greatly. The degree of absorption of any salt seems to be independent of the concentration present in the solution over a wide range. Certain relationships are pointed out between calcium and mag- nesium absorption and the presence of iron and zine salts in the solution. Antagonism as evidenced by growth is correlated with absorption of the ions, which were determined, in every instance. Stimulation of growth was recorded when ferric sulphate was present in the nutrient solution in certain concentrations and with ferric sulphate and zine sulphate together. The amounts of the two ions uniformly determined were not neces- sarily found in the same proportions in roots and tops. The possible effects of changes in concentrations of the various solutions are considered, and the conclusion reached that the changes in concentration were of secondary importance over the range of con- centrations of the various salts used. Data are presented showing that growth is the same with widely varying ratios of calcium to magnesium in the nutrient solution. The results in general confirm those of Loeb, Osterhout, and Brooks in finding that antagonistic salt action tends toward the preservation of normal permeability of the plasma membrane in living tissue. This problem was suggested by Dr. C. B. Lipman. The writer wishes to express his thanks for this and for many other valuable suggestions offered while the work was in progress. The writer is also indebted to Prof. L. T. Sharp for helpful advice. 1918] Waynick: Antagonism and Cell Permeability 167 NOTE The following key applies to ail the graphs. The numbers on the abscissas represent both the actual weight of tops and roots and percentages of calcium and magnesium, or of iron, when the latter were plotted. The numbers on the ordinates correspond to the number of cultures as given in the table on the opposite page. The heavy lines always refer to the roots, the light lines to the tops. The following type lines are used: — —_ (Solid line) Weight of tops. — — er (Short dashes) Weight of roots. —————— ——— —— — — — (Long dashes) Percentage of calcium. —— — — (One long and two short dashes) Percentage of magnesium. —— — (One long and one short dash) Percentage of iron. The numbers given in the ‘‘Explanation of Plates’’ always refer to the plants arranged in order from left to right, the control being on the extreme right in every case. ox N oO 10 11 12 Full Nutrient Tops 0. 168 Solution CaCl. .002 .004 01 04 .06 .08 10 16 .20 24 Dry weight Tops .7633 .7104 Roots. Tops 3608 .6486 4976 Roots Tops .6555 .6419 .6138 Roots Tops 5628 4814 .6600 Roots Tops 5750 5950 5442 Roots Tops 5959 "5692 4998 Roots Tops 5048 .6706 5015 Roots Tops 5250 .6114 .4182 Roots Tops .3827 4832 4778 Roots Tops 3918 5668 5218 Roots Tops .6123 687 -7637 Roots Tops 6305 5266 5793 Roots .6067 .7937 .7418 Roots .6900 Grown October 24—December 5, 1915. Mean .7368 1804 731 3277 .6279 .2814 5707 .2875 5696 .2979 5845 .2524 860 2625 5148 1913 4805 1959 5443 3066 .6662 3154 5529 3033 7677 3450 TABLE 1 Calcium Chloride Percentage of Ash 15.38 15.34 26.24 15.34 17.34 29.98 17.29 16.81 28.10 16.80 17.69 31.56 17.52 16.59 33.54 17.67 17.00 29.45 13.92 11.82 29.46 18.46 19.94 30.18 16.80 17.15 29.12 17.45 18.47 29.43 17.03 17.13 31.82 17.62 17.34 27.08 18.80 19.10 20.03 Mean 15.36 16.34 17.05 17.24 17.05 17.33 12.87 19.20 16.97 17.08 17.48 18.95 i» Percentage of Ca University of California Publications in Agricultural Sciences Mean ATT 435 O15 ATT .602 715 545 434 434 436 .368 373 391 Percentage of Mg | Vol. 3 Mean .049 .086 .045 .046 .069 057 .064 962 1.32 320 226 218 1918] Waynick : Antagonism and Cell Permeability 169 Fig. 1 Caleium Chloride (See Table 1) No. | 10 11 13 University of California Publications in Agricultural Sciences Solution MgCl, CaCl, 24 .004 24 01 24 .02 24 04 24 .06 24 .08 24 10 24 12 24 16 24 20 24 24 24 30 24 TABLE 2 Magnesium Chloride + Caleium Chloride Dry Weight Tops Roots Tops Roots Tops Roots Tops Roots Tops Roots Tops Roots Tops Roots Tops Roots Tops Roots Tops Roots Tops Roots Tops Roots Tops Roots 3407 .3666 2456 5106 0862 3038 .2758 0885 2533 4450 4828 .3018 3150 3716 2994 6871 .6679 4238 A797 4476 .3000 4583 4279 .2843 .3243 3543 .2276 3404 3132 .2508 .2707 2924 2107 4834 0226 3888 4281 106 .2463 Grown a x v a 3536 1218 5484 1519 4321 .1266 4619 1509 3433 .1497 6775 .2119 4636 1500 4431 1421 .3393 1138 3268 1254 .2815 1053 5030 1944 4693 1231 Percentage of Ash Mean 12.95 16.86 15.58 16.92 18.18 15.97 14.99 16.81 15.29 17.06 18.18 18.06 17.02 Percentage of Ca O85 437 387 383 .208 Mean 491 197 339 * 163 457 1.46 O74 385 January 2—-February 13, 1916. =" i) for) ee — Percentage of Mg bo — Mean 1.16 .918 943 .440 .650 1.52 1.83 816 .691 .898 [ Vol. 3 Percentage of Fe Mean 012 .012 .015 -1 1918 | Waynick: Antagonism and Cell Permeability 171 \ a ; ae INV Za . het a ma 6" Ca Free a roa -— 7 cee a= Pasi ers Sa Cane ay oe oF ata 4 les ae oe or ae oe are a as Sa, Se, - | | ! | | | I | | ! | 1 2 3 4 5 6 a 8 9 10 jib 12 Fig. 2 Magnesium Chloride + Calcium Chloride (See Table 2) University of California Publications in Agricultural Sciences 172 Solution No. MgCl. CaCl, l .30 001 2 .30 002 3 30 004 4 .30 01 5 .30 02 6 .30 .04 7 30 .06 8 30 .O8 9 30 10 10 .30 12 11 .30 16 12 30 .20 13 30 24 14 30 .30 Full Nutrient TABLE 3 Magnesium Sulphate + Calcium Chloride Dry Weight Tops Roots Tops Roots Tops Roots Tops Roots Tops Roots Tops Roots Tops Roots Tops Roots Tops Roots Tops Roots Tops Roots Tops Roots Tops Roots Tops Roots Tops Roots 1986 .2650 2700 .2766 2566 2236 3194 1744 2074 .2249 5249 4166 .1309 3036 1836 .0850 .2184 2403 .0648 3978 .3842 2759 1059 8819 9600 6900 .2100 .2700 .2576 .1930 .2600 .2000 .7937 .7418 .6900 Mean 2318 .2300 .7677 3450 Percentage of Ash 16.60 15.60 16.44 16.39 18.43 17.39 16.49 14.28 14.56 15.73 15.19 15.57 18.10 16.83 17.42 14.70 17.90 15.99 13.05 30.08 17.92 19.57 27.29 17.41 18.11 33.71 18.80 19.10 20.03 16.94 15.40 14.30 18.95 Percentage of Ca Grown October 24 to December 5, 1915. Mean .209 526 409 025 398 160 [Vol. 3 Percentage of Mg ei g = 440 413 426 571 O14 42 595 533 564 O15 .088 O15 749 565 .607 405 437 .418 649 .790 719 700 .663 681 .230 1.15 1.15 399 63 481 124 .047 .037 .042 .047 3.660 4,210 3.799 235 202 218 .259 1918] Waynick: Antagonism and Cell Permeability 173 me | \ \ \ \ read vl Fig. 3 Magnesium Chloride + Calcium Chloride (See Table 3) 174 Solution No. MgCl CaCl 1 36 .02 2 36 .04 3 36 .06 + 36 .08 5 36 10 6 36 12 7 36 16 8 36 .20 9 36 24 Full Nutrient University of California Publications in Agricultural Sciences TABLE 4 Magnesium Chloride + Calcium Chloride Tops Roots Tops Roots Tops Roots Tops Roots Tops Roots Tops Roots Tops Roots Tops Roots Tops Roots Tops Roots Dry Weight .2878 3189 1644 .4128 0210 3144 .2952 .2640 .1560 .1878 2034 .0684 2292 .1698 1272 4788 3938 .2244 3616 .4410 2287 .2963 .2505 .1355 3100 .2106 1734 .7819 .7459 .6209 = Percentage of Ash TN = So = Ge me e bo Or bo bd = —_ oS cn bo cor Cr Ol 20. 16.31 17.21 17.90 18.10 .2400 17.80 15.13 16.20 17.90 14.60 13.65 17.60 14,12 15.17 16.00 13.21 12.17 16.99 14.21 13.17 14.20 20.40 19.70 21.70 Mean 17.68 21.05 15.66 14.64 12.69 13.69 20.05 Percentage of Ca 330 .242 398 461 400 O73 721 787 1.03 339 Grown January 7—February 21, 1916. ge of Mg ~] _ - - Percenta to mH oe — jt co © Oo © 1.24 2.14 2.37 3.00 2.22 2.48 4.43 2.90 2.61 4.71 890 1.02 3.33 1.23 1.72 2.47 2.01 2.32 4.82 2.31 3.02 4.89 .223 .268 .248 Mean 1.94 2.25 2.35 2.75 1.47 2.16 2.66 295 [Vol.3 Percentage of Fe .039 .047 Mean 043 1918] Waynick: Antagonism and Cell Permeability Fig. 4 Magnesium Chloride + Calcium Chloride (See Table 4) 176 University of California Publications in Agricultural Sciences [ Vol. 3 TABLE 5 Magnesium Sulphate a Es ey Solution : 3 oe 5 Be 3 Ee E No. MgSO, Dry Weight = Wi = Ay = Vi = 1 .06 Tops .7326 16.78 358 785 .7838 .7587 16.46 16.62 379 .368 .750 767 Roots .6383 3191 16.84 495 550 2 10 Tops .7150 15.73 .302 .320 .9420 8276 16.21 15.97 313 .307 320 320 Roots .4822 2411 22.91 80 1.270 3 14 Tops .6888 15.09 .201 350 6546 .6717 15.64 15.36 .230 215 .390 370 Roots .4437 2218 20.31 148 740 4 16 Tops .3042 12.65 337 350 .3657 .3349 11.81 12.23 331 334 310 .330 Roots .0762 .0381 21.52 985 me A 5 18 Tops .2875 12.32 496 .280 .2978 .2926 12.72 12.52 371 434 310 295 Roots .0542 .0271 20.49 1.130 1.300 Full Nutrient Tops .7819 20.40 349 , 223 .7459 .7639 19.70 20.05 330 339 .268 295 Roots .6209 21.70 242 .248 Grown December 9—January 20, 1915-16 1918] Waynick: Fig. 5 Magnesium Sulphate (See Table 5) Antagonism and Cell Permeability 178 University of California Publications in Agricultural Sciences [ Vol. 3 TABLE 6 Magnesium Chloride + Calcium Chloride ae Be Ete Ec Solution EES a 2 < “ 50 4 he e oe é ry Wei = v ‘S oS o's No. CaCl MgSO, ee s a © = a, ° s 5° © &° a 1 04 18 Tops 1.1626 19.91 261 A407 036 1.2526 1.2076 19.75 19.83 .3832 .296 .722 .564 .023 .080 Roots .9895 .4942 16.52 .030 1312 017 2 .O8 18 Tops 1.1888 20.43 12 O77 .060 1.0948 1.1418 21.15 20.79 .377 .844 .084 .081° .060 .060 Roots .9037 .4518 26.13 151 .180 .020 3 12 18 Tops 1.1287 19.50 275 021 .024 1.2691 1.1989 21.22 2036 .276 .275 .023 .022 .021 .023 Roots .9591 .4795 20.93 560 185 .020 4 .16 18 Tops 1.2293 17.85 .169 .035 .036 31.9134 12218 16.75 17.30 131 250 .049 .042 —— .036 Roots .5444 .2722 16.47 .690 101 .024 5 .20 18 Tops 1.1786 21.67 .333 .039 .033 1.1021 1.1403 21.07 21.387 .256 .294 .044 .041 ...... .033 Roots 1.0500 .5250 25.40 .820 299 .028 6 24 18 Tops .9773 21.47 448 462 . 045 9923 .9848 21.65 21.56 .545 .496 .486 .470 .033 .039 Roots .8600 .4300 26.07 1.290 407 .024 7 28 18 Tops .8459 18.62 A76 437 .032 .7450 .7954 20.05 19.33 .523 .499 .409 .420 .037 .035 Roots .6014 3007 24.87 1.580 565 .023 8 oa 18 Tops .4608 21.43 .640 1.05 .027 wale 4968) 2.22: 21.43 .5568 .604 1.24 114 1.019 .023 Roots .3350 .1675 29.00 3.330 1.07 .026 9 36 18 Tops .1916 18.56 TAT 1.43 .048 2349 .2132 18.80 18.68 .955 .851 1.59 1.50 .049 047 Roots .0976 .0488 18.05 1.000 2.80 2269, .1819 13.60 13.50 .235 370 1.72 1.71 O32 tee 10 18 Tops .1369 13.40 505 2.03 .016 Roots .0614 .0307 16.62 At2 3.68 i Grown January 24—March 6, 1916. 1918 | Waynick: Antagonism and Cell Permeability 179 Fig. 6 Magnesium Sulphate + Calcium Chloride (See Table 6) LSO Solution é- Z Ca(NOz)2 MgSO, 1 .04 2 408 8 22 &: 16 5 .20 6 .24 7 28 8 Full Nutrient 15 15 15 15 15 15 15 Dry Weight Tops 1.8850 1.1941 Roots .9776 Tops 1.7825 1.5648 Roots .8813 Tops 1.6850 Roots .6284 Tops 1.2078 Roots .5668 pigs). eee aa Roote <:....: Tops .5818 Roots .1581 TVons.’ ..-...:. MOGtE oo 5 Tops 1.5682 1.5775 Roots .9776 Grown April 14—May 27, 1916. TABLE 7 Potassium Chloride 1 Percentare of Ash 1.6731 4406 8425 0141 .6030 2834 No growth 18.50 p08 .0740 21.90 No growth 18.33 1.5728 19.40 20.40 Mean 18.95 19.90 16.67 18.50 18.86 Percentage of Ca oo as 4-3 293 312 271 Mean 067 110 90 302 oo to Percentage 08 101 .762 .842 430 2.190 2.390 University of California Publications in Agricultural Sciences Mean .887 802 2.190 2.120 9.200 255 [Vol.3 © Percentage of Fe oO = bo Co Amounts too small to determine. Mean .022 023 OE 1918] Waynick: Antagonism and Cell Permeability 18] od Fig. 7 Magnesium Sulphate + Calcium Nitrate (See Table 7) 182 University of California Publications in Agricultural Sciences [ Vol. 3 TABLE 8 Magnesium Sulphate + Calcium Nitrate Lv 2, a) Ly oe &0 i eo bh bp Se : = : $ Ba Oe. 2S oe) Oa. eee sag Solution s Es $ he * St $ Ee : bs s KCl Dry Weight = a, ° a a A a By - & oa .04 Tops 1.1563 19.65 .078 228 028 1.37 1.1128 1.1345 19.65 19.65 _...... 201 .214 .045 .037 1.80 1.58 Roots .5038 .2519 17.07 .256 175 173 61 .06 Tops 1.0773 24.00 128 .083 .041 3.54 1.0791 1.0782 25.90 24.95 .113 .120 .118 .100 .030 .036 3.54 3.54 Roots .5979 .2989 16.27 .241 10) Fh ee 0 ee .08 Tops .7638 27.50 302 201 .064 4.81 4.56 Roots .4659 .1829 17.20 238 180 .106 4.80 10 Tops .8417 25.90 .204 302 .268 3.56 7900 .8158 24.40 25.15 .186 .195 .205 .253 .280 .274 3.80 3.68 Roots .3135 .1567 14.20 570 300 072 1.02 12 Tops .5656 31.00 .283 .378 195 4.78 5815 .5734 29.80 30.40 .265 .274 .657 .567 .072 .133 4.30 4.54 Roots .2215 .1107 18.00 .780 101 175 1.67 14 Tops .4825 39.50 217 478 091 9.11 4200 .4531 32.30 35.90 .222 .219 .454 .466 .092 .091 7.10 8.10 Roots .1762 20.83 .617 139 .021 1.53 16 Tops .5375 42.00 .248 .730 071... See oo OBE cacnsy 42,00 ....... .248 2% 6780 .: O72 eee Roots .1339 .0669 23.83 505 1.34 250 2.31 Grown January 31—March 13, 1916. 1918] vism and Cell Permeability Waynick: Antagoi 9 - = | | ' ' 1 2 3 4 5 6 Fig. 8 Potassium Chloride (See Table 8) 183 Solution No. MgSO, KCl 1 ot 8 2 8 418 3 22 18 4.36.38 5 .20 18 6 .24 .18 7 8 . 38 S208: 18 o- 26: 38 Full Nutrient University of California Publications in Agricultural Sciences TABLE 9 Magnesium Sulphate + Potassium Chloride Drv Weight Tops Roots Tops Roots Tops Roots Tops Roots Tops Roots Tops Roots Tops Roots Tops Roots Tops Roots Tops Roots .6579 .6379 .2800 .6800 .7162 .2682 A957 0202 .2200 .6229 6464 3123 3645 4819 .2063 1.0992 1.0750 .8120 ~ ~ et ae a? 19.65 141 490 6479 21.20 20.42 .162 .151 500 TA SOT. hee Se, 2.79 22.07 138 430 6981 25.10 23.58 .171 .154 480 1341 23.50 590 1.350 22.60 BOO wae Pe, Ce 5079 26.50 24.55 .310 .3801 923 1100 25.25 745 104 23.50 152 382 .6346 24.70 24.10 .169 .161 wel 1561 333.70 991 561 26.20 440 O77 oS a ees BESO 2 Yi eee 1031 24.00 678 1.060 33.20 407 1.040 2700 37.60 35.40 .423 .415 2.920 0648 22.10 750 1.490 31.10 299 1.030 1786 35.10 33.10 ..265 .289 990 .0456 24.10 tab 2.900 36.10 .263 890 2850 36.20 36.15 211 - 337 S810 0733 239.57 6229 S18 23.90 261 S01 2823 25.00 24.45 .278 .269 895 -0708 21.60 699 .248 20307 310 .268 1.0872 19.12 18.69 .297 .3038 238 20.00 ey gl 233 Grown January 31—March 13, 1916. Mean A495 923 381 848 Percentage of Fe Amounts too small to determine. [Vol.3 tage —- = © Percen 67 Mean 1.92 3.10 4.16 5.01 7.66 3.64 1918] Waynich: A ntagonism and Cell Permeability Fig. 9 Magnesium Sulphate + Potassium Chloride (See Table 9) 185 186 University of California Publications in Agricultural Sciences [ Vol. 3 TABLE 10 ~ Solution AlCls .0000033 .0000165 .000033 .000066 .000132 .000331 .00331 Dry Weight Tops Roots Tops Roots Tops Roots Tops Tops Roots . Tops Roots . Tops Roots . 4438 4688 4315 .2934 2745 1976 2872 3995 2964 3028 .3200 Roots . Aluminum Chloride o LT) ee F e< i a” 22.42 4563 20,40 2157 20,20 23.20 2839 22.70 0988 18.70: 21.09 3233 22.60 1482 19.55 21.09 3114 22.80 1211 19.55 22.60 2599 19,00 1322 26.60 20,20 3597 21,90 1275 27.90 22.30 3116 21.82 1076 = 29.40 Grown August 26—October 7, 1916. Mean 21.40 22.95 21.84 21.94 20.80 21.05 22.60 Percentage of Ca 188 318 338 436 246 263 Percentage of Mg Mean 970 .610 836 ol 88 Percentage of Fe oo a4 “1 Or Mean .O76 145 163 141 L27 130 150 1918] Waynick: Antagonism and Cell Permeability + I I \ \ il 2 3 4 Fig. 10 Aluminum Chloride (See Table 10) 188 University of California Publications in Agricultural Sciences | Vol. 3 TABLE 11 Caleium Chloride + Aluminum Chloride & & & & s = & s So bo oO o 17.90 19.30 17.60 15.70 18.10 17.10 16.78 16.51 20.98 20.17 19.12 20.00 Mean 16.85 16.60 16.90 16.64 18.69 bo Percenta ge of Ca Mean .045 .030 303 Grown January 24—March 6, 1916. io bo Percenta we ~] ge of Mg ol @ .238 .224 [ Vol. 3 Percentage Mean 198 239 123 1918] Waynick: Antagonism and Cell Permeability 193 Fig. 13 Ferrie Chloride (See Table 13) 194 University of California Publications in Agricultural Sciences [ Vol. 3 TABLE 14 Ferric chloride + Calcium Chloride & Se bi bi ee s g s Solution I o 4 5 of 5 is E 6 2 cI a 2 8s B 5% ¢ 535 §& Es No. FeCl; CaCle Dry Weight si a, ° = a” = a? = a ° S 1 .000089 .20 Tops .4826 18.27 1.02 104 ff 4116 .4471. 18.50 18.88 1:83 148 137 20.2 Roots .4143 .2071 28.35 531 222 100 2 000168 .20 Tops .5238 17.72 1.77 194 080 5847 .5592 16.04 16.88 1.01 1.39 .101 .147 .090 .085 Roots .6115 .3057 22.70 188 229 03, 3 .0003852 20 Tops .2732 20.42 2.78 256 370 3204 .2918 20.61 20.51 3.28 3.03 .255 .255 .400 .38 Roots .1774 .0887 22.40 1.76 692 120 4 000712 .20 Tops .5910 19.01 2.85 212 50 3910 4860... 19.01 2.15 2.00 .262 .237 .40 .45 Roots 5053 .2526 31.30 1.06 .026 .02 5 00142 .20 Tops .5427 16.56 - 1.06 064 36 6353 5890 17.79 17.17 1.33 1.19 .051 .058 .50 .43 Roots .6238 .3119 29.50 350 .010 16 6 .00356 20 Tops .2715 14.76 1.32 097 1.18 2632 .2673 17.09 15.92 1.23 127 .183 .115 1.02 1.10 Roots .2196 .1098 20.03 1.13 018 98 7 0058 .20 Tops .1792 20.03 2.37 256 800 2514 .2153 20.92 20.47 2.08 2.22 .297 .276 .900 .85 Roots .0636 .0318 29.30 1.68 .020 200 8 .0168 20 Tops .3293 17.03 584 246 148 4393 .3843 19.08 18.05 .460 .522 .175 .210 120 .134 Roots .3565 .1783 28.04 505 049 .06 Grown December 9—January 19, 1916. Tron determined colorimetrically in this series. 1918 | Waynick: Antagonism and Cell Permeability ig. 14 Ferric Chloride + Calcium Chloride (See Table 14) bo oO ~ 196 University of California Publications in Agricultural Sciences TABLE 15 Ferrie Chloride + Magnesium Chloride Pr & 3a [=] E43 Ba Solution 8 oa | sO —— ON = os $ Be FeCl; MgCl Dry Weight Ss a, ° = a” 000089 =.20 Tops .9650 18.48 182 7444 8547 18.70 19.59 .163 Roots’ .6126 3063 25.05 .204 000168 .20 Tops 7875 18.12 181 — 9525 8700 18.67 18.44 .164 Roots .6816 3408 21.40 .229 000352 .20 Tops 8787 1547 172 .7365 BOTE: U7-15 VI6:36 387 Roots .6525 3262 22.95 176 000712 220 Tops 1.0414 16.77 324 TST (IT? +B 1.1515 1.1464 Roots .4837 .2418 no —_ mn oO Do oC 16 6) * 00142 20 Tops .6648 17.40 209 7927 6.7287 16.22 16.81 185 Roots .4627 .2313 22.12 .258 .00356 20 Tops 1.1639 16.50 176 9476 1.0557 16.10 16.30 .109 Roots .3298 .1649 20.28 433 0058 .20 Tops .6608 17.08 340 6189 .7398 16.07 16.57 .400 Roots .4846 .2423 20.09 239 .0168 .20 Tops 1.0927 18.96 44 1.0824 1.0875 20.05 19.45 .391 Roots .6358 .3179 21.05 LTT Grown January 24—March 6, 1916. 154 367 t0 GO Percentage O47 Mean 853 190 .264 .086 153 1.06 [Vol.3 Percentage of Fe =) =) — Mean .210 070 .093 221 137 .040 130 1918] Waynick: Antagonism and Cell Permeability 197 1 2 3 4 5 6 7 8 Fig. 15 Ferrie Chloride + Magnesium Chloride (See Table 15) 195 Solution No. CuCle 1 .000038 2 .000079 .00015 .00031 5 .00047 .00063 * .00079 ~] .00198 .00392 Full Nutrient University of California Publications in Agricultural Sciences [ Vol. 3 TABLE 16 Copper Chloride ee Se ee ee be Ba be} be} be] $ aa Se oo Seo es rR yg 283 2 a ee Poe Drv Weight Bo f° 2. 8° #8 8° S 6” fe Tops .4611 25.60 425 194 1900-/ foe Roots .4692 .4651 23.60 24.60 .420 .412 .191 .192 .201 .160 ....... Tops .2492 20.20 455 .716 155 «Agee Roots .3242 .2867 24.12 22.16 .563 .509 .723 .719 .221 .188_ ...... Tops .3887 24.50 312 1.10 114 (oe Roots .4198 .4042 25.30 24.90 .361 .336 .90 1.00 .0261 .070 ...... Tops .2744 18.45 150 1.43 .040 001 Roots 1372 18.45 150 1.48 .040 Tops .2581 22.00 176 1.35 214 .002 Roots .2344 .2462 18.10 20.05 .102 .139 1.02 1.18 .094 .154 .002 .002 Tops .0785 19.10 254 oe 0B eee .003 Roots .0700 .0742 18.21 18.65 .425 .339 5.10 4.43 .248 .248 .005 .004 POG. ese Roots .....-.- No growth OR, «oe Roots .......- No growth FODe. ccs Roots: ......:- No growth. Tops 1.1234 19.20 211 213 1.0268 1.0751 21.00 20.10 .241 .276 .199 .206 Roots .7210 18.99 299 .216 Grown March 9—April 20, 1916. 1918] Waynick: Antagonism and Cell Permeability 199 Fig. 16 Copper Chloride (See Table 16) [Vol.3 University of California Publications in Agricultural Sciences 200 L00° uvayW L00° LOO” 100° £00° ug jo eF¥jUII019 J 080° 690° 8E0° 6F0° uvoyW gd ByUdILI Stl [Fe rol COT él TL 96°L Lg fa! Ost OL9'E [oe 9EE" ose’ 96. BW 5° a3ejUele dg FLO’ ueoyy apoyo ousag + eptaopyD seddop ‘QIGL ‘Lz 09g 696° 896° Oca L C66" cle bSG" 66° 6o6° 0L0° 06L 16 a3vjue0l8 gq ABWFL [dy umory 08°61 L9°06 FS1G 06°61 Oa LL 06°81 OF 16 OL GL c8°6L OS 16 03°06 09°06 6F' GG 06°81 Ost 0°06 c6 LT 00°61 6S'06 ysy Jo a3¥}U0010 qd LT wav C350" OSlY ¢990° Go8F O6FL ogsc¢" Lo6v 6090" 8866" CPLy uvoyt OSSL s}oo"y ogse’ ocir —- sdoy, ger . 8300N CHOP 6cLy = Sdoy, 186¢° $}00"4 009¢° cog¢g sdoy, CCgG s}O0Y 0016" 6IST IT sdor Legg $}00% 9Z8F° t99F = Soy, isa M St 68000" ¥60000° 820000° 490000° 3F0000° =32F0000° €920000° 860000 4800000° 600000° *10°0 71000 a uornpog ‘ON 1918] Waynick: Antagonism and Cell Permeability 201 Fig. 17 Copper Chloride + Ferrie Chloride (See Table 17) No. or University of California Publications in Agricultural Sciences 202 Solution HgCl. CuCl. .0000047 .0000023 .0000094 .0000047 .0000184 .0000094 .000047 = .000023 .000094 .000047 .000189 .000094 .000378 .000188 TABLE 18 Mereurie Chloride + Copper Chloride © Percentage of Ash Percentage of Ca Percentage of Mg =| a r= 5 = S Dry Weight = | a Tops .1175 20.15 674 1.21 1608 .1392 21.20 20.67 517 .595 935 Roots .0869 .0434 18.65 1.220 .276 Tops .1792 20.00 OoL 873 .2675 .2233 20.32 20.16 612 .572 .942 Roots .0846 .0423 16.71 1.410 .291 Tops .3778 24.70 493 A488 3328 .38503 23.30 2430 .570 531 _...... Roots .0928 .0467 15.45 1.360 211 Tops .3600 21.22 431 834 2334 .2967 23.20 22.21 521 .471 921 Boote .1109° .0554 17.88 © © cum 361 Tops .3643 22.00 399 737 4372 .4007 20.12 21.06 354 .3856 .695 Roots .1109 .0554 17.32 — ...... 361 Tops .2385 22.30 21 921 3105 .2745 24.71 23.50 .503 512 973 Roots .1146 .0573 12.71 1.340 333 Tops .1500 21.60 O73 1.212 2150 .1825 23.40 22.50 .672 .622 1.071 Roots .0609 .0304 12.82 — ...... .412 Grown January 24—March 6, 1916. [ Vol. 3 907 488 S877 .716 947 1.14 Percentage of Fe Too small amounts to determine. 1918 | Waynick: Antagonism and Cell Permeability . 203 Fig. 18 Mercurie Chloride (See Table 18) No. ~“ .0000 204 Solution CuSO, 0000048 .0000094 .Q000188 .0000378 .0000567 Fe * “I { { ~ .0000945 .000189 .000378 University of California Publications in Agricultural Sciences Dry Weight Tops Roots Tops Roots Tops Roots Tops Roots Tops Roots Tops Roots Tops Roots Tops Roots Tops Roots . .6148 .7726 4406 5394 .8462 4512 4712 5188" ; 2948 1.5098 1.0836 9436 7544 .8022 5265 .7598 6632 889 3339 .2439 1567 3267 TABLE 19 Copper Sulphate Percentage of Ash a s A 22.80 6937 21.71 2203 20.61 21.42 6928 17.50 2256 16.40 24.40 3920 18.90 1474 22.50 22.02 1.2967 18.90 4718 18.85 21.18 7783 20.44 2632 18.10 21.60 7125 20.83 2944 19.71 23.21 2889 23.60 0783 18.00 22.61 3526 24.80 0815 21.40 24.22 .2533 22.00 .0348 23.80 a 20.46 20.81 21.41 23.11 Percentage of Ca Mean 110 .061 020 a4 576 469 Grown April 14—May 27, 1916. tw Percentage of Mg 446 .688 348 433 1.32 | Vol. 3 Percentage — os of he .082 .025 .042 054 013 Percentage oeeee 1918 | Waynick: Antagonism and Cell Permeability 205 Copper Sulphate (See Table 19) [| Vol. 3 University of California Publications in Agricultural Sciences Uva; 206 ‘OIGL ‘g AVIN-ZZ Yue UMOIH sco" 110° OL6'L 803" O8'FS 6ICO' SeOL’ S}00y AC) ee) a) ec OTL OIST. Si 68I' BOE: ESE BI'SE osrE’ 910" Lt0° C00" 83° 09°82 r1cg sdoy, 092000" 681000° 8 eto" #0" SOF 209" 09°03 Z9FO' F260" S}00y 610° 90° go’ [sl O60°T 062° 808° OS'SS OBFS 1893 9608" 920° TL0° OFG'T 06L" 06°92 199%° sdoy, €C1000° ZFlO000" 2 C30" 630° 9¢9° 066° OS'6L 66IL' 6683" $3004 A 080° O80" Bez" GGL 969° 866° OL'F3 O&'93 SFr 816g" = 060° 062" F6L" OL'Ss 616F sdoy, 910000° ¢f60000° 9 20" S10" 199° e1¢" OS Fl IFILT €833° SJooy i 090° 990° LIZ 869" I9¢° 6S OFS S6FS OFISG’ EeEEes = GO’ L¥L ogg" 0€'&3 6c6r sdoy, 960000° 82£0000° & 110" 9IT’ QF" LLY LEEL LSI’. GSL1Es syooy es €0l Zol’ ggg" 109° Lig If O13 O66 OEEr - SzEr — col’ 999° oo" 0€'3s Lyer sdoy, $¢¢10000° 6810000° F 800° 160° Lo SIL’ 069 I1E3 320g" s}00 st 860° SOr T&L’ 136° ecs i635 ee'ds ogee £062 Lee <— 060° cE" 963" LESS tFL9° Sdot ¢L10000' ZFI0000° ¢& G00" £80" $ES" CHL’ 0Z6I 8¢9% 91Eg° S}oOy mo 690° 810° ggg ZFS" OCI’ FIL SL°3S 0636 TOES 9TEF a 190° PLE 930" O&'&3 9829 sdoy, 9100000° +#600000° 32 200° 690° 663° 6FL O86 8362 LEsg’ s}ooy om COL sr OLF ZOF’ 8Zl° 80° 0632 O024FS 9St9° LSTL’ po 880° O6F Ist" 09° Iz g11¢° sdoy, Zgg00000° L#00000° tT o- = a, = ow = ay = ot iS Wyse M S1q *OSuz Fosno ‘ON 23 2 23 2 22 ® 22 ® 22 ® —_ ___ — -_ - 23 3 az = 23 = 8 3 > 5 wolznlog 3 os mS a = a ayeyding surz + a3eydjng saddop 0Z WAV 1918 | Waynick: A ntagonism and Cell Permeability ONT Fig. 20 Copper Sulphate + Zine Sulphate (See Table 20) | Vol. 3 University of California Publications in Agricultural Sciences 208 £90° 600° 600° uvay coo’ L00° o00° 500° LOO" 160° oLe" Les" Lz9" ae 16L SFO" SLU" L6L LIT G20" C30" 061" 1F0" £0" Isr 10" 1€0° 990" £90" 9¢0" SFO" 10" Lc0" 890" 960" OT JO a3e}UsI1e g 8£9° Gor 98° 18C° Leo" 063°S OFS'T OLO'L LoS" G19" Z09" LEG 696° PIL CFS [él 9ST" COG 6LU 89L FES" g3vjUII19 J OIGL ‘g ABVIN-ZS Gore UMOID LPG SLL 91¢° ayeyding ool 666" 696" 66° FIT tol LLV 99° L9G LI9° 86L 906° 069° 61G Fo 996° LLU SLT él Lov 1 60 FOL LIT F0'6L 16°€6 L616 ae IZ WIAVI, OF'06 éUst 96°6L _ I8'6L 068% BS'3s OF'OL 29°13 13°33 G9'IZ 16°02 O32 LP'FS 0°32 ard 0°02 OL'E2 28'S OL'E2 00°02 aad ge'0e 19°13 CO'IZ SUSE 09°08 0G'33 LPS OFZ 3'ES ysy jo ade} UId10 9660'L €SE0° 6666 L860 cOLy 8680" esr FL80° 6969 1660" 6TLL 88ro° COFL'T L60¥F" 6LOO'L IFES 0096" = oO = 5 aT119,¢ + oyvydtng szsddog 6E6L° 0068" eLSUT 1020" L663 1883" PPLO" PLLE SL9F" 961° SbLP 74 a SPL. cog" QLES" 338" L6F6" 136" 8686" LL80'T L306" 9160°T 7620'I LIGO'T F618" 8¢16" 18Z0°L £699" [8¢6" 6&6" $4003] sdo J, $}00}] sdoy, $100% sdoy, $,00Y sdoy, sjooy sdoy, $j00Y sdog, sjooy sdoy, $100Y sdoy, sjooy sdoy, sjooy sdoy, WISIN AT ES 9200000° ‘OS4UZ Z00000° = #600000° 86000" 8f000° FL000° 68 L000" COLO00'~ 6F L000 020000° F60000° 860000° 82€0000° FLOO00’ ~=68T0000° £OL0000° ~=s6FL0000° 0400000° #600000" £€00000° = 2400000° ®(FOS) 00 rosno — / uolnpog OL wD ‘ON 1918] Waynick: Antagonism and Cell Permeability + 2 3 4 5 Fig. 21 Copper Sulphate + Ferrie Sulphate (See Table 21) 209 210 University of California Publications in Agricultural Sciences [ Vol. 3 TABLE 22 Ferric Sulphate a ee Se Ee So g g g 2 S42 gs iS 5 $3 g oth me No. Fe(800s Dry Weight s sc os sy @ ¢° S| oe 1 .0000014 Tops 2.2399 17.09 107 098 .246 1.3062 1.7730 17.55 17.382 .099 #.108 113 =.105 281 .263 Roots 1.0626 21.81 122 763 315 peat a. 5313 erie 8 | Berg 122 meee 763 ~ssaes | SU 2 .0000028 Tops 1.9198 20.50 119 O70 264 1.5236 1.7210 30.21 231385 .115 £117 OTS '= O71 201 . .231 Roots .8731 25,50 013 145 220 4850-6769 26.50 25.85 .020 .016 .158 150 286 .253 3 0000070 Tops 1.4150 24.00 05 - ).-* Sia: .393 1.5247 1.4698 22.62 28.31 .080 .087 °&#.102 102 895 304 Roots .6984 31.10 .032 263 223 7624 .7304 30.61 30.85 O41 036 .224 .243 277 .250 4 000014 Tops 2.3544 20.57 .032 O89 258 2.3461 2.3502 18.90 19.73 041 036 .106 8 .097 318 =©.368 Roots 1.0361 27.20 .022 .184 172 1.1861 1.1111 29.20 28.31 O11 016 .250 217 278 ee 5 00007 Tops 4.2000 14.80 018 ° 072 .236 3.6033 3.9016 15.15 14.97 017 017 #£.073 072 268 (252 Roots .9813 25.81 .056 134 103 9168 .9490 26.00 25.90 .077 .067 178" «tae 129 136 Full Nutrient Tops 1.5682 18.33 .293 231 1.5775 1.5728 19.40 18.86 212 302 .279 .200 Roots .9776 20.40 tl 279 Grown April 22-June 3, 1916. 1918] Waynick: ror) | be | Antagonism and Cell Permeability 211 Fig. 22 Ferric Sulphate (See Table 22 212 Solution No. ZnSO, 1 00000767 2 = .0000131 3 .0000395 4 .000153 5 .000395 Full Nutrient University of California Publications in Agricultural Sciences Dry Weight Tops Roots Tops Roots Tops Roots Tops Roots Tops Roots Tops Roots .6718 7541 .6138 .7164 8350 .6009 .6142 .8607 5864 5109 .3800 4628 8208 Lost 4432 1.0992 1.0750 8120 TABLE 23 Zine Sulphate Percentage of Ash : = 23.00 7129 = 24.04 3069 17.88 25.30 7757 ~=—-24.65 3004 17.20 21.19 7374 22.50 2932 15.90 21.90 4454 19.40 2314 20.50 20.38 CA” Se nee 2216 22.30 20.17 1.0872 19.12 20.00 Grown January Mean 23.52 25.07 21.84 20.65 20.38 18.69 Percentage of Ca Mean 344 404 .200 303 24~March 6, 1916. tr tw Percentage for) Oo Mean 467 348 22 .710 321 224 | Vol. 3 Percentage Mean .089 073 e a ee, r ; Waynick: Autagonism and Cell Permeability 213 _ — eee peat Fig. 23 Zine Sulphate (See Table 23) No. 1 Grown April 24—June 6, 1916. Mean 097 .159 140 .090 150 .160 150 ATT Percentage of Mg 214 University of California Publications in Agricultural Sciences TABLE 24 Zine Sulphate + Ferric Sulphate 3 Se Solution a o<4 8 oO 5) a .) w& ZnSO, Fes(SQ,)3 Dry Weight Si & ° si a? .0000019 .0000035 Tops 1.0594 18.50 .096 1.5294 1.2944 18.70 18.60 .098 Roots .10444 .5222 29.80 045 .0000038 .000005 Tops 1.5364 18.60 .149 1.4964 15114 16.16 17:35 270 Roots 1.0716 5258 31.00 .042 .0000057 .000007 Tops 1.2300 18.10 172 1.6150 1.4225 16.90 17.00 .124 Roots 1.1250 5625 32.30 .068 .0000076 .000014 Tops 2.3088 16.40 .083 2.5100 2.4094 17.00 16.70 .098 Roots 1.5623 .7812 28.00 .040 .0000152 .000028 Tops 2.3429 15.70 154 8:0199 23.1774 16.70 15.70 247 Roots 1.5133 .7566 30.30 .050 .0000379 .000070 Tops 2.0533 18.10 .160 1.5544 1.8038 16.20 17.15 .160 Roots 1.4194 7097 25.30 025 .000076 .00014 Tops 1.6164 18.40 57 1.7228 1.6696 19.70 19.05 .144 Roots 1.7611 8801 27.00 .019 000152 .00028 Tops .9850 18.35 179 1.0268 - 1.0029. 20.00 19.17 .17 Roots .6987 .3493 27.30 .006 [ Vol. 3 110 136 .250 Percentage of Fe .031 Mean .030 .033 .070 .063 .049 045 .043 1918] to Waynick: Antagonism and Cell Permeability Fig. 24 Zine Sulphate + Ferric Sulphate (See Table 24) 21! No. | .0000189 .000047 .000094 .000189 .000378 216 University of California Publications in Agricultural Sciences Solution .0000094 . Fes (SO,)s .0000047 .0000035 Tops 0000070 .00005 .00014 .0007 .00105 .00210 TABLE 25 Mercurie Chloride + Ferrie Sulphate Dry Weight Roots .0! Tops Roots . Tops Roots . Tops Roots . Tops Roots . Tops Roots . Tops Roots . g, ao =4 si a? 2039 22.40 2868 .2553 16.70 0518 .0259 18.70 Mean 19.55 18.05 16.10 16.95 16.50 Percentage of Ca Grown March 22—May 3, 1916. Mean .206 420 .166 146 Percentage of Mg | Vol. 3 PA s | oo si I ee 3 Ss f°: & 618 A421 E E vo ® 391-2 niet are." | ® 3 463 = an = ° =| eo 100s ° Z .769 101 722 157 .129 1222 —_— — 1918] ~l Waynick: Antagonism and Cell Permeability Fig. 25 Mercurie Chloride + Ferrie Sulphate (See Table 25) bo 215 Solution HgCle .0000135 .000066 .000135 University of California Publications in Agricultural Sciences Dry Weight Tops .4904 4967 Roots .1493 Tops .2200 .2236 Roots .0239 Tops .1514 TABLE 26 Mercurie Chloride fo] oS Mane eae © See S Be Es Es 3 = ev = Ay =) 17.20 141 4935 16.71 16.95 098 120 .0746 19.31 478 15.70 .oa2 .2218 14.24 14.97 .380 .396 0119 10.50 4.31 9.12 421 1467 8.95 9.03 .3899 .410 Grown March 14—April 24, 1916. tp Percentage of Mg Lod Mean 1.28 [Vol.3 to Percentage of Fe ns w Mean .248 .013 .012 . Fig. 26 Mercurie Chloride (See Table 26) ee i.e eee EXPLANATION OF PLATES PLATE 13 Appearance of plants as mounted in corks at expiration of the six weeks’ growing period. UNIV. CALIF. PUBL. AGR. SCI. VOL. 3 [WAYNICK | PLATE PLATE 14 No. 1. .24 M. MgCl. .004 M. CaCl, No. 2. .24 M. MgCl, .01 M. CaCl, No. 3. .24 M. MgCl, .02 M. CaCl. No. 4. .24 M. MgCl. 04 M. CaCl, No. & .24 M. MgCl, .06 M. CaCl, No. 6. .24 M. MgCl, .08 M. CaCl, No. 7. .24 M. MgCl, .10 M. CaCl, No. 8. .24 M. MgCl, .12 M. CaCl, No. 9. .24 M. MgCl, 16 M. CaCl, No. 10. .24 M. MgCl, .20 M. CaCl, No. 11. .24 M. MgCl, .24 M. CaCl, No. 12. .24 M. MgCl, .30 M. CaCl, No. 13. .24 M. Control. [222] ¥ UNIV. CALIF. PUBL. AGR. SCI. VOL. 3 | WAYNICK | PLATE 14 Fe a PLATE 15 No. 1. .30 M. MgCl, .004 M. CaCl. No. 2. .30 M. MgCl, .01 M. CaCl, No. 3. .30 M. MgCl, .02 M. CaCl, No. 4. .30 M. MgCl, .04 M. CaCl, No. 5. .30 M. MgCl, .06 M. CaCl, No. 6. .30 M. MgCl, .08 M. CaCl, No. 7. .30 M. MgCl, .10 M. CaCl, No. 8 .30 M. MgCl, .12 M. CaCl, No. 9. .30 M. MgCl, .16 M. CaCl, No.10. .30 M. MgCl, .20 M. CaCl, No.11. .30 M. MgCl, .24 M. CaCl, No.12. .30 M. MgCl, .30 M. CaCl, Control. [224] UNIV, CALIF. PUBL. AGR. SCI. VOu, s | WAYNICK | el i de ft SS UNIV, CALIF, PUBL. AGH SEY, be) Mele [WAYNICK] PLATE 4 6 ee ve No. 1. No. 2. No. 3. No. 4. No. 5. No. 6. No. 7. PLATE 17 00331 - M. AICI, 000331 M. AICls 000132 M. AlCl, 7 000066 M. AICls 900033 M. AICI, 0000165 M. AICI, 0000033 M. AICI, Control. NOS 'YDV ‘1ENd ‘4INWS “AINA “1OA oO i) 3ivid LyoINaAvm | fg No. No. No. No. No. No. No. No. — 2 ie) PLATE 18 0168 M. 058 M. 00356 M. 00142 M. .000712 M. .000352 M. 000168 M. 000089 M. FeCl, FeCl, FeCl, FeCl, FeCl, FeCl, FeCl, FeCl, Control. [230] 20 M. 20 M. 20 M. 20 M. 20 M. 20 M. 20 M. 20 M. MgCl, MgCl, MgCl, MgCl, MgCl, MgCl, MgCl, MgCl, | WAYNICK | PLATE 18 UNIV. CALIF. PUBL. AGR. SCI. VOL. 3 No. No. No. No. No. No. No. TD Op Po PLATE 19 .00331 M. AIC), .000331 M. AICI, .000132 M. AICI, .0000662 M. AICI, .0000331 M. AIC), .0000165 M. AICI, .0000033 M. AICI, Control. [232] 20 M. .20 M. 20 M. 20 M. 20 M. .20 M. 20 M. CaCl, CaCl, CaCl, CaCl, CaCl, CaCl, CaCl, Jivid | MOoINAvM | 6l No. 1 No. 2. No. 3 No. 4 No. 5. PLATE 20 000094 _M. CuCl, .00082 M. FeCl, .000067 M. CuCl, .000058 M. FeCl, ) .000047 M. CuCl, 000042 M. FeCl, 000028 M. CuCl, .000026 M. FeCl, — 0000094 M. CuCl, .0000089 M. FeCl, Control. | = UNIV. CALIF, PUBL. AGR. SCI. VOL, 3 [WAYNICK] PLATE 20 =~ No. No. No. No. No. No. No. No. No. 5. 2 3. 4. 5. 6 7 8 9 PLATE 21 000378 M. CuSO, 000189 M. CuSO, 0000945 M. CuSO, 0000755 M. CuSO, 0000567 M. CuSO, 0000378 M. CuSO, 0000188 M. CuSO, 9000094 M. CuSO, 0000048 M. CuSO, Control. [236] “~ TOA 1SS R13 ame f= | a ‘AITVS ‘AINA QO ww be 3Lwid [YoINAvM] MD OTR ge po - oo PLATE 22 .0000047 M. .0000094 M. .0000142 M. .0000189 M. .0000378 M. .000094 M. .000142 .000189 M. .00058 M. M. CuSo, CuSo, CuSo, CuSo, CuSo, CuSo, CuSo, CuSo, CuSo, .0000035 M. .0000070 M. .0000105 M. .000014 .000028 .000070 .000105 .00014 .00028 M M M M. M M Control. [238] Fe, (SO,)s Fe, (SO,), Fe, (SO,); . Fe, (SO,)s . Fe, (SO,)s . Fe, (SO,)s Fe, (SO,)s . Fe, (SO,)s . Fe, (SO,)s “AINA INd *4INVO ¢ C ‘YOV 7 LOK “Os oO GU 22 3Llvid [MOINAvVM] PLATE 23 0000014 M. Fe, (SO,)s 0000028 M. Fes (SO,)s 0000070 M. Fe: (SO,)s 000014 _M. Fe, (SO,)s 00007. _-M. Fe. (SO4)s Control. (mm os = 7 e ba io : mi > OS & * eae 4 a + =k i] . [<> aff. ay a e a. PLATE 24 No. 1. .000135 M. HgCh No. 2. .000066 -M. HgCl, No. 3. .0000185 M. HgCl, Control. UNIV, CALIF. PUBL. AGR. SCI. VOL. 3 } | WAYNICK | PLATE 24 > Ye UNIVERSITY OF CALIFORNIA PUBLICATIONS iN AGRICULTURAL SCIENCES Vol. 3, No. 9, pp. 243-270, 2 text figures June 22, 1918 VARIABILITY IN SOILS AND ITS SIGNIFI- CANCE TO PAST AND FUTURE SOIL INVESTIGATIONS I. A STATISTICAL STUDY OF NITRIFICATION IN SOIL BY DEAN DAVID WAYNICK It is very generally recognized that different soils vary widely as regards their physical, chemical, and biological nature. It has also been recognized among soil investigators, at least, that different samples of the same soil type taken from a comparatively limited area may show considerable variation among themselves if we apply quantitative measurements to the various constituents of the soil mass. In any small area of the size usually employed in field experiments, these variations seem to have been regarded as of such limited magnitude as to be worthy of but secondary consideration. In many instances, a single sample from such an area has been taken and the assumption made that it represented the entire soil mass of the depth to which it was taken. In other words, the soil has been considered as a constant to which no corrections need be applied. Most workers in the field of soils have been content with taking relatively few samples and regard- ing determinations made upon the composite of these samples as accur- ate within the limits of error of the experiment. That the variations between different samples taken from a small area may be of such magnitudes as to bring experimental data obtained with one or a limited number of samples into very serious question, or even to invalidate such data entirely, seems not to have been considered. It is the purpose of this paper to emphasize the importance of this phase of soil investigation as regards both past and future endeavors. It is obviously impossible, within the limits of a single paper, to consider the variations which characterize all the constituents of any 244 University of California Publications in Agricultural Sciences | Vol. 3 given soil, so that the results reported at the present time relate only to one phase of the biochemistry of soils. But few attempts have been made by investigators to determine actually the magnitude of varia- bility in those products of microdrganic activity which are capable of quantitative measurement and in no instance has a mathematical inter- pretation been attempted with such measurements. There are but three references’ * * in the literature, as far as the writer is aware, dealing with this phase of the biochemistry of soils, and none of them is extensive enough to be of any value as statistical studies of varia- bility. A number of papers* have appeared dealing with the variation in the weight of the crop produced over different parts of an appar- ently uniform field. Such variations reflect the variability of the soil, serving simply as a substratum for the growth of plants, but it is evident that the variations between such measurements as those given do not depend upon the soil as the only variable factor. Any attempt to correlate the crop produced on any given soil with the chemical composition of that soil, for instance, must necessarily take into account variations in both crop and soil. In fact, it appears to the writer that any correlation which may exist between the properties of any given soil and its crop-producing power can only be worked out by the statistical interpretation of data obtained as recorded below, together with the data secured in a similar manner for the crops produced on that soil. The problem of variability in the soil itself is worthy of careful experimental study, both from the standpoint of soil investiga- tions in themselves and from that of their possible bearing upon the problems of variability in field experiments with crops. The results of such a study, as regards nitrate production, are presented below. Merruops The field selected was one on the University Farm at Davis. For the three years preceding 1917, corn, Sudan grass, and grain sorghum had been grown in the order named. In 1917, the field was allowed to lie fallow and at the time the samples were taken (Oct. 20), was free of vegetation of any kind. No rain had fallen since April so that the surface soil was practically air-dry, the subsoil, however, being quite moist. The soil is classified as a silty clay loam. The particular area chosen was apparently as uniform as one could well find, being level, of uniform texture and color, and free from small local depressions of any kind. 1918 } Waynick: A Statistical Study of Nitrification in Soil 245 The samples were taken at the locations as shown in figure 1, the diameter of the plot being one hundred feet. Each number in the following table represents two samples, soil and subsoil, the latter term being used for convenience in expression rather than to represent any sharp line of demarcation between the two samples taken at any given Fig. 1 place. All the surface samples were taken with a trowel to a depth of six inches, an area having a diameter of approximately six inches being included in each sample. ‘The subsoil samples were taken with a three- inch auger to a depth of twenty-four inches and, therefore, represent the section from six to twenty-four inches in depth. All the samples were placed in sterile soil bags as soon as taken, the total amount of soil in each sample being about twice that necessary for the laboratory 246 University of California Publications in Agricultural Sciences [ Vol. 3 determinations. Not more than twenty-four hours elapsed between the time the first sample was taken and the time all the samples were at the express office ready for shipment to Berkeley, where they arrived forty-eight hours later. At the laboratory, the samples were allowed to air-dry for six days in the original canvas bags, this time for drying being necessary because of the moisture present in the subsoil samples. At the expiration of the six-day period all of the samples were sieved through a two-milli- meter sieve and four one hundred gram portions of each sample weighed into tumblers. One tumbler from each sample was reserved for the determination of residual nitrate; to a second no nitrogen com- pounds were added, and to the others two-tenths of a gram of am- monium sulfate and one gram of dried blood, respectively, these amounts having been most frequently used in nitrification experiments in this laboratory. All the tumblers were brought to an optimum moisture content by the addition of twenty cubic centimeters of sterile distilled water and placed in the incubator at 28° C for twenty-eight days. During the incubation period, the water lost was replaced at weekly intervals. At the expiration of that period, the soil was dried at a temperature of 100° C and the nitrates determined colorimetri- cally by the phenoldisulfonie acid method as modified by Lipman and Sharp.’ All results are reported as milligrams of nitrate nitrogen in one hundred grams of soil. It was not deemed necessary to make duplicate determinations on all the samples, since from previous results secured in this laboratory, the variation between duplicates, as regards nitrification studies, is small and well within the limits of the error made in the readings, which were never recorded in this study further than to one-tenth of a milligram of nitrate nitrogen. Aside from this fact, it is doubtful if duplicate determinations are of value in experiments of this kind in which the variation between the samples was found to be so large. The amount of nitrate nitrogen produced was chosen as the criterion of variability because of the generally accepted idea that nitrate nitrogen is more directly available to plants than other nitrogen com- binations and for that reason more significance may rightly be attached to the amount of nitrate nitrogen found or produced in any given soil. Then, too, small amounts of nitrate may be determined rapidly, with a very fair degree of accuracy, and moreover, are less subject to fluctuations in the duplicate determination as discussed above. The absolute accuracy of the nitrate determination by the phenoldisulfonie 4 a ee pi I ree ee ee ee 1918 | Waynick: A Statistical Study of Nitrification in Soil 247 acid method is not of moment in this connection, because neither very low nor very high amounts of nitrate were ever determined and all of the determinations are directly comparable one with the other, since exactly the same procedure was followed in every case. It must be emphasized that no attempt has been made to segregate the causes of variation and the results as given are the summation of all the factors which are of importance in causing differences between samples. All the work was done in a careful manner with due atten- tion to detail, no new or modified procedure being attempted. The results of this study, therefore, are intended to serve as a basis for interpreting the mass of data which has already been obtained by soil biologists and to emphasize the extreme importance of applying statis- tical methods to results secured in the future before their value as contributions to science or practice can be recognized. CALCULATIONS® The amounts of nitrate found are reported in tables 1 to 4, follow- ing, the individual determinations always being given. The mathe- matical treatment will be discussed briefly from the data given in table 1, the discussion being applicable to all the tables as well. The mean as given is obtained by dividing the sum of all the determinations by the number of determinations. This figure repre- sents, therefore, a hypothetical composite sample of all the samples taken. The deviation from the mean of any determination is found by taking the difference between the mean and the individual result. The mean deviation of a series of determinations is an expression of the average amount any single observation taken at random is lkely to differ from the mean of the series. This figure may be either plus or minus, but as the sign is of no importance as regards subsequent calculations, it is not recorded but may easily be found by inspection. The standard deviation (oc) is found, after the manner usual in statis- tical investigations, by squaring the deviation of each determination from the mean, taking the sum of the squares thus found, dividing this figure by the total number of determinations made and taking the square root of the quotient. The percentage ratio of the standard deviation to the mean.expresses the coefficient of variability (C.V.) for a given series of determinations. It is an expression of the per- centage deviation on either side of the mean, within which approxi- mately two-thirds of the determinations may be expected to lie. The 248 University of California Publications in Agricultural Sciences [ Vol. 3 coefficient of variability of the amount of nitrate as found in the field soil is high, no less than 25.9 + 2.1 per cent in the surface six inches and 51.4 + 3.3 per cent in the vertical section from six to twenty-four inches. The range, therefore, within which two-thirds of the deter- minations may be expected to fall is from 2.0 to 3.4 milligrams in the surface soil and from 0.3 to 1.1 milligram in the subsoil. The extreme range is, of course, much greater than this, but the bulk of the deter- ' : : ; ¢ minations fall within the limits given. A single determination, or the mean of a series of determinations can never be an absolute value and hence before any large degree of confidence can be placed in any experimental result, its degree of reliability must be known. The reliability of any determination is expressed by the probable error (#) of the determination. This figure is of such a magnitude that the probability of making an error ereater than it is equal to the probability of making an error less than it, both probabilities being one-half. The probable error (E£,) of a single determination is calculated by the formula E, = +.6745 X 2 | where o is the standard deviation, as given above, and » the number of determinations. Since with a single determination the \/n is equal to 1] E, = + .6745 X ea. or in other words, the probable error of a single variant is equal to approximately two-thirds of the standard deviation of the series in which it lies. The probable error of the mean (Ey), is given by the formula Es .6745 XK o Ex es ee ae Vn Vn Ey, will vary as the square root of the number of determinations and thus decreases but slowly as we increase the number of determinations. The probable error (Eo) of the standard deviation is caleulated from the formula C V2n and for the coefficient of variability : vj eee ot eee e\el& Be = 6145 E 4 aon | when C.V. is greater than ten per cent as is the case with the results recorded below. Eo = +.6745 1918 | Waynick: A Statistical Study of Nitrification in Soil 249 TABLE 1 RESIDUAL NITRATE IN SOIL AS SAMPLED 1”—6” 6”—24" 1”-6" 6”—24” Nitrate Devia- Nitrate Devia- Nitrate Devia- Nitrate Devia- nitro- tion from nitro- tion from nitro- tion from nitro- tion from No gen mean + gen mean + No. gen mean + gen mean - Mgs. Mgs. Mgs. Mgs. Mgs. Mgs. Mgs. Mgs. 1 2.5 0.2 1.0 0.3 42 3.0 0.3 0.6 0.1 2 2.8 0.1 aa 0.4 43 3.4 0.7 0.7 0.0 3 3.0 0.3 1.0 0.3 dd 1.8 0.9 0.5 0.2 4 2.5 0.2 1.2 0.5 45 2.5 0.2 0.6 0.1 5 3.8 bol 1.9 1.2 46 2.1 0.6 0.5 0.2 6 2.7 0.0 1.5 0.8 47 4.0 1.3 0.8 0.1 7 3.3 0.6 1.5 0.8 48 3:1 0.4 0.6 0.1 8 3.2 0.5 1.2 0.5 49 4.4 1 4 0.4 0.3 9 2.5 0.2 1.2 0.5 50 3.5 0.8 0.5 0.2 10 2.9 0.2 1.4 0.7 51 2.3 0.4 0.7 0.0 1] 3.0 0.3 1.5 0.8 52 3.1] 0.4 0.6 0.1 12 2.7 0.0 0.8 0.1 53 2.3 0.4 0.8 0.1 13 1.9 0.8 1.2 0.5 54 2.3 0.4 0.6 0.1 14 3.7 1.0 Ha | 0.4 55 1.4 1.3 0.8 0.1 15 3.8 i 0.8 0.1 56 2.5 0.2 0.5 0.2 16 3.0 0.3 10 0.3 57 1.8 0.9 0.5 0.2 17 2.0 0.7 0.8 0.1 58 Le 1.0 0.4 0.3 18 2.2 0.5 1.0 0.3 ' 59 1.3 0.4 0.5 0.2 19 2.9 0.2 1.0 0.3 60 2.0 0.7 0.4 0.3 20 3.5 0.8 0.8 0.1 61 1.5 1.2 0.4 0.3 21 3.0 0.3 1.0 0.3 62 4.0 1.3 0.4 0.3 22 4.5 1.8 0.8 0.1 63 3.0 0.3 0.3 0.4 23 3.5 0.8 0.9 0.2 64 mt, 0.3 0.5 0.2 24 3.6 0.9 0.5 0.2 65 2.0 0.7 0.4 0.3 25 1.8 0.9 0.6 0.1 66 2.0 O7 0.5 0.2 26 3.4 0.7 0.8 0.1 67 3.0 0.3 0.6 0.1 27 3.0 0.3 2.2 1.5 68 4.3 1.6 1.2 0.5 28 1.5 0.8 0.8 0.1 69 3.2 0.5 0.4 0.3 29 2.3 0.4 0.6 0.1 70 2.6 0.1 0.5 0.2 30 2.6 0.1 0.5 0.2 71 3.5 0.8 0.4 0.3 31 1.3 1.4 0.5 0.2 72 2.7 0.0 0.3 0.4 32 3.1 0.4 0.9 0.2 73 2.4 0.3 0.4 0.3 33 2.6 0.1 0.4 0.3 74 2.0 0.7 0.4 0.3 34 2.8 0.1 0.3 0.4 75 2.1 0.6 0.4 0.3 35 1.8 0.9 0.3 0.4 76 2.6 0.1 0.6 0.1 36 1.3 1.4 0.4 0.3 77 1.5 1.2 0.6 0.1 37 1.0 pth 0.5 0.2 78 2.6 0.1 0.6 0.1 38 4.0 13 0.9 0.2 79 2.4 0.3 0.9 0.2 39 3.0 0.3 0.6 0.1 80 2.2 0.5 - 1.2 0.5 40 3.6 0.9 0.4 0.3 81 2.0 0.7 0.8 0.1 41 3.8 ist 0.6 0.1 a ———= Mean 2.70+.05 0.5 0.70+.03 0.3 o — EY | ee = I! eo) * 36202 C.V. = 25.9+2.1% = 51.4+3.3% E =z 1.8% == 43% 250 University of California Publications in Agricultural Sciences | Vol. 3 TABLE 2 NITRATE PRODUCED FROM THE SOIL’S OWN NITROGEN APTER TWENTY-EIGHT Days’ INCUBATION—INCUBATED BLANKS 7 Iowr wow F ie 2) 1”-6" 6”"—-24" 1"-6" 6”-24” Nitrate Devia- Nitrate Devia- Nitrate Devia- Nitrate Devia- nitro- tion from __initro- tion from nitro- tion from nitro- tion from gen mean + gen mean+ No. gen mean + gen mean + Mgs Mgs. Mgs. Mgs. Mgs. Mgs. Mgs. Mgs. 4.3 0.9 1.2 0.2 42 4.5 1 | 1.2 0.2 2.4 1.0 1.0 0.4 43 3.8 0.4 1.4 0.0 2.2 1.2 1.0 0.4 +4 3.0 0.4 1.2 0.2 1.6 1.8 0.8 0.6 45 4.0 0.6 1.0 0.4 2.7 0.7 1 0.3 46 3.0 0.4 1.2 0.2 4.0 0.6 1.2 0.2 47 3.8 0.4 1.3 0.1 1.8 1.6 1.8 0.4 48 3.3 0.1 ¥.2 0.2 3.0 1.4 1.0 0.4 49 5.2 1.8 1.2 0.2 4.8 1.4 2.2 0.8 50 4.8 1.4 1.4 0.0 3.0 0.4 3.0 1.6 51 4.0 0.6 2.0 0.6 4.2 0.8 2.1 0.7 52 3.5 | 0.1 1.6 0.2 4.5 a Fe 1.5 0.1 53 3.1 0.3 0.8 0.6 3.1 0.3 1.4 0.0 54 4.7 1.3 1.5 0.1 4.6 1.2 1.5 0.1 55 3.2 0.2 0.7 0.7 4.2 0.8 1B 0.2 56 4.1 0.7 12 0.2 4.2 0.8 1.6 0.2 57 1.2 1.2 2.0 0.6 2.4 1.0 1.5 0.1 58 3.4 0.0 1.0 0.4 2.8 0.6 A Be 0.3 59 2.0 1.4 1.0 0.4 1.8 1.6 3.0 1.6 60 3.0 0.4 2.2 0.8 4.8 1.4 2.2 0.8 61 1.0 2.4 0.5 0.9 4.8 1.4 1.4 0.0 62 1.5 1.9 0.6 0.8 3.5 0.1 1.5 0.1 63 pee | 2.3 0.7 0.7 3.7 0.3 1.4 0.0 64 1.0 2.4 d yy 0.3 3.0 0.4 1.2 0.2 65 3.1 0.3 1.3 0.1 4.2 0.8 i By | 0.3 66 5.0 1.6 1.8 0.4 3.8 0.4 1.8 0.4 67 3.6 0.2 1.5 0.1 3.1 0.3 1.6 0.2 Gs ./ 21 13 _ 2.0 0.6 2.8 0.6 1.4 0.0 69 4.4 1.0 bai | 0.3 4.8 1.4 1.5 0.1 70 3.1 0.3 1.2 0.2 3.5 0.1 1.5 0.1 71 5.0 2.1 Ld 0.3 2.8 0.6 0.4 0.0 72 3.6 0.2 1.4 0.0 3.2 0.2 2.0 0.6 73 3.8 0.4 1.0 0.4 5.2 1.6 1.8 0.2 74 3.8 0.4 0.3 ba | 3.3 0.1 1.2 0.2 75 5.4 2.0 1.2 0.2 4.5 2 i I 0.3 76 3.8 0.4 1.2 0.2 2.8 0.6 1.4 0.0 77 4.6 1.2 1.6 0.2 3.0 0.4 3.7 2.3 78 1.5 1.9 1.5 0.1 4.7 be 6 1 0.3 79 5.0 1.6 1.8 0.4 3.8 0.4 1.2 0.2 80 3.1 0.3 1.9 0.5 4.0 0.6 Lay 0.3 81 3.5 0.1 Ae 0.4 4.1 0.7 1.0 0.4 | -_—_o- Mean 3.40+.08 0.9 1.40+.03 0.4 c == 1.067.056 om 50202 C.V. = 31.2+1.7% = 35.7+2.1% E == 2.3% = 2.1% vA So Cre G ho “1 6 1918 | Waynick: A Statistical Study of Nitrification in Soil 2% TABLE 3 NITRATE PRODUCED FROM 0.2 GRAM OF AMMONIUM SULPHATE IN 100 GRAMS OF SOIL 1”~6" 6”-24" 1”—6” 6”-24" Nitrate Devia- Nitrate Devia- Nitrate Devia- Nitrate Devia- nitro- tion from __nitro- tion from nitro- tion from nitro- tion from gen mean + gen mean-+ No. gen mean + gen mean + Mgs. Mgs. Mgs. Mgs. Mgs. Mgs. Mgs. Mgs. 6.6 1.6 1.8 1.0 42 2.1 2.9 6.3 3.5 4.3 0.7 3.7 0.9 43 6.2 1.2 3.0 0.2 8.0 3.0 2.9 0.1 tt 5.2 0.2 1.0 1.8 6.0 1.0 3.3 0.5 45 2.3 2.7 1.2 1.6 4.2 0.8 3.3 0.5 46 1.8 3.2 1.8 1.0 6.0 1.0 2.5 0.3 47 2.5 2.5 1.5 1.3 5.6 0.6 3.2 0.4 48 2.5 2.5 1.2 1.6 5.0 0.0 ' 43 1.5 49 2.0 3.0 1.2 1.6 5.8 0.8 4.0 1.2 50 2.3 2.7 2.2 0.6 5.3 0.3 3.8 1.0 51 4.8 0.2 2.3 0.5 4.0 1.0 1 fl ieg'4 52 5.9 0.5 3 Ely 1.1 5.9 0.5 3.0 0.2 53 5.4 0.4 L7 1.] 5.0 0.0 2.8 0.0 54 6.5 1.5 2.8 0.0 4.6 0.4 2.8 0.0 55 2.3 2.7 3.2 0.4 5.0 0.0 3.1 0.3 56 5.2 0.2 1.2 1.4 6.5 1.5 3.3 0.5 57 2.2 2.6 1.5 1.3 4.6 0.4 5.7 1.9 58 3.6 1.4 3.2 0.4 5.0 0.0 4.0 1.2 59 2.2 2.6 5.0 2.2 6.0 1.0 4.0 1.2 60 3.5 1.5 6.0 3.2 5.0 0.0 2.4 0.4 61 4.2 0.8 3.5 0.7 5.4 0.4 2.8 0.0 62 7.2 2.2 2.0 0.8 6.0 1.0 3.4 0.6 63 7.3 2.3 2.4 0.4 6.5 1.5 3.2 0.4 64 3.7 13 4.1 1.3 4.8 0.2 2.0 0.8 65 5.7 0.7 0.2 0.0 5.3 0.3 2.7 0.1 66 3.8 1.2 2.5 0.3 5.5 0.5 5.4 2.6 67 4.9 0.1 3.0 0.2 4.4 0.6 4.8 2.0 68 4.8 0.2 4.0 1.2 7.5 2.5 4.7 1.9 69 6.8 1.8 1.0 1.8 7.6 2.6 2.8 0.0 70 5.8 0.8 1.3 1.5 6.2 1.2 1.9 0.9 (A 4.0 1.0 1.0 1.8 4.2 0.8 2.6 0.2 72 1.8 3.2 4.0 1.2 5.0 0.0 3.2 0.4 73 5.3 0.3 2.3 0.5 6.0 1.0 3.0 0.2 74 5.8 0.8 3.8 1.0 4.5 0.5 2.2 0.6 75 8.2 3.2 1.5 1.3 4.8 0,2 1.6 1.2 76 5.5 0.5 2.5 0.3 4.8 0.2 1.5 1.8 77 6.2 1.2 3.1 1.5 4.0 1.0 2.6 0.2 78 6.0 1.0 3.0 12 5.4 0.4 2.5 0.3 79 6.3 1.3 2.6 0.2 5.2 0.2 2.8 0.0 80 6.0 1.0 3.9 0.7 6.6 1.6 2.0 0.8 81 6.0 1.0 3.2 0.4 6.4 1.4 2.0 0.8 ———_ —- ——_—_—_—_—_—_——- -— Mean 5.00.10 1.0 2.80+.08 0.9 o = 1.50+.08 G== LOAF C.V. = 29.4+1.6% = 40.7+2.4% E = 2.0% = 3.4% 1 — University of California Publications in Agricultural Sciences | Vol. 3 7 ur wore © 1m 6) bd —- © ie) cosy co OI bo bo bo bo bo ne bo po bo bo Oo TABLE 4 NITRATE PRODUCED FROM 0.2 GRAM OF BLOOD IN 100 GRAMS OF SOIL 1”—6” 6”—24” 1”-6” 6”—24" Nitrate Devia- Nitrate Devia- Nitrate Devia- Nitrate Devia- nitro- tion from nitro- tion from nitro- tion from nitro- tion from gen mean + gen mean + No. gen mean + gen mean + , Mgs. Mgs. Mgs. Mgs. Mgs. Mgs. Mgs Mgs. 27.0 6.0 11.0 0.3 42 7.0 14.0 20.0 9.5 20.0 1.0 10.0 0.7 43 18.0 3.0 10.0 0.5 13.0 8.0 14.0 3.3 44 18.0 3.0 13.0 2.3 30.0 9.0 15.0 4.3 45 21.0 0.0 12.0 1.3 18.0 3.0 25.0 14.3 46 13.0 8.0 14.0 3.3 40.0 19.0 25.0 14.3 47 18.0 3.0 19.0 8.3 20.0 1.0 18.0 7.3 48 20.0 1.0 12.0 1.3 14.0 7.0 16.0 5.3 49 21.0 0.0 18.0 7.3 | 20.0 1.0 10.0 0.7 50 =. 20.0 1.0 17.0 6.3 22.0 1.0 16.0 5.3 51 24.0 3.0 9.0 1.7 4 18.0 3.0 14.0 3.3 52 21.0 0.0 10.0 0.7 22.0 1.0 12.0 1.3 58 27.0 6.0 12.0 1.3 ; 23.0 2.0 13.0 2.3 54 32.0 11.0 22.0 11.3 22.0 1.0 5.5 5.2 55 = 82.0 11.0 7.0 3.7 16.0 5.0 5.6 5.1 56 =. 20.0 1.0 18.0 | . 21.0 0.0 7.0 a7 57 27.0 6.0 10.0 0.7 } 16.0 5.0 8.0 2:7 58 27.0 6.0 4.3 6.4 20.0 1.0 5.0 5.7 59 14.0 7.0 3.0 1 Bh F 21.0. 0.0 5.5 5.2 60 30.0 9.0 20.0 9.5 . 13.0 8.0 7.7 3.0 61 22.0 1.0 4.3 6.4 } 24.0 3.0 5.0 5.7 62 23.0 2.0 10.0 0.7 7 15.0 6.0 10.0 0.7 63 24.0 3.0 9.0 1.7 ; 22.0 1.0 14.0 3.5 64 14.0 7.0 4.8 5.9 24.0 3.0 8.0 2.7 65 29.0 8.0 10.0 0.7 : 19.0 2.0 8.0 27 66 21.0 0.0 10.0 0.7 4 20.0 1.0 10.0 0.7 67 28.0 7.0 6.5 4.2 4 21.0 0.0 20.0 3.5 68 23.0 2.0 7 0.0 i 21.0 0.0 12.0 1.3 69 19.0 2.0 5.5 5.2 20.0 1.0 4.4 6.3 70 »3=16.0 5.0 3.7 7.0 11.0 10.0 5.9 4.8 Ee - 150 4.0 2.7 8.0 20.0 1.0 7.4 3.3 72 97.0 6.0 4.0 6.7 17.0 4.0 14.0 3.3 73 ~=30.0 9.0 5.3 5.4 10.0 11.0 13.0 2.3 74 28.0 7.0 24.0 13.3 20.0 1.0 5.0 5.7 75 25.0 4.0 10.0 0.7 15.0 6.0 2.4 8.3 76 22.0 1.0 12.0 1.5 12.0 9.0 8.5 2.2 77 2380 7.0 4.2 6.5 19.0 2.0 11.0 0.3 78 24.0 3.0 9.0 17 16.0 5.0 14.0 2.3 79 220 1.0 12.0 1.3 14.0 7.0 8.0 2.7 80. 17.0 4.0 7.2 3.5 13.0 8.0 5.7 5.0 81 30.0 9.0 21.0 10.3 27.0 6.0 11.0 0.3 ————— ee Mean21.10+0.4 4.0 10.70+0.4 4.5 o = 5.70+0.30 o= 5.30+.30 C.V. =27.141.5% = 49.4+3.1% E = 2:8% = 40% 1918 | Waynick: A Statistical Study of Nitrification in Soil 253 TABLE 5 SUMMARY OF STATISTICAL DATA Coefficient Probable Standard of error of Mean Ixtremes deviation variability mean + Milligrams Milligrams Milligrams Per cent Per cent Residual nitrate, Surface .......... 2.70.05 1.4—4.5 0.70+.04 25.9 2.1 1.8 PE DBGIE « ccnacgacks 0.70.03 0.38-1.2 0.36.02 51.4+ 3.3 4.3 Incubated blanks. Surface .......... 3.40.08 1.0-—5.5 1.06.05 o1.2+ 1.7 2.3 SOUL \wcncacacndec 1.40.08 0.1-—2.2 0.50+.02 5 i ew ly Ded (NH,).80.. Surface .......... 5.00.10 1.8—8.2 1.50+.08 29.4+ 1.6 2.0 Sc) oo 2.80.08 0.2-3.2 mW ON Doo mag OO 40.7 2.4 5 Blood. eke: hee i 21.00.40 7.0—40.0 5/02: .30 oth Le 1.9 PRE BOLL: padvcteecice 10.70+.40 1.7—25.0 FE TN reas 1 49.4+ 3.1 4.0 Unless otherwise stated, the probable error of any value has been used directly as found in the discussion which follows so that there is simply an even chance that the results so treated fall within, or without, the limits of their respective probable errors. The effect of multiplying the probable error by two, three, or any higher number, may be found by referring to the reference cited above. DISCUSSION OF EXPERIMENTAL RESULTS To express the results in concise form, table 5 has been inserted to summarize briefly the data of the preceding tables. In the first column the means of the various series are given with their respective probable errors. In the case of residual nitrate, 2.7 milligrams in one hundred grams of soil represent .0027 per cent of the soil or approximately 54 pounds of nitrate nitrogen per acre, considering only the upper six inches of the soil mass. The probable error of the determination amounts to .00005 per cent of the soil so that it is an even chance that the mean of the eighty-one determinations is correct within one pound per acre. In the subsoil, the mean of 14 pounds per acre, is within 0.6 pounds of the correct figure, on the same basis. The extreme range amounts to 62 pounds in the surface soil and 18 pounds per acre in the subsoil, both figures being of greater magnitude than the means of the two series. It is not possible to translate the other figures into a practical pounds per acre basis, since they represent laboratory treat- ments. 254 University of California Publications in Agricultural Sciences | Vol. 3 The extremes recorded in column two are simply the extreme deter- minations found in any one series. The extreme range may be deter- mined by taking the difference between these two figures. The greatest extremes are shown by the samples to which dried blood was added, with the ammonium sulfate samples a close second. The results for any one series emphasize the very large difference found between a large number of samples treated as uniformly as possible. It will be noted that the coefficients of variability as regards the surface samples with their various treatments differ but little among themselves, this difference amounting to only 5.3 per cent. The differ- ence is greater with the four series in which the subsoil was used, being 15.7 per cent or nearly three times that of the surface samples. The point is again emphasized here that we are dealing with the summations of all the errors to which the samples are subject, both field and laboratory. One source of error has been allowed for, which is of a purely mechanical nature, namely, that of making the readings with the colorimeter. This error will be considered in the following section, and the coefficients of variability discussed at greater length there. The percentage ratios given as the probable error of the mean place all the results on a comparable basis as regards the error to which the various means are subject. Attention is called to the fact that these figures are of similar magnitudes in the four series of surface samples while showing much larger differences in the subsoil samples with their various treatments. It will be noted from tables 1, 2, and 3 that in a number of samples there was less actual nitrate nitrogen found in the subsoil samples after incubation without the addition of anything but water, or with the addition of 0.2 gram of ammonium sulphate, than was present in the soil of corresponding samples as they came from the field. This result was not anticipated and no explanation to account for this loss of nitrate nitrogen is offered at the present time. It is, however, regarded as of biochemical interest largely and not of importance as regards the variation between samples at the time the determinations were actually made. ERROR OF THE DETERMINATIONS DUE TO THE COLORIMETER Reference has already been made to the absolute accuracy of the nitrate determination and its bearing upon the results reported in the present paper. Aside from the absolute accuracy of the determina- 1918 } Waynick: A Statistical Study of Nitrification in Soil 255 tions, it is desired to consider briefly the error in making the readings on the colorimeter due to the inability of the eye to detect small changes in the depth of color between the standard employed and the unknown solutions. All workers in soil chemistry are familiar with the Kenicott-Sargent colorimeter, so that the instrument itself needs no description here. To check the readings on the unknown solutions, a solution was prepared of the average strength of the residual nitrate determined in the first series reported. Sixteen equal volumes of this solution were taken and treated exactly as the soil extracts were treated. The average amount of nitrate nitrogen found in the sixteen portions was the same as that for the series referred to above, namely, 2.7 milligrams. The actual determinations, together with the calculated statistical constants, are reported in table 6. The probable error of the mean of sixteen samples, together with the error to which both larger and smaller numbers of samples are subject, is given in table 7. The calculations have been made by the use of the formulae already given. It is evident that the calculation of the probable error from sixteen, instead of a larger number of samples, makes it less reliable than if a larger number had been used, but since the error from this source is relatively small as compared to the error due to field sampling, it is deemed of sufficient accuracy for the purpose in hand. This error will be referred to as the laboratory error to distinguish it from the error due to sampling. TABLE 6 COEFFICIENT OF VARIABILITY AND PROBABLE ERROR OF COLORIMETER READINGS Nitrate Deviation Nitrate Deviation No. nitrogen from mean+ No. nitrogen from mean + Milligrams Milligrams Milligrams Milligrams ] 2.5 0.2 9 2.6 0.1 2 2.8 0.1 10 2.8 0.1 3 2.8 0.1 1] 3.0 0.3 4 2.9 0.2 12 2.6 0.1 5 2.5 0.2 13 2.4 0.0 6 2.6 0.1 14 yy | 0.0 7 2.8 0.1 15 2.6 0.1 8 2.6 0.1 16 2.7 0.0 Mean 2.7+.02 0.1 ee = eee C.V. —48+.5% E = 0.8% M 256 University of California Publications in Agricultural Sciences | Vol. 3 It will be noted that the probable error of a single nitrate deter- mination is 2.7 + .09 milligrams or 3.2 per cent of the amount deter- mined. The error for a single determination, expressed on the field samples as a percentage, is 17.4 or about 5.1 times greater than the laboratory error, even after making allowance for this error. With sixteen determinations, the probable error becomes 2.7 + .022 milli- grams or 0.8 per cent. Further, with eighty-one samples, the probable error is only 2.7 + .009 milligrams or 0.3 per cent. In allowing for this laboratory error in the various series reported, it is evident that it becomes relatively larger the smaller the amount of nitrate determined within the lmits of the amounts found in the present study. In other words, the probable error will remain the same while the amount of nitrate determined decreases, so that the probable error will form a larger percentage of the determination. On the other hand, the probable error becomes relatively smaller as we increase the actual amount of nitrate nitrogen again within the limits of the amounts reported here. The same is true for the ¢o- efficient of variability. This increased ratio is brought out in table 8, which is simply a reconstruction of table 5, after making allowance for the laboratory error. The coefficient of variability computed from the standard deviation (.18 + .01 mg.) and the average amount, of nitrate nitrogen reported for the various series is given in column one. This figure is the largest for the subsoil samples in the field and the smallest for the surface samples treated with blood, the mean of the eighty-one readings being 0.7 and 21.0 milligrams, respectively, in the two eases. In the second column, the corrected coefficients of variability for the field samples are given, these being the difference between coefficients of variability before the laboratory error was allowed for and the various coefficients of variability given in column one. It will be noted that the same TABLE 7 SHOWING THE DECREASE OF LABORATORY ERROR AS NUMBER OF DETERMINATIONS INCREASE Number Probable Probable Number Probable Probable of error of error of of error of error of samples mean mean samples mean mean Milligrams Per cent Milligrams Per cent 1 2.700+.087 &.2 36 014 0.5 4 .043 1.6 49 .012 0.4 9 .039 i Fa 64 O11 0.4 16 .022 0.8 81 .009 0.3 25 017 0.7 1918 | Waynick: A Statistical Study of Nitrification in Soil 257 qualitative relations hold as between the various treatments in every case except the incubated subsoil samples which are somewhat less variable than the surface samples. With the other three series, the subsoil samples still show a much higher coefficient of variability than the surface samples, as do the samples treated with fertilizers in the laboratory in contrast with the untreated field samples. The per- centage probable errors or laboratory errors are shown in column three, while the corrected figures for the field samples are given in eolumn four. Referring again for a moment to table 6, it is evident that the laboratory error increases as the square root of the number of deter- minations made, so that the mean of any number of readings on the colorimeter becomes less reliable, the fewer the number, exactly as the mean of a fewer number of samples is less accurate than the mean of a larger number. In other words, the curves of the errors of the various determinations are parallel, as will be seen by reference to figure 2. This fact must be kept in mind in considering the results given in the following section. RESULTS OF RANDOM SAMPLINGS It is of very direct interest to consider for a moment the accuracy of the mean of a limited number of samples taken at random. Ten surface samples are included in the first group (table 9) and sixteen in the second (table 10), since about these numbers of samples have TABLE 8 SUMMARY OF STATISTICAL DATA AFTER MAKING ALLOWANCE FOR THE LABORATORY ERROR Coefficient Corrected Corrected of variability coefficient probable (laboratory of Laboratory error of error) variability error mean Per cent Per cent Per cent Per cent Residual nitrate. oh oe 4.8+ 0.2 91 1 34 0.3 £5 ES eS ee 18.5 1.0 32.9 3.4 1.2 3.1 Ineubated blanks. Le a oe 3.8 0,2 oT ae Lat 0.3 2.0 Le Re 9.2% 0.5 25.52: 2.1 0.7 Ammonium sulfate. purines 2.5. 54... 2.6 0.1 26.8 1.6 0.2 1.8 So ee 4.6+ 0.2 36.1 2.4 0.4 3.0 Blood. I Soci ecncnmeetcnss 0.6 0.03 26.5-= 1.56 0.05 1.9 2 | Se 1.2+ 0.10 48.2+ 3.1 0.09 3.9 258 University of California Publications in Agricultural Sciences | Vol. 3 frequently been used in making up a composite sample. It is assumed — EEE for the time being that the amount of nitrate actually found in a composite sample is that expressed by the mean of any given number of samples. All the calculations have been made upon the samples reported in the tables below just as if these were the only samples taken from the area, as would be done if such a number of samples were used in an independent investigation. In this case, however, we have a much larger number of samples to check the accuracy of the results obtained with the fewer number. Table 9 gives the amounts i i a i a i of nitrate found in ten surface samples, numbered from forty-two to TABLE 9 VARIABILITY OF TEN SURFACE SAMPLES TAKEN AT RANDOM } Residual nitrate Incubated blanks (NH,)2SO, Blood . Nitrate Devia- Nitrate Devia- Nitrate Devia- Nitrate Devia- : : nitro- tion from _nitro- tion from nitro- tion from nitro- tion from No. gen mean + gen mean —+— gen mean + gen mean + Mgs. Mgs. Mgs. Mgs. Mgs. Mgs. Mgs. Mgs. 42 3.0 0 45 06 21 10 7.0 10.0 ; 43 3.4 0.4 3.8 0.1 6.2 3.1 18.0 1.0 44 1.8 1.2 3.0 0.9 5.2 2.1 18.0 1.0 | 45 2.5 0.5 4.0 0.1 2.3 0.8 21.0 3.0 46 2.1 0.9 3.0 0.9 1.8 13° > 138 4.0 47 4.0 1.0 3.8 0.1 2.5 0.6 18.0 1.0 48 3.1 0.1 3.3 0.6 2.5 0.6 20.0 3.0 49 4.4 1.4 5.2 1.3 2.0 1.1 21.0 4.0 f 50 3.5 0.5 4.8 0.9 2.3 0.8 20.0 3.0 ; 51 2.3 0.7 4.0 0.1 4.8 0.7 24.0 7.0 ; Mean 3.0041.7 0.6 3.90+.15 0.6 3.10+.31 1.3 17.00.89 3.7 { o 0.80+0.12 0.70+.10 1.50+.22 4.70+.63 ’ C.V. 26.7+4.3% 17.9+2.7% 48.4+3.9% 24.7+3.8% ’ E 5.7% 3.8% 10.0% 5.2% ' M fifty-one, inclusive. It will be noted that these samples are taken in a straight line (see fig. 1), while the sixteen samples are taken indis- criminately over the area. Considering the residual nitrate alone, it is seen that the mean of the ten samples is 0.30 milligrams above the mean of the total number of samples. Further, the probable error of the mean is increased from + .05 milligram to + .17 milligram or, in terms of the probable error, the chances are about 3 to 1 that the difference between the two results is a significant one.* The coefficients of variability are very nearly the same in the two instances. * The probable error of the differences between two results is caleulated from the formula: Probable error of difference = 2° ES E. 1918 | Waynick: A Statistical Study of Nitrification in Soil 259 In the incubated samples, the probable error of the difference be- tween the samples is 0.50 + .17 milligrams, for the samples to which ammonium sulfate was added 1.90 + .31 milligrams, and for dried blood 4.00 + .97 milligrams. It is worthy of note that the probable error of the differences between eighty-one samples, to which ammonium sulfate was added, and the ten samples given above is no less than 6 to 1.7 The coefficient of variability of the ten samples is greatly increased, TABLE 10 VARIABILITY OF SIXTEEN SURFACE SAMPLES TAKEN AT RANDOM Residual nitrate Incubated blanks (NH,)2SO, Blood RE SE a Nitrate Devia- Nitrate Devia- Nitrate Devia- Nitrate Devia- nitro- tion from _ nitro- tion from _nitro- tion from _nitro- tion from No. gen mean + gen mean + gen mean + gen mean + Mgs. Mgs. Mgs. Mgs. Mgs. Mgs. Mgs. Megs. 1 2.5 2.0 4.3 1.0 6.6 2.2 27.0 8.0 3 3.0 0.5 2.2 be 8.0 p.6 13.0 6.0 7 3.3 0.8 1.8 1.5 6.6 2.2 20.0 1.0 9 2.5 0.0 4.8 1.5 5.8 1.4 20.0 1.0 30 2.6 0.1 3.0 0.2 6.2 1.8 11.0 8.0 34 2.8 0.3 3.3 0.0 4.5 0.1 20.0 1.0 37 1.0 1.5 3.0 0.3 4.0 0.4 19.0 0.0 40 3.6 a i 4.0 0.7 6.6 2.2 13.0 6.0 42 3.0 0.5 4.5 1.2 2.1 2.3 7.0 12.0 46 2.1 0.4 3.0 0.3 1.8 1.6 13.0 6.0 49 4.4 1.9 5.2 1.9 2.0 2.4 21.0 2.0 53 2.3 0.2 3.1 0.2 6.4 2.0 27.0 8.0 57 1.8 0.7 1.2 2.1 2.2 2.2 27.0 8.0 59 1.3 1.2 2.0 1.3 2.2 2.2 14.0 5.0 60 2.0 0.5 3.0 0.3 3.5 0.9 30.0 11.0 72 2.7 0.2 3.6 0.3 1.8 2.6 27.0 8.0 Mean 2.50+.14 0.6 3.30+.17 0.9 4.40+.35 1.9 19.00+1.1 6.0 o 0.80+.10 1.00.12 2.10+.26 6.70.08 C.V. 34.444.5% 30.3+3.9% 47.7+6.4% 35.244.6% E,, 5.6% 5.2% 7.9% 5.8% being 48.4 + 3.9 per cent. On the other hand, it happens that the incubated blanks vary even less than the eighty-one samples, the co- efficients of variability being 17.9 + 2.7 per cent and 31.2 + 1.7 per cent respectively. It is seen from these results that very wide varia- tions may be found when only ten samples are used in making a composite sample and that that number of determinations is by no means enough to be an accurate measure of the actual nitrate nitrogen content when the variations are of the magnitudes of those noted above. Turning for a moment to the results given in table 10, we find that + For table of odds to aid in estimating the significance of differences between two results, see Batchelor and Reed, Jour. Agr. Res., vol. 12, pp. 265-266, 1918. 260 University of California Publications in Agricultural Sciences [ Vol. 3 the probable error of the difference between the mean of the sixteen samples taken purely at random, and the entire number of determina- tions made, to be .20 + .15 milligrams, with a coefficient variability of 34.4 + 4.5 per cent as contrasted with 25.9 + 2.1 per cent for the total number. The difference between the number of samples considered here and the total number is not significant with the incubated blanks, but with the ammonium sulfate samples the probable error of the difference between the means is 0.66 + .33, and with dried blood 20+ 1.1. The chances are somewhat less than 2 to 1 that the differ- ences between the sixteen samples here considered and the total eighty- TABLE 11 EFFECT OF DISTANCE UPON THE VARIABILITY IN SAMPLING—RESIDUAL NITRATE Five-foot radius Twenty-five foot radius Fifty-foot radius Nitrate Deviation Nitrate Deviation Nitrate Deviation No. nitrogen from mean No. nitrogen from mean No. nitrogen from mean Milligrams Milligrams Milligrams Milligrams Milligrams Milligrams 2 2.8 0.4 6 2.7 0.3 1h 3.0 0.5 12 2.7 0.5 16 3.0 0.6 21 3.0 0.5 22 4.5 1.3 26 3.4 1.0 31 13 1.2 32 a 0.1 36 1.3 y R| 41 3.8 13 42 3.0 0.2 46 2.1 0.3 51 2.3 0.2 52 3.1 0.1 56 2.5 0.1 61 1.5 1.0 62 4.0 0.8 66 2.0 0.4 t 3.5 1.0 72 2.7 0.5 76 2.6 0.2 81 2.0 0.5 Mean 3.20+.14 a3) 2.40+.14 0.4 2.50.19 0.6 ¢ 0.60+.10 0.60+.10 0.80.13 C.V. 18.7+3.3% 25.0+4.5% 32.0+5.8% Ey 44% 5.8% 7.6% one samples are significant. It is evident that caleulations made from the mean of sixteen samples are of a higher degree of accuracy than when only ten samples are used, but the number is still too few to give results of a high order of reliability, and could by no means be taken as truly representative of the entire area under consideration. Other numbers and other groupings may be selected and the mag- nitude of their means and their accompanying probable errors and coefficients of variability computed from the data reported in tables 1 to 4. EFFECT OF DISTANCE UPON VARIABILITY To determine whether or not the distance apart the samples were taken is a factor of importance in sampling, the arrangement given in table 11 has been made. The results shown in the table are for residual 1918 | Waynick: A Statistical Study of Nitrification in Soil 261 nitrate in the surface samples only. The first group of determinations, from numbers two to seventy-two, inclusive, by intervals of ten, were recorded from samples lying within a radius of five feet of number one. The mean of the eight readings is 3.20 + .14 milligrams or 0.5 —& .15 milligrams above the mean for the whole number of samples. The coefficient of variability is, however, relatively low. The second group of determinations from numbers six to seventy- six, varying as those of the group above, are of the samples on the circle with a radius of twenty-five feet from the center. The mean of this group of eight determinations is 2.40 + .14 milligrams or 0.3 + .15 below that of the established mean as already given. The coefficient of variability in this case is nearly the same as for the total of eighty- one samples, however. The last group of determinations represents the nitrate found in the samples taken as the fifty-foot radius. The mean of the eight determinations is 2.50 + .20 milligrams; 0.70 + .24 milligrams and 10 + .24 milligrams. In two eases, the differences are significant; in the third, the probable error is greater than the difference and holds between the most widely separated samples taken on the twenty-five and fifty-foot radii. Even though only eight samples are considered in any one group, the conclusion seems justified that the distances apart samples are taken is of little importance, except in so far as their distribution be uniform over the area to be sampled. —— a Vn 30 I. Laboratory Error. 2. Residual Nitrate. 6224" 3. “ " 1-6" 4. Incubated Blanks 6" 24" 5 . " '- 6" 6 Ammonium Sulfate 6-24" Z . - 76" 8 Blood 6"-24" 20 9. ” 1"--6" mg. Nitrate. Nitrogen a 1 eee rs fe) 4S, Se —_——__= ———— 14 9 16 25 36 49 64 8) No. of Samples. 1918 | Waynick: A Statistical Study of Nitrification in Soil 263 and since the standard deviation in this instance is 0.7 gram, hence 6745 & 0.70 Vn We can make Hy of any dimension desired and since our method of 4M— determining nitrates allows of direct determinations only to 0.1 milli- gram, we will use this number for the probable error of the mean of the desired number of determinations so that 6745 & 0.70 0,40 == Vn from which:n = 22. It must be remembered, however, that the labora- tory error increases as we decrease the number of determinations in the same manner as the probable error of our sampling, so that this increased error must be taken into account in estimating the number of samples necessary to ensure any desired degree of accuracy. Refer- ring to table 7, we find that the probable error of making the readings on the colorimeter for twenty-five samples is .017 milligram or very nearly .018 milligram for twenty-two samples, so that for a probable error of 0.1 milligram we have __ .6745 & 0.13 = Vn and n=1. Thus twenty-three samples are sufficient so that the probable error in the mean is 0.10 milligram. The taking into +().] account of the laboratory error involves an extra calculation, which, for all practical purposes, may be avoided by the use of a table, such as shown by table 12 (represented graphically in figure 2), which has been calculated from the data given in tables 1, 2, 3, and 4, after the manner already outlined. It will be noted that this table is of limited range and accounts for numbers of samples less than eighty- one, but may be extended for a range greater than the one given if desired. The approximate number of samples may be readily found after the following manner. It is desired to determine the number ot ammonium sulfate samples necessary to be taken to ensure the same degree of accuracy as for twenty-three residual nitrate samples, of which the probable error of the mean was calculated to be 0.10 milligram. By reference to table 12, it is found that about eighty-one samples are required without taking the laboratory error into account. This error is .009 milligram (table 7) for eighty-one samples, an amount less than one per cent of the error which we are allowing for and hence 264 University of California Publications in Agricultural Sciences | Vol. 3 negligible, for all practical purposes, when the probable error of the sampling is of as great a magnitude as 0.1 milligram. It must be recognized that the mean of the number of samples so calculated may be found to have a greater or less probable error in practice so that a greater number of samples than calculated should be taken. This relation has already been brought out in the previous section, where it was shown that the fewer the samples, the less representative of the total area they became. By an inspection of table 12, it is evident that the number of samples necessary to secure the degree of accuracy which we established for the residual nitrate samples must be very greatly increased, when we are dealing with ammonium sulfate or blood treated samples. TABLE 12 PROBABLE ERROR WITH VARYING NUMBERS OF DETERMINATIONS Number’ Residual nitrate Incubated blanks Ammonium sulphate Blood on 1"-6" 6”-24” 1"-6" 6-24" 1”"-6" 6”-24” 1”-6" 6”-24” Mgs. Mgs. Mgs. Mgs. Mgs. Mgs. Mgs. Mgs. 47 .24 ay mH} 1.01 74 3.8 3.5 + .23 12 oT 16 oO .oT 1.9 BB 9 16 .08 25 af o 20 1.2 be 16 12 .06 18 .O8 .20 19 1.0 0.9 25 .09 .05 14 .06 20 15 .08 0.7 36 08 — .04 12 .05 me Wy 12 0.6 0.6 49 07 .035 10 .048 14 10 0.5 0.5 64 .06 .03 .09 04 12 .O9 0.48 0.45 81 05 .03 .08 .03 10 .08 0.4 .04 It will be remembered that throughout the discussion, we have con- sidered the probable error of the mean of any given series of samples directly, so that we have but an even chance that the mean for any given number of determinations made will be of significance. It is usual to consider about three times the probable error as a significant difference between two given means, hence if we are to establish this standard as regards the number of samples taken, we must increase all the figures given by three times.* It is obvious that such a number of samples in the case of dried blood, for instance, would be far beyond practical limits as regards the making of the determinations. The chances are that the use of a fewer number of samples means a low degree of reliability for any determinations made. If soil biologists are to continue to make beaker tests with fertilizers, the results must be interpreted from this viewpoint. * By multiplying the probable error found by 3.17 the chances are thirty to one that a difference greater than the figure so found is significant. 1918] Waynick: A Statistical Study of Nitrification in Soil 265 While we are not justified in using the results obtained from labora- tory treatments as direct criteria of what will happen in the field, it is probable that greater variability will be found in field plots which have been subject to treatment with fertilizers than in the normal soil to which no fertilizers have been added, especially when the fertilizer is of such a complex nature as dried blood. It must further be emphasized that the figures as given above apply only to the soil under discussion; each soil with the treatment applied must be considered as a unit in a statistical study. It is evident that a standard established for the residual nitrate, for instance, will not hold for the nitrate produced from a one per cent application of blood. The exact correlation between the various laboratory treatments and between those treatments and results secured in the field is reserved for discussion in a future publication. REPRESENTATIVE AND COMPOSITE SAMPLES It is evident from the results already presented in various group- ings that a representative sample of any soil is a purely hypothetical quantity whose constituents may only be determined indirectly. It is also evident that determinations reported from only one sample of a given area are practically worthless, when the errors to which it is subject are of the magnitudes shown above. Composite samples made up from a small number of single samples are of little more value. Not until enough samples have been taken to enable the proper calcu- lation of the probable error of the mean of a given number of samples is the making of a composite sample justified, since the results obtained from working with such a sample are of very limited value unless the error to which the composite sample, itself, is subject, can be deter- mined. It seems, therefore that the use of the word composite as relating to soil samples is only justified when the variations to which the individual samples are subject are known and enough samples taken to establish the error to which the composite, as a mean of all the samples, is hable. The magnitude of the error which is liable to creep into the determinations due to imperfect mixing in a composite sample is no doubt worthy of consideration, but since its value is undetermined, it has been assumed that a composite actually represents the mean of all the samples taken. Just how reasonable such an assumption may be remains for future investigations to bring out. 266 University of California Publications in Agricultural Sciences [ Vol. 3 GENERAL DISCUSSION It has already been stated that the area under discussion was of very limited extent and as free from apparent variations as any area is likely to be. Also, that the treatment and climatic influences had all tended toward a state of biologic equilibrium as regards nitrate production in this particular soil. With this viewpoint in mind, the importance of applying a statistical interpretation to results obtained from working with a given soil type obtained under conditions much less favorable, becomes doubly important. It is not at all improbable that variations several times greater than those reported will be found in many instances and the number of samples deemed sufficient in this case must be increased to obtain any considerable degree of accuracy. It is possible that areas more uniform than the one used will be found, but it is hardly probable that such will be the case. While the present paper deals only with the production of nitrates, not only the variability of the products of microdrganic activities, but the chemical constituents of any soil should be studied in a similar manner to determine just how reliable past results in soil investigations may be. It is beyond question that before we can have faith in future results, we must apply the principles outlined. . Typical Washington Navel tree in San Joaquin Valley, showing heavy bloon oa « Ms UNIV. CALIF. PUBL. AGR. SCI. VOL. S [ COIT—HODGSON ] PLATE 27 PLATE 28 ry Nearer view of same tree, showing details of heavy bloom, “1ENd ‘dl So 1A oS sal > 3JiWid [ NOSDSGOH-LIOOD ] PLATE 29 One branch with leaves removed, showing large number of buds produced. _ [842] PLATE 30 _ Typical abscissed fruits. Those to the right abscissed at the base of the pedicel, those to the left at the base of the ovary. The two in the center a healthy fruits picked from the tree for comparison. q Te UNIV, GALIF. PUBL: AGR.USGI. VOL. Ss [ COIT—HODGSON ] PLATE 30 PLATE 31 Small dead orange persisting though abscissed both at base of ovary and pedicel. Large fruit safely through both abscission periods. The dead style abscissed much earlier but was retained in position by the ragged nature of the break. [346] 31 { COIT—HODGSON ] PLATE ra Oo VOL, 4 Ss PUBL. AGR. UNIV, CALIF. Teese ri uel Ah) Ae To. PLATE 32 “ | The serious wounds produced by katydids which never result in abs¢ iss UNIV, CALIF, must, AGR. S( VOL, n ] [ COIT HODGS ( 4 fr | 1 | PLATE af 2& ts i, § en ON fe Seen De a Neues ry al i) mm tf i a | ceo T hia . ; 6 i. } eT a ees yd Pee | . \ - . # ee ‘ 7 > 7 ‘ eS ahs i * oe 2 7 Pg a tie i, 7 4 es .. 7 - = ie. PLATE 33 Terminal and axillary fruits. UNIV. CALIF. PUBL. AGR. S( l, VOL. { COIT HODGSON |] PLATE Qn Ow . ¢ a i) ) pu n PLATE 34 7 _ Apical end of ovary of Navel orange just after the style has been shed. _ aS Enlarged 10 diameters. Notice the ragged condition of the stylar scar. a * > er: UNIV, CALIF. PUBL. AGR. SCI. VOL, & [ COIT—HODGSON ] PLATE 34 PLATE 35 ae oe & je oe Large late drops showing discolored area beneath the navel, caused db. infection with Alternaria citri. [354] a” an +) oa op de =f. Pie, s ~ 2 y a ” eee Jen “ i Mie 7 ae 4 a aa A ©) > aie? a A 7 . JS = > I y .) Lar mt : th a8 me 1. — 77 : ~ 7 : i. ihe eA ct: UNIV. CALIF. PUBL. AGR. SCI, VOL. 3 [ COIT—HODGSON ] PLATE 5 PLATE 36 Photomicrograph of Alternaria citri, showing the spores borne in long ch ui ns 7 UINIVe GALIF. PUBL. AGR. SCI, VOL. S [ COIT—HODGSON ] PLATE 36 *. PLATE 37 Young Navel oranges, showing the ragged break of the style. 2 diameters. UNIV. CALIF. PUBL. AGR. SCI. VOL. 3 [ COIT—HODGSON ] PLATE ie he a oy ve we » e J ' a 2 PLATE 38 Mummified oranges infected with Alternaria citri. UNIV, CALI! - " ; Ser.) ‘ yg? ue » A fe Ne | A 8 Pate (ey ' 7 ty > i? § ; a 4 Ay 4 PLATE 39 Small Valencia orange, showing clean break between the base of the sty! and the ovary. Knlarged 10 diameters. Compare with plate 34. ay. Mn ON OIE ie > ( AGR PUBL, UNIV. CALIF. PLATE 40 Showing the method of enclosing orange trees under the tents o in order that bees may be included in one and excluded from t tree in foreground shows the method of covering inoculated flows sacks. ; = a4 UNIV. CALIF. PUBL. AGR. SCI. VOL. 3 [ COIT—HODGSON ] PLATE 40 ™ ‘ wees bo yy; a © Po oe | b> oe PLATE 41 The Livingston white porous cup atmometer as set up at our Desert s ta 41 PLATE HODGSON | [ COIT CALIF UNIV. PLATE 42 Distribution of orange roots by six-inch layers at Edison station. cultivation. [368] <6 sf , " ¥ a a! SAP 4 ye he if | - he oe ae ot if dahl [ COIT—-HODGSON } PLATE 42 BL. AGR. SCI. VOL. UNIV. CALIF. PU UNIVERSITY OF CALIFORNIA PUBLICATIONS +6" IN AGRICULTURAL SCIENCE Vol. 3, No. 12, pp. 369-498, 33 text-figs., pls. 43-74 June 30, 1919 ARE SOILS MAPPED UNDER A GIVEN TYPE NAME BY THE BUREAU OF SOILS METHOD CLOSELY SIMILAR TO ONE ANOTHER? BY ROBERT LARIMORE PENDLETON CONTENTS PAGE I Be eh sect Wea 2c te aan da cab ove du acboccutanbankesupetecvidsinereenaiwennnmcuavexéeiibiepesnccesid Oe EEE eR MERC: SUSAR Me Festa 1 Ser RAEe tens JdeN CE Oke ee ean nee es See 370 IS USE UE sg 0) |, ann Sl a 371 Historical development of the classification of soils .....................2---:ccscee-eeeeeees 371 emmeecen GG Prewent. Sey cc cee ig Ren iets ee. 376 ER gE USS SASSER eee Ope nS Ct Sl eee nee ae, See 377 CESS, 1 Sigg gO be RCE Ree ss Rn ee lee 380 ER Se A ee SP tet Sn Pe De ae ok ee eae: ROLE ee 395 ES SSE NS ORO ae Sere eee On | cS ee eee See 414 8 SIRE EERIE Se Ra ib ees (ieee | eee ne Se > a 432 NNER oe eis ar a A ae ac vigincndcaadenbeaghae ees 467 Ee A eee ae kee ee ene TCE de 2 ol rT Oa 481 (EE Eo TE RT ae On ne Renae Ue on 0 te er. © 483 ) we Methods and technique: 02.) oo Soar euanctae. 483 yp OTST y 97 ana OR SU OE AL 2 nn ce ere 490 FOREWORD It is due the author, as well as to the undersigned, that a few words be said by way of preparing the reader for what follows in this paper. It will be observed, first, that the manuscript was, for an unusually long time, in the printer’s hands. Those who appreciate, as few do today, the great rapidity with which the theories and the methods in soil and plant study change, will readily catch the signifi- cance of the foregoing sentence. Much of the work done by Mr. Pendleton and some of the methods used may now properly be con- sidered obsolete, or, conservatively speaking, at least obsolescent. Nevertheless, I deem it of some importance to give the results obtained in more or less detail, because of their historical value, and because Mr. 370 University of California Publications in Agricultural Sciences | Vol. 3 Pendleton’s residence in India since the paper was written by him has rendered satisfactory changes and deletions practically impossible. Under these circumstances, with the burden of preparing the paper for the press and the reading of the proof falling to me, the author cannot well be held responsible for the inaccuracies and the infelicities of expression which have been carried over from the original manu- script without change. Moreover, the investigation was carried out under my direction, and the plan of attack on the problem, together with the methods employed, were suggested by me. Much that, in the light of present knowledge, is superfluous or patently inexact or erroneous in the paper is due to points of view held by me in 1915, but now happily discarded. For all these, I assume the entire responsibility, and absolve Mr. Pendleton in that regard. On the other hand, the work having been carried out at my sugges- tion and under my direction, I feel constrained, in justice to myself, to say that the views expressed in this paper, and the conclusions drawn are wholly Mr. Pendleton’s and are not in agreement with those held by me. I fail to see the cogency of the arguments set forth for soil classification and mapping at this juncture in soil studies, and cannot admit the pertinence of the analogy between classification of other objects and of soils which the author of this paper employs. My own general conclusion from the results obtaied by Mr. Pendle- ton is that they cast grave doubt on the validity of the Bureau of Soils method of soil classification and mapping, and, incidentally on all methods devised for that purpose to date. I cannot see how such methods can serve us in scientific work at all, and, from the practical standpoint, it would surely seem that guides for the purchaser of land could be arranged more cheaply and less elaborately than by the soil mapping methods extant. This statement has particular reference to the subdivision of types very minutely, such as, for example, sandy silty clay, clay loam adobe, ete. Such minute classification and sub- division in view of the present state of our knowledge of soils, is analogous, in my opinion, to carrying figures out to four decimal places when it is known that the accuracy of the method makes it impossible for them to be correct beyond the first decimal place. In support of this seemingly radical conclusion, the reader will find much of interest in the recent studies of this laboratory on variability in soils, which have already appeared in this same series. Cnuas. B. LIPMAN. INTRODUCTION For several years the University of California has been cooperating with the United States Bureau of Soils in the mapping of the soils of the agricultural portions of the State of California. The system of mapping used is that developed by the Bureau of Soils. During the year 1914-1915 the writer, representing the University of California, was engaged in some of this soil survey work. In that year, in the field, many questions arose regarding the criteria used, the methods, 1919 } Pendleton: A Study of Soil Types 371 and the results of the scheme of mapping. It was thought that pos- sibly some of the many questions could be answered through a labora- tory study of some typical soils. This paper is a description of cer- tain parts of the work done in this connection. THE NEED OF A CLASSIFICATION OF SOILS Since soils consist of a number of more or less distinct groups they are fitting subjects for classification. In fact, it is my belief that it is as necessary to have a classification for soils as for any other group of natural objects in order that ‘‘the various and complex relations 1 and that there be a definite may be shown as far as practicable, basis for systematic and thorough investigations.” The advantages of a classification of soils are apparent. But because soils grade gradu- ally into one another, rather than exist as discrete individuals which ean be more easily considered and treated from a systematic stand- point, the problem of evolving a satisfactory classification has been particularly difficult. The many and diverse classifications proposed, and the difficulty of applying many of these classifications under con- ditions other than those for which they were evolved, testify to the difficulty of the task in question. The mapping of soils without a classification is impossible, and so a brief summary of the development of soil mapping will bear a close relation to the development of soil classification. HISTORICAL DEVELOPMENT OF THE CLASSIFICATION OF SOILS The early history of the making of soil maps is that of geologic maps as well, when soils, from the agricultural standpoint, and the less distinct geological formations as such, were not sharply distin- guished. Blanck*® has an excellent treatment of the development of soil mapping and of the modern continental European conceptions of the nature and significance of soil maps. According to Blanck the earliest record of a proposal to make a map to show something of the nature of the actual material composing the surface of the earth is that of Lister’s proposal, in 1683, to the Royal Society of London. 1 Coffey, G. N., Proc. Amer. Soc. Agron., vol. 1 (1909), p. 175. 2 Cameron, F. K., Eighth Internat. Cong. Chem., vol. 26 (1912), sees. Via—xiIb; app. pp. 699-706. 3 Fihling, Landw. Ztg., vol. 60 (1911), pp. 121-45. 372 University of California Publications in Agricultural Sciences [| Vol. 3 But it was not until 1743 that Packe executed a map of Kent, showing the occurrence of minerals by symbols. Apparently the next advance was by the Germans, when Fiichsel, 1773, and Gloser, 1775, first used colors to show granite, limestone, ete. This work constituted the first real geologic map in the modern sense, There was not much activity in this line of geologic work until 1870 or later. Such activity as there was showed a lack of emphasis on soils in the agricultural sense of the term. The work on the geologic drifts of northern Europe, and studies of the more recent lowland formations and soils of Germany led to soil mapping. The first real soil map, according to Blanck, was prepared by Benningsten-Forder of Halle, in 1864-67; while Carnot* states that in 1863 M. Scipion Gras used superposable maps of the Depart- ment of Isére, showing (1) geology, (2) agricultural soils, (3) alti- tudes of agricultural regions, and (4) culture. The first true geologic- agronomic map published by the Preussischegeologische Landesan- stalt appeared in 1878. The school of soil classification and mapping just mentioned, using the geologic maps and methods as a point of departure have evolved numerous though similar systems of recording the agrogeologic data on the map. The geologic formation is shown by the color, and the soil textures by symbols, while one or more of the following groups of data appear and may be shown: topography by contours, subter- ranean water by blue figures, location of borings in red with figures referring to tables, amount of plant food elements or substances by figures or hatchings, varying directions, color, or nature of lines, ete. The nature and amount of the data shown and the manner of repre- senting them vary a great deal. Some soilists, to use a term proposed by Coffey,® advocate and use superposable maps to show one or more eroups of data, thus avoiding unnecessary confusion on the main map. Hazard® proposed a scheme of classification which is quite as directly connected with the economie factors controlling the crops erown, and with the assessable valuation of the land, as with the actual or potential fertility of the soil itself. There are several classi- fications of this type, involving the assessable values of the land. 4 Rapport sur les cartes agronomiques, Bull. Min. Agr. France, 1893, no. 8, pp. 956-73. 5 Jour. Amer. Soc. Agron., vol. 8 (1916), p. 239. 6 Landw. Jahrb., vol. 29 (1900), pp. 805-911. Gregoire, A., and Halet, F., Bull. Inst. Chem. et Bact. Gembloux, 1906, no. 75, pp. 1-43. al 1919 | Pendleton: A Study of Soil Types 373 This development of the mapping of soils as an outgrowth of areal geology in France and Germany may be contrasted with the develop- ment of soil classification from other viewpoints, such as that of the Russian school. In Russia there is not the predominance of residual and shallow soils which characterize much of western Europe and which in France especially have led to the adoption of the geologic basis of classification. Dokoutchayev and Sibirtzev have been the chief proponents of a classification of soils based upon the ‘‘ conception of a soil as a natural body having a definite genesis and a distinct nature of its own.’ The genetie conditions of the formation of natural soils include the following variable factors which cause variation : (1) The petrographic type of the parent rock; (2) the nature and intensity of the processes of disintegration, in connection with the local climatic and topo- graphic conditions; (3) the quantity and quality of that complexity of organisms which participate in the formation of the soil and incorporate their remains in it; (4) the nature of the changes to which these remains are subjected in the soil, under the local climatic conditions and physico-chemical properties of the soil medium; (5) the mechanical displacement of the particles of the soil, provided this displacement does not destroy the fundamental properties of the soil, its geo- biological character, and does not remove the soil from the parent rock; and (6) the duration of the processes of soil formation. Upon this genetic basis there has been developed a series of soil zones, ranging from the laterite soils in the tropics to the tundras in the Arctie regions. The outstanding and controlling factor in the scheme proposed is the relation of these zones to climate. For this reason the statement usually seen is that climate is the basis of the classification.® There are nearly as many groups of intra-zonal and azonal soils as of those belonging to the zones proper. The former include alka, marshy, alluvial, and other soils. Hilgard, while actively interested in the genetic viewpoint of soil classification, was the foremost proponent of a classification upon the basis of the natural vegetation growing upon the soil.? This criterion is not always available, though some groups of plants, as the alkali tolerant ones, are almost invariably present where the condi- 7 Exp. Sta. Record, vol. 12 (1900), p. 704. . See also Sibirtzev, Cong. Geol. Intern., 1897, pp. 73-125; abstract in Exp. Sta. Rec., vol. 12 (1900-01), pp. 704-12, 807-18. ee Tulaikof, N., The Genetic Classification of Soils, Jour. Agr. Sei. . Vol. 3 (1908), 8 Coffey, U. S. Bur. Soils, Bull. 85 (1912), p. 32; Jour. Amer. Soc. Agron., vol. 8 (1916), p. 241. 9 Hilgard, E. W., Soils (New York, Macmillan, 1906), pp. 487-549. 374 University of California Publications in Agricultural Sciences [ Vol. 3 tions are unfavorable for the less resistant plants. Later Hilgard and Loughridge’® claimed that it is impracticable to attempt ‘‘a sat- isfactory tabular classification in which each soil shall at once find its pigeonhole prepared for it . . . because the subject matter is as yet >? so imperfectly known.’’ However, this does not dispute the justifica- tion for making classifications for specific purposes or of specific regions. With respect to this point there seems to be confusion. The question is not whether soils can be classified at all or not, for every observant farmer classifies the soil with which he is familiar, but whether a satisfactory classification is possible over a large territory, where soils are subject to the varying action of the important soil forming agencies. Still another type of soil mapping is that of Hall and Russell, which is given in their admirable Report on the Agriculture and Soils of Kent, Surrey, and Sussex.’’"! In this district the soils are largely residual, and form quite distinct groups, depending upon the parent geologic formation. These groups of soils, such as the Clay-with- flints and the Thanet beds, have very definite agricultural properties ; hence the treatment of all phases of agriculture upon. each separate eroup of soils. Hall and Russell’? present an excellent discussion of the methods of soil classification and the interpretation of the soil analyses used in their study. Russell*® gives a very similar though briefer treatment. There are other more or less specialized classifications that have been applied to local conditions and problems. As an example may be cited Dicenty’s work on grape soils.*# Various modifications of the above schemes of classifying and map- ping soils are found in general texts on soils.1° Nowacki'® proposes a curious system, Genera et Species Terrarum. It is in Latin terminology. The genera are based on the quality of the soil, whether stony, sandy, clayey, peaty, etc., and the species are dependent upon the quantities of organic matter and clay. 10 The Classification of Soils, Second Intern. Agrogeol. Conf., Stockholm, 1910, p. 231. 11 London, Bd. Agr. and Fish., 1911. 12 Jour. Agr. Science, vol. 4 (1911), pp. 182-223. 13 Soil Conditions and Plant Growth (London, Longmans, 1913), pp. 132-48. 14 Die ampelogeologische Kartierung. First Intern. Agrogeol. Cong., Budapest, 1909, pp. 257-71. 15 Ramann, E., Bodenkunde, Berlin, Springer, 1911. Mitscherlich, E. A., Bodenkunde, Berlin, Parez, 1905. 16 Praktische Bodenkunde (Berlin, 1892), pp. 130-80. 1919 | Pendleton: A Study of Soil Types 375 Soil Surveying in the United States.—In a brief way, it has been shown how there arose the different systems of soil classification. Only a few typical systems of classifications, and something of the reasons for the divergences, have been mentioned.’* Probably the one agency that has carried on the most extensive soil classification and mapping is the Bureau of Soils of the United States Department of Agriculture. It is now proposed to discuss and in a measure criticize the work of the Bureau of Soils, the one organization that has, more than any other, succeeded in applying a detailed system of soil classi- fication over extensive areas. The problems that the Bureau had to face during its early exist- ence were special studies of the soils of certain crops, especially of the tobaeeo districts.‘ Later the soil utilization work of the Bureau of Soils was transferred to other branches of the Department of Agri- culture, leaving as the main task for the Bureau the systematic classi- fication and mapping of the soils of the United States. Coffey’? has so well discussed the present day conceptions of the bases for the classification of soils, that it does not seem necessary to repeat any portion of that excellent statement here. He showed that the Bureau of Soils, in its method of classifying soils, uses a combina- tion of a number of systems. This matter is dealt with more in detail in an article by Coffey,?° and the Report of the Committee on Soil Classification of the American Society of Agronomy.” The question often arises as to the validity of making the close distinctions regard- ing color, texture, geologic origin, ete., and is one which should be dealt with in order to render less empirical the nature of most of the criteria which are used at present. See the Report of the Committee on Soil Classification and Mapping.”” Because of different views regarding soils and soil fertility from those held by the Bureau of Soils, the Illinois Agricultural Experi- ment Station has undertaken a soil survey and classification, under the direction of Dr. C. G. Hopkins, which is independent of the Bureau "47 Bee Coffey’s excellent treatment of the soil survey work in this country. The Development of Soil Survey Work in the United States with a Brief Reference to Foreign Countries, Proc. Amer. Soe. Agron., vol. 3 (1911), pp. 115-29. 18 Whitney, Extension and Practical Application of Soil Surveys, Off. Exp. Sta., Bull. 142 (1903), pp. 111-12; The Purpose of a Soil Survey, U. S. Dept. Agr., Yearbook, 1901, pp. 117-32. 19 A Study of the Soils of the United States, U. S. Bur. Soils, Bull. 85 (1912), pp. 24-38. 20 Jour. Amer. Soc. Agron., vol. 8 (1916), pp. 239-43. 21 Ibid., vol. 6 (1914), pp. 284-88. 22 [bid., vol. 8 (1916), pp. 387-90. 376 University of California Publications in Agricultural Sciences [ Vol. 3 of Soils, and differs from its methods in a number of ways. Since the soils of Illinois are of a much narrower range of variation than are those of the whole of the United States, the system of classification for the state need not be so elaborate. The soils are divided accord- ingly as they have been glaciated or not, and if glaciated, in what glaci- ation period. They are further divided according to color, topogra- phy, and texture of soil and subsoil.** Correlation of the types of soil mapped in the various areas, one of the greatest sources of criti- cism of the Bureau of Soils survey methods, is more easily handled in the Illinois work, since it is possible for the one in charge of the work to pass personally, while in the field, upon all correlation and the establishment of all new types. It is insisted that the field men map accurately and in sufficient detail. This insures the accuracy of the maps as regards the standards adopted, the information is specific, and the local users of the maps are not misled.** In connection with the field classification and mapping, pot and plot cultures are carried on, not so much to test the relative fertility of the untreated soils, but to determine the effects of the application of various sorts and quanti- ties of fertilizers. Hopkins,”° to show the differences in detail between the U. S. Bureau of Soils mapping and that of the Illinois Experi- ment Station, compares a U. S. Bureau survey of 1902 with a state survey published in 1911. This is not entirely fair, because with the increase of field knowledge of soils gained by them and the realiza- tion of the need of representing the soils in more detail, a survey made by the Bureau in 1911 would almost certainly show much more detail and show it with greater accuracy than the maps made in the early period of the work. This point may be strengthened by the notes given below on the comparison of a portion of an early survey made in southern California by the Bureau of Soils with a recent survey of the same soils made by the Bureau and the University of California working in codperation. PLAN OF THE PRESENT STUDY The present study is an attempt to see if certain soil types mapped as the same from different areas in the state of California, and judged to be the same by the criteria used by the Bureau of Soils, are the — 23 Hopkins, Soil Fertility and Permanent Agriculture (Boston, Ginn, 1910), pp. 54-57. 24 Ibid., p. 115. 25 Ibid., pp. 114-15. oe, a 1919] Pendleton: A Study of Soil Types 37 same or similar when examined from the laboratory standpoint. For example, we may take the Hanford fine sandy loam, which is one of the types that has been used in the present study. According to the eriteria of color, mode of formation, origin (as judged by the presence of mica), nature of subsoil, texture, ete., this soil has been found and mapped in a number of areas that have been mapped in this state. But will these various bodies of soil, from widely separated portions of the state, when judged by laboratory and greenhouse studies on samples as nearly representative as possible, appear to be the same or similar ? The types selected for such a study as this should fulfil the follow- ing conditions: first, they should have at least a reasonably wide dis- tribution in the state so as to have been mapped in a number of differ- ent soil survey areas; and second, the several types should be repre- sentative of different classes of soils (clays, loams, sandy loams, etce.), so that contrasts could be obtained between the types. In the collection of samples it was aimed to obtain representative samples from each of a number of bodies of soil of the types selected ; not to obtain possible variations from the ideal in any one body. In the laboratory the soils were compared with regard to their physical composition in the surface horizon, to their chemical composition in three horizons, and to their relative bacteriological activities. In the greenhouse the soils (surface horizon only) were placed in large pots and their comparative ability to produce various crops was studied. No claim is made that these criteria should be the ones used in determining the systematic classification of soils or in determining the relative fertility of the soils. They were merely used to determine how nearly the soils classed under a given type name agree from the standpoints named. DISCUSSION OF RESULTS The bacteriological and chemical determinations were run in dupli- eate so that the figures presented are averages. It is considered that this gives fairer figures for comparison, especially since the determina- tions were run on separate samples, and not on aliquots of a single solution from a single sample. There is a very important factor which should always be kept in mind especially when considering the bacteriological and greenhouse comparisons. This is the factor of the probable error. Though the 378 University of California Publications in Agricultural Sciences [Vol.3 advisability of judging all results in the light of the probable error is admitted, no attempt has been made to apply this factor to the results reported in this paper. As the result of the effect which such a factor might have upon the results of bacteriological determina- tions carried on only in duplicate, or upon the results of greenhouse work done in triplicate, one hesitates to draw conclusions, especially those based upon minor variations. Hence in this work only the more marked results will be considered of significance. When planning the work it was thought that three or four samples of a type would be enough to show whether or not a given type was approximately uniform, or widely variable, and as to whether the types were similar to one another, or quite dissimilar. But it now seems, after comparing the determinations run on the larger number of samples of the Hanford and San Joaquin types, 9 and 8 respec- tively, with the determinations run on the Altamont and Diablo types, of-which there were a much smaller number of samples, 3 and 4 respectively, that the larger series gives a much better insight into the variations of a given type and affords a much better basis for con- clusions. Hence, as regards the laboratory work thus far carried out, the emphasis has been placed upon the Hanford fine sandy loam and the San Joaquin sandy loam. Determinations have not been completed on the Altamont and Diablo series to the extent that they have on the former two. It is of no little significance that the Hanford fine sandy loam and the San Joaquin sandy loam are very widely contrasted soils agricul- turally. The Hanford is typical of good recent alluvial soil in this state ; while the San Joaquin is typical of wide expanses of ‘‘old valley filling’’ soils that are considered poor as regards crop producing power and are underlain by compact iron-cemented hardpan. Conse- quently, the results of comparing soils so different from an agricul- tural point of view, and so radically different as regards soil survey eriteria (though the textures are quite similar) will be of considerable interest. They are of greater interest than the comparisons between the Diablo and Altamont soils, as the latter are quite similar in agri- cultural value and use, as well as in field appearances. Between the Diablo or Altamont and the Hanford or San Joaquin one cannot judge as closely regarding variations, for the soils are so radically different. On the other hand, one can compare the soils of the heavy and light types to see to what extent the chemical and bacteriological results differ as compared with the physical results. 1919} Pendleton: A Study of Soil Types 379 See O ee 025 AN I. ; Me 8. 16. 32. 64. Grits. Size of Particles bi abd Fig. 1. Graph showing the results of the Hilgard elutriator method of mechanical analysis on the four samples of Diablo clay adobe. 380 University of California Publications in Agricultural Sciences [ Vol. 3 MECHANICAL ANALYSIS Hilgard Elutriator Method.—That there is a wide variation be- tween the samples is apparent (figs. 1-4). In fact, there is about as wide a range of differences among the samples of the Hanford Co A ‘O 45 Fig. 2. Graph showing the results of the Hilgard elutriator method of mechanical analysis on the three samples of Altamont clay loam. fine sandy loam and among those of the San Joaquin sandy loam as between the two types. The most outstanding differences are where they ought to be, to show the differences that the type names presup- pose, i.e., in the ‘‘coarse sand’’ (64 mm.) and the ‘‘grits.’’ The sam- ples of the San Joaquin sandy loam average a larger proportion of each of these separates than do the Hanford fine sandy loam soils. 1919] Pendleton: A Study of Soil Types 381 In the Hanford, no. 14 is notably heavier than the others, as shown by its silt content, which is nearly half again as great as that of the next highest sample. The gravel content (sizes above 2 mm.) is interesting in its uni- formity. In the San Joaquin soils the two samples above 1% are 40 o/, Oo, Play 0 oks & Ro a | VA 4 8 16 32 64 Grits Size of Particles. mm. Fig. 3. Graph showing the results of the Hilgard elutriator method of mechanical analysis on the eight samples of San Joaquin sandy loam. nos. 11 and 26. The material in the latter soil is composed almost wholly of iron concretions, leaving sample no. 11 as the only soil with more than 1% actual gravel. In the Hanford samples none were found to have more than 1.5% gravel. The Hilgard method does not include any precise subdivision of the soils into groups or classes according to texture. Dr. Hilgard was not in favor of making the fine distinctions in texture that other 382 University of California Publications in Agricultural Sciences [Vol.3 investigators have emphasized. But if there were such a scheme, similar to that which the Bureau of Soils uses,*° it would be an easy matter to compare the results obtained through the use of the elutri- ator, and determine whether or not the soils examined belong to a given class. The simple comparison of the quantities, in different 0.25 Q5 lO 20 40 80 14 32 64 Grim Size of Particles. mm, Fig. 4. Graph showing the results of the Hilgard elutriator method of mechanical analysis on the nine samples of Hanford fine sandy loam. samples, of any given separate or separates is not absolute. For it must be realized that the conception of a soil class includes a certain range in the quantities of particles of the various sizes. This must be so since soils are ordinarily grouped into but ten or twelve class textures, while there exist among soils those with all gradations in the quantities of particles of the various sizes. 26 Instructions to Field Parties, U. S. Bur. Soils, Bull. 1914, p. 75; ibid., Bull. 85 (1912), p. 28. Oe og, A CE EE A ELE : a ‘ % 4 1919 | Pendleton: A Study of Soil Types 383 And because the ranges in the sizes of the soil particles separated by the Bureau of Soils method cut across those of the Hilgard method, it is impossible to regroup the results so that the Bureau of Soils grouping into textures may be applied. But without any such scheme, desirable as it may be, it has been pointed out that there is clearly apparent a rather wide variation in the analyses of the several samples of a type. All the soils representative of a given type are by no means closely similar to one another. TABLE 1—COMPARISON OF TEXTURES Texture as judged in the field *1 Diablo clay adobe 2 Diablo clay adobe 3 Altamont clay loam 4 Altamont clay loam 5 Diablo clay adobe 6 Diablo clay adobe 7 Altamont clay loam 10 San Joaquin 11 San Joaquin 2 San Joaquin 13 San Joaquin 14 Hanford fine 15 Hanford fine 16 Hanford fine 17 San Joaquin 18 San Joaquin 19 Hanford fine 20 Hanford fine 21 Hanford fine 22 Hanford fine 23 Hanford fine 24 Hanford fine 25 Hanford fine 26 San Joaquin sandy loam sandy loam sandy loam sandy loam sandy loam sandy loam sandy loam sandy loam sandy loam sandy loam sandy loam sandy loam sandy loam sandy loam sandy loam sandy loam sandy loam Texture determined by mechanical analysis Clay Clay *Silty clay Clay loam (sandy) Clay Clay Clay loam (heavy) *Fine sandy loam Sandy loam (heavy) *Tine sandy loam *Fine sandy loam (heavy) - Fine sandy loam (loam) Fine sandy loam *Sandy loam Sandy loam Sandy loam *Sandy loam (heavy) Fine sandy loam Sandy loam Fine sandy loam . Fine sandy loam Fine sandy loam Fine sandy loam Sandy loam Note.—Textures not judged correctly in the field. Mechanical Analysis by the Bureau of Soils Method—Among the other determinations made by the Division of Soil Technology on the surface horizons of the twenty-four soils used in this investigation was that of making the mechanical analysis. The tables show the percentages of the several separates. In all cases the figures represent averages of duplicate determinations and in some cases the averages of quadruplicate determinations. With this method, as well as with the Hilgard elutriator, there are shown wide variations between the 384 University of California Publications in Agricultural Sciences [ Vol. 3 (O68 005: O85 .dA0° 425 os LO mm =05 ~/0.:- 325 . “2 “LO -20 mm mm. mm mm MM. Wits Fig. 5. Graph showing the results of the Bureau of Soils method of mechanical analysis on the four samples of Diablo clay adobe. 1919] Pendleton: A Study of Soil Types 385 samples of a given type. But the graphs of the percentages (figs. 5-8), determined by the Bureau of Soils method for the several types are not as closely similar as the graphs of the elutriator results for the same types. That is, using the Bureau of Soils method, the graph of the Hanford fine sandy loam does not resemble that of the San Joaquin sandy loam as much as do the graphs of the results made % 40 30 .005 .005-.05 .05-.10 .10-.25 .25-.5 .5-1.0 1.-2. Fig. 6. Graph showing the results of the Bureau of Soils method of mechanical analysis on the three samples of Altamont clay loam. upon the same soils by the Hilgard elutriator method. This would lead one to believe that the Bureau of Soils method of mechanical analysis is the better suited for separating soils into groups; even though these soils which were classified in the field according to the differences which are the more prominent would be expected to show greater differentiations when examined by the Bureau of Soils labora- tory methods. 386 University of California Publications in Agricultural Sciences [ Vol. 3 Comparison of Textures.—Table 1 gives the texture as shown on the soil survey map of the locality, as well as the results of the labora- tory check. This texture as given on the map was also judged by me 50% 45% 40% 55% % 005005 .05 406 25 5 LOmm -O5 -10 “25 -=5 -10 2.0mm. Size of Particles. Fig. 7. Graph showing the results of the Bureau of Soils method of mechanical analysis on the eight samples of San Joaquin sandy loam. in the field to be more or less true to the type as mapped. I say more or less true, for the field notes, as given in appendix B, show that in several gases I was unable to obtain in the locality what I believed to 1919] Pendleton: A Study of Soil Types 387 be a sample of the soil thoroughly typical of the class and type in question. Sample no. 3 had a large lime content which I thought might more or less obscure the texture. ‘‘Slightly heavy, and barely enough sand for a sandy loam’’ is the comment on sample 12, while ‘fa heavy sandy loam, approaching a loam’’ is found in the notes on sample 138. The second column of the table shows the class sub- divisions into which the soils were placed according to the mechanical analysis. The words in parenthesis show modifying conditions but do not indicate a change in the class. In considering the class groups such as sandy loam, fine sandy loam, ete., it should be remembered that though the groups are rather broad, the limits are arbitrary and quite sharp. So the results of a mechanical analysis may place a soil in the sandy loam class if 25% or more is fine gravel, coarse and medium sand, while if less than 25% be present the soil belongs to the fine sandy loam class, providing at the same time the amounts of silt, clay, and fine sand are within the specified limits. The two soils may be a great deal alike in texture though placed in different classes. The failure of my judgment regarding the texture shows one of the difficulties that the field man is continually facing. And his failure to judge textures correctly is one of the causes of criticism of soil survey work. TABLE 2—MECHANICAL ANALYSES, HILGARD ELUTRIATOR METHOD Diablo Clay Adobe Separates Samples Velocity, Diameter, mm. per 1-A 2—-A 5—-A 6-A Name mm. second Jo Jo Jo Jo Clay 01 0.25 44.16 35.81 44.97 64.63 Fine silt .01 —.016 0.25 23.91 34.08 25.57 25.13 Medium silt .016—.025 0.5 5.97 7.37 4.14 1.03 .025—.036 i 8.10 9.09 5.28 1.83 Coarse silt .036—.047 2 7.77 TAT 5.45 1.99 .047-—.072 + 6.05 4.09 6.18 2.13 Fine sand .072—.12 8 3.28 1.33 5.81 2.07 12 —.16 16 0.48 0.43 1.73 0.90 Medium sand 16 —.30 32 0.08 0.21 0.38 0.21 Coarse sand 30 —.50 64 0.18 0.11 0.49 0.11 Total weight of separates, gm. 19.18 19.62 19.30 19.68 Weight of original sample, gm. 18.83 18.88 18.66 18.16 Grits, % 0.5-2.0 mm, 0.26 0.29 0.57 0.10 Hygroscopic moisture, % 6.20 5.93 7.18 10.12 388 University of California Publications in Agricultural Sciences [ Vol, 3 “ : iO fee Aa. -- OD : 25 Ro | LO mm. “05, 310..-25 -5 0. 20mm Size of Particles Fig. 8. Graph showing the results of the Bureau of Soils method of mechanical analysis on the nine samples of Hanford fine sandy loam. re 1919] Pendleton: A Study of Soil Types 389 TABLE 3—MECHANICAL ANALYSES, HILGARD ELUTRIATOR MetrHop Aliamont Clay Loam Separates Velocity Name GORE: | Lae Clay 01 0,25 Fine silt OL —.016 0.25 Medium silt .016—.025 0.5 .025-.036 1 Coarse silt .036-.047 2 .047-—.072 4 Fine sand .072-.12 8 12 —.16 16 Medium sand .16 —.30 32 Coarse sand 230 —.50 64 Total weights of separates, gm. Weight of original sample, gm. Grits, % 0.5-2.0 mm, Hygroscopie moisture, % Samples TABLE 4—MECHANICAL ANALYSES, HILGARD ELUTRIATOR METHOD San Joaquin Sandy Loam Separates Velocity, Diameter ar 10-A 11-A Name mm. second % Jo Clay .O1 0.25 11.14 15.46 Fine silt .01 -—016 0.25 20.24 31.88 Medium silt .016-.025 0.5 1.44 2.73 .025-.036 6.54 SL}: Coarse silt .036-.047 2 Soo)" | 10:23 .047-.072 9.50 8.41 Finesand .072-.12 8 10.66 7.47 12-16 16 10.30 5.97 Medium sand 16-30 32 14.69 6.91 Coarse sand .30 —50 64 7.11 1.32 Total weight of separates, gm. 20.02 20.44 Weight of original sample, gm. 19.80 19.51 Grits, % 0.5-2.0 mm. 16.70 23.54 Hygroscopie moisture, % 0.98 2.48 12—A To 8.99 26.57 Z.31 1.33 Lao 10.14 10.72 10.88 11.75 3.54 19.99 19.72 8.84 1.38 Notr.—aAll weighings made on the water free basis. Samples 13-—A 17—-A % 6 Pie > 30:53 24.04 16.20 4.64 1.81 9.86 5.89 9.59 5.82 10.05 8.46 10.92 12.04 16.14 13.438 1.96 19.21 2.12 6.60 20.10 20.38 19.76 19.85 8.10 23.12 1.22 0.75 390 University of California Publications in Agricultural Sciences [Vol.3 TABLE 5—MECHANICAL ANALYSES, HILGARD ELUTRIATOR METHOD Hanford Fine Sandy Loam Separates Velocity, Samples mm, Diameter per 14-A 15-A 16-A 19-A 20-A 22-A 23-A 24-A Name mm. second % Yo Jo %o Jo %o % %o Clay O01 0.25 12.89 8.16 11.97 11.09 1055 7.97 868 6.47 Fine silt 01 -016 0.25 37.25 19.39 2461 595 22.09 1415 22.57 11.11 Medium silt .016—-.025 0.5 419 3.05 3.22 167 640 3.15 5.90 1.20 .025-.036 1 8.63 5.04 5.06 5.27 840 5.29 6.89 5.08 Coarse silt .036-.047 2 7.905 657 5.99 7.14 7.68 6.47 10.53 7.48 .047-.072 4 6.23 10.23 7.27 12.76 9.93 11.380 18.08 13.91 Fine sand 072-12 8 5.26 12.31 8.57 17.79 10.48 17.15 12.71 19.27 12-16 16 7.15 13.93 9.76 12.00 12.29 17.39 794 21.56 Medium sand .16— .30 32 8.81 15.29 16.05 24.20 10.03 14.87 9.88 12.36 Coarsesand .30— .50 64 148 602 751 218 3.70 237 ~s5, 2 Total weight of separates,gm. 20.19 20.23 20.53 20.08 20.27 20.06 20.30 20.26 Weight of original sample, gm. 19.46 19.90 19.69 19.82 19.73 19.81 19.78 19.83 Grits, % 0.5-2.0 4.12 13.23 25.47 7.85 6.71 3.07 17.24 6.85 Hygrosecopic moisture, % 2.73 049 154 089 1.34 094 1.10 £0.84 TABLE 6—MECHANICAL ANALYSES, BUREAU OF SOILS METHOD Diablo Clay Adobe Separates Samples Diameter 1—A 2-A 5-A 6-A Name mm. % % %o % Clay .005 44.81 44.44 45.67 56.01 Silt .005— .05 32.00 42.51 23.01 14.28 Very fine sand .05 — .10 19.61 11.35 21.58 25.58 Fine sand 10 — .25 1.36 1,33 4.81 2.10 Medium sand 25 -— 5 0.26 0.69 0.95 2.05 Coarse sand 5 1.0 0.58 0.20 1.56 0.00 Fine gravel 1.0 -2.0 0.03 0.02 0.04 0.00 Nore.—Determinations made by the Division of Soil Technology. TABLE 7—MECHANICAL ANALYSES, BUREAU OF SoILS METHOD Altamont Clay Loam Separates Samples Diameter 3-A 4—A 7-A Name mm. % Jo % Clay .005 33.19 26.50 31.84 Silt .005— .05 31.76 17.35 37.40 Very fine sand .05 — .10 22.81 39.15 24.70 Fine sand 10 — .25 8.97 6.08 3.27 Medium sand 25 — 5 1.99 7.78 ~ 0.92 Coarse sand 5 -1.0 1.74 3.06 0.55 Fine gravel 1.0 -2.0 1.01 1.22 0.22 Nore.—Determinations made by the Division of Soil Technology. 1919] Pendleton: A Study of Soil Types 391 TABLE 8—MECHANICAL ANALYSES, BUREAU OF SOILS METHOD San Joaquin Sandy Loam Separates Samples Diameter 10—-A 11—A 12-A 13—A 17—A 18—A 21-A Name mm, % % %o Yo % %o To Clay .005 10.78 15.77 16.16 16.94 Lat 10.49 8.28 Silt 005— .05 21.60 35.97 25.04 22.70 15.97 26.74 17.70 Very fine sand .05 — .10 28.07 18.53 27.42 47.01 20.42 12.02 15.92 Fine sand 10 — .25 19.96 2.66 17.07 3.99 22.57 16.61 21.27 Medium sand 25 — 9.20 6.96 5.80 4.69 10.75 138.85 13.57 Coarse sand o 1.0 9.08 8.51 6.52 2.96 13.81 16.52 21.41 Fine gravel 1.0 -2.0 1.34 12.52 2.15 1.81 3.13 4.07 2.07 NorTe.—Determinations made by the Division of Soil Technology. TABLE 9—MECHANICAL ANALYSES, BUREAU OF SOILS METHOD Hanford Fine Sandy Loam Separates Samples Diameter 14-A 15-A 16-A 19-A 20-A 22-A 23-A 24-A Name mm. %o Yo %o % % %o %o Jo Clay .005 14.10 12.08 16.84 15.28 15.95 7.79 10.61 9.83 Silt .005— .05 39.25 22.42 16.16 15.03 32.90 22.70 2438 11.42 Very fine sand 05 —.10 22.66 37.12 16.46 32.87 22.58 36.15 38.73 42.05 Fine sand 10 — 25 17.54 651 17.32 813 18.20 27.78 16.51 28.73 Medium sand 29 — wo 4,71 1140 :21.70 35.42 4.97 421 4.66, 427 Coarse sand » 1.0 1.99 649. 15.54 827 3:07 147 © 3.28) -3.01 Fine gravel 1.0 -2.0 Oise 091 6.27" *a.05. (0.20 0.20 148 £02 NoTEe.—Determinations made by the Division of Soil Technology, Moisture Equivalent—The moisture equivalents of the surface horizon samples were determined by the Division of Soil Technology (table 10, and figs. 9, 10). The different types gave quite distinct averages, though there was considerable variation within the type. The Diablo clay adobe varied from 37% to 57%, with an average of 47%. The Altamont clay loam varied from 22% to 37%, with 28% as an average. The San Joaquin sandy loam varied from 7% to 15%, with the average of 11%. The Hanford fine sandy loam varied from 11% to 25%, with 15% as the average. These figures show that as a whole the moisture equivalents of the several types are distinct, though there is the usual overlapping in some cases. The samples of a given type are in many instances closely similar, though not always or even usually so. To 17.38 18.17 13.84 10.26 14.72 24.26 2.02 25-A %o 7.60 12.90 67.37 5.88 3.47 1.27 1.02 392 University of California Publications in Agricultural Sciences [ Vol. 3 Moisture Equivalent Moisture Equivalent Fig. 9. Graph showing the results of the determination of the moisture equivalent and of the hygroscopic coefficient on the four samples of Diablo clay adobe and the three samples of Altamont clay loam. . 1919 | Pendleton: A Study of Soil Types TABLE 10—MOISTURE EQUIVALENT San Joaquin Sandy Diablo Clay Adobe Altamont Clay Loam Loam A... rac Average Average Average No. % % No. % % No. Yo % 1-A_ 49.70 3-A 38.10 10-A 10.30 48.90 49.30 37.80 37.95 10.10 10,20 2-A 37.40 4-A 23.41 11-A_ 15,52 36.80 37.10 22.30 22.88 15.54 15.53 5-A 46.55 7-A. 23.90 12-A 13.72 48.10 47.32 23.90 23.90 12.62 13.67 6-A 58.80 Average 28.94 13-A 14.50 56.80 57.80 14.60 14.55 Average 47.88 17-A_—-: 8.90 §.98 $8.94 18-A° =—s 7,92 1.87 7.89 21-A 7.16 7.09 7.12 26-A 11.30 Eiiea. 17.55 Average 11.18 Norr.—Determinations made by the Division of Soil Technology. TABLE 11—HyGroscoric COEFFICIENT San Joaquin Sandy Diablo Clay Adobe Altamont Clay Loam Loam Average Average Average No. % % No. %o % No. * % % 1-A_ 15.88 3-A 17.48 -14-A_ 5.35 15.08 15.48 1845. 17:93 4.70 5.03 2-A = 9.90 4-A 9.60 15-A 1.31 9.48 9.69 7.00, 8.30 1.39 1:35 5-A 14.18 7A 7.92 16-A 3.90 13.90 14.04 5.92 6.92 3.60 3.75 6-A 15.20 Average 11.05 19-A 1.66 15.70 15.45 EA ee 1°73 Average 23.66 20-A_ 2.90 3.02 2.96 22-A 2.48 2.89 2.69 23-A 2.38 2.53 2.46 24-A 2.39 24-A 2.39 2.07 2.38 25-A 1.78 1.84 1.81 NorTe.—Determinations made by the Division of Soil Technology. Loam No. /, 14-A 25.80 25.20 5-A 11.50 11.20 16-A 15.60 15.60 19-A_ 13.30 14.30 20-A 18.41 18.38 22-A 12.73 12.22 23-A 11.08 19.90 24-A_ 16.30 16.17 25-A 11.17 12.72 393 Hanford Fine Sandy Average os JO 25.50 11.35 15.60 13.80 18.39 12.47 10.99 16.23 11.94 Average 15.14 Hanford Fine Sandy Loam No. Jo 10-A_ 2.46 2.51 11-A_ 3.44 3.45 12-A_ 3.58 3.45 13-A_ 2.50 2.60 17-A_ 1.84 1.62 18-A_ 2.10 2.00 21-A 1.98 1.92 26-A 3.57 3.52 Average Average % 2.49 394 University of California Publications in Agricultural Sciences [Vol.3 Moisture Equiv. NG Equiv. 14 15 16 19 20 22 23 24 25 Soils Fig. 10. Graph showing the results of the determination of the moisture equivalent and of the hygroscopic coefficient on the eight samples of San Joaquin sandy loam and the nine samples of Hanford fine sandy loam. Hygroscopic. Coefficient—The determination of this coefficient, also by the Division of Soil Technology, shows no very distinct values for the several types under consideration (table 11, figs. 9,10). The Diablo clay adobe samples vary from 9.6% to 15.4%, with the average of 13.6%. The Altamont clay loam samples vary from 6.9% to 17.9%, averaging 11%. The San Joaquin sandy loam varies from 1919] Pendleton: A Study of Soil Types 395 1.7% to 3.5%, with the average of 2.66%, while the Hanford fine sandy loam varies from 1.3% to 5%, with the average of 2.68%. There is no question that here the range of values within every type is greater than that from type to type. Even excluding those sam- ples shown by the mechanical analysis to be not true to name there is a wide range within each type—a range too wide to allow one to answer the question of this paper in the affirmative. 1 2 5 6 Soils Fig. 11. Graph showing the percentages of nitrogen and of phosphorus in the four samples of Diablo clay adobe. THE CHEMICAL DATA ToTAaL NITROGEN Diablo clay adobe.—There is more variation in nitrogen content between the different representatives of the type than one would expect from a visual examination of the soils (table 12 and fig. 11). No. 2 would be expected to contain less nitrogen than no. 5 because of the lighter color, but such is not the case. In the A horizon, no. 5 shows the lowest notal nitrogen content with 0.084%, no. 2 is higher with 0.092%, no. 1 with 0.104%, and no. 6 is the highest with 0.117%. The decrease in the nitrogen content with the increase in depth is normal. In the C horizon, no. 1 has the lowest total nitrogen content with 0.057%, and no. 6 the highest, with 0.078%. Altamont clay loam.—The agreement between the A samples is fairly close (table 13, and fig. 12). No. 4 has 0.103%, no. 7, 0.104%, and no. 3 has 0.123%. This gives an average for the surface soil of 0.110%, as compared with 0.099% in the Diablo clay adobe. It is to be noted that the nitrogen content of the subsoil is relatively less than that in the Diablo subsoils, 0.071% and 0.056% in the Altamont B and C horizons, respectively, as against 0.076% and 0.065% in the 396 University of California Publications in Agricultural Sciences [Vol.3 B and C horizons of the Diablo. The average amount of nitrogen is higher in the A horizon of the Altamont than in the Diablo, contrary to what one would expect from the color of the soils, since the Alta- mont is typically a brown soil and the Diablo a dark gray to black soil. San Joaquin sandy loam.—The nitrogen content of these soils is uniformly low (table 14 and fig. 13), from 0.03% to 0.05%, and is but a third to a half of what Hilgard believed adequate for crop production. 3 4 7 Soils Fig. 12. Graph showing the percentages of nitrogen and of phosphorus in the three samples of Altamont clay loam. Fig. 18. Graph showing the percentages of nitrogen and of phosphorus in the eight samples of San Joaquin sandy loam. The nitrogen content is seen to vary more or less directly with the amount of the finer sediments present in the soil—nos. 11 and 12 being heavy members of the type, with 0.05% and 0.047% respec- tively, and nos. 17 and 18 light members of the type with 0.029% and 0.027% respectively. It may be noted that the nitrogen content of the various horizons are not as far apart as in the other types. The averages for the three horizons are: A—0.037%, B—0.027%, and C—0.026%. It must be borne in mind that the San Joaquin sandy loam horizons are not full 12-inch samples, and that the total depth of the sampling is less. wre 1919 } Pendleton: A Study of Soil Types 397 Hanford fine sandy loam.—Uere again in the A horizon the nitro- gen content is fairly uniform (table 15, and fig. 14), with from 0.045% to 0.072%, if the extra typical no. 14, with 0.119%, be left out of consideration. One would suppose these soils to be higher in their 0.9 — pen P20Os5 0.8 LSS PISRARS IRL aed Beene | | | 0.7 hE mae es | : eee : 2a 0.4 ae a } = : ae 0.1 14 15 16 19 20 22 23 24 25 Soils Fig. 14. Graph showing the percentages of nitrogen and of phosphorus in the nine samples of Hanford fine sandy loam, nitrogen content, as compared with the San Joaquin series, than the results show. The B and C horizons of the Hanford samples contain 0.038% and 0.028% nitrogen, respectively, showing that with the increase of depth there is a more rapid decrease of nitrogen than in the San Joaquin samples, with the nitrogen content of the C horizon of the Hanford only 0.002% above that of the C horizon of the San 398 University of California Publications in Agricultural Sciences [ Vol. 3 Joaquin. The greenhouse pot cultures showed the effect of the much higher nitrogen content in no. 14 in giving better color and growth to the plants and especially to the grains. The increase of the nitrogen in the surface of no, 23, as compared with the B and C horizons, might be ascribed to the fertilizers applied to the orange grove where this sample was collected; yet no. 24 is a truck soil which has been fertilized to a considerable extent with barnyard manure. The nitro- gen content of this type, as judged by the previous standards, is quite inadequate. Compare the nitrogen content of the A horizons of the four types: The Diablo has an average of 0.099%, with a range or from 0.084% to 0.117% ; the Altamont has an average of 0.110%, with a range of from 0.103% to 0.123% ; the San Joaquin has an average of 0.037%, with a range of from 0.027% to 0.050%; and the Hanford has an average of 0.062%, with a range of from 0.045% to 0.119%. Thus the total nitrogen content of the several types is reasonably constant within the type and rather distinct for the types. / TABLE 12—ToTAL NITROGEN Diablo Clay Adobe Horizon A Average B Average C Average Sample % %o % % Jo Jo 0.109 0.105 0.076 0.069 0.056 0.057 1 0.101 0.063 0.059 2 0.100 0.072 0.062 0.084 0.092 0.064 0.068 0.058 0.060 5 0.085 0.065 No sample 0.084 0.084 0.065 0.065 6 0.114 0.097 0.075 0.122 0.118 0.107 0.102 0.083 0.079 Average 0.100 0.076 0.065 TABLE 13—ToTaL NITROGEN Altamont Clay Loam Horizon A Average B Average Cc Average Sample % % % Jo % %o 3 0.123 0.089 0.069 0.124 0.123 0.087 0.088 0.067 0.068 4 0.103 0.054 "@04) 0.041 0.103 0.103 0.053 0.053 0.041 0.041 a 0.106 0.070 0.061 0.104 0.105 0.077 0.073 0.059 0.060 Average 0.110 0.071 0.056 1919] A Sample’ % 10 0.037 0.038 ll 0.051 0.051 12 0.049 0.045 13 0.040 0.040 17 0.028 0.030 18 0.028 21 0.029 0.030 26 0.041 0.041 Average A Sample % 14 0.113 0.126 15 0.052 0.055 16 0.058 0.054 19 0.046 0.044 20 0.062 0.058 22 0.057 0.061 23 0.075 0.071 24 0.050 25 0.045 0.047 Average Pendleton: A Study of Soil Types TABLE 14—ToTaL NITROGEN San Joaquin Sandy Loam Average Yo 0.037 0.051 0.047 0.040 0.029 0.028 0.029 0.041 0.038 TABLE 15—ToTaL NITROGEN Hanford Fine Sandy Loam Average /0 0.119 0.053 0.056 0.045 0.060 0.059 B % 0.026 0.029 0.042 0.046 0.032 0.034 0.038 0.043 0.019 0.018 0.016 0.017 0.012 0.012 0.026 0.027 B Jo 0.084 0.081 Horizon “ee 0,027 0.044 0.033 0.040 0.018 0.016 0.012 0.026 0.027 Horizon Average (4) 0.082 0.041 0.030 0.025 0.033 0.034 0.029 0.034 0.031 0.038 © % 0.022 0.020 0.038 0.040 0.042 0.040 0.033 0.033 Average To 0.02] 0.039 0,041 0.033 No sample 0.018 0.021 0.014 0.014 0.016 0.017 Cc %o 0.060 0.057 0.028 0.027 0.020 0.023 0.024 0.023 0.024 0.022 0.025 0.023 0.020 0.016 0.028 0.022 0.024 0.019 0.014 0.016 0.026 Average oO 0.058 399 400 University of California Publications in Agricultural Sciences | Vol. 3 HuMUS Diablo clay adobe.—The variations in the humus content of the A samples (table 16, and fig. 15) are moderate, 1.1% to 1.4%, while the B and C horizons do not agree so closely with each other or with the Loss on Ignition 4 K20 Tlumus 1 2 5 6 Soils Fig. 15. Graph showing the loss on ignition, the amount of humus, and the percentages of calcium, magnesium, and potassium in the four samples of Diablo clay adobe. surface foot. The average content of humus in the A samples is 1.26%, in the B samples 0.95%, and in the C samples 0.75%. It is worthy of note that soil no. 2, with the lightest color of the four, and what might be supposed to be a lower humus content, has next to the highest amount. } 1919] Pendleton: A Study of Soil Types 401 Altamont clay loam.—Here the variations in the humus content (table 17, and fig. 16) are small in the A horizon, 1.1% to 1.3%. The average is 1.24%. The B and C samples show a good parallelism among themselves, but not so good when compared with the surface. The average of the B horizon is 0.84%, and of the © horizon 0.57%. % 9 Loss on Ignition 3 4 7 Soils Fig. 16. Graph showing the loss on ignition, the amount of humus, and the percentages of calcium, magnesium, and potassium in the three samples of Alta- mont clay loam. San Joaquin sandy loam.—This type contains a considerable quan- tity of humus (table 18, and fig. 17) when one takes into considera- tion the popular criteria for the presence of humus, for the red to reddish brown San Joaquin soils are very different from the brown Altamont or the black Diablo soils. The samples of this type gave 402 University of California Publications in Agricultural Sciences [Vol.3 light colored or nearly colorless humus solutions. But when the ali- guots were ignited, after evaporation, there was a very noticeable blackening and charring of the residue, together with a considerable Loss on Ignition 10 1l 12 13 17 18 21 26 Soils Fig. 17. Graph showing the loss on ignition, the amount of humus, and the percentages of calcium, magnesium, and potassium in the nine samples of San Joaquin sandy loam. loss in weight. This phenomenon, in the hight of the work of Gortner,?* shows that these soils have a ‘‘humus’’ content above that which they might be supposed to have, because of the almost complete absence of 27 Soil Science, vol. 2 (1916), pp. 395-442. 1919} Pendleton: A Study of Soil Types 403 the ‘“‘black pigment.’’ Soil no. 26, probably the only virgin soil in the series, shows a particularly high content of humus for such a soil, though from the color of the soil one would suspect but very little humus. The agreement between the three horizons of the San Joaquin sandy loam samples is close. The average content of humus was 0.68% in the A, 0.51% in the B, and 0.38% in the C horizon. Hanford fine sandy loam.—The variations in humus content in this type are greater than in any of the others (table 19, and fig. 18). This is possibly because of two factors: the open texture of the soil, hence the rapid loss of organic matter by oxidation processes ; and secondly, the high agricultural value of this soil, which has led to a greater appli- eation of fertilizers than has been the case with the other soils. The actual variations in the humus content are large, 0.7% to 2.1% with the average of 1.15% for horizon A, from 0.5% to 1.8% with the aver- age of 0.81% for B, and from 0.44% to 1.07% with the average of 0.59% for C. The extra-typical sample no. 14 is above any of the others in the total humus content. The variations in the subsoil humus content are more or less parallel to those of the surface soil. The following averages of the humus content of horizon A, Diablo 1.26%, Altamont 1.24%, San Joaquin 0.68%, Hanford 1.15%, show that there is not much difference between the soils, except for the San Joaquin sandy loam, which has an average of half the others. Within the type the soils may be nearly alike, as in the San Joaquin and Alta- mont, or may be variable to a large degree, as in the Hanford. The variations in the humus content of the soils are small, considering the diverse nature of the soils, and the usual methods for judging the quantity of humus. TABLE 16-—HuMus (AND Humus ASH) Diablo Clay Adobe Humus Humus ash Horizons Horizons Aver- A Average B Average OC Average A Average B_ Average C age Sample % Jo Jo Yo Jo Ye %o Jo Jo Je Ye Jo 1 1.08 0.51 0.18 0.55 0.75 0.45 1.08 1.08 0.51 0.51 0.24 0.21 0.56 0.56 0.73 0.74 0.46 0.46 2 1.40 1.16 1.09 1.01 0.96 1.09 1.38 1.39 1.15 1.15 1.02 1.06 1.03 1.02 0.96 0.96 0.96 1,03 5 a17 Case \aiees, 1.08 1. ees hae 44S ODT - O.88)* ssc. - - s- 250-480-114. LAR as. ka 6 1.48 1.26 0.95 0.98 0.88 0.78 1.37 1.43° 1.26 1.26 0.99 0.97 0.95 0.96 0.91 0.90 0.85 0.81 Average 1.26 0.95 0.72 0.91 0.95 0.77 404 University of California Publications in Agricultural Sciences [Vol.3 Fig. 18. Graph showing the loss on ignition, the amount of humus, and the percentages of calcium, magnesium, and potassium in the nine samples of Hanford fine sandy loam. 1919] Sample 3 4 Average Sample 10 11 12 13 17 18 21 26 Average A Average f %o % 1.09 1,31 1.32 1.24 Average Jo 0.64 0.77 0.51 0.58 0.52 1.02 0.66 Excluding no. 26 Pendleton: A Study of Soil Types TABLE 17—Humus (AND Humus AsH) Altamont Clay Loam Humus Humus ash Horizons Horizons B Average © Average A Average B_ Average Yo %o % % Yo To Yo Jo 0.89 0.59 1.29 1.08 0.84 0.86 0.58 0.59 1.28 1.26 1.28 1.18 0.69 0.59 0.80 0.98 0.71 0.70 0.28 0.43 0.85 0.83 0.98 0.98 0.95 0.68 0.72 0.87 0.96 0.96 0.68 0.68 0.75 0.74 0.88 0.88 0.84 0.57 0.94 1.01 TABLE 18—Humus (AND Humus AsH) San Joaquin Sandy Loam Humus Humus ash Horizons Horizons B Average C Average A Average B Average Yo Jo %o Yo Jo To To Yo 0.53 0.27 1.31 1.33 ‘ame O35 © xc) OLE es ls ES, SO 8 1 0.41 0.37 0.51 0.66 Wes. O30 seat War) -UGos 6.60 ..5 0.66 0.49 0.32 0.88 1.50 nem. 049 ...... 0.32 Goer ee os. LO 0.50 0.35 1.38 0.90 le O30) Sta Ae We AO oc O90 PES yd ll chats 0.53 1.23 ey Se Oe ees Gere PL LOD, cae ee 0.60 0.42 0.61 0.76 Gass U9". iss, 0.42 0.56 0.59 0.75 0.76 0.19 0.18 0.53 0.37 0.21 0.40 0.21 0.19 0.54 0.53 0.37 0.37 0.79 0.68 0.89 ' 3.57 0.79 0.79 0.82 0.75 0.76 0.83 3.63 3.60 0.51 0.38 . 0.83 1.24 Ct ye! ee | ae eee, 0.95 Loss ON IGNITION 0 % 0.95 0.95 0.91 1.03 1.09 1.08 Aver- oe 0.95 0.97 1.08 1,00 The loss on ignition of the A horizon varies directly with the tex- ture of the soil, the heavier soils losing more on heating. the water of combination of the clay is a large factor in this loss. Obviously In the San Joaquin sandy loam the loss on ignition was determined in the three horizons. only one examined (tables 20, 21, and figs. 15-18). In the other three types the A horizon was the 406 University of California Publications in Agricultural Sciences | Vol. 3 TaBLE 19—-HuMus (AND HuMUS ASH) Hanford Fine Sandy Loam Hummus Humus ash Horizons Horizons je Ee [ E A Average B Average C Average A Average B Average C age 4 Sample % % % Yo % % % % Yo % % Jo 14 2.11 1.81 1.10 1.14 1,24 1.01 8.00 2130 1.78.1.79 1.05 1:07 -1.27 136 3.37 1.36 100-35 15 1.79 0.88 1.04 1.88 0.94 0.92 1.77 1.78 0.93 0.90 0.67 0.86 1.85 1.86 0.89 0.92 0.91 0,92 16 1.20 0.73 0.41 0.91 0.93 0.90 1.20 1.20 0.73 0.73 0.46 0.44 0.91 0.91 1.47 0.93 0.90 0.90 19 0.73 0.51 0.45 0.48 0.57 0.78 0.74 0.73 0.50 051 0.55 050 047 048 0.58 0.58 0.76 0.77 20 1.08 0.86 0.59 0.52 0.90 0.79 1.06 1.07 0.89 0.88 0.50 0.55 0.56 0.54 0.90 0.90 0.78 0.78 22 0.96 0.73 0.58 0.59 0.60 0.58 0.96 0.96 0.71 0.72 0.56 0.57 0.59 0.59 0.60 0.60 0.63 0.61 23 1.04 0.59 0.38 0.58 0.45 0.39 1.07 1.05 0.62 0.61 0.38 0.38 0.57 0.58 0.41 0.43 0.37 0.38 24 0.73 0.55 0.56 0.58 0.69 0.82 0.73 0.73 0.61 0.58 0.51 0.54 0.56 0.57 0.69 0.69 0.80 0.81 25 0.71 0.58 0.45 0.57 0.67 0.74 0.69 0.70 0.56 0.57 0.42 0.44 0.61 0.59 0.71 0.69 0.78 0.76 Average £15 0.82 0.59 0.81 0.78 0.78 Diablo clay adobe-—The variation in these samples was from 5.6% to 8.6%, with the average of 6.8%. The Altamont clay loam has a variation of from 5% to 8.7%, averaging 6.7%. The San Joa- quin sandy loam has a range of variation between 1.6% and 4.2%, with an average of 2.6%. The loss on ignition of the lower horizons increases over that of the surface, because of the increase in texture. The B horizon shows an average loss of 3.9% and the C horizon of 4.67%. The Hanford fine sandy loam range of variation in the loss on ignition is, excluding no. 14, from 2.2% to 3.9%, with an average of 3.4%. Thus the curve for this type is quite uniform, except for no. 14, which shows a loss of 6.9%. It is seen that the averages in the loss on ignition of the A horizons of the Diablo and Altamont soils are close, and high, 6.8% and 6.7% respectively. The averages of the San Joaquin and Hanford sam- ples, 2.6% and 3.4% respectively, are low and not widely separated. Since the values for the types overlap considerably, and the averages are not distinct, except between the light and heavy groups, there is no significant distinction between the four types by this determination. 1919] Pendleton: A Study of Soil Types Diablo Clay Adobe % % 1-A 6.62 6.66 6.64 2-A 6.57 6.64 6.60 5-A 5.61 senee 5.61 6-A 8.67 8.71 8.69 Average 6.88 A Sample % 10 2.13 2.17 11 3.23 3.20 12 5.37 3.22 13 2.94 2.96 17 1.85 1.88 18 1.82 1.83 21 1.68 1.69 26 3.30 Average (Surface horizon only ) Altamont Clay Loam 3-A San Joaquin Sandy Loam Average % a) 2.15 % 8.74 8.82 5.05 5.05 6.58 6.46 Average Horizon B Average Jo 0 2.32 2.27 2.29 6.33 6.16 6.24 2.97 3.18 3.07 6.58 6.75 6.66 2.54 2.61 2.57 2.18 2.18 2.18 1.60 1.56 1.58 6.97 6.95 6.96 3.94 % 1) TABLE 20—Loss oN IGNITION Hanford Fine Sandy Loam 24-A 25-A Yo 6.90 6.95 2.27 2.30 3.26 3.24 3.10 3.13 3.90 3.94 3.06 3.07 3.48 3.45 2.60 2.60 2.68 2.72 Average TABLE 21—Loss oN IGNITION 6.07 5.02 No sample 2.90 2.89 % 6.92 2.28 40 408 University of California Publications in Agricultural Sciences [Vol.3 CALCIUM The Diablo, Altamont, and Hanford soils were analyzed for their calcium in the A horizon only, while the A, B, and C horizons of the San Joaquin sandy loam were analyzed (tables 22, 23, and figs. 15-18). Diablo clay adobe.—There is much divergence in the amounts of CaO in this type, varying from 0.36% to 2.05%, with the average of 1.23%. Altamont clay loam.—In this type there is a little greater varia- tion than in the Diablo samples, with a range of from 0.78% to 5.64%, averaging 2.44% CaO. In both this soil and in the Diablo the wide variation in the lime content is undoubtedly due to the nature of the parent rock, since the soils are residual. San Joaquin sandy loam.—In the CaO content there is no uni- formity among the samples. The A samples of this type contain from 0.47% to 2.98%, with an average of 1.65%. It would seem that the materials from which the soils were derived were of varying composi- tion. For from the present climatic conditions soil no. 25 is the one subject to the least leaching, and yet has the least CaO content. The B and C percentages follow the surface very closely—sufficiently so to necessitate no particular explanation. The range of variation in the B horizon is from 0.11% to 2.42%, and the average is 1.42%. The C samples vary from 0.17% to 2.81%, with the average of 1.52%. Hanford fine sandy loam.—The A samples of this type contain from 2.56% CaO to 4.69%, with 3.33% as the average. The varia- tions are not so marked among the series of this type as in the cases of the other three soils. The absolute range is nearly as great, but the relative variation is less. Even though there are differences between the average CaO con- tent in the several types, the wide variation in the amount found in the several samples of a given type, and the overlapping of these amounts from the different types entirely preclude any statement that as regards the calcium content the soils of any one type are closely similar to one another, or that one type has a higher or lower lime content than another. 1919] Pendleton: A Study of Soil Types 409 TABLE 22—CaLciuM AS CaO (Surface horizons only) Hanford Fine Sandy Diablo Clay Adobe Altamont Clay Loam Loam %o Jo Yo %o To Yo 1-A 1.86 3-A 5.64 14-A 2.91 1.80 3: i i i 5.64 2.99 2.95 2-A 2.12 4-A 0.92 15-A 2.98 1.98 2.05 0.88 0.90 3.22 3.10 5-A 0.56 7T-A 0.89 16—A 2.48 0.17 0.36 0.67 0.78 2.65 2.56 6-A 0.67 Average 2.44 19-A 3.28 ses 0.67 3.17 3.22 Average 1.23 20-A 2.69 2.73 2.71 22-A 3.80 3.92 3.86 23-A 2.88 3.00 2.94 24-A 3.88 4.00 3.94 25-A 4.58 4.80 4.69 Average 3.33 TABLE 23—CALCIUM AS CAO San Joaquin Sandy Loam Horizon A Average B Average C Average Sample %o %o %o % Jo Jo 10 0.67 0.82 5 a AY 0.62 0.64 1.03 0.92 1.12 itt 11 1.94 1.62 1.65 1.26 1.60 1.70 1.66 1.55 1.60 12 3.12 2.21 2.61 3.50 Bot eo ema 2.21 3.01 2.81 13 2.83 2.38 2.46 3.13 2.98 2.46 2.42 2.79 2.62 17 1.83 1.92 No sample 2.08 1.95 2.08 2.00 18 1.40 1.00 1.48 toe (aT 1.45 1.22 1.42 1.45 21 0.91 0.89 0.85 0.84 0.87 0.83 0.86 0.89 0.87 26 0.48 0.13 0.17 0.47 ~- 0.A7 0.10 0.11 0.17 0.17 Average 1.65 1.42 1.52 410 University of California Publications in Agricultural Sciences [ Vol. 3 MAGNESIUM AS MGO Diablo clay adobe.—This type shows a moderate variability in the magnesium content, with from 1.13% MgO to 3.26%, averaging 2.09%. The largest quantity is three times that of the smallest (tables 24, 25, figs. 15-18). Altamont clay loam.—Within the three samples of this type the range in the MgO content is very great, from 0.07% to 1.90%, with the average of 1.05%. The largest is twenty-seven times that of the smallest. San Joaquin sandy loam.—The total MgO in the samples of the type is low, considering that some soils reported by Hilgard contain from 1% to 3% magnesia by the acid digestion. The variation within the A horizon is from 0.34% to 0.90%, with the average of 0.62%, i.e., the largest is three times the smallest. The quantities in the B horizon are somewhat erratic as compared with those of the surface, yet in both the B and C horizons the results approach those of the surface sufficiently to give a rough parallelism. The greater amount of clay and fine silts with the increase of depth gives, as one would expect, an inerease of magnesium. The average MgO content in the B horizon is 0.81%, and in the C horizon 1.05%. TABLE 24—MAGNESIUM AS MGO (Surface horizon only) Hanford Fine Sandy oam Diablo Clay Adobe Altamont Clay Loam i Tl are Jo Jo Jo Jo Jo Jo 1-A 1.64 3-A 1.85 14-A 2.49 2.20 1.92 1.95 1.90 2.49 2.49 2-A 2.16 4—-A 1.21 15-A 0.93 1.95 2.05 1.17 1.19 1.02 0.97 5-A 1.25 7-A 0.09 16-—A 1.10 1.03 1.13 0.05 0.07 0.99 1.04 6-A 3.62 Average 1.05 19-A 2.11 2.90 3.26 1.99 2.05 Average 2.09 20-A 1.77 1.92 1.84 22-A 2.44 2.71 2.57 23-A 1.94 1.70 1.82 24-A 2.14 2.13 2.13 25-A 2.31 2.40 2.35 Average 1.92 1919 } Pendleton: A Study of Soil Types 41] Hanford fine sandy loam.—The MgO content of the surface soil varies from 0.97% to 2.57%, averaging 1.92%. The relative varia- tion within this type is about that of the Diablo and San Joaquin types. Comparing the average amounts of magnesium oxide in the sur- face horizon of the several types, we find the San Joaquin with 0.56%, the Altamont with 1.05%, the Hanford with 1.93%, and the Diablo with 2.09%. The averages do not signify much, however, because of the wide ranges within the types. Therefore as regards magnesium the types are neither distinct nor are the soils within the type closely similar. TABLE 25—-MAGNESIUM AS MaGO San Joaquin Sandy Loam Horizon Sample %o %o % %o %o % 10-A 0.31 0.33 0.53 0.30 0.30 0.45 0.39 0.53 0.53 11-A 0.79 1.21 1.48 0.44 0.61 1.22 1.21 1.25 1.36 12-A 0.83 0.79 1.57 0.79 ln 00 0.79 1.62 1.59 13-A 0.90 1.70 1.67 0.80 0.85 1.63 1.66 1.82 1.74 17-A 0.53 0.51 No sample 0.74 0.63 0.77 0.64 18—A 0.50 0.40 0.64 0.48 0.49 0.69 0.54 0.75 0.69 21-A 0.29 0.28 0.52 barra! 0.29 0.31 0.29 0.56 0.54 26-A 0.50 0.52 0.52 0.52 0.51 0.44 0.48 0.53 0.52 Average 0.56 0.75 1.00 PHOSPHORUS AS P.O; Diablo clay adobe-—The variations in the P,O,; content in the samples of this type are relatively small, from 0.092% to 0.162%, with 0.108% as the average (tables 26, 27, figs. 11-14). Altamont clay loam.—The range of variation in the amount of P.O, is large, from 0.031% to 0.265%, the largest quantity being eight times the smallest. The average is 0.132%. 412 University of California Publications in Agricultural Sciences [ Vol. 3 San Joaquin sandy loom.—The variations in the P,O, content of the surface soil are from 0.039% to 0.11%, with the average 0.068%. The curve is fairly regular. The subsoils follow the surface in a gen- eral way. The B horizon samples vary in the phosphoric acid con- tent between 0.028% and 0.156%, and average 0.069%. The C sam- ples vary between 0.03% and 0.109%, and average 0.067%. The averages of the three horizons are seen to be almost identical. No particular significance can be attached to the minor variations. Hanford fine sandy loom.—The P.O, content in the samples of this type is very variable, from 0.195% to 0.819%, with the average of 0.363%. The average of the San Joaquin sandy loam samples is 0.069%, of the Diablo clay adobe 0.108%, of the Altamont clay loam 0.132%, and of the Hanford fine sandy loam 0.363%. Except between the Diablo and Altamont types these averages would show considerable differences, if it were not that the samples frequently show such wide departures from the averages. The ranges of the several types fre- quently overlap. TABLE 26—PHOSPHORUS AS P.O; (Surface horizon only) Hanford Fine Sandy Diablo Clay Adobe Altamont Clay Loam Loam %o % %o Yo % To 1-A 0.088 3-A 0.278 14-A 0.373 0.096 0.092 0.252 0.265 | 0.292 0.333 2—-A 0.064 4—A 0.081 15-A 0.287 0.078 0.071 0.117 0.099 0.260 0.273 5-A 0.137 7T-A 0.034 16-A 0.260 0.082 0.109 0.028 0.031 0.277 0.268 6-A 0.143 Average 0.132 19-A 0.303 0.181 0.162 0.272 0.287 Average 0.108 20-A 0.190 0.200 0.195 22-A 0.397 0.401 0.399 23-A 0.242 0.270 0.256 24—-A 0.421 0.454 0.437 25-A 0.879 0.759 0.819 Average 0.363 1919] Pendleton: A Study of Soil Types 413 TABLE 27—PHOSPHORUS AS P,O, San Joaquin Sandy Loam Horizon A Average B Average O Average Sample % % % % % % 10 0.118 0.060 0.047 0.102 0.110 0.068 0,064 0.057 0.052 11 0.049 0.047 0.049 0.060 0.054 0.046 0.046 0.028 0.028 12 0.057 0.028 0.064 0.071 aoe? tt Pome 0.028 0.095 0.078 13 0.049 0.037 0.036 0.064 0.056 0.038 0.039 0.024 0.030 17 0.036 0.041 No sample 0.042 0.039 0.082 0.061 18 0.043 0.097 0.086 0.055 0.049 0.074 EES: swt. qigiten 0.086 21 0.069 0.088 0.094 0.068 0.068 0.066 0.077 0.062 0.078 26 0.117 0.130 0.120 0.092 0.104 0.182 0.156 0.098 0.109 Average 0.068 0.069 0.067 PoTASSIUM AS K,O Diablo clay adobe—There is a moderate range in the variation in the amount of K,O within this type, the lowest amount being 1.48% and the highest 2.06%, the four samples averaging 1.71% (table 28, figs. 15-18). Altamont clay loam.—aA greater variation, from 1.09% to 2.14%, of K,O, occurs in the three samples of this type. The average is 1.74%. San Joaquin sandy loam.—This type shows the greatest variation, from 0.98% to 2.84%. But even so, the the largest quantity of K,O is less than three times the smallest. 1.88% K,O is the average of the eight samples. Nos. 11 and 12 of this type show the smallest amounts of K,O of any of the twenty-four samples. Hanford fine sandy loam.—The variation in the K,O content of the samples of this type is not great—from 1.73% to 3.16%, with the average of 2.33%. This is the highest average, as the Diablo clay adobe samples show 1.71%, the Altamont clay loam 1.74%, and the San Joaquin sandy loam 1.88%. Because of the considerable range in the amounts of K,O for the several samples of a type, and because of the many overlappings of the values for one type over another, the averages do not mean much and do not show the soils within a type to be closely similar, nor do they show the types distinct. 414 University of California Publications in Agricultural Sciences [| Vol. 3 TABLE 28—PorTassiuM as K,O (J. Lawrence Smith Method) Hanford Fine Sandy Diablo Clay Adobe Altamont Clay Loam San Joaquin Sandy Loam Loam Average Average ta Average Average No. % % No. % % No. Yo % No. Io oe 1—-A 1.68 3-A 1,06 14-A 1.79 10-A 2,14 1,67 1.67 1.13 1.09 1.67 1.73 2.12 2.13 2—-A 1.62 4-A 1.92 15—-A 2.54 11-A 0.99 169 1.65 2.86 2.14 2.62 2.58 0.98 0.98 5-A 1.45 7-A 1.90 16—A 2.42 12-A = 1.03 1.51 1.48 2.10 2.00 2.46 2.44 1.02 1,02 6-A 2.01 Average 1.74 19-A_ 2,10 13-A=s-:1.50 2.12 2.06 2.03 23.06 «» /j0e 1.50 Average 1.71 20-A 2.00 17-A = 2.40 1.81 1.90 2.24 2.32 22-4 = 2.68 18-A 207 2.62 2.65 2.28 2.17 23-A = 3.10 21-A 2.81 3.23. 3.16 2.88 2.84 24-A=s-_- 2.29 26-A 2.04 2.21 2.25 2.09 2.06 25-A 2.18 Average 1.88 2.21 2.19 Average 2.33 BACTERIOLOGICAL DATA The bacteriological work was not entirely satisfactory, partly be- cause the conditions in one of the incubators were not all that might be desired, and partly because of the refractory physical properties of some of the soils. The Diablo and Altamont types, in all three horizons, were very heavy and hard to mix and keep in even fair physical condition. The San Joaquin soils were predominantly of a heavy texture in the B and C horizons, while the surface horizon was light and the crumb structure was entirely lost if even a small excess of water was added to the culture. AMMONIFICATION There are very marked differences between the various types in this determination, though the samples in a given type vary among themselves to a large extent. Diablo clay adobe-——The highest ammonia production was about three times the lowest, 7.7 mg. and 26 mg. In both this type and the following, the B and C horizons follow the surface horizon quite 1919 | Pendleton: A Study of Soil Tyves 415 Mg N.as NH; Produced Fig. 194. Graph showing ammonification in the four samples of Diablo clay adobe. The quantities are expressed in terms of nitrogen produced per 100 grams of soil with 2% of dried blood. 10 “5 50 Mo N Fixed Soils. Ria, Io Fig. 198. Graph showing nitrogen fixation in the three horizons of the four samples of Diablo clay adobe. The quantities are expressed in terms of milli- grams of nitrogen fixed per gram of mannite in 50 grams of soil. 416 University of California Publications in Agricultural Sciences [Vol.3 closely from sample to sample (table 28 and fig. 194). This may be due to the textures, which are quite similar throughout the soil column. The averages for the three horizons were: A, 18.6 mg.; B, 12.6 mg.; and C, 8.9 mg. 7 Soils Meg N. as NHs3 Produced Fig. 204. Graph showing ammonification in the three horizons of the three samples of Altamont clay loam. 3 + 7 Soils Mg N. Fixed Fig. 208. Graph showing nitrogen fixation in milligrams in the three horizons of the three samples of Altamont clay loam. Altamont clay loam.—As regards horizon A the amount of am- monia produced in one soil is three times that in the lowest, 10 mg. nitrogen and 33 mg. nitrogen as ammonia, with 8.9 mg. as the average (table 30 and fig. 20a). The amount of nitrogen as ammonia pro- duced in the B horizon averaged 12.6 mg., in the C horizon 8.9 mg. 1919 | Pendleton: A Study of Soil Types 417 San Joaquin sandy loam.—The amount of ammonia produced in the A horizon varied between 30.4 mg. of nitrogen and 57.1 mg., the average was 40.2me. (table 31 and fig. 214). The production of ammonia, in milligrams of nitrogen, by the B samples varied between 4.5 mg. and 38.1 mg., with 20 mg. as the average. In the C samples the variation was nearly as great, between 5.7 mg. and 32 mg., with the average of 20.9 mg. Thus there are notable variations among the 26 Soils Mg N. as NHs3 produced Fig. 21a. Graph showing ammonification in the three horizons of the eight samples of San Joaquin sandy loam, samples of this type, the proportional variation being very great, con- sidering the three horizons. Possibly the reason that the B and C horizons are so divergent from the surface is that there is a very marked variation in the texture between the surface horizon and those below the surface. Hanford fine sandy loam.—The variation is large here also (table 32, fig. 224), the largest quantity of ammonia produced in the surface soil is twice that of the smallest production, 72 mg. and 35 mg. The subsoil variations, in a general way, parallel those of the surface. The average production of ammonia in the three horizons is as fol- 418 University of California Publications in Agricultural Sciences [ Vol. 3 lows: A, 56.9 mg. nitrogen; B, 46.3 mg. nitrogen; and C, 38.7 mg. nitrogen. In attempting to correlate the variations in ammonifying powers with the known variations of the soils, or with the known his- tories of the soils, there seem to be no relations of significance. The Altamont and Diablo types are about alike in their low am- monifying power. The Hanford and San Joaquin are both higher and nearer to each other than to the two heavy types, yet the Hanford is noticeably higher than the San Joaquin. This is as one would ex- pect, from a knowledge of the soils in the field. Considering the types as a whole, as represented by the A horizon, there are more marked variations between the types than between the samples of a given type though the variations within a given type are very large. TABLE 29—AMMONIFICATION Diablo Clay Adobe Milligrams N as NHg Produced A B Cc Increase Increase Increase Checks over Checks over Checks over Samplé Cultures average checks Cultures average checks Cultures average checks 1 31.48 28.58 24.24 40.32 252 33.38 22.98 2.28 23.50 14.99 2.42 17.19 2 19.81 9.45 8.41 17.07 1.68 16.76 9.84 1.91 7.73 9.95 1.05 8.13 5 15.90 11.55 No sample acme 1.75 14.15 12.54 1.54 10.50 6 12.33 7.76 12.33 ae 2.11 10.22 13.55 2.07 8.58 12.33 2.03 - 10:30 Average 18.63 12.58 11.87 . TABLE 30—AMMONIFICATION Altamont Clay Loam Milligrams N as NHg Produced A B Cc Increase Increase Increase Checks over Checks’ over Checks over Sample Cultures average checks Cultures average checks Cultures average checks 2 8.14 6.97 5.89 10.58 1.68 7.68 ito.” ~ KAO 5.16 4.91 1.54 3.86 +t 19.75 6.59 5.41 19.12 2.66 16.77 6.67 136 5.27 5.12 1.19 4.07 7 28.66 19.66 8.00 27.53 2.03 26.06 16.25 1.75 16.20 12.37 1.33 8.95 Average 16.84 8.88 5.63 1919] Pendleton: A Study of Soil Types TABLE 31—AMMONIFICATION San Joaquin Sandy Loam Milligrams N as NH, Produced A B Increase Increase Checks over Checks over Sample Cultures average checks Cultures average checks 10 54.24 42.63 41.95 1.72 46.73 36.11 1.28 38.09 11 44.47 7.47 73.23 1.70 57.15 12.52 1.81 8.18 12 44.48 18.73 40.07 1.56 40.71 21.81 1.50 18.77 13 41.66 5.41 45.94 1.30 42.50 5.36 0.86 4.52 17 30.19 27.59 33.88 1.66 30.37 20.68 1.51 22.62 18 35.04 30.56 35.24 1.48 33.66 22.81 1.30 25.38 21 34.44 37.41 30.89 1.48 31.18 37.74 1.388 36.19 26 40.81 7.50 tices 1.64 39.17 8.41 1.44 6.51 Average 40.18 20.03 TABLE 32—AMMONIFICATION Hanford Fine Sandy Loam Milligrams N as NHzg Produced A B Increase Increase Checks over Checks over Sample Cultures average checks Cultures average checks Horizons 14 37.35 27.96 43.57 1.78 38.68 48.46 1.46 36.75 15 33.11 45.68 ai.vo.° 17D 35.68 48.38 1.70 45.33 16 56.59 44.08 56.77 1.83 54.85 42.10 1.61 41.48 19 52.92 46.70 51.85 1.47 650.91 as.ga. . dS" 45.68 20 72.49 45.49 74.21 1.36 71.99 38.52 1.03 40.97 22 64.92 57.44 67.56 1.75 64.49 55.384 1.51 54.88 23 71.56 50.84 68.66 1.61 68.50 43.01 1.37 45.55 24 65.02 50.09 59.51 1.50 60.76 46.54 1.32 46.99 25 68.20 69.29 67.29 1.43 66.31 60.03 1.25 63.41 Average 56.91 46.34 419 0 —— Increase Checks over Cultures average checks 28.89 38.25 1,59 31.98 6.05 6.78 1.68 4.78 10.91 6.1] 1.14 7.87 3.80 15.17 0.88 8.60 No sample 21.96 16.92 1.47 17.97 25.72 29.66 1.42 26.27 9.08 5.43 1.54 5.71 " 12.89 Cc Increase Checks over Cultures average checks 14.39 41.70 1.24 26.80 59.90 52.59 1.62 54.62 44.58 52.10 1.69 46.65 24.56 28.12 1.24 25.10 22.05 30.35 1.00 25.20 46.08 47.55 1.60 45.21 35.15 35.23 1.35 33.84 37.56 40.21 1.33 37.55 61.01 47.70 1.22 53.13 38.67 420 University of California Publications in Agricultural Sciences | Vol. 3 NITROGEN FIXATION28 Diablo clay adobe.—This type shows the highest quantity of nitro- gen fixed, 9.6 mg., with the subsoil quantities, much lower than the surface. The variation within the type is seen to be the largest of that in any of the types. Altamont clay loam.—The surface samples have 1.0, 4.7, and 9.1 mg. nitrogen (table 34 and fig. 20B). The soils shows a wide diver- vence between the surface samples and between the surface and sub- soils. This is to be expected in the heavier soils. Mg N. Fixed Fig. 218. Graph showing nitrogen fixation in the three horizons of the eight samples of San Joaquin sandy loam. San Joaquin sandy loam.—The quantity fixed in the A horizon (table 35 and fig. 218) is small and quite variable. It is between nothing and 5.5 mg., with the average of 1.9 mg. Instead of nitrogen fixation denitrification took place in a number of cases, especially in horizon C. Considering the wide variation in textures of the horizons, it is rather odd that there should not be a greater variation between the soils from the various depths. Hanford fine sandy loam.—The amount of nitrogen fixed by the surface soil (table 36, and fig. 228) averages much higher, 5.7 mg., than that in the San Joaquin sandy loam, though the range of varia- tion is about the same. It is noticeable that the amounts of nitrogen fixed by the B and C horizons of the soils nos. 14 and 19 are much 28 All of the figures on nitrogen fixation refer to the milligrams of nitrogen fixed per gram of mannite in 50 grams of soil (table 33 and figs. 9-13). 1919] Pendleton: A Study of Soil Types 421 less (even to denitrification) absolutely and relatively as compared with the surface horizons, than the amount fixed by the B and © horizons of the soils nos. 20 to 25 inelusive. Comparing the nitrogen fixation of the various types, there seem to be no characteristic differences between the heavy Altamont and Diablo types, while the lighter Hanford and San Joaquin types are considerably different from each other. degree of similarity between the samples of a given type. of variation within types is large. A B ee Increase Checks over Checks’ over Sample Cultures average checks Cultures average checks 1 60.25 31.52 63.40 02.22 9.60 29.56 34.67 -4.13 2 55.34 32.92 49.39 45.88 6.48 38.18 33.80 1.75 5 48.68 35.73 48.68 41.92 6.76 37.12 32.389 4.03 6 45.88 39.64 46.86 58.49 —12.12 42.72 50.77 9.59 Average 1 1.44 TABLE 34—NITROGEN FIXATION Altamont Clay Loam Milligrams N fixed per gram of mannite A B Increase Increase Checks over Checks over Sample Cultures average checks Cultures average checks 3 71.26 49.04 70.40 61.71 9.12 51.84 43.78 6.66 4 60.25 28.02 52.19 51.49 4.73 27.32 26.48 1.19 7 52.95 37.75 53.44 02.12 1.08 37.40 36.60 1.00 Average 4.98 2.95 TABLE 33—NITROGEN FIXATION Milligrams N per gram of mannite Diablo Clay Adobe As a whole there is but a fair The degree C Increase Checks over Cultures average checks 22.77 24.87 28.61 -4.79 30.47 32.22 29.77 1.57 No sample 35.02 39.01 39.05 -2.03 0.52 0 Increase Checks over Cultures average checks 37.13 38.51 33.76 4.06 20.31 21.01 2048 018 30.81 27.18 29.94 -0.94 1.41 422 University of California Publications in Agricultural Sciences [ Vol. 3 14 15 16 19 20 22 23 24 26 Soils Mg N. as NHs produced Fig. 224. Graph showing ammonification in the three horizons of the nine samples of Hanford fine sandy loam. Meg N. Fixed Fig. 228. Graph showing nitrogen fixation in the three horizons of the nine samples of Hanford fine sandy loam. ne Poe ge @ 1919] — Sample 10 25.01 23.47 11 27.25 31.87 12 25.85 23.82 13 22.77 21.58 Le 13.52 13.45 18 15.55 13.24 21 14.85 16.11 26 19.54 19.34 Average Sample 14 71.52 63.05 15 38.18 29.56 16 30.33 32.92 19 25.56 26.41 20 38.04 38.11 22 35.59 31.80 23 38.95 43.57 24 28.79 34.61 25 26.55 26.41 Average A Checks Cultures average A Checks Cultures average 59.61 26.55 27.84 22.49 29.66 29.17 36.10 Pendleton: A Study of Soil Types TABLE 35—NITROGEN FIXATION San Joaquin Sandy Loam Milligrams N fixed per gram of mannite 2. ae, | Increase over checks 0.66 0.98 —0.94 1.91 -~ B Checks a a Increase over Cultures average checks 17.16 16.67 22.91 22.84 20.17 17.09 18.49 17.86 9.46 10.23 8.76 8.20 7.98 6.44 12.61 12.82 13.34 1.25 —0.72 1.09 TABLE 36—NITROGEN FIXATION Hanford Fine Sandy Loam Milligrams N fixed per gram of mannite Increase over checks 7.67 7.32 3.78 4.49 8.41 4.52 5.16 6.03 3.78 5.69 B Checks Increase over Cultures average checks 41.61 41.69 22.07 21.09 16.46 16.04 14.43 13.59 22.84 23.61 22.20 23.40 19.19 20.25 19.89 21.52 17.86 17.93 41.01 20.12 14.85 0.64 1.46 1.40 3.21 423 0 a, Increase Checks over Cultures average checks 15.83 18,14 10.33 §.65 21.72 22.00 19.43 2.43 18.98 20.10 20.41 —0.87 13.31 14,50 16.35 -2.45 No sample 9.18 11.42 9.74 0.56 6.58 7.28 7.01 -0.07 7.14 7.36 8.24 -0.99 1.20 Cc Increase Checks over Cultures average checks 31.10 30.19 29.07 1.57 12.40 14.08 13.87 -0.63 9.67 8.97 10.61 -1.29 Bite 12.33 11.80 —-0.25 17.09 20.60 11.52 7.32 17.30 16.46 11.87 5.01 11.90 11.98 8.90 3.04 18.52 17.51 13.91 4.11 15.55 13.87 11.31 3.41 2.27 424 University of California Publications in Agricultural Sciences [Vol.3 NITRIFICATION 29 The most noticeable thing about the nitrification results is the very wide range of variation in the various representatives of the Hanford fine sandy loam as compared with the quite uniform and consistent results obtained with the other types. Diablo clay adobe—The percentage of nitrogen nitrified (table 37, 38, and fig. 23) is uniformly low. The B samples showed a less vigorous nitrifying flora (except in the case of no. 6) than the sur- face ones. Dried blood in the quantities used seems to depress the A S.N.+Cottonseed Meal A S.N.+ (NH4)2S04 A S.N.+ Dried Blood A Soil Nitrogen 1 2 5 6 Soils Percentages of N. Nitrified Fig. 23. Graph showing the percentages of nitrogen in various nitrogen containing materials nitrified in the four samples of the Diablo clay adobe. normal activity (A horizon average 0.81%), while the (NH,).SO, (A horizon average 3.03%) and the cottonseed meal (A horizon average 2.91%), as compared with the incubated control tend to in- crease the percentage of nitrogen nitrified. It should be kept in mind that an absolute increase in the nitrogen content may accompany a deerease in the pereentage, due to the greatly increased amount of nitrogen present after the addition of a nitrogenous substance. The variation of the samples within this type is very moderate as compared with the San Joaquin and Hanford types. 29 The figures used in the discussion shows the percentages of the nitrogen in the cultures which were nitrified. There are two tables for the samples of each type. The percentages of nitrogen nitrified are rearranged in a second table for greater ease in comparing results. ad 1919 } Pendleton: A Study of Soil Types 425 Altamont clay loam.—The percentages of nitrogen nitrified (tables 39 and 40, fig. 24) are as a whole lower than in the Diablo soils. A similar relative effect of the several nitrogenous materials is seen, for (NH,).SO, is first, cottonseed meal, second, the soil’s own nitrogen third, and dried blood fourth in the percentages of nitrates produced. As in the Diablo soils the variation is not great from soil to soil. San Joaquin sandy loam.—A wide range of variation (tables 41, 42, and fig. 25), from 1.2% to 4.5%, is found in the incubated control, possibly due, in part, to the considerable variations in the physical nature of the samples. The relative action of the nitrogenous ma- YA S.N.+ (NH4)2S0x A 8. N. +Cottonseed Meal ; |A Soil Nitrogen —“JA 8. N.+ Dried Blood 3 4 7 Soils Percentages of N. Nitrified Fig. 24. Graph showing the percentages of nitrogen in various nitrogen containing materials nitrified in the three samples of the Altamont clay loam. terials in the soils of the San Joaquin samples as compared with that in the Diablo and Altamont soils is well shown by the following aver- ages of the A horizon: dried blood had 0.02%. cottonseed meal had 0.33%, and ammonium sulfate had 0.56% of the nitrogen nitrified, while the incubated control had 2.47% nitrified. The soils are normally low in nitrogen, and this, together with the poor physical condition, made an unfavorable medium for any bacterial activity. This applies especially to horizons B and C. Hanford fine sandy loam.—This is by far the most inexplicable set of results in the nitrification studies (tables 48, 44, and fig. 26). The physical nature of this type is admirably suited for bacteriological tumbler cultures, the soil being friable, not puddling readily, and while in the incubator may be kept at the approximately optimum moisture content with little difficulty. This property is fairly con- 426 University of California Publications in Agricultural Sciences [Vols3 stant throughout all the samples (except no. 14) and cannot well be supposed to affect the results greatly. No. 14 has a low nitrifying power throughout, but it is not representative of the type, for it is heavier in texture than the rest. Moreover, it had been submerged by river overflows shortly before the collection of the sample. One would expect these factors to influence the numbers and the activity of the bacterial flora. There is but little similarity in the way the different samples of the A or B horizons behave toward any given A Soil Nitrogen A S.N.+ (NHa)2S0O« A S.N. +Cottonseed Meal © 26 Soils Percentages of N. Nitrified Fig. 25. Graph showing the percentages of nitrogen in various nitrogen containing materials nitrified in the eight samples of the San Joaquin sandy loam. nitrogen containing material. Variations from 1% to 50%, from 0% to 14%, from 4.5% to 8%, or from 15% to 15.5% from soil to soil, without regularity, give shgeht basis for generalizations. The average effect of the A horizon samples of the Hanford fine sandy loam as regards the several nitrogenous materials is as follows: dried blood, 5.62% ; cottonseed meal, 13.72%; ammonium sulfate, 3.29% ; incubated control, 1.55%. In a general way there is a similarity between the effects of a given nitrogen containing material on the surface sample, and on the B horizon. This should be so, since these soils are very deep and uniform in texture. However, in the C horizon there were still greater decreases in the bacterial activity. Sample 1-B 6-A 6-B | AP 1919 } Pendleton: A Study of Soil Types 427 As regards nitrification in general there is difficulty in showing any greater resemblance between the samples of a type than there is from type to type. In certain features, however, the types are some- what distinct: (1) The relation of the nitrification of the soil’s own nitrogen to the soil’s action upon added nitrogen is rather distinct for the types. The normal soil in the San Joaquin type gave a much larger per cent of nitrogen than did the soil plus the added nitrogen containing materials. In the Diablo type (fig. 25) the normal soil was about midway in its production as compared with the soils to which the nitrogenous materials were added. In the Hanford fine sandy loam the normal soils gave a much lower percentage nitrifica- tion than in the greater number of instances where the soils were treated with nitrogenous materials. (2) The relative nitrification of the various nitrogenous materials is somewhat distinct for the types. The Diablo, Altamont, and San Joaquin show the ammonium sulfate first, with the cottonseed meal second, and the dried blood third. The Hanford type shows cottonseed meal first, with dried blood second and ammonium sulfate third. TABLE 37—NITRIFICATION Diablo Clay Adobe Soil nitrogen and Soil nitrogen and Soil nitrogen and Soil nitrogen ammonium sulfate dried blood cottonseed meal 5 5 5 5 im” «(ee & Su oe s Sea 0S SS me 88 SS Ce eS ay ey Pees se a Ba ec. £5 Hin tl ee eee Es Z|. SS 53 25. Ss eee “hee re eee es fe”. UR” a ar | ao 0.90 104.43 0.86 5.35 146.82 3.65 2.20 347.22 0.63 5.00 198.42 2.50 0.28 93.34 0.30 0.77 135.74 0.57 Jee k | Se Te. EST aa) ce 0.19 - 57.22 0.33 0.25 99.62 0.25 0.07 300.02 0.02 Ogi6.” Sig 23 enor 0.47 91.76 0.51 3.47 134.16 2.58 4.07 334.56 1.22 6.82 185.76 3.77 0.33 67.60 0.49 1.17 110.00 1.06 0.08. 210.40... 0.19 161.60 0.12 0.59 59.54 _...... 26 SOL08 ok. 0.80 302.34 _...... 0.80 153.44 °° 0.47 83.82 0.56 3.81 126.22 3.02 1.66 326.62 0.51 3.76 177.82 2.1 0.36 64.78 0.56 0.42 107.18 0.39 0.19 307.58 0.06 0.97 158.78 0.6 0.59 116.58 0.51 4.58 158.98 2.88 3.13 359.38 0.87 6.88 210.58 1.65 101.54 1.63 3.00 143.94 2.08 1.19 344.34 0.35 4.55 195.54 0.96 78.10 1.23 1.01 120.50 0.84 0.37 320.90 0.01 0.47 172.10 . 428 University of California Publications in Agricultural Sciences | Vol. 3 Percentages of N. Nitrified Fig. 26. Graph showing the percentages of nitrogen in various nitrogen containing materials nitrified in the nine samples of the Hanford fine sandy loam. 1919 | Pendleton: A Study of Soil Types 429 TABLE 38—NITRIFICATION——PERCENTAGES OF NITROGEN NITRIFIED Diablo Clay Adobe Soil nitrogen and Soil nitrogen Soil nitrogen Soil nitrogen ammonium sulfate and dried blood cottonseed meal a, i a ———_—_— Sample A B © A B © A B © A B 6) 1 0.86 0.30 0,33 3.65 0.57 0.25 Ch Se 0,02 Sasa .cn2t. a aero 2 On ee 2. 258° P06 - oo 5 ee OST. “OAS ss ataies 5 0.56 666’ ..... G:08 O38 A a ee oie alee EF oe 3-A 0.60 123.42 0.49 4.12 165.82 2.49 1.17 ~~ 366.22 0.32 3.57 217.42 1.64 3-—B 0.04 87.56 0.05 0.39 129.96 0.32 (dt ees 1 O08 161 56%) 322 3-C 0.27 67.52 0.40 0.20 109.92 0.18 eieeatUse Se ik tbe 4A 1.30 102.58 7 2.95 144.98 2.05 2.34 345.38 0.68 4.83 196.58 2.46 4B 0.45 52.96 Si Ob .eO.. ick ee O iaccas SN Uccgs 146.965. eT A ee a eae eae Bao: onbckey +. tees i 0.20 134.96 0.15 7-A 0.50 104.24 0.48 1.35 146.64 0.93 0.40 347.04 0.12 1.27 198.24 0.64 7-B 0.25 73.20 0.34 O32: 116:60) 028 Vw ae = 185) | a a eee LOT.2Ory eis | a ae Wacten? our Slack: TUS.) aac Cheers Se enn, Fee 153.88 TABLE 40—NITRIFICATION—PERCENTAGES OF NITROGEN NITRIFIED Altamont Clay Loam Soil nitrogen and Soil nitrogen Soil nitrogen and Soil nitrogen ammonium sulfate and dried blood cottonseed meal Sample A B C A B CO A B C A B C 3 0.49 0.05 0.40 2.49 0.32 0.18 ee aaa DGG * cul Fee 4 ter 0.80 . SV ee horn et J aie 3:46 0.15 7 0.48 0.34 ..2.. ive, OSE «22. Lo) ee OUGS = kn eee Average 0.75 0.41 0.13 1.82 0.20 0.06 i = ieee OO ee eaten 0.05 450 Sample 10-A 10-B 10—C 11—A Sample 10 7 12 13 uf 18 21 26 Average University of California Publications in Agricultural Sciences Soil nitrogen pro- duced, mg. ; Total N present bo ~“ lor) & - jp in soil, mg. oo w © nitrified, % S © © Nitrate ow w ww DS b& oo Oo © & Nitrogen i ~] ior) on S wo i) bo Or ad ~ | oo wouwn _ bo foot , Oo jw} 4.5 4.3 2.3 TABLE 41—NITRIFICATION San Joaquin Sandy Loam Soil nitrogen and ammonium sulfate -~ Nitrate pro- duced, mg. —_) bo rs otal N present in soil, mg. 122.26 111.98 105.46 135.10 126.36 123.66 131.32 117.92 125.62 124.80 125.21 117.50 113.72 103.22 112.26 100.98 104.28 113.80 96.72 98.82 125.48 111.48 trified, % 2 © t& ni oC © © © Nitrogen ior) Soil nitrogen and dried blood © Nitrate pro- duced, mg. i) ior) otal N present n soil, mg. 1 2.46 292.18 285.66 Sy 315.30 306.56 303.86 311.52 298.12 305.82 305.00 305.41 297.70 293.92 283.42 292.46 281.18 284.48 nitrified, % © Nitrogen =) bo eeeeee (Vol. 3 Soil nitrogen and cottonseed meal > Nitrate pro- duced, mg _ i) TABLE 42—NITRIFICATION—PERCENTAGES OF NITROGEN NITRIFIED Soil nitrogen A B Cc 14 09 0.3 25 .... 04 17 0.5 0.3 1.2 2 1.9 4.5 4.3 2.3 2.47 0.17 0.3 San Joaquin Sandy Loam Soil nitrogen and ammonium sulfate A 0.56 0.03 0.18 Soil nitrogen and dried blood B waeeee weeeee weeeee aeeeee aeeeee Soil nitrogen and A B Cc 0. 0.33 0.01 0.01 © Total N present in soil, mg nitrified, % © Nitrogen, ° ® weeeee cottonseed meal lL 1919] Sample 14—A 14—-B 14—C 15-A 1. 15-—B 15-C 16—-A 16—B 16—C 19-A 19-B 19-—C 20-—A. 20-B 20-—C 22—A 22-B 22-C 23-A 23-B 23-—C 24-A 24-B 24—C 25-A 25-B 25-C Sample 14 15 16 19 20 22 23 24 25 Soil nitrogen Nitrate pro- duced, mg. i ° = bo or 0.07 Average Total N present in soil, mg. Nitrogen nitrified, % 45.40 1.2 31.01 1.0 22.62 0.5 Pendleton: A Study of Soil Types TABLE 43—NITRIFICATION Hanford Fine Sandy Loam Soil nitrogen and Soil nitrogen and 4 ammonium sulfate g. “1 £& db duced, m So © CO Nitrate pro- op oO 0.32 0.16 SE as Cee, | : tb s R - a3 Bs =A 161.62 0.1 ct ba 100.54 0.7 95.50 3.4 $2.64. .02 70.14 98.08 2.5 7210 8. 63.62 87.38 2.3 66.98 0.2 66.00 0.2 IOI 2 Aye Toole: + AH 65.44 100.74 6.4 76.86 0.3 66.14 82 114.6 78 71.54 12.5 60.20 20.6 93.74 4.4 76.30 0.5 70:29 - 05 S780) (71:5 73.41 0.4 65.02 0.2 to duced, mg. © Nitrate pro- or _ dried blood Total N present in soil, mg. 254.22 217.02 193.14 188.10 175.24 162.74 190.68 164.70 156.22 179.98 159.58 158.60 194.32 167.78 158.04 193.34 169.46 158.74 207.20 164.14 152.80 186.34 168.90 162.82 180.40 166.01 157.62 ww Nitrogen iu nitrified, % oS; Saad 0.2 0.2 0.1 4A 9.2 1.4 0.02 0.3 hieo 0.3 0.01 11.9 0.3 0.4 0.7 Soil nitrogen and cottonseed meal Nitrate pro- U1 0.07 13.58 Lv 2.50 18.25 2.65 1.30 14.35 5.91 0.73 8.65 0.05 Ji 2 TABLE 44—NITRIFICATION—PERCENTAGES OF NITROGEN NITRIFIED Hanford Fine Sandy Loam Soil nitrogen A B 2.7 0.4 16 0.4 2.2 0.3 13 0.4 14. 0.8 2.0 2.6 te: la | hee 61.0 1.55 0.66 C 0.1 0.1 0.1 0.7 3.6 1.8 1.1 0.5 0.88 Soil nitrogen and ammonium sulfate A 0.1 3.4 2.5 2.3 1.2 6.4 7.8 4.4 1.5 3.29 1.59 3.38 B 0.2 0.1 0.2 0.1 0.3 12.5 0.5 0.4 Cc 0.7 0.2 8.2 20.6 0.5 0.2 B 4.1 0.2 0.2 8) (ee 14.1 9.2 14 0.02 17.9 0.3 11.9 0.3 0.7 —_ 5.62 1.09 Soil nitrogen and dried blood C 0.1 0.3 0.01 0.4 0.09 otal N present in soil, mg e 166,22 129.02 105.14 100,10 87.24 74.74 102.68 76.70 68.22 91.98 71.58 70.60 104.32 77.78 68.04 103.34 79.46 68.74 117.20 74.14 62.80 96.34 78.90 72.82 90.40 76.01 67.62 -, nitrified, % Nitrogen, 0.1 13.1 2.4 3.6 15.5 3.6 2.1 14.9 Soil nitrogen and cottonseed meal A B 1 | a 4.5 4.8 45 4.8 8.1 0.3 59 1.9 13.1 2.4 15.5 3.6 1449 75 9.6 0.06 13.72 2.55 C 0.1 0.2 0.2 0.3 0.1 3.6 2.1 1.0 0.82 432 University of California Publications in Agricultural Sciences | Vol. 3 GREENHOUSE DATA There are objections to all greenhouse work due to somewhat un- natural conditions for the usual indicator crops, the lack of a normal water supply, the small amount of root space, ete. Crowding of the pots is also apt to cause variations. Even the slight change in the loca- tion of a pot on the bench will affect the growth of plants, as some of the elaborate precautions for moving the pots daily, and in a given order, testify. The outstanding advantage of greenhouse work is that with a given indicator crop a group of soils, or soil conditions, may be compared under very similar conditions. In the present case, the leaks in the sash allowed rain water to fall into some of the pots to a considerable extent. The pots’ so affected showed a poorer growth in the cases of the heavy Altamont and Diablo samples, where the soil was readily compacted, while in the poor Hanford and San Joaquin soils the pots receiving leakage water showed markedly better growth. To minimize such errors, as much as possible, triplicates were used, as above explained, besides repeating the series. In working out the final averages of the crop it was suggested that a selection be made of the crop dry weights, in case that there was a marked varia- tion between the triplicates, using the two weights close together, and excluding the third if it were widely divergent. However, when one begins to select certain figures from a series, and bases comparisons upon these alone, there is apt to be the tendeney to select those figures that will prove the point in question, unless there is some known dis- turbing factor causing the divergence and which warrants the exclu- sion of certain figures. Other cases that are rather hard to deal with are those in which the number of plants reaching maturity was not up to the standard to which the series was thinned when the plants were young. This fail- ure may have been due to poor germination, or to accidental destrue- tion of the plants during growth. Sometimes less than the standard number of plants will give a much greater dry weight per plant than the normal number. It was not deemed advisable to use the weight per plant, but rather to use the total dry weight of the crop, and only consider of value the series in which the number of plants per pot was practically constant. In the greenhouse work the Diablo clay adobe, the Altamont clay loam, and the Hanford fine sandy loam samples were compared by 1919] Pendleton: A Study of Soil Types 433 two croppings, while one crop was grown on the San Joaquin sandy loam soils. The infertility of the San Joaquin soils, in some cases extreme, greatly retarded crop growth. Diablo clay adobe. First crop.—Due to the presence of wild oat seed in all the four samples of this soil, and the inability to distin- guish the young wild oat plants from the planted oats, wheat, or barley when thinning, the value of the results of the grain crops in this series is much decreased. The averages plotted include the total ds) 20 rane Bur Clover 05 Bur Clover £ ‘a oO lO Oats 5 Barley Wheat O Phaseolus | 2 Ss 6 Soils Fig. 27. Graph showing the total dry matter produced by wheat, barley, oats, Phaseolus, bur clover, and oats and bur clover on the four samples of Diablo clay adobe. First crop. crop, whether pure or with a greater or less quantity of the wild oats, though the number of plants harvested was usually six or less. Planting the oats and bur clover together was not a success. In three of the soils the crop of bur clover alone was greater than that of the six bur clover plants plus the six oat plants. Plate 44 shows how, in some cases, the oats dominated, and in others the bur clover was superior. On the soils of this type bur clover was the most satisfactory crop, while the white beans were the most unsatisfactory of all. Comparing the total crops (see fig. 27 and tables 45-50), it will be seen that 1, 5, 2, 6 is the order for bur clover, soil no. 1 giving the 434 University of California Publications in Agricultural Sciences [Vol.3 best crop and soil no. 6 the poorest, while nos, 5, 1, 2, 6 is the order for barley and wheat. Oats show nearly double the crop on soil 5 that it does on any of the other three soils. There is thus a general agreement between the indicators that the soils are not of the same productivity. TaBLE 45—DraBLo CLay ADOBE, First Crop WHEAT Planted, November 6, 1915. Harvested, July 10, 1916 Straw Grain Total dry matter No. Average Average Average Pot plants Weight weight Weight weight Weight weight ; Notes 1-1 Wheat 2 3.65 0.25 Oats 4 2.15 0.69 6.74 i a, Xe es Oe Oats 6 4.05 2.47 6.51 1-3. Wheat l 1! SS YR en ee Pe Oats 5 5.20 5.62 1.64 1.68 8.66 7.30 2-1 Wheat 5 5.33 0.05 Oats 1 eee ee. NTE 5.81 2-2 Wheat 4 3.53 0.03 Oats 2 0.69 0.04 4.31 o- Whats: fon* °° oO L Oats 3 1.39 4.63 0.49 0.21 4.43 0.84 5-1 Wheat 2 4.33 0.90 Oats 4 1.56 0.42 7.21 5-2 Wheat 3 7.28 1.81 Oats 2 3.23 1.02 13.44 5-3 Wheat 3 7.09 «0.48 Oats 2 0.64 8.04 0.47 1.70 8.68 9.74 6-1 Wheat 2 2.19 Oats 4 1.03 ee ee, “aco ll 1.72 2 Wheete 880 = nc: o Oats 4 251 325 0.70 O17 £5.58 3.49 oh 3,29 1919] Pendleton: A Study of Soil Types 435 TABLE 46—Drasio Cray Apose, First Crop BARLEY Planted, November 6, 1915. Harvested, April 28, 1916 Straw Grain Total dry matter No. Average Average Average Pot plants Weight weight Weight weight Weight weight Notes 1-1 6 5.19 1.06 6.25 1-2 + Barley 5 4.79 0.75 mee Se earl 6 Wy |) on! AM ee 5.54 1-3 Barley 4 5.75 1.34 Oates) <2" - 2:5. 5.24 0.98 1.38 8.07 6.62 2-1 6 5.12 1.05 6.17 2-2 6 4.87 5 IO 6.58 2-3 Barley 5 2.78 0.49 Oats 1 0.69 4.49 0.23 1.16 4.19 5,65 5-1 6 6.59 2.12 8.70 5-2 Barley 5d 3.01 Oats 1 2.56 0.25 3.25 5-3 Barley 5 3.01 Oats 1 8.43 5.86 0.04 1.95 11.48 7.81 6-1 6 GR: ti 1.26 5.88 6-2 6 4.36 1.25 5.61 6-3 Barley 5 0.33 Oats 1 3.49 4.16 0.24 1.02 4.06 5.18 TABLE 47—DIABLO CLAY ADOBE, FIRST CROP OaTs Planted, November 6, 1915. Harvested, May 8, 1916 Straw Grain Total dry matter No. Average Average Average Pot plants Weight weight Weight weight Weight weight Notes 1-1 6 4.11 1.24 5.35 1-2 6 6.56 2.59 9.15 1-3 6 4.76 5.14 1.34 1.72 6.10 6.86 2-1 6 4.36 1.10 5.46 2-2 6 total only total only 6.92 2-3 6 6.66 5.01 2.06 1.58 8.72 7.03 5-1 is 7.55 2.59 10.15 5-2 6 10.66 4.38 15.04 _ One barley plant 5-3 6 10.10 3.12 13.22 6-1 6 4.70 1.48 6.18 6-2 6 6.81 1.42 8.22 6-3 6 6.78 1.09 7.88 436 University of California Publications in Agricultural Sciences [Vol.3 TABLE 48—D1aBLo CLay ApbosBe, First Crop Burk CLOVER Planted, November 6, 1915. Harvested, May 8, 1916 Straw Grain Total dry matter No. Average Average Average Pot plants Weight weight Weight weight Weight weight Notes 1-1 5 11.01 15.13 26.32 1-2 + 9.07 14.15 23.22 1-3 6 12.18 10.75 18.02 1416 25.20 24.91 2-1 6 8.26 9.89 18.16 2-2 5 7.45 8.93 16.39 2-3 6 7.97 7.89 8.02 8.98 15.99 16.84 5-1 7 11.14 12.33 23.48 5-2 8 10.67 13.05 23.72 5-3 7 10.55 10.79 9.76 L372 20.31 22.50 6-1 6 7.96 8.73 16.69 6-2 6 8.26 9.76 18.02 6-3 6 6.87 7.69 6.04 8.18 12.91 15.87 TABLE 49—D1ABLo CLAY ADOBE, First Crop OaTs AND BuR CLOVER Planted, November 6, 1915. Harvested, May 8, 1916 Straw Grain Total dry matter No. ye Average Average Pot plants Weight -weight Weight weight Weight weight Notes 1-1 Clover 3 10.37 11.93 22.30 Oats 6 2.38 0.14 2.52 1-2 Clover 6 8.19 9.28 17.47 Oats 6 3.48 0.70 4.16 1-3 Clover6 13.53 9.81 23.34 Oats 6 2.65 13.53 0.27 10.71 2.92 24.24 2-1 Clover 6 2.13 2.57 4.70 Oats 6 5.77 1.81 7.08 2-2 Clover 6 4.24 4.62 8.87 Oats 6 4.56 1.26 5.82 2-3 Clover 6 3.43 4.51 7.94 Oats 6 3.20 7.75 0.46 5.08 3.66 12.85 5-1 Clover6 10.88 9.78 20.66 Oats 6 2.45 0.27 2.71 5-2 Clover5 10.52 9.32 19.84 Oats 6 2.19 0.51 2.79 5-3 Clover 5 8.31 8.36 16.66 Oats 6 3.45 12.60 0.66 9.63 4.10 22.26 6-1 Clover 6 8.90 9.56 18.46 Oats 6 3.10 0.35 3.45 6-2 Clover 6 9.01 5.82 14.83 Oats 6 2.09 0.52 2.61 6-3 Clover 6 6.51 10.45 16.97 Oats 5 2.33 10.65 0.47 9.06 2.80 19.71 1919] Pendleton: A Study of Soil Types 437 TABLE 50—DraBLo CLAY ADOBE, FIRST. Crop Phaseolus vulgaris Planted, April 4, 1916. Harvested, October 7, 1916 Straw Grain Total dry matter i Tl aie Tt No. Average Average Average Pot plants Weight weight Weight weight Weight weight Notes 1-1 8 2.05 0.58 2.63 Growth poor and 1-2 1 0.94 0.87 1.81 slow through- 1-3 12 2.86 1.95 1.37 0.94 4,23 2.89 out 2-1 3 0.53 0.21 0.74 2-2 10 ie ey 8) Sepak 0.83 2-3 17 1.26 0.87 Ott 0.10 Lol 0.98 5-1 3 0.53 0.40 0.93 5-2 2 0.46 0.41 0.87 5-3 eevy UN PEs a=)”, aed eed Ve te ce 0.60 6-1 2 eee 4 a oe areds 0.22 ORL apes a ee a ey OP eae 6-3 i 0.23 eB 3, i Abzcas) whe es 0.23 0.15 Diablo clay adobe. Second crop.—The erops used in this plant- ing were milo (two series, one following oats and bur clover, and the other following oats alone), cowpeas, millet, and soy beans. The crop was thinned as follows: milo to eight plants, millet to twelve, soy beans to six, and cowpeas to six. The total dry weight (tables 51-55) of the largest leguminous crop in this planting is about one- third of that of the bur clover in the first planting; though the grains are proportionately not nearly so much less than in the first crop. Soil no. 2 has the least pronounced adobe structure, but was the most easily puddled. The plants in one of the pots of soy beans of soil no. 2 were entirely killed by too much water. Comparing the relative growth on the soils, the notes made while the crops were growing coincide very closely with the dry weights. As to the relative crop production (fig. 28), it can be said that soils nos. 1 and 5 produced larger crops than soils nos. 2 and 6. Thus the second crop results substantiate those of the first crop. 438 University of California Publications in Agricultural Sciences [ Vol, 3 10 ¥ Soy Beans Es Milo B GS) pa Cow Peas Milo A Soils Fig. 28. Graph showing the total dry matter produced by milo (two series), millet, soy beans, and cowpeas on the four samples of Diablo clay adobe. Second crop. Te) _ Wheat € FS + Bur Clover oF arley 85 ee Pal Se O Phaseolas Ka ram Soils Fig. 29. Graph showing the total dry matter produced by wheat, barley, oats, bur clover, Phaseolus, and oats and bur clover on the three samples of Altamont clay loam. First crop. Fig. 30. Graph showing the total dry matter produced by milo (two series), cowpeas (two series), and soy beans (two series) on the three samples of Altamont clay loam. Second crop. 1919 | Pendleton: A Study of Soil Types 439 TABLE 51—D1ABLO CLAY ADOBE, SECOND Crop Mito A (following oats) Planted, June 8, 1916. Harvested, November 16, 1916 Straw Grain Total dry matter No. ae Average Average Average Pot plants Weight weight Weight weight Weight weight Notes 1-1 8 8 Te a ee 4.87 Excluded from 1-2 8 SASS hy. Sere evaae 10,00 average 1-3 7 4.50 mioec 1.) ath © Rae 4.50 4.68 2-1 8 Bo Se ee he ee oe 2.59 2-2 8 Dietee eye i) acces 3.73 2-3 8 2.92 os le ee aa ae oe 2.92 3.08 5-1 8 7 A a one hit acne 4.03 5-2 6 Bane A 8 eee: 5.13 5-3 7 Oe ee Hy dates 8.44 6-1 9 Ee a) es oe 3.49 6-2 8 Bie Oe iy hee 3.08 6-3 8 2.98 Sets a lck ¢ ees 2.98 3.18 TABLE 52—D1ABLO CLAY ADOBE, SECOND CROP Mito B (following oats and bur clover) Planted, June 3, 1916. Harvested, November 16, 1916 Straw Grain Total dry matter No. Average Average Average Pot plants Weight weight Weight weight Weight weight Notes 1-1 8 SAA ee Sas 6.41 1-2 8 EA eee 8.78 1-3 8 6.21 Gis” SO Been ae eee 6.21 7.14 2-1 8 ery Mee | Ee Ae 3.92 2-2 8 oi gi i AAT Baeeaee 4.52 2-3 8 3.63 SE 2.32 4-8 16 2.08 aR eee i eae. 2.08 1.87 7-1 8 rl Ss aga amore 0.59 7-2 12 O007. = foe 1.29 7-3 16 1.29 Es Hi. ace aw ees 1.29 0.95 TABLE 62—ALTAMONT CLAY LOAM, SECOND CROP Mito B Planted, August 10, 1916. Harvested, November 15, 1916 Straw Grain Total dry matter ee No. Average Average Average Pot plants Weight weight Weight weight Weight weight Notes 3-1 8 ee re i an 0.82 3-2 12 3 1 bs Tes 13 3-3 16 1.15 2 |< a ise ee ea 1.15 1.03 4-1 8 jist ge) 0S Si ee 1.28 4-2 12 eee gS So a 1.82 4-3 16 1.45 13S Ar SO Nem i dae 1.45 1.52 7-1 8 Jd 1 SS i aera 0.66 7-2 12 1 oS ih orca 0.96 7-3 16 0.92 ee)? 624.) Ree 0.92 0.85 1919 | Pendleton: A Study of Soil Types Taste 63—ALTaAMoNnT CLay LOAM, SECOND Crop Cowrras A (following barley) Planted, August 10, 1916. Harvested, November 17, 1916 Straw Grain Total dry matter — No. Average Average Average Pot plants Weight weight Weight weight Weight weight Notes 3-1 6 nee ae 3.48 3-2 6 Gb Be 8 i ). Seisacten 4.50 3-3 6 3.00 a0) © C. Yascpae ae ae 3.00 3.66 4-1 6 i Oy OR i eee 2.44 4-2 6 Beer. Lk ee 2.59 4-3 6 3.40 Ba. acant, Lh. beeen 3.40 2.81 7-1 6 Bal hi secs 2.64 7-2 6 Lis? Ue Sela)» ees 1.93 7-3 6 2.15 rf ee aie a ae 2.15 2.24 TABLE 64—ALTAMONT CLAY LOAM, SECOND CROP CowPEaSs B (following oats and bur clover) Planted, August 10, 1916. Harvested, November 14, 1916 Straw Grain Total dry matter No. Average Average Average Pot plants Weight weight Weight weight Weight weight Notes 3-1 6 ar Ly ee a 4.16 3-2 6 Seacaen o.:t eet iy ule 3.63 3-2 6 rat Bf Dida) _- cae 6 ees 2.77 3.52 4-1 6 3 Bsn SS ee eee 3.35 4-2 6 Bethe i. ee OP ede akces 2.70 4-3 6 1.94 OO. ihe ie ae 1.94 2.66 7-1 6 gee eye oO Ot oe 1.51 7-2 6 Et Whe jy Si) Sees 2.10 7-3 6 2.85 Be dieds GOR) gcthcccte BAe 2.85 2.15 TABLE 65—ALTAMONT CLAY LOAM, SECOND Crop Soy Beans A (following oats) Planted, August 10, 1916. Harvested, November 17, 1916 Straw Grain Total dry matter No. Average Average Average Pot plants Weight weight Weight weight Weight weight Notes 3-1 6 Se 555 RON al Re ee Se ere 4.85 3-2 6 Baie iabeh Ul ixdéee 4.25 3-3 6 4.50 BGA AG coe |. Stak 4.50 4.53 4-1 6 Garo. 8) FIL We ohee 3.53 4-2 6 Bide wh hin abs ot) ° kee 3.59 4-3 6 4.88 ns eee 4.88 4.00 © 7-1 6 li ae eee 3.42 7-2 6 i: SR ie ee 3.34 7-3 6 3.42 Bid fo ease ceskce 3.42 3.39 445 446 University of California Publications in Agricultural Sciences [Vol.3 TABLE 66—ALTAMONT CLAY LOAM, SECOND Crop Soy Beans (following Phaseolus) Planted, August 10, 1916. Harvested November 17, 1916 Straw Grain Total dry matter een een eX _ mm see ss No. Average Average Average Pot plants Weight weight Weight weight Weight weight Notes 3-1 6 Seale |e fk 5,64 3-2 6 4 | Oe) ee Ae caeeanes 4.94 3-3 6 4.84 ae SW eee 4.84 5.14 4-1 6 co. i a ae 4.74 4-2 6 ae ered exe 4.64 4-3 6 4.71 At | | jhe tO Cam yae Tee 4.71 4.70 7-1 6 OR ee ig My eek 5.29 7-2 6 at lw Quel fy -veeece, 3.28 7-3 6 4.39 Se + ge ee eee 4.39 4.31 Hanford fine sandy loam. First crop.—trThis soil type, with sam- ples from nine different localities in California, gave a much wider range of conditions and made a much more interesting series. The plants used as indicators in this series were milo (twice), millet, cow- peas (twice), and soy beans. The milo was thinned to eight plants per pot, the millet to twelve plants, and the’ cowpeas and soy beans to six plants. Set A of cowpeas, and set B of milo were unfavorably located, so that the results of these sets should be discounted. It is interesting to note the large differences in the average weights from soil to soil (tables 67-72, and fig. 31), as compared with the photographs, in which little variation appears. See especially the soy bean series. In this series two things are to be noted: 1. Averages on soils nos. 15 and 25 are hardly representative be- cause in both cases excess moisture, from a leaky roof and too heavy watering, depressed growth. The tendency to become compact and to remain wet and cold shown by soil no. 15 aided the milo and depressed - the soy beans. 2. The loose, open texture of soil no. 22 seemingly favored the soy bean growth, though the other plants did not do as well on this soil as on most of the others. 1919] Pendleton: A Study of Soil Types 447 Comparing the more satisfactory grains, milo A and millet, it will be seen that there is somewhat of a parallelism from soil to soil. The legumes do not always respond similarly to the grains, as in the Diablo first crop, yet in the Diablo second crop and the Altamont first and second crops the response of grain and legume seems quite similar. Hence, it is not safe in every case to judge as to the relationships shown by legumes and non-legumes. RS Fid. Of Fig. 31. Graph showing the total dry matter produced by millet, milo (two series), cowpeas (two series), and soy beans on the nine samples of Hanford fine sandy loam, First crop. Considering all the variations, one might say that soil no. 23 was seemingly among the better soils, and soils nos. 16 and 22 among the poorer soils. Yet when discussing whether the soils be the same or similar, according to the criterion of the dry weight, one of the Han- ford groups will be similar according to one crop, and an overlapping group similar according to the second crop. It can be said with rea- sonable certainty that these Hanford soils are not closely similar to one another. 448 University of California Publications in Agricultural Sciences [Vol.3 TABLE 67—HaAnrorD Fine Sanpy Loam, First Crop Planted, June 10, 1916. Harvested, November 18, 1916 Straw No. Average Pot plants Weight weight 14-1 8 15.34 14-2 8 12.50 14-3 8 10.15 12.66 15-1 8 13.14 15-2 8 14.50 15-3 5 15.21 14.28 16-1 8 8.67 16-2 8 5.86 16-3 8 4.76 6.43 19-1 8 7.65 19-2 8 14.11 19-3 8 7.01 20-1 8 14.10 20-2 8 10.15 20-3 8 7.68 10.64 22-1 8 5.34 22-2 8 5.88 22-3 8 5.35 5.52 23-1 8 8.90 23-2 8 10.04 23-3 8 8.67 9.20 24-1 7 10.82 24-2 8 9.92 24-3 8 6.01 8.92 25-1 8 11.26 25-1 8 11.26 25-2 8 5.70 25-3 8 9.33 8.76 Mito A Grain Average Weight weigh t Total dry matter Average Weight weight Notes 15.34 Most plants bore 12.50 no grain; some 10.15 12,66 8fain was im- mature at har- vest. These cases noted, but no grain weighed. 15.21 14.28 Not mature 4.76 6.43 7.68 10.64 Not mature 5.35 5.592 8.90 Not mature 10.04 Not mature 8.67 9.20 9.92 Not mature | 6.01 8.92 Not mature 9.33 8.76 1919] Pendleton: A Study of Soil Types 449 TABLE 68—HANForD FINE SANDY Loam, First Crop Mito B Planted, June 10, 1916. Harvested, November 20, 1916 Straw Grain Total dry matter No. Average Average Average Pot plants Weight weight Weight weight Weight weight Notes 14—. 8 PUM ok iy Si 10.75 14-2 8 RAS he ee ee ccins 10.95 14-3 8 8.84 PEs) h NG oe hee bs deka 8.84 10.18 15-1 5 te eee 5.25 15-2 4 Gyan WAL Sie Wy aeons 4.62 15-3 2 3.92 RA Se a eer 3.92 4.60 16-1 7 Tames). © AE & nacho 7.36 16-2 2 ML i ie Oper 2.18 16-3 4 2.74 Se ere ae ieee ee 2.74 4.09 19-1 3 78 9: ae ae a or 3.73 19-2 8 ene aT wal © 4 ye, 4.79 19-3 8 9.60 ht = oo. Bee we once 9.60 6.04 20-1 8 pee et te be chs 8.14 20-2 8 Ons eee 3.23 20-3 8 3.22 Wired © 2... 7.06 fon 3.22 4.86 22-1 6 a sae 4.74 22-2 5 ie on 8 py See 3.01 22-3 ff 3.19 7 A Wy MN Ne” pees 3.19 3.64 23-1 8 i Ve 5.68 23-2 5 ete soe) Big Sess 7.72 23-3 8 6.93 Cie 9 etl) be Rene 6.93 6.78 24-1 3 = a a eee 3.16 24-2 6 a ey ee eae 5.64 24-3 6 3.26 RCs Bo cczates We tess 3.26 4.02 25-1 - Rk ot or ee 3.07 25-2 3 Gaeees ) e go ue 2.34 25-3 8 4.34 os ee ae Tee 4.34 3.25 450 University of C Planted, June 10, 1916. Straw No. Pot plants Weight 14-1 12 14-2 13 14-3 14 15-1 12 15-2 12 15-3 12 16-1 13 16-2 12 16-3 12 19-1 12 19-2 12 19-3 12 20-1 12 20-2 12 20-3 12 22-1 12 22-2 12 22-3 12 23-1 12 23-2 12 23-3 12 24-1 12 24-2 12 24-3 11 25-1 12 25-2 12 25-3 12 3.75 4,23 3.46 3.63 . 4.63 3.86 1.96 3.10 1.52 1.85 1.71 2.00 6.54 1.70 6.57 2.04 2.32 4.44 6.12 6.13 6.01 4.18 2.80 4.89 2.06 2.01 4.31 Average weight 3.81 4.04 2.19 1.85 6.55 2.93 6.08 3.96 2.79 MILLET October 6, 1916 Grain Weight 2.90 2.95 2.01 1.02 1.31 1.12 0.74 1.81 0.73 0.73 0.76 0.69 2.78 1.01 2.21 0.65 0.68 1.90 1.21 2.14 1.97 1.50 0.91 2.08 0.77 0.51 2.15 Average weight 2.62 1.15 1.09 2.50 1.08 1.50 1.14 alifornia Publications in Agricultural Sciences Total dry matter Weight 6.65 7.18 5.47 4.65 5.93 4.98 2.70 4.91 2.25 2.58 2.48 2.69 9.32 2.71 8.78 2.69 3.00 6.34 7.33 8.27 7.99 5.69 3.70 6.98 2.83 2.52 6.46 Average weight 6.43 5.19 3.29 2.58 9.05 4.01 7.86 5.46 3.94 [ Vol. 3 TABLE 69—HANFORD FINE SANDY LoaM, First Crop Harvested: Nos. 15-25, September 20, 1916; No. 14, Notes Seed immature Poor. Lack of drainage? Possible error in grain weight. Original shows 6 grams ae 1919 | Pendleton: A Study of Soil Types 451 TABLE 70—HANFoRD FINE SANDY Loam, First Crop Soy BEANS Planted, June 10, 1916. Harvested, December 11, 1916 Straw Beans Total dry matter No. Average Average Average Pot plants Weight weight Weight weight Weight weight Notes 14-1 6 RO ates 16.69 Immature seed 14-2 6 SMM hy) Pda, Vainde 16,28 Immature seed 14-3 6 11.89 14.95 0.44 0.15 12.338 15.10 Immature seed 15-1 6 14.08 0.23 14.31 Immature seed 15-2 6 a I eh nl So re 5.17 Immature seed 15-3 6 6.53 | ee 0.08 6.53 8.67 Immature seed 16-1 6 12.63 0.32 12.95 Immature seed 16-2 6 Te eg tS = ees 14.60 Immature seed 16-3 6 POO aOR adele 0.11 16.60 14.72 Immature seed 19-1 6 Pe as ah a ce 1. eee 12.84 Immature seed 19-2 6 ee rite UC at Re 11.68 Immature seed 19-3 6 pee: ve bebuehin | Pe ie 4 Ake 16.03 13.52 Immature seed 20-1 6 eT tl ih eee 8.77 Immature seed 20-2 6 Pact eel Ba. 16.33 Immature seed , 20-3 6 Sh gay Rt ie a PR ce 14.27 13.13 Immature seed 22-1 6 ee Wii paar eee. 20.28 Immature seed 22-2 6 Ay ayn |e > hl aaan 19.44 Immature seed 22-3 6 rie: Maga © © Salar ng ra bai 15.60 18.44 Immature seed 23-1 6 Pier ee Wee 21.42 No seed 23-2 6 Re Pe) i Ba ae 20.75 No seed 23-3 6 Pees. C2OGo). . Bw () Se 20.68 20.95 Immature seed 24-1 6 iwc ul, 0. . foes 17.37 Immature seed 24-9 6 jh Ar 21.24 Immature seed 24-3 6 is: Pet hi 2c eT eg meee 13.70 17.43 Immature seed 25-1 6 atte Th ee 5.53 Rained on; exclud- ed from average 25-2 6 ‘b's! i a aes 17.85 No seed 25-3 6 21.58 Te. 0 She Ss 21.58 19.71 Immature seed LS : University of California Publications in Agricultural Sciences [Vol.3 TaBLe 71—HaAnrorD Fine Sanpy Loam, First Crop CowPEas A Planted, June 10, 1916. Harvested, October 21, 1916 Straw Beans Total dry matter No. Average Average Average plants Weight weight Weight weight Weight weight Notes 6 2.99 0.93 3.92 6 on * =.) Cee 3.52 6 4.18 WO” te lee 4.18 3.87 1 ee ee 8 2.98 Immature seed 3 3.05 1.50 4.58 2.60 2.88 2.16 1.22 4.76 4.10 6 1.49 0.27 1.77 6 1.54 0.28 1.82 2 1.10 1.38 0.47 0.34 1.57 1.72 6 2.86 0.32 3.18 6 2.08 0.58 2.66 6 2.99 2.64 0.33 0.41 3.32 3.05 5 1.80 0.23 2.02 2 1.96 1.88 0.39 0.31 2.35 2.19 1 1.80 0.76 2.57 pier 1.80 ee 0.76 ees 2.57 2 1.06 0.25 1.30 1 1.80 1.29 3.09 2 1.75 1.54 0.45 0.66 2.20 2.20 3 2.74 2.03 4.78 1 1.88 2.28 4.17 2 2.12 2.25 1.24 1.85 3.36 4.10 1919] Pendleton: A Study of Soil Types 453 TABLE 72—HANFoRD FINE SANDY LOAM, First Crop COWPEAS B Planted, June 10, 1916. Harvested, November 21, 1916 Straw Beans Total dry matter Pe Peay. th aN No. Average Average Average Pot plants Weight weight Weight weight Weight weight Notes 14-1 6 Siero 8) Oh 3.94 14—2 6 ier a’ a Pt iaeees 5.92 14-3 6 3.32 BOO 2 cccee ie eed 3.32 4.39 15-1 6 Fie he oe Ae 7.24 15-2 6 Romo wr wy Mas, Bau 5.34 15-3 6 4.61 ay” Sg ener ny pee 4.61 5.74 16-1 6 et he Ch he ee 5.90 16-2 6 Bites bt, 2 Oo po haenk 5.82 16-3 6 3.65 5.12 Nar OY ane ORR 3.65 5.12 19-1 6 et SE ae eae 3.34 19-2 6 ae pes 3% aioae 3.38 19-3 6 3.87 ee, int be me occa 3.87 3.53 1 died early 20-1 6 cl, See a eee 3.09 20-2 6 Sete ey ee 3.15 1 died early 20-3 6 2.80 Sa” Wi Sc we LS 2.80 3.01 22-1 6 CAN a ee Wie 3.12 22-2 6 i cr CC ie ee oer 3.61 22-3 6 4.92 pol: Den ETS gh me ates 4.92 3.88 23-1 6 Ree . Nahi ee 4.59 23-2 6 8: is ie © tk 6.04 23-3 6 4.08 | 6 Sk ee eI 4.08 4.90 24-1 6 ite nhl beh | Cece 3.81 24-2 5 ye ip eT ee So 4,28 24-3 6 6.42 S.G8 0 5 a eee 6.42 4.84 25-1 5 ee ee i nk kee 4.17 25-2 6 eee hata ty OC ae 3.93 1 died early 25-3 6 4.86 ee eee 4.86 4.32 Hanford fine sandy loam. Second crop.—Barley (twice), oats, wheat, bur clover (Medicago sp.), and Melilotus indica were the indi- eator crops used when the Hanford soils were planted the second time. In all cases a sufficient quantity of seed was used to insure the growth of more plants than would be raised to maturity. Later the plants in each pot were thinned to six in number, good specimens and well 454 University of California Publications in Agricultural Sciences [ Vol. 3 spaced. The final number of plants varied, but was almost always six. An attempt was made to reduce at least partially the shading and exposure effects. ‘The pots were periodically changed from position to position on the bench. The total dry weights produced on the several soils are interesting (tables 73-78, and fig. 33). The grains gave more uniform results in this crop than in the first. Soils nos. 14 and 23 show the best crops, and they are the ones that have the highest amounts of total nitrogen. The legumes selected must have been particularly well adapted to the erowing conditions and the soils, because the growth was enormous. In the amount of dry matter produced the parallelism between the two legumes from soil to soil is close. It is noteworthy that soil no. 14, 15 Wheat 2 ES Bur Clover Oats fe) Melilotus lO. Ti 2p 15. If © 16 > Bf Pe e6 oe Soils Fig. 52 Fig. 32. Graph showing the total dry matter produced by barley, wheat, oats, rye, bur clover, and Melilotus indica on the eight samples of San Joaquin sandy loam. First and only crop. which showed the highest total nitrogen and produced the most dry matter from the grains, gave the poorest crop of legumes. The notes taken during the growing period show that the relative appearances quite early and throughout the period of growth are usually a good index to the relative amounts of dry matter produced. This is so, even though the photographs of the mature plants do not show dif- ferences nearly as great in magnitude as do the dry weights. This type does not show any marked tendency for the several soils te approach a more uniform crop producing capacity through being kept under the same conditions. In fact, the second crop shows ereater variations than the first. And this type does not show that these nine soils, mapped under a single type name, are closely similar to one another in crop producing power. 1919] Pendleton: A Study of Soil Types 455 TABLE 73—HANForD Fine SAnpy Loam, Second Crop Wueat (following millet) Planted, October 30, 1916. Harvested, June 21, Straw Grain Total dry matter Average Average Average No. plants Weight weight Weight weight Weight weight ao ao a 10.75 3.55 14.30 5.20 2.10 7.30 14.85 10.26 6.45 4.03 21.30 14.30 3.55 1.30 4.65 4.85 1.50 6.35 2.80 3.66 1.10 1.30 3.90 4.96 3.20 0.95 4.15 8.20 3.70 11.90 2.80 3.00 0.70 0.82 3.50 3.82 2.80 0.75 3.99 2.80 0.65 3.45 2.20 2.60 0.60 0.66 2.80 3.26 5.45 2.80 8.25 4.05 1.55 5.60 21.35 4.75- ~12.90 2.17 34.25 6.90 4.15 0.90 5.05 3.95 0.40 4.35 4.45 4.18 0.90 0.73 5.35 4,92 4.90 1.60 6.50 4.75 1.60 6.35 3.75 4.46 1.10 1.43 4.85 5.90 18.60 8.30 26.90 3.20 0.90 4.10 23.75 3.20 5.40 0.90 29.15 4.10 2.25 2.37 0.80 0.57 3.05 2.95 1917 Notes Rained on, exclud- ed from average Rained on, exclud- ed from average Rained on, exelud- ed from average Rained on, execlud- ed from average Rained on, exelud- ed from average 456 University of California Publications in Agricultural Sciences [Vol,3 No. plants 6 6 6 6 6 ann ano a aa oD TaBLE 74—HaANForRD FINE Sanpy Loam, Seconp Crop Oats (following milo A) Planted, November 22, 1916. Straw Weight 3.80 3.40 3.20 2.45 1.75 2.00 11.15 2.15 1.15 1.75 4.55 1.35 10.45 1.55 1.65 1.65 2.10 2.50 2.70 1.90 3.20 4.80 16.75 3.39 1.95 2.25 1.80 Average weight 3.47 2.06 2.15 2.55 1.60 2.08 2.60 4.07 2.00 Grain Weight 2.90 1.85 2.40 1.35 1.25 1.50 8.40 2.30 Average weight 2.38 1.36 2.30 1.02 1.25 1 ey 9) 2.73 1.30 Weight 6.70 5.25 5.65 3.80 3.00 3.50 19.55 4.45 1.85 3.00 7.50 2.30 16.75 2.60 2.65 2.75 3:25 4.00 425 3.50 5.20 7.90 26.55 5.70 3.25 3.65 3.00 Average weight 5.86 3.43 4.45 4.27 2.62 4.32 6.80 3.30 Harvested, June 18, 1917 Total dry matter Notes Rained on, exelud- ed from average Pot saturated with soluble salts, ex- eluded from av- erage Rained on, exclud- ed from average Rained on, exelud- ed from average ~ 1919] Pendleton: A Study of Soil Types 45 TaBLeE 75—HANForD Fine SANDY LOAM, SECOND Crop BarLEY A (following cowpeas A) Planted, October 30, 1916. Harvested, May 20, 1917 Straw Grain Total dry matter _ No. Average Average Average Pot plants Weight weight Weight weight Weight weight Notes 14-1 6 4.75 4.30 9.05 14-2 6 9.22 9.00 18.22 14-3 6 11.97 8.65 10.85 8.05 22.82 16.69 15-1 6 15.47 15.30 30.77 Rained on, exelud- ed from average 15-2 6 3.78 3.29 1.07 15-3 6 5.00 4.39 4.12 3.70 9.12 8.09 16-1 6 7.28 6.42 13.70 16-2 2.55 2.55 5.10 16-3 6 2.20 4.01 At 3.96 3.91 7.57 19-3 6 2.89 2.70 2.25 1.98 5.14 4.68 20-1 6 3.57 2.90 6.47 20-2 6 3.32 2.80 6.12 20-3 6 19.35 3.44 7.45 2.85 26.70 6.29 Rained on, exclad- ed from average 22-1 2.73 2.07 4.80 22-2 5.89 3.53 9.42 22-3 6 3.69 4.10 2.73 2.78 6.42 6.88 23-3 6 7.98 6.24 4.20 3.93 12.18 10.41 e§ Cw bo a bo yh “1 © wo On Ko) ~ Or is) aa for) fan) 3.90 3.57 3.05 8.30 6.95 25-1 6 2.47 1.75 4.22 Rained on, exelud- ed from average 25-2 6 eee ee ee ne OSs Pot broken, ex- cluded from av- erage 25-3 6 3.01 2.74 2.18 1.96 5.19 4.70 458 University of California Publications in Agricultural Sciences. [Vol.3 TaBLE 76—HANFORD Fine Sanpy Loam, SeconpD Crop Baruey B (following soy beans) Planted, January 31, 1917. Harvested, June 21, 1917 Straw Grain Total dry matter No. Average Average Average ; Pot plants Weight weight Weight weight Weight weight Notes 14-1 6 9.55 6.80 16.35 14-2 6 6.05 5.40 11.45 14-3 6 3.80 6.47 2.10 4.76 5.90 11.23 15-1 6 3.50 2.80 6.30 15-2 6 3.20 1.70 4.90 15-3 6 405 358 260 236 665 5.95 16-1 3.10 1.45 4.55 16-2 9.20 8.20 17.40 Rained on, exclud- ed from average 16-3 6 7.35 3.10 4.50 1.45 11.85 4.55 Rained on, exclud- ed from average 19-1 6 3.05 0.80 3.85 19-2 6 2.65 2.20 4.85 19-3 6 2.15 2.62 1.85 1.61 4.00 4.23 20-1 6 3.35 2.60 5.95 20-2 6 4.20 3.20 7.40 20-3 6 2.55 3.36 2.15 2.65 4.70 6.02 22-1 6 2.05 1.75 3.80 22-2 6 2.90 2.35 5.25 22-3 6 3.15 2.70 2.25 2.12 5.40 4.82 23-1 6 3.10 2.05 5.15 23-2 6 3.10 2.95 6.05 23-3 6 3.40 3.20 2.75 2.58 6.15 5.78 24-1 6 3.10 1.45 3.70 24-2 6 10.10 5.80 15.90 Rained on, exclud- ed from average 24-3 6 3.05 2.65 2.35 1.90 5.40 4.55 25-1 6 3.35 2.90 6.25 25-2 6 3.10 1.85 4.95. 25-3 6 4.70 3.72 4.60 3.12 9.30 6.83 —— 1919] Pot 14-1 14-3 14-3 15-1 15-2 15-3 16-1 16-2 16-3 19-1 19-2 19-3 20-1 20-2 20-3 22-1 22-2 22-3 23-1 23-2 23-3 24-1 24-9 24-3 25-1 25-2 25-3 6 Pendleton: A Study of Soil Types TABLE 77—HANFoRD Fine SAnpy LOAM, SECOND Crop Melilotus indica (following cowpeas B) Planted, November 22, 1916. Harvested, June 21, 1917 Straw Unhulled seed ‘Total dry matter siaais Weight eh Fn Weight Sack Weight pra 17.00 15.80 32.80 13.25 16.45 29.70 6 6 4.40 15,12 3.10 1618 7.50 31.25 35.00 34.75 69.75 24.85 27.28 52.05 28.95 ' 29.60 32.70 /31.58 61.65 61.15 23.50 24.90 48.40 30.80 25.50 56.30 23.65 25.98 25.70 25.37 49.35 51.35 20.50 18.35 38.85 26.90 23.20 50.10 26.20 24.53 27.40 22.98 53.60 47.52 20.55 17.80 38.35 20.75 21.20 41.95 28.85 23.38 26.05 21.68 54.90 45.07 28.00 28.10 56.10 32.30 34.20 66.50 28.25 29.52 31.85 31.38 60.10 60.90 38.05 34.25 72.30 34.40 36.55 70.95 32.25 34.90 32.35 34.38 64.60 69.28 37.35 31.40 68.75 25.90 28.10 54.00 29.05 30.77 30.15 29.88 59.20 60.65 . 25.35 30.45 55.80 33.90 35.90 69.80 32.10 3045 36.65 34.33 68.75 64.78 Notes Excluded from average 459 460 University of California Publications in Agricultural Sciences [Vol,3 TABLE 78—HANFORD FINE Sanpy LoaM, SECOND CROP Bur Ciover (following milo B) Planted, November 22, 1916. Harvested, June 25, 1917 Straw Burs Total dry matter No. Average Average Average Pot plants Weight weight Weight weight Weight weight Notes 14-1 7 6.70 17.55 24.25 14-2 6 7.00 16.85 23.85 14-3 6 6.10 6.60 14.50 16.30 20.60 22.90 15-1 6 13.30 29.10 42.40 15-2 6 14.45 33.10 47.55 15-3 6 17.10 14,95 26.65 29.62 43.75 44.56 16-1 6 8.85 15.40 24.25 16-2 6 12.25 29.60 41.85 16-3 6 10.05 10.38 21.90 22.30 31.95 32.68 19-1 6 9.90 19.90 29.80 19-2 6 7.70 17.80 25.50 19-3 6 8.20 8.60 22.40 20.03 30.60 28.63 20-1 6 7.90 22.50 30.40 20-2 6 9.75 23.30 33.05 20-3 6 8.70 8.78 20.50 22.10 29.20 30.88 22-1 6 15.90 38.00 53.90 22-2 6 13.20 23.40 36.60 22-3 6 14.50 14.53 31.30 30.90 45.80 45.43 23-1 6 14.45 37.40 51.85 23-2 6 13.55 27.30 40.85 23-3 6 12.05 13.35 28.00 30.90 40.05 44.25 24-1 6 10.60 24.30 34.90 24-2 6 12.10 34.10 46.20 24-3 6 10.25 10.98 24.00 27.46 34.25 38.45 25-1 6 17.90 40.00 57.90 25-2 6 14.60 30.80 45.40 25-3 6 13.35 15.28 26.40 32.40 39.75 47.68 San Joaquin sandy loam.—The samples of this type were the last to be weighed into pots and planted, because of the lack of available greenhouse space; therefore the time allowed for the growing of but one crop, instead of two, on each pot of soil. The crops used were wheat, barley, rye, oats, bur clover (Medicago sp.), and Melilotus indica. As was done for the other types, an excess of seed was planted. When the plants were well established, thinning reduced the number to six plants per pot. Since the specific gravity of this soil was high, because of the large amount of quartz and the small amount of organic matter in its com- position, six kilos of soil, instead of five, were weighed out into each pot. The samples of this type have the very annoying peculiarities of becoming very mushy if an excess of water be added, and of setting 1919] Pendleton: A Study of Soil Types 461 with a very hard surface on drying. This makes the soils hard to handle in greenhouse pot culture work. The variation in crop growth from soil to soil, as shown by the total dry matter produced (tables 79-84 and fig. 32), is rather marked. That the several samples do not show equal crop producing powers is very evident, though with regard to the several indicator erops the soils would frequently not maintain the same order. Soil no. 26 gave the poorest yields with all six crops. Except for wheat, the soils nos. 10, 11, and 12 gave low yields with both the grains and the legumes. It is interesting to note that wheat gave relatively high yields with a number of the soils, and wheat has probably been raised on these soils more than any other one crop. This series shows that, as far as the samples represent the type and the crops used represent crops as a whole, the soils mapped under a given type name are not closely similar in crop producing power under greenhouse conditions. TABLE 79—San JOAQUIN SANDY LOAM RYE Planted, November 22, 1916. Harvested, June 21, 1917 Straw Grain Total dry matter No. Average Average Average Pot plants Weight weight Weight weight Weight weight Notes 10-1 6 1.70 0.30 2.00 10-2 6 2.30 0.35 2.65 10-3 6 2.05 2.02 0.65 0.43 2.70 2.45 11-1 6 Ps 0.70 3.85 11-2 6 2.25 0.70 2.95 11-3 4 3.20 2.87 0.70 0.70 3.90 3.57 12-1 6 1.65 0.45 2.10 12-2 6 2.45 0.85 3.30 12-3 6 2.40 2.17 0.65 0.65 3.05 2.82 13-1 6 4.20 1.25 5.45 13-2 6 4.30 0.80 5.10 13-3 6 aro 4.08 1.60 1,22 2.00 5.30 17-1 6 7.09 1.60 9.15 Rained on 17-2 6 1.95 0.55 2.50 17-3 6 1.80 1.87 0.45 0.50 2.25 2.00 18-1 6 2.35 0.85 3.20 18-2 6 0.90 0.30 1.20 18-3 6 3.70 2.32 1.20 0.78 4.90 3.10 21-1 6 2.20 0.80 3.00 21-2 6 2.70 0.95 3.65 21-3 6 6.55 2.45 2.35 0.87 8.90 3.33 Rained on 26-1 6 1.50 0.60 2.10 26-2 6 2.55 0.75 3.30 26-3 6 2.50 2.18 0.70 0.68 3.20 2.87 462 University of California Publications in Agricultural Sciences [ Vol. 3 Gr Melilotus 14 15 16 19 20 22 23 24 25 Soils Fig. 33. Graph showing the total dry matter produced by wheat, oats, barley (two series), bur clover, and Melilotus indica on the nine samples of Hanford fine sandy loam. Second crop. 1919] Planted, October 30, 1916. Pendleton: A Study of Soil Types TABLE 80—SAN JOAQUIN SANDY LOAM Straw Average No. plants Weight weight 6 6 6 2.93 1.87 1.47 1.91 2.02 2.97 10.27 3.60 3.49 2.14 3.19 3.28 3.89 3.74 2.44 4.65 3.74 5.61 2.05 2.10 3.81 1.12 1.08 1.20 2.09 2.30 3.04 2.87 3.35 4.66 2.65 1.13 BARLEY Grain Weight 0.92 0.81 0.85 0.66 1.28 0.90 4.95 1.32 0.43 1.46 1.78 Le 2.17 1.80 0.80 1.93 1.94 2.34 1.53 1.80 2.33 0.63 0.41 0.70 Average weight 0.86 0.95 0.87 1.67 1.59 1.88 0.58 Total dry matter Weight 3.85 2.68 2.32 2.57 3.30 3.87 15.22 4.92 3.92 3.60 4.97 5.05 6.06 5.54 3.24 6.58 5.68 7.95 3.98 3.90 6.14 1.75 1.49 1.90 2.95 3.25 4.42 4.53 4.95 6.74 463 Harvested, June 17, 1917 Average weight Notes Rained on; exelud- ed from average 464 University of California Publications in Agricultural Sciences [Vol.3 TABLE 81—San Joaquin Sandy LOAM WHEAT Planted, October 30, 1916. Harvested, June 21, 1917 Straw Grain Total dry matter No. Average Average Average Pot plants Weight weight Weight weight Weight weight Notes 10-1 6 3.59 0.85 4.80 10-2 6 3.45 0.45 3.90 10-3 6 6.35 4.58 0.75 0.68 7.10 5.26 11-1 6 5.60 1.15 6.75 11-2 6 2.75 0.60 3.35 11-3 6 3.45 3.93 0.70 0.81 4.15 4.75 12-1 6 6.85 2.00 8.85 12-2 6 7.50 1.35 : 8.85 12-3 6 4.45 6.27 1.35 1.56 5.80 7.83 13-1 6 3.90 0.85 4.75 13-2 6 3.25 0.45 3.70 13-2 6 3.95 3.70 0.75 0.68 4.70 4.38 17-1 6 2.70 0.25 2.95 17-2 6 1.20 0.45 1.65 17-3 6 2.75 2.21 none 0.23 2.75 2.45 18-1 6 5.90 1.50 7.40 18-2 6 7.90 2.40 10.30 Rained on 18-3 6 5.00 5.45 1.00 1.25 6.00 6.70 21-1 6 3.10 1.05 4.15 21-2 5 4.30 0.75 5.05 21-3 6 8.40 3.70 2.45 0.90 10.85 4.60 Rained on 26-1 6 2.35 0.55 2.90 26-2 6 0.40 none 0.40 Rained on 26-3 6 2.60 2.47 0.35 0.45 2.95 2.92 1919] Pendleton: A Study of Soil Types 465 TABLE 82—SAn JOAQUIN SANDY LOAM OATS Planted, November 22, 1916. Harvested, June 17, 1917 Straw Grain Total dry matter No. Average Average Average Pot plants Weight weight Weight weight Weight weight Notes 10-1 6 2.25 0.90 3.15 10-2 6 3.65 1.90 5.55 10-3 6 1.70 2.53 0.50 1.10 2.20 3.63 11-1 2.25 1.25 3.50 11-2 6 1.75 0.95 2.70 11-3 6 2.10 2.03 1.00 OY. 3.10 3.10 12-1 6 1.70 0.90 2.60 12-2 6 2.40 1.00 38.40 12-3 6 2.35 2.15 1.05 0.98 3.40 3.13 13-1 6 2.25 1.20 3.45 13-2 6 2.40 1.10 3.50 13-3 6 2.70 2.45 1.70 1.33 4.40 3.78 17-1 6 0.80 0.55 1.35 17-2 6 1.50 0.90 2.40 17-3 6 1.25 1.90 0.70 0.72 1.95 1.90 18-1 6 1.70 1.00 2.70 18-2 6 1.15 0.60 1.75 18-3 6 1.10 1.32 0.50 0.70 1.60 2.02 21-1 6 1.85 0.95 2.80 21-2 6 2.35 1.05 3.40 21-3 6 1.00 ite 0.55 0.85 1.55 2.58 26-1 6 1.55 0.60 2.15 26-2 6 1.35 0.80 2.15 26-3 6 1.65 1.52 0.70 0.70 2.35 2.22 466 University of California Publications in Agricultural Sciences [Vol.3 TaBLeE 883—San Joaquin Sanp¥ Loam Bur CLOVER Planted, November 22, 1916, Harvested, June 17, 1917 Straw Seed in burs Total dry matter ome, weight ATSROS? weight “Weight Welght weight’ Notes 6 0.50 0.95 1.45 6 1.50 1.65 3.15 6 0.50 0.83 1.75 1.45 2.25 2.28 6 0.90 2.00 2.90 6 0.25 1.00 1.25 6 0.30 0.48 1.10 1.37 1.40 1.85 6 0.90 3.00 3.90 2.15 5.30 7.45 1.50 1.52 1.90 3.40 3.40 4,92 6 1.55 3.45 5.00 0.75 2.80 3.55 4.35 1.15 5.70 3.12 9.05 4.27 Excluded from av- erage 6 0.70 2.05 2.75 6 2.35 3.85 6.20 Excluded from av- erage 6 0.90 0.80 1.70 1.87 2.60 2.67 6 1.20 3.40 4.60 6 3.25 6.65 9.90 Excluded from av- erage 6 1.80 1.50 4.85 4.12 6.65 5.62 6 3.35 3.70 7.05 6 2.00 3.90 — 5.90. 6 1.75 2.37 5.15 4.25 6.90 6.62 6 0.60 1.45 2.05 6 1.20 2.75 3.95 0.40 0.73 1.30 1.83 1.70 2.56 1919 | Pendleton: A Study of Soil Types 467 TABLE 84—SAN JOAQUIN SANDY LOAM Melilotus indica Planted, November 22, 1916. Harvested, June 21, 1917. Straw Unhulled seed Total dry matter No. Average Average Avirics Pot plants Weight weight Weight weight Weight weight Notes 10-1 6 1.20 1.20 2.40 10-2 6 1.03 0.92 1.95 10-3 6 1.30 1.18 1.65 1.26 2.95 2.44 11-1 6 1.05 0.85 1.90 11-2 6 0.50 0.35 0.85 11-3 6 1.00 0.85 0.80 0.67 1.80 1.52 2-1 6 1.07 2.05 3.12 2—2 6 1.70 2.45 4.15 2-3 6 1.20 1.33 1.40 1.96 2.60 3.29 13-1 6 3.05 3.70 6.75 13-2 6 3.10 3.95 7.05 13-3 6 3.50 3.22 4.45 4.03 7.95 7.25 17-1 6 3.05 4.05 7.10 17-2 6 2.25 3.55 5.80 17-3 6 2.85 2.72 3.20 3.60 6.05 6.32 18-1 6 3.25 3.90 7.15 18-2 6 2.05 2.65 4.70 18-3 6 2.85 2.42 3.95 3.50 6.80 6.22 21-1 6 2.50 3.40 5.90 21-2 6 2.65 3.95 6.60 21-3 6 3.45 2.87 3.30 3.59 6.75 6.42 26-1 6 1.10 0.85 1.95 26-2 6 0.95 0.85 1.80 26-3 6 1.30 1.12 1.05 0.92 2.35 2.04 GENERAL DISCUSSION The limited time available for this study made it impossible to make all the determinations upon each of the several horizons of all the soils collected for this study. It was believed, however, that the additional data were not re- quired, since that already at hand seemed to give ample evidence upon which to base conclusions. Therefore, in many cases determinations were run on the surface horizon only. This makes some of the tables appear incomplete. 468 University of California Publications in Agricultural Sciences [ Vol. 3 On the basis of the preceding results and discussions some general treatment is possible, as well as a more or less critical discussion of the methods of soil surveying pursued by the Bureau of Soils. The types and the localities of collection of the soils studied were as follows: Diablo clay adobe: Thalheim (17) San Juan Capistrano (1) Madera (18) Los Angeles (2) Merced (21) Calabasas (5) Del Mar (26) Danville (6) Hanford fine sandy loam: Altamont clay loam Elk Grove (14) Walnut (3) Acampo (15) San Fernando Valley (4) Woodbridge (16) Mission San José (7) Waterford (19) San Joaquin sandy loam: Snelling (20) North Sacramento (10) Basset (22) Lincoln (11) Anaheim (23) Wheatland (12) Los Angeles (24) Elk Grove (13) Van Nuys (25) Nore.—Figures following localities designate sample numbers. COMPARISONS OF PHYSICAL Data The mechanical analyses of the soils were carried out with both the Hilgard elutriator and the Bureau of Soils centrifuge methods. The tedious nature of the elutriator method has been emphasized else- where. The results by this method show that the soils of each type as a whole are somewhat similar, though no two are identical and some samples of a type are widely divergent from the rest. The Bureau of Soils method appears to give a sharper and more satisfac- tory separation into classes than does the elutriator method. This is to be expected since the separates represent greater ranges of particle sizes. As a check on the texture of the samples collected, it shows that some of the soils are not true to name, therefore that all soils mapped under a given type name are not closely similar to one another. Of course, this is the belief of many soil surveyors, but it seems strange that in the present work, where there was the attempt to select soils representative of the class and type chosen for study, that such diver- gences developed. It is an interesting commentary on the personal equation of the field worker, in this case of the writer, who collected the samples. 1919 | Pendleton: A Study of Soil Types 469 With regard to the methods of mechanical analysis, one should not overlook Mohr’s work on The Mechanical Analysis of Soils of Java,*° which gives an excellent discussion of the relative merits of the better known systems of mechanical analysis. He describes a modified cen- trifuge method preferred by him. l dis- Under a discussion of the physical constants of soils, Free® eusses the value of mechanical analysis as a soil constant, and shows that there are three serious errors in the determination, all of which impress themselves upon one making and using such analyses. They are: ‘‘(1) disunity of expression; (2) failure to express conditions within the limits of individual groups; and (38) failure to take 9) account of variations in the shapes of the particles.’’ Yet he empha- sizes, and rightly so, ‘‘that mechanical analysis is by no means useless nor to be belittled as a means of soil investigation.’’** Moisture equivalents—This determination showed quite distinct averages for the types, though there was considerable variation within each of the types. Eliminating those samples shown to be non-typical according to the mechanical analysis, the variation within the type is reduced considerably. Yet it cannot be said that as regards this con- stant that all soils mapped under a given type name, or even those soils under a given type name which the mechanical analysis has shown to be true to name, have closely similar moisture equivalents. Briggs and McLane** express the belief that ultimately moisture equivalent determinations will replace mechanical analysis in the classification of soils, because the determination is simple and the result can be expressed as a single constant. Hygroscopic coefficient—The two heavy types show averages dis- tinct from those of the two light types, but the wide and erratic varia- tion within the type, together with the nearly universal failure of Briggs and Shantz’s formula** to convert these values into values even approximating those of the moisture equivalent, leads one to doubt the accuracy of these figures of the hygroscopic coefficient. It is because of the ease of determining the moisture equivalent, and because of the difficulties involved in correctly carrying out the hygro- scopic coefficient, that the doubt is cast upon the latter determination. 30 Bull. Dept. of Agr., Indes Neerland, 1910, no. 41, pp. 33. _ 31 Free, E. E., Studies in Soil Physics, Plant World, vol. 14 (1912), nos. 2, oo, 7, 8. 32 Tbid., p. 29. 83 Proc. Amer. Soc. Agron., vol. 2 (1910), pp. 138-47. 84U. S. Bur. Pl. Ind., Bull. 230 (1912), p. 72. 470 University of California Publications in Agricultural Sciences [ Vol. 3 COMPARISON OF CHEMICAL Data The total nitrogen content of the samples of each type varies within somewhat wide limits. The average amounts for the several types are distinct, though the variations are such that some of the quantities of one type overlap those of another type. It is believed that for the types selected the field differentiations do indicate dif- ferences. Regarding the humus content of the four types under considera- tion, the results are somewhat different. The average amounts of humus are almost alike in three of the four types, while the nitrogen- poor San Joaquin soil has an average of about half that of the others. Within the type the soils may be very nearly alike in the humus con- tent, as is the case in two of the types, or may be widely variable, as in the Hanford fine sandy loam. It should be noted that the amount of humus as shown by the method used, is not indicated by the inten- sity of the color either of the soil or of the resulting extract. This confirms the findings of Gortner, which are cited elsewhere. There was quite a wide range shown in the results of the deter- mination of the loss on ignition. The Diablo and Altamont soils, be- cause of the heavier textures and the relatively large amounts of com- bined water, and of considerable amounts of CaCO, in at least one case, gave high losses on ignition. The averages were close, 6.8% for the Diablo, and 6.7% for the Altamont. The Hanford soils were lower, though with a wider range. Soil no. 14, with 6.9% loss on igni- tion, shows almost double that of any other soil in the type. The San Joaquin soils, with an average of 2.6%, show the lowest average loss on ignition. The smaller amounts of organic matter in these soils is one reason for the smaller loss. The two heavier types have averages close together, and the hghter types have averages not far apart, but because of the wide variations within each type, the results of the determination of the loss on ignition certainly do not show that all soils classified in one type are closely similar. Hall and Russell, in their discussion of the soils of southeastern England,*° consider of value the ratio of PBatdoee he ht asl ee “but apply- % loss on ignition, ing this ratio to the California soils under consideration does not seem to give any relations of value. The Diablo ratio varies from 0.0136 to 0.0158, the Altamont from 0.0141 to 0.0204, the San Joaquin from 0.0144 to 0.0232, and the Hanford from 0.011 to 0.0172. 35 Jour. Agr. Sei., vol. 4 (1911), pp. 182-223. 1919 | Pendleton: A Study of Soil Types 471 The calcium (as CaO) content of the soils is interesting especially because of the variability. The Altamont samples show the greatest variation, for the largest quantity of CaO is about seven times the smallest. The San Joaquin samples are second, with the largest over six times the smallest. The Diablo samples are third, with the largest over five times the smallest, while the Hanford soils show the least variation, the largest being less than twice the smallest. There are quite marked differences between the averages of the Diablo, Alta- mont, and Hanford soils (the San Joaquin samples are intermediate), but the wide variations within the types greatly minimize any sig- nificance the averages might have. Hence it is not possible to state that one or another type, as represented by these samples, is charac- terized by high, low, or moderate amounts of calcium. As the analyses of the samples for calcium failed to point out any striking characteristics, unless it be that of variability, so it is with magnesium. Magnesium (as MgQ) is variable within each of the four types. The largest quantity is about three times the smallest in the Diablo, San Joaquin, and Hanford types, while in the Altamont the largest is twenty-seven times the smallest. Considering the Hanford and San Joaquin, or the Diablo and San Joaquin, it is seen that the eurves do not overlap, while the Diablo and Altamont, or the Diablo and Hanford curves do. The averages of the four types are distinct, except between the Hanford and Diablo, which are quite close. But, here again, because of the more or less wide range of values within each of the types, the averages are of little significance. The lime- magnesia ratio is very variable in these soils. Comparing the calcium and magnesium curves for the several soils gives a good idea of the relations. The Diablo curves are quite similar except for soil no. 6, which shows 3% MgO and 0.5% CaO. In the Altamont soils the curves are somewhat similar in direction, though the ratios differ widely. In the Hanford and San Joaquin types the ratios of CaO and MgO are also far from constant, yet it is readily seen from the graphs that the amount of magnesium varies more or less directly with the amount of calcium. Respecting the total phosphorus (as P,O,), if the San Joaquin and Hanford samples alone be considered, there would be no doubt as to the significance of the field separation, the variations within the type notwithstanding. But when the other two types are considered, the case is not so good in favor of the field classification. The Diablo soils show considerable variation in the amount of P,O.,, while the three 472 University of California Publications in Agricultural Sciences [Vol.3 Altamont samples show much variation. Therefore with reference to the amount of phosphorus, and the types studied, the separation into types may or may not be of significance. If the results of the potassium (K,O) determinations are com- pared, it is very evident that but one conclusion can be drawn, and that is that the variations in the amount of potassium within each type are great enough so that any differences between the averages of the several types have no significance whatsoever. Therefore, with regard to total potassium the field separation of soils as represented by these twenty-four samples of four types means nothing. COMPARISON OF BACTERIOLOGICAL DATA The wealth of the data obtained from over nine hundred bacteri- ological tumbler cultures is hardly of sufficient significance to com- pensate for the effort involved. There is one outstanding conclusion from all this work, namely, the lack of any very definite, distinct, and constant bacteriological activity of the samples of one type that is not to a considerable extent shared by the samples of the other types. There are tendencies in certain types with regard to bacteriological activity which show that some of the types as a whole are more or less distinct from one or more of the others. Ammonification.—The amount of ammonia produced from dried blood varies to a great extent. The Altamont samples gave between 10 and 33 mg. nitrogen as ammonia; the Diablo samples gave between 7 and 26 mg., and the Hanford samples gave between 35 and 72 mg. The Altamont and Diablo types are thus seen to be about alike in their low ammonifying power, as compared with the higher ability of the San Joaquin types and still greater ability of the Hanford types. And since there are somewhat greater variations between the types than between the samples of a given type, the ammonifying power may be significant. Nitrogen fixation—The two heavy types, Diablo clay adobe and Altamont clay loam, show no characteristic differences, while the two lighter types show considerable differences. As a whole the types are different one from another, yet the variations within the type are sufficient to prevent any statement that the rate of nitrogen fixation is a function of the type as determined in the field, or vice versa. Nitrification The nitrification data are the most puzzling. The figures are extremely variable within a given type; the erratic way 1919] Pendleton: A Study of Soil Types 473 in which the Hanford samples behave is not paralleled by any other type. There are certain ways in which the types are distinct : The nitrification of the soil’s own nitrogen as compared with the soil’s action upon added nitrogen is in some degree separate for each type. The San Joaquin samples nitrified their own nitrogen to a greater degree than they did the nitrogen added to the soil. The relative nitrification of the several nitrogenous materials (dried blood, cottonseed meal, ammonium sulfate) is in some measure distinct for the several types. The Diablo, Altamont, and San Joaquin types show ammonium sulphate to be nitrified the best, cottonseed meal less, and dried blood still less. The Hanford samples show cottonseed meal to give the highest percentage of nitrates, with dried blood less, and ammonium sulfate still less. When any one soil is compared through the three sets of deter- minations there are no apparent similarities. The Hanford type shows the greatest bacterial activity, while the San Joaquin shows less, with the heavier types showing sometimes greater activity and sometimes less than that of the San Joaquin. WorK IN OTHER STATES In connection with the original chemical work reported in this paper, there should be mentioned the large amount of work done in a number of states on the analysis of the types of soils as mapped by the Bureau of Soils. Apparently, these analyses have been made without any question as to the validity of the existing subdivisions into types. The various analyses have been reported with some com- ment, but that which does appear usually deals with the ‘‘adequacy’’ or “‘inadequacy’’ of the plant food present. Blair and Jennings*® present a large amount of data on chemical composition, some of which on rearrangement show interesting relationships (table 85). From the data the four series of soils with the largest number of analyses were selected (see following table). Under each series there are from 2 to 4 soil types, and from 2 to 6 analyses under each type. The averages from each type are tabulated, also the averages of all the types within the series. This is both for the strong acid extraction and the fusion methods of analysis for significant plant food elements. There are no doubts but that each series of soils shows characteristic chemical peculiarities, peculiarities which are to a great extent con- 86 The Mechanical and Chemical Composition of the Soils of the Sussex Area, New Jersey, Geol. Surv. N. J., Bull. 10, 1910. oe) = ° > — University of California Publications in A gricultural Sciences 474 osuvusy— 6g 696 1aysaonol[f) tet. sot ¢9° gc" Os l 96° #os" ¢LTL C80" £60" els to'P GFO 60° FLT 6et 90°S 60° 6hSG 961 LO CFO" cor cr or “TL Olt OV C96" col 90° LO FL68 e968 G é meor'yt TROT Apues ould —_+, osarusyO PLT Fl a 63U 63'L LOT 987 ert O'S GG 90'S 89's éLL LOG el 6ST 6eL PLT rev ost 19°9 PPL cT9 LOL c0’ FSO ¢10° FO" en alee CFO 90° oct 96L 9st 60. 036'F lov 6L'E GG soe 66S OLS 0G% 90° £0" LO 90° eP Lg oe ¥9° ce" 6 cy 96° IV Iv or 80° ra 0G" ae Ie $0 LO €0° co Irts 60F8 0078 coPs ¥ ¥ & S TOT WIROT wro, weory Apurs kuojg = Apueg Auoyg i 1aqsaono[y cg Wav 160° sol ver og 86° 09° 6LL CLS 9F'S orl crt PGT oll séT crt LIT9 oes 1o9 CEO" CEO" C30" ON tes oe ae LLO’ 90 830s SL 68° LG'S 60° GEG €8°S L9G C10 CFO" 90° ols 19 1g est ¥G €& LSO0° cso" LO OLT ra £03" 60° ¢90° co" 99°98 18°98 £698 € z & meOol (eseyd wlvory Au0}g y4311) wvory I9A0d LST cle" 9T 909°L sol am sro LLB TL 6s L Ele €LT ToT go It 169 LOL €S0° FEO 8¢0° 90° 90° £90’ L&T 98° cer €L'9 OLS 96°F 6FY 16€ CO's C0" C90" $0" oor Ole 89° Tt LOV 80° FL0 LS0° €80° ac ce 83° 90° 690° G0’ Gc6cL, LOO8 3868 ] ¥ 9 wero, (asvyd ulBory areys Aapeys) weory ssoyond o sje}, O1FRLOA 2078, *OS °O'd *O'1V ‘OO t PUTA OoW orp O'UN os ‘oISs erqnyposuy 1919] Pendleton: A Study of Soil Types 47} en | stant throughout the several representatives of the type. In some cases, the differences or similarities are more clearly seen in the total analyses, and in other cases, they appear in the acid analyses and not in the fusion analyses. Within any series the variations between analyses of any one type are about the same as the variations from type to type. There are many other papers*’ which provide material for similar comparisons. A paper by Van Dyne and Ashton** reports chemical analyses for lime, phosphorie acid, potash, and nitrogen on the samples collected in the course of the survey of Stevens County, Washington. Though sometimes there is a much greater range within a type than between types, in a general way the analyses for any one type agree quite well. As a whole the chemical analyses seem to show that the field eriteria are also a basis for grouping soils into certain chemical groups. It should be mentioned that the work of Blair and Jennings, also that of Van Dyne and Ashton, deals with individual areas, and not with samples from several scattered areas. The work of Fraps and Williams, and the original work here reported represent scattered areas. ‘ THE GREENHOUSE CULTURES By far the most interesting results were obtained in the pot culture work. It is realized that there are variations in the physical nature of the samples of a given type, yet since these samples were collected with considerable care by one familiar with field classifications, the samples so selected should be fairly representative of the type. It is probable that if all the soils in each of the types used were exactly the same in texture, ie., if the mechanical analysis showed the same results for the several soils, the crops produced on the several soils of a type would be less divergent in appearance or weight. Yet it is not at all likely that the crops would be the same. Pot cultures pre- sume that the conditions in all the pots can be kept uniform, but this is obviously impossible. Greenhouse work is subject to many interfer- ing factors. Nevertheless, the results are believed to be significant, 37 Williams, and others, Report on the Piedmont Soils, North Carolina Dept. Agr., Bull. 206, 1915. Fraps, G. 8., Composition of the Soils of South Texas, Texas Agr. Exp. Sta., Bull. 161, 1913; Composition of the Soils of the Texas Panhandle, ibid., Bull. 173, 1915. 88 Van Dyne and Ashton, Soil Survey of Stevens County, Washington, Field Operations, U. 8. Bur. Soils, 1913, pp. 2165-2295. 476 University of California Publications in Agricultural Sciences [ Vol. 3 despite the large correction that the consideration of the probable error might introduce. The differences in the crop producing power of the soils are very marked in the Diablo clay adobe, where the second crop, as well as the first, shows evident variations in the ability to support a crop. In the Altamont clay loam the second crop almost loses the variations seen in the first crop from pot to pot. The samples of both types seem to show one thing in common—the approach of the several sam- ples toward a uniform ability to produce crops, as the soils are kept for longer periods under the same conditions. The Hanford soils did not show, with the several crops, the parallelism in the fertility from crop to crop as did the Diablo and Altamont soils. Some soils pro- duced good crops of grain and poorer crops of legumes, others did the opposite. The low nitrogen content in this type seemed to be a limit- ing factor. This would account for the variation between the grain and the leguminous crops. Also, the presence, or absence of Bacillus radicuola inoculation in this connection might greatly affect the total crop produced. There does not seem to be much doubt but that the soils of the several types compared in this way are not the same, though they are in certain respects similar. The Place of Soil Classification—With all these evidences that the soils within the several types are not closely similar, though they are classified the same by the Bureau of Soils, what conclusion is one to reach as to the value of such a classification? If it were true that there were no appeal from the findings of such laboratory and greenhouse determinations as these, and that these determinations were a final proof of the fertility or infertility of a soil, obviously there would be but one thing to do—discard all such field classifications as useless. But the writer is one of a great many soilists who are not willing to rely on laboratory or even greenhouse results for an absolute deter- mination of fertility, and for the grouping together of soils inte a workable classification. Not enough is definitely known as to the mean- ing of such findings, though there are certainly many valuable points shown by laboratory analyses.*® As examples of the value of natural classifications we may con- sider those of botany, zoology, or mineralogy. If available, a wholly satisfactory classification of soils would be equally useful. The appre- 39 Jordan, W. H., Measurements of Soil Fertility, New York Agr. Exp. Sta., Geneva, Bull. 424; 1916. 1919] Pendleton: A Study of Soil Types 477 ciation of this is shown in the many systems of soil classification that have been proposed. Despite the foregoing facts that have been obtained showing the divergent properties of different samples of one type presumably alike, yet it must be admitted that soil surveys, even such as are no more refined than those of the Bureau of Soils, have considerable value for field use. It is felt that the additional effort required to modify the practices of the Bureau of Soils in the mapping and classifying of soils would be more than justified by the increased accuracy and usefulness of the maps. To point out some of the causes of the present practices and to give suggestions for possible methods of improvement, the following discussion of the Bureau of Soils methods has been prepared. Discussion of the Bureau of Soils’ methods—The methods of map- ping and classifying soils, as devised and used by the Bureau, have resulted from some definite and important considerations. 1. The necessity for keeping down the cost of surveying and map- ping prevents the use of laboratory and culture methods in the study of the soils classified, even if it were not for the fact that one of the outstanding policies of the Bureau apparently denies the validity of such studies in the classification of soils. This does not include the mechanical analysis of soils, which is not a separate laboratory deter- mination, but a method of checking the field man’s decision as to the texture. It should also be added that some of the reports as published in the Field Operations of the Bureau of Soils, for 1913, show the subdivision of the soils into two groups based upon the CaCO, content. Keeping down the cost has also prevented the use of sufficient time to map the soils correctly, even according to the criteria admittedly of value in the system adopted. Many of the other methods of classify- ing and mapping soils, even if applicable to most of the agricultural regions of the United States, would be absolutely out of the question on account of cost. 2. The large and widely diversified area of the United States, and the attempt to map representative areas in various parts of the coun- try, early led to difficulties. There seemed to be a lack of understand- ing as to what criteria to use in the classification of the soils. Re- cently, some of the areas first mapped in the state of California have been resurveyed. The texture, series, and province differences of the early mapping seem not to have been clear. For example, we may con- 475 University of California Publications in Agricultural Sciences | Vol. 3 sider the differences between the older and the recent survey of two localities east of Los Angeles. The notes were made by C, J. Zinn, a member of the party which made the recent survey: Locality A—About 15 square miles with Eaton Wash on the west, center of Monrovia on the east, mountains on the north, and a line about 3 miles south of mountains as the south boundary. The old survey4® has four types of three series and two miscellaneous types: San Gabriel gravelly loam, San Gabriel gravelly sand, Placentia sandy loam, San Joaquin black adobe, and Riverwash and Moun- tains. The new survey (1915, unpublished) has 13 types of 6 series and 3 mis- cellaneous types: Hanford stony sand, gravelly sand, loam, sandy loam, fine sandy loam, and sand; Tejunga stony sand; Zelzah loam and stony loam; Pla- centia loam, Holland loam, Chino loam and silt loam. The miscellaneous types are Rough Mountain land, Rough Broken land, and Riverwash. Locality B—In the city of Pasadena, comprising about 3.5 square miles, with the southwest corner at the center of the city. The old survey4! shows San Gabriel loam occuping about 0.6 of the area, San Gabriel gravelly sand about 0.3, and Placentia sandy loam about 0.1... The new survey (1915, unpublished) shows Zelzah gravelly loam occupying about 0.9 of the area, Zelzah loam about 0.1, with a very small body of Holland loam. The older survey showed a recent alluvial soil where the recent one shows an old valley filling soil. Besides these errors (detected as such by the practical man, who might attempt to use the soil maps in the field) there are in addition those of another nature which were the source of much eriticism in the earlier history of the survey the so-called ‘‘ procrustean classification ’’ eriticism of Hilgard.*? Due apparently to an insufficient study of the soils of the United States, there was the attempt to classify in the same series soils of widely differing properties—differences of an important nature being ignored. At the present time there is an increasing tendeney toward limit- ing series groups of soils to a more or less definite climatological region. In this connection see the later changes in the correlation of many soils.** These changes tend to limit the geographic range of the series, and make these series narrower and more exact. Moreover, it is understood that as the knowledge of the soils has increased, the changes in correlation have been proceeding rapidly since the above list was issued. This indicates that as the facts accumulate the ‘‘pro- crustean classification’’ criticism is losing its force. 40 Field Operations of the U. S. Bur. of Soils, 1901, San Gabriel sheet. 41 Ibid. 42 Hilgard, E. W., and Loughridge, R. H., Proce. Second Intern. Agrogeol. Conf., Stockholm, 1910, pp. 228-29; Hilgard, E. W., U. 8S. Office Exp. Sta., Bull. 142 (1904), p. 119; Hilgard, E. W., Proc. First Intern. Agrogeol. Conf., Budapest, 1909, pp. 52-54. 43 U. S. Bur. Soils, Bull. 96, 1913. 1919 } Pendleton: A Study of Soil Types 479 3. There was a lack of trained men early in the work. This was to be expected. As has been shown, the early surveys were very crude in certain places. It must be added that some of the errors and omis- sions made in the more recent maps are not due to a lack of training, but to the carelessness of the field men with respect to details. 4. The policy of the Bureau has been to recognize the physical characteristics of the soil as factors in fertility to the virtual exclusion of the chemical or biological factors. Therefore the use of physical eriteria is necessary. Besides, the criteria must be such as can be applied in the field, and are: (1) color, (2) texture, determined by rubbing between the thumb and finger, (3) structure, (4) nature of subsoil, (5) presence of hardpan, (6) height of water table, (7) pres- ence of alkali, (8) topography, (9) physiographic form and hence mode of formation, and (10) source of material (sedimentary, igne- ous, or metamorphic rocks). Humus, and the presence or absence of appreciable quantities of lime, also the reaction of the soil (acid or alkaline) are frequently guessed at. These criteria are practically the only ones that can be applied in field work. It is believed that these same criteria indicate the chemical nature of the soil, though there has been no attempt to correlate some of the factors. However, the original work reported in this paper would indicate that the chem- ical nature is not the same, of soils classified the same by the Bureau of Soils criteria. 5. The desire to limit the number of groups of soils is a wholly sound one. In discussing the problems of classifying soils there should always be kept in mind the fact that some of the problems are not very different, fundamentally, from some of the problems that have been causing perplexity among biologists for a long while. The tendency, as seen in some of the recent surveys, to make the series more inclusive and to introduce the term, phase, is heartily commended. By making the series broader there will be less difficulty in placing a soil in its proper group. The phase will take care of many of the series differences between area and area. 6. It seems certain that if there were more emphasis placed upon the inspection of the area, during the progress of the field work and after its completion, there would be a much closer approach to accuracy throughout the map and report. At the present time the field man is not closely checked up. The careless or indifferent worker can map more or less as he pleases, especially in the out-of-the-way places. 480 University of California Publications in Agricultural Sciences [VoL 3 7. Whether the soil survey should include more than a simple classification of the soils or not, is an unsettled question. It is thought hardly possible that in a soil survey the field man could handle all the phases of an agricultural survey of an area, when his energies should be fully employed in the classification of the soils. It is believed that the place of the survey, in this country at least, is to handle the classification of the soils, leaving the study of the remaining factors largely to other specialists, who would use the soil survey as a basis.** But to make the soil maps of more general use for such work, they must be more accurate. These maps never can become the basis of other agricultural studies as long as many experiment station workers ridicule them. Hence, the ultimate effort of the survey should be toward better work, rather than covering a wide range of agricultural studies. 8. There is not the incentive to make as many separations of the soils in the field, as the field man might think best, because frequently the feeling of the editors is that there would be too many small bodies of soil shown on the manuscript maps which would not warrant the additional cost of publication. In conelusion, the Bureau of Soils’ system has much to commend it as a field method, and the resulting maps and classification are be- lieved to be of distinct value. It is felt that a more general under- standing of: (1) the limitations under which the maps, the earlier ones especially, have been made; (2) the difficulties under which the field work is at present carried on; (3) the meaning of the correlation of soils; and (4) the general policy of the Bureau of Soils would give people more sympathy with their work. 44 Fippin, E. O., Proce. Amer. Soc. Agron., vol. 1 (1908), pp. 191-97. a 1919] Pendleton: A Study of Soil Types 48] SUMMARY Presumably typical samples of four soil types were collected for laboratory and greenhouse study from widely distributed localities in the state of California. The field appearance of each sample was usually sufficient to warrant the classification as it exists. PHYSICAL RELATIONS 1. The mechanical analysis by the Hilgard etutriator shows that the soils of a given type are in some cases quite divergent from each other in their content of certain of the sizes of particles. The mechan- ical analysis by the Bureau of Soils method shows that 6 of the 24 soils were not true to their type names, and that of those soils within the type there is considerable variation. 2. The moisture equivalents for the several types show distinct enough values to substantiate the field separation. 3. The hygroscopic coefficients vary widely within each type and the types are not shown to be distinctly different by this criterion. CHEMICAL RELATIONS 1. The total nitrogen averages vary markedly from type to type, with the Altamont clay loam containing three times that in the San Joaquin sandy loam. 2. The average humus content of the San Joaquin samples is about half that of the other types. The variations in the humus con- tent between the types are small, considering the diverse nature of the types and the large range in the amount of humus within the type. 3. The loss on ignition shows a considerable variation within the type and no significant distinction between the four types. 4. The average total calcium content of the types is distinct, though the wide range within each type minimizes the significance of the variation in the averages. 5. With regard to magnesium, the types are neither distinct nor are the soils within the type closely similar, 6. The average phosphorus content of the types is. distinct, though the ranges within the several types frequently overlap. 7. The total potassium results do not show the types to be distinct nor the soils within a type closely similar. 482 University of California Publications in Agricultural Sciences [ Vol. 3 BACTERIOLOGICAL RELATIONS 1. The ammonifying power shows rather larger variations from type to type than between the samples of a type. 2. The nitrogen fixation data do not show characteristic differences for the several types. 3. Regarding nitrification as a whole there may be a greater divergence between the samples of a type than between types. The relative nitrification of the soil’s own nitrogen varies with the type, as does the relative nitrification of the several nitrogenous materials added. Por CULTURES IN THE GREENHOUSE In addition to the effect of the probable error, the impossibility under the conditions herein described of growing the same crops on all the soils, during the same season of the year in the greenhouse, prevents close comparisons between the types, or between the first and second crops on a given soil. The comparison of several samples of a given soil type and the comparisons of various soil types, according to the previously outlined greenhouse methods show that: 1. Different representatives of a given type are not the same in their ability to produce crops. 2. The arrangement of the samples of a given type according to their fertility may or may not vary with the special crops used as the indicators. 3. The types are distinct with respect to their fertility, considering their average production. Therefore it is concluded that with regard to the 24 soils of 4 types examined, all soils mapped under a given name by the Bureau of Soils method may or may not be closely similar, depending upon the criteria used. The greater number of the criteria show the soils of a type to be not closely similar, and the types to be but litle differ- entiated from each other. In connection with the results of the author’s study of the soils, there is given an historical sketch of the development of soil classifica- tion and mapping, also a discussion of certain of the methods em- ployed by the Bureau of Soils of the United States Department of Agriculture. It is pointed out that despite its defects, the work of the Bureau of Soils is of value, and is practically the only type of soil classification and mapping possible under the conditions imposed. 4 1919] Pendleton: A Study of Soil Types 483 APPENDIX A METHODS AND TECHNIQUE COLLECTION OF SAMPLES There was difficulty in finding types that would meet the requirements of wide distribution and of differing from one another as to series as well as texture. The types chosen were: Diablo clay adobe, a residual soil. Altamont clay loam, a residual soil. San Joaquin sandy loam, an ‘‘old valley filling’’ (old alluvial soil). Hanford fine sandy loam, a recent alluvial soil. The first task was the collection of the samples of soil for study in the labora- tory and in the greenhouse. Of course, there were kept in mind the errors and difficulties involved in the collection of representative samples. The selection of the localities in which to collect samples was frequently made in consultation with the persons who had originally mapped the areas under the Bureau of Soils. This was done so that the soil chosen might as nearly as possible represent what the surveyor had in mind as characteristic of the type within the area. It was to be expected that the ideal type which one man would use as a guide as he did the mapping in one area would not always be identical with that which another man might use in mapping another area, despite the aid of the inspector in keeping the ideal types of the field men as nearly alike as possible. Some of the accompanying index maps, showing the places where the soil samples were collected, are dupli- eates of the same locality. As the dates show, one is a portion of a less recent, and the other of a more recent survey. In many cases the index maps have been copied from the manuscript maps, a number of surveys in this state not yet being published. For a discussion of the differences in these maps, see below the section on The Criticism of the U. S. Bureau of Soils Method of Surveying. Not only were the field men questioned about the locality, but as nearly as possible an exact designation was obtained on the soil map itself. In the collec- tion of some of the samples the writer had the good fortune to have the assistance of the man or men who actually mapped the soils in question. Sometimes there was no trouble at all in locating a typical body of the soil where a sample might be taken. On the other hand, as in the case of the collection of the Hanford fine sandy loam from Woodbridge (nos. 15 and 16), more than two hours were spent in driving about, trying to find a place that seemed a typical fine sandy loam. Experience shows that the personal equation in field work is very important and is hard to control.45 No special attempt was made to obtain virgin soil, for the types of soils that had been selected for study were mainly agricultural, and most of the soils have been at some time under cultivation, if they are not now. Also, there has been little, if any modification of the agricultural soils by the addition of fertilizers. Hence the small tracts of the Hanford fine sandy loam, for instance, that are still virgin are largely non-agricultural, waste land areas, and would not illustrate the properties of the type as a whole. Not so large a part of the San Joaquin sandy loam is under cultivation now, though almost all of it has been farmed to grain in the past. The two minor types studied, the Altamont clay loam and the Diablo clay adobe, being of residual origin and occupying rolling to hilly or mountainous land are also not very extensively farmed. The topography is the limiting factor in most cases. * Fippin, E. O., Practical Classification of Soils, Proc. Amer. Soc. Agron., vol. 3 (1911), pp. 76-89; Increasing the Practical Efficiency of Soil Surveys, Proc. Amer. Soc. Agron., vol. 1 (1907-1909), pp. 204—06. 454 University of California Publications in Agricultural Sciences [ Vol. 3 The ideal way to collect a representative sample of soil for laboratory studies is to make a number of borings scattered about the field or fields, so that the sam- ple will approximate an average. But in the case of collecting the samples for this study it was considered best not to attempt such a procedure, for the reason that it was desired to have the samples for the greenhouse work and for the physical, chemical, and bacteriological studies, come from the same lot of soil. The collec- tion of such a large amount of soil, about 250 pounds in all, from a number of places about the selected field would be very tedious. Hence as nearly a typical place as possible was selected, close to a wagon road, in order that the samples could be transported readily. Care was used that the location be far enough out into the field to allow the sample to be representative of the conditions in the field. The subsequent procedure was as follows: The selected spot was cleared of grass or other surface material or accumulation that did not belong to the soil. A hole was dug, usually one foot deep (the depth depending entirely upon the nature of the surface soil and any noticeable changes toward the subsoil), and big enough to give sufficient soil to make up the greenhouse sample of from 225 to 250 pounds. The soil was shoveled directly into tight sugar or grain sacks, no attempt being made to mix the sample at this time. Some sacks of the soil would contain more of the surface material, and others more of the lower portion, but a later thorough mixing and screening at the greenhouse gave a uniform sample. After the large sample was collected, the hole was usually dug two feet deeper, giving a hole three feet deep. One side of this hole was made perpendicular, and from this side the small samples were collected. The A, B, and C horizons were marked off on this wall, and the samples collected by digging down a uniform section of the designated portion, using a geologic pick and catching the loosened material on a shovel. About ten pounds of soil were so collected, and placed in clean, sterile canvas sample sacks. Care was used not to contaminate the samples, so that the bacterial flora might remain nearly unaltered. It seemed imprac- ticable to attempt to collect the laboratory sample under absolute sterile condi- tions, especially since some of the deeper (B and C) samples were obtained by means of the soil auger. When the auger was used to collect the samples from greater depths the boring was done from the bottom of the hole made in collect- ing the larger sample. The size of the laboratory sample required the boring of five or six holes with the usual 1.5 inch soil auger. The laboratory sample of the first foot, or the A sample, was always collected from the side of the large hole. Notes regarding the sample, field condition, the place of collection, together with photographs and marked maps are given in appendix B. As described above, the soils were collected in separate portions from the sur- face to the 12 inch, from the 12 to 24 inch depth, and from the 24 to 36 inch depths where there were no abrupt or marked changes in the color, texture, or the like, as in the Hanford fine sandy loam. But since in some cases, as most fre- quently in the San Joaquin sandy loam, the samples do not represent the first, second, or third foot depths, as the case might be, the term, horizon, has been used. Horizon A indicates the surface sample, horizon B the second sample, and horizon C the third sample. LABORATORY PREPARATION OF SAMPLES The large samples were stored in the greenhouse until ready for use. The lab- oratory samples were allowed to remain in the sacks until air dry, when they were passed through a 2 mm. screen. This was a difficult matter, with the heavy soils, as well as with the heavy subsoils of the San Joaquin sandy loam. Cautious use ——————— 1919 | Pendleton: A Study of Soil Types 485 of the iron mortar was necessary to supplement the rubber pestle.” The samples were thoroughly mixed after screening, when they were weighed and placed in sterile containers—glass jars and large bottles. Precautions were taken as far as possible to avoid contamination of the samples during this preparatory process. The screens, mortars, scoop, and pans were flamed out between samples. Obvi- ously contamination could not be avoided absolutely without too great a prolonga- tion of the work. The material not passing the 2 mm. screen was subsequently washed on the screen, with a stream of water to remove the finer material. The residue not passing the screen by this treatment was dried and weighed. It seemed unneces- sary to adopt elaborate precautions, like those described by Mohr," to obtain the exact quantities. MECHANICAL ANALYSIS The Hilgard elutriator was used for the purpose of making the mechanical analysis of the samples (surface horizon only). For the purpose of this work the method described by Hilgard® has been modified in several respects. The pre- liminary preparation by sifting through the 2 mm. sieve in the dry state, and through the 0.5 mm. sieve by the aid of water was used. One hundred grams was sifted with the 0.5 mm. sieve, and the fine material plus the water was evaporated to dryness on the water bath. The dry material was broken up and from this the samples were weighed out for the analysis. The samples were not disintegrated by boiling, since it was believed that such treatment would affect the ‘‘colloid’’ content of the sample. Instead, the samples were shaken with water in sterilizer bottles for three hours, similar to the treat- ment preparatory to the mechanical analysis by the Bureau of Soils method. However, not boiling the samples caused more work later. The colloidal clay was removed by placing the previously shaken sample in a large precipitating jar and stirring up with several liters of distilled water. (Dis- tilled water was used throughout the analysis.) The quantity of water was not important, but rather the depth of the suspension, which was 200 mm. After allowing to stand for 24 hours the supernatant turbid water was siphoned off, when the residue in the bottom of the jar was again stirred up with water and the clay again allowed to settle out of a 200 mm. column. This was repeated until the supernatant liquid contained practically no material in suspension after standing for 24 hours. The clay suspensions were placed in large enamelware preserving kettles, and the solutions reduced in volume by boiling. The final evaporations were carried on over the water bath, so as to avoid too high a tem- perature. A large portion of the finest sediment (0.25 mm. hydraulic value) was removed as follows: After the greatest portion of the clay had been removed by the 24 hour sedimentation and decantation, the sample was placed in a 1 liter beaker and stirred up with sufficient water to make a 100 mm. column. After standing 6 to 8 minutes the suspended material was decanted off. This was repeated until the supernatant solution was practically clear. The entire time for these decanta- tions usually occupied 2.5 or 3 hours. The decanted material was allowed to stand for 24 hours, as before, and the 200 mm. column decanted as with the original clay suspension. This was continued until the clay was practically all removed. 46 Hilgard, Calif. Agri. Exp. Sta., Cire. 6, June, 1903. ‘7 Bull. Dept. Agr. Indes Neerland., no. 41, 1910. 8 Calif. Agr. Exp. Sta., Cire. 6 (1903), pp. 6-15; see also Wiley, Agricultural Analysis, vol. 1 (1906), pp. 246-62. 456 University of California Publications in Agricultural Sciences | Vol. 3 The residue constituted the main portion of the 0.25 mm, hydraulic value sep- arate. The residue from the 6 to 8 minute decantation was placed in the elutri- ator, and separated by the usual method into the various sizes. Since, however, the sample was not prepared by boiling previous to the separation of the clay, the clay was never as thoroughly removed from the coarser particles and the finer aggregate particles were not completely broken down, Hence when the sample was placed in the elutriator and subjected to the violent agitation of the stirrer an appreciable amount of clay passed off with the finest separate. Therefore, instead of allowing the water to return to the carboy from the settling bottle, during the running off of the finest separate, the following procedure was em- ployed: The water was run into precipitating jars and allowed to stand for 24 hours, and the clay water was then decanted off and boiled down with the other clay water. A further modification of the Hilgard method was found advisable after the change from the large elutriator tube to the small one, preparatory to running off the coarser separates. The mechanical defects in the elutriator always allowed for the collection of a portion of the sample in crevices where the stream of water could not reach to carry off the particles. Hence, when the large tube was removed, and cleaned, there was found an appreciable amount of the finer sedi- ments that had not passed over. These were all added to the small tube of the elutriator, and the additional material of the smaller sizes run off, using an hour or so for each size. This seemed a better method than the separation of such sediments by the beaker method, as was done by Dr. Loughridge. The separates, after decanting most of the water, were dried first on the water bath and later in the drying oven at 100°C—110°C and weighed. All of the deter- minations were made on the water free basis.” ADDITIONAL PHYSICAL DETERMINATIONS Upon the surface or A horizon samples of the 24 soils considered in this study additional physical determinations were made by the Division of Soil Technology, through the courtesy of Professor Charles F. Shaw. These determinations were of the mechanical analysis by the Bureau of Soils method,” of the moisture equiva- lent by the Briggs and McLane method," and of the hygroscopic coefficient accord- ing to Hilgard’s method.” CHEMICAL METHODS At first the chemical work was based upon the ‘‘strong acid extraction’’ method, so well known through the work of Dr. Hilgard.” There are some very pertinent objections, as well as advantages, to the method of acid extraction for the purpose of comparing soils among themselves.” In the analysis 2.5 gram samples, air dry, were used throughout. The acid extraction results are not included in this paper. 49The writer wishes to emphasize the tedium of the elutriator process, and to advise strongly against the use of the apparatus for the comparison of the soils as to texture. The elutriator is excellent from a theoretical point of view, but the results do not at all warrant the extravagant use of time in the laboratory that the apparatus requires. 5°U. S. Bur. Soils, Bull. 84, 1912. 51 Jbid., Bull. 45, 1907; Proc. Amer. Soc. Agron., vol. 2 (1910), pp. 138-47. 52 Calif. Agr. Exp. Sta., Cire. 6 (1903), p. 17; Soils, pp. 197—99. 53 Calif. Agr. Exp. Sta., Cire. 6 (1903), pp. 16ff; Soils, pp. 340ff. 54 See Hissink, Intern. Mitt. fiir Bodenkunde, vol. 5 (1915), no. 1. 1919 | Pendleton: A Study of Soil Types 487 The sodium peroxide fusion method® was carried out on the two larger series of soils, the Hanford and the San Joaquin. The elements sought were phosphorus, calcium, and magnesium. Five gram samples, air dry, were used throughout. The general method of analysis, as set forth by Hopkins, was employed, though there were a number of refinements used to increase the accuracy of the results. As such might be mentioned the double precipitation of the iron, aluminum, and phosphorus. Phosphorus was determined volumetrically, according to the method of Hib- bard.” Total nitrogen was determined by the modified Gunning-Kjeldahl method, using ten gram samples. Loss on ignition was determined upon the 10 gram, air dry samples that were used for the determination of the hygroscopic moisture of the samples used in the chemical analysis. The soils were ignited in a muffle furnace to constant weight. Humus was determined by the Grandeau-Hilgard method,” using 10 gram samples, air dry. Potassium was determined by the J. Lawrence Smith method, using one gram samples. BACTERIOLOGICAL METHODS The only bacteriological methods employed were the determination by the tum- bler or beaker method of the ammonifying, the nitrifying, and the nitrogen fixing powers of the soils.* All cultures were run in duplicate. Ammonification tests were made using 50 grams of soil and 2 grams (4%) of dried blood. The checks were distilled at once, and the cultures kept in the incu- bator at 24°C-30°C for one week. (The incubator thermostat was unsatisfactory in its action, hence the variation in the temperature. ) The nitrifying power of the soil was tested as regards the soil’s own nitrogen, dried blood, cottonseed meal, and ammonium sulfate. In the Diablo clay adobe and the Altamont clay loam 50 grams of soil were used, to which was added 1 gram (2%) of dried blood, or of cottonseed meal, or 0.1 gram (0.2%) of am- monium sulfate. In the case of the San Joaquin sandy loam 50 grams of soil were used, together with 1 gram (2%) of dried blood or of cottonseed meal, or 0.2 gram (0.4%) of ammonium sulfate. In the series run on the Hanford fine sandy loam 100 grams of soil were used, to which were added 1 gram (1%) of dried blood or of cottonseed meal or 0.2 gram (0.2%) of ammonium sulfate. It is to be regret- ted that the several series could not all be run on exactly the same basis as the Hanford series. But the small amount.of stock soils of the samples of the earlier series precluded the use of larger original samples, not to speak of the impossi- bility of repeating these series. The cultures were incubated for four weeks at 24°C-30°C. At the end of this period the cultures were dried in the oven at about 90°C and the nitrate content determined by the phenoldisulfonic acid method according to the modifications of Lipman and Sharp.” Nitrogen fixation. For this determination uniform quantities of soil were used throughout—50 grams, to which was added 1 gram of mannite. These cul- 55 Hopkins, Soil Fertility and Permanent Agriculture, pp. 630-33; Hopkins and Pettit, Soil Fertility Laboratory Manual (Boston, Ginn, 1910), pp. 42—45. 56 Jour. Ind. Eng. Chem., vol. 5, pp. 998-1009. 57 Calif. Agr. Exp. Sta., Circ. 6 (1903), p. 21. _.*% Burgess, P. S., Soil Bacteriology Laboratory Manual, Easton, Pa., The Chemical Pub- lishing Co., 1914. 59 Univ. Calif. Publ. Agr. Sci., vol. 1 (1912), pp. 21-37. 485 University of California Publications in Agricultural Sciences [ Vol. 3 tures were incubated for four weeks at 24°C-30°C, at the end of which time bae- terial action was stopped by drying in the oven for 24 hours. Subsequently, the samples were broken up in a mortar, and 10 grams weighed out for the determina- tion of the total nitrogen. Por CULTURES IN THE GREENHOUSE The large samples of the surface foot of soil were stored in the greenhouse until used. The preparation of the samples was in most cases as follows: The sample was placed on a large table and screened through a quarter inch sieve. This treatment of screening was attempted with the Diablo clay adobe and the Altamont clay loam, but was abandoned as practically hopeless. The samples of these two types had been collected in the late summer, when the ground was very hard and dry, hence the clods defied any efforts to break them up. As an alterna- tive the samples were as thoroughly mixed as possible and weighed out into the pots. Several waterings during a week, together with carefully breaking up the lumps by hand, rendered the soils finely divided enough to permit the planting of the seeds. The Hanford and San Joaquin types were readily screened. All the soils were weighed out into nine inch flower pots. In most cases the pots had been previously paraffined. Care was taken to clean the pots thor- oughly, as far as surface material was concerned; many of the pots were scrubbed with a brush and water. All previously used pots were examined to exclude the use. of such as had formerly been used for soils containing high percentages of soluble salts, but such examination was not always successful in eliminating the undesirable pots, as was afterwards evident. In the Diablo, Altamont, and Han- ford soils the quantity of soil used was five kilos per pot. In the San Joaquin soils six kilos were used. Enough soil was collected to fill eighteen pots. This would allow for the arrangement of six sets of triplicates of every sample; and the planting of a dif- ferent crop in each of the sets would allow for the growing simultaneously of six different crops on every soil. For example, there were placed together in the greenhouse and considered as a unit in the culture work the series of the Diablo clay adobe, including three pots of the sample taken from San Juan Capistrano, three from that taken near Los Angeles, three from that of the San Fernando valley, and lastly three from the sample taken in the Danville region. This group of pots was planted to oats, barley, bur clover, or any one other crop. The pots were kept together in the greenhouse, that the conditions for each one in the set would be as nearly uniform as possible, for even a slightly different location in the greenhouse was found to affect the crop appreciably. The other five sets of pots were similarly treated. No fertilizing materials were added to any of the soils. All were used in their normal condition. The aim was to compare the crop producing power of the representatives of a given type of soil from various localities. Several crops were grown, as the desire was to get a series of plants that would grow well under greenhouse conditions, and act as indicators. It was known that barley was about the best crop to use, but supplementary plants were desired. Barley, wheat, oats, rye, millet, milo, cowpeas (black eye beans), soy beans, beans (small white), bur clover (Medicago denticulata), sweet clover (Meli- lotus indica), and oats and bur clover in combination were tried. Some were a marked success under greenhouse conditions, and others were practically total failures; the better crops were given by barley, soy beans, bur clover, and millet. Sweet clover gives excellent results. This wide range of varieties of plants was 1919 | Pendleton: A Study of Soil Types 489 necessary because of the fact that it was desired to grow two crops a year on the soils. The winter crops will not do well in summer, and vice versa, even though the summers in Berkeley are relatively cool, and though the greenhouse was whitewashed during the summer months. The seed was obtained in most cases from the Division of Agronomy of the Department of Agriculture of the University of California. Such varieties as were not available from this source were obtained from the commercial seed houses in San Francisco. Usually the seed was planted directly in the pots, using sufficient seed to be sure that enough would germinate and grow to give the desired number of plants per pot, usually six. After the plants were well established, and before there was any crowding in the pots, the plants were thinned. In some cases an insufficient number of plants germinated to give the desired number per pot. Difficulty was found in getting the soy beans and cowpeas to germinate, especially in the heavier soils. This was overcome by sprouting the seeds in an incubator and planting them when the radicle was half an inch long or more. An excellent stand was thus obtained. No actual measurements of the height of the plants, or the length of leaves were made in the greenhouse work. But photographs were taken, and in these photographs the attempt was made to secure representative records of the entire series, without photographing the crop in every pot. The usual procedure in the Altamont and Diablo series was to photograph two pots out of each set of tripli- cates, an attempt being made to select average, representaiive pots. In the large Hanford series one representative pot of each set of triplicates in each crop series was photographed, and three representative sets of triplicates were also photographed. Thus some of the pots appear twice, and allow of comparisons. If any doubt be entertained as to the relative weights of the crops in the pots photographed as compared with those not so recorded, the relative weights of the crops may be easily obtained by referring to the tables of dry weights. In prac- tically every case the pot label can be read from the photograph. The method of labeling is exemplified as follows: 6 Soil sample no. 6 (Diablo clay adobe from Danville). W_ Wheat, first crop. 2 Pot 2 of the triplicate set first planted to wheat. CP Cowpeas, second crop. During the growth of the crops, notes were taken as to the relative growths and the general conditions of the plants. When the crop had ceased growing it was harvested, whether or not it was mature in the sense of having set and developed seed. The plants from a given pot were put in a paper bag, labeled, and placed in the drying oven for 24 hours. The plants were weighed when dry and cool. If any mature seed was produced it was weighed separately. Between the first and second crops the soil was allowed to rest from two to three weeks or longer. Each pot was emptied and the soil passed through a quarter inch screen before replacing in the pot. This broke up the lumps and removed most of the roots. The roots were not saved. The weight of the roots would have been interesting, but their recovery, especially from the heavy soils, would have involved careful washing, and the loss of much ofthe soil. It was thought that some washing would be necessary, even in the Hanford series, in order that the resulting figures might be at all accurate. 490 University of California Publications in Agricultural Sciences [ Vol. 3 APPENDIX B SOIL SAMPLE LOCATIONS FieLtp NOTES ON THE Sort SAMPLES COLLECTED No. 1—Diablo Clay Adobe Location: A little over a mile east of San Juan Capistrano, Orange County. On the lower slopes of the hills to the south of San Juan Creek. Sample sta- tion is on a little shoulder running northwest, between Mr, Echenique’s house and the fence following the road to Prima Deshecka Canada. Ap- proximately one-quarter mile from the above house. Soil: 0-12 inches—Dark gray adobe; much cracked. 12-36 inches—Soil becomes gradually lighter in color, approaching a light bluish gray mottled with brown. 36 inches—The subsoil becomes a silty clay loam in the lower depths. History: The field was pastured up to and including 1906. From 1907 to date the field has been annually planted to barley. Data from Mr. Echenique, the owner. Sample collected August 19, 1917. Depths of horizons: 1-A 0-12 inches. 1-B 12-24 inches. 1-C—_-. 24-36 inches. No. 2—Diablo Clay Adobe Location: One and three-quarter miles east of southeast of Eastlake Park, Los Angeles. Station is 0.7 mile by secondary road south of Pacific Electric railroad crossing, and 1.2 miles southeast of the Southern Pacific railroad crossing. Station is about 150 feet up the hill to the west of the road, in grain field, and 75 feet south of a 10 or 12 year old eucalyptus grove. The road, going south, emerges from the grove, and is then flanked by pep- per trees. Soil: 0-12 ineches—Dark gray to almost black, but with a shade of brown rather than a bluish gray. 12-24 inches—Dark grayish brown clay adobe, becoming a little lighter with depth. 24-36 inches—Dark brown with soft, whitish fragments. Fragments probably the partially weathered parent rock, though no outcrops of the rock were seen in the vicinity. Previous to the collection of the sample, Mr. E. C. Eckman, who mapped the area as the Bureau of Soils representative, said in substance: ‘‘We have no good Diablo in the area; the body I am directing you to is as good as any, but it is pretty brown.’’ History: Property owned by Mr. Huntington. Farmed to grain the past 2 years; pasture previously. Data from the son of the tenant. Sample col- lected August 20, 1915. Depths of horizons: 2-A 0-12 inches. 2-B 12-24 inches. 2-C = 24-36 inches. No. 83—Altamont Clay Loam Location: 1.4 miles southeast of Walnut, Los Angeles County, on the shoulder of a low hill, about 200 feet east of the wagon road running south through the hills. The station was selected so that the texture was about right, for in a very short distance there were variations from a heavy dark clay loam or clay adobe to the light clay loams. 1919] Pendleton: A Study of Soil Types 491 Soil: 0-36 inches—A medium textured brown friable clay loam. The soil column throughout was more or less filled with small soft whitish fragments, por- tions of the parent rock. 36 inches—The weathered parent rock was encountered. History: A. T. Currier, owner. The field is in pasture, and has not been eculti- vated for forty years, to the knowledge of the ranch foreman. The soil is probably virgin. Sample collected August 20, 1915. Depths of horizons: 3-A 0-12 inches, 3-B 12-24 inches. 3-C 24-36 inches, No. 4—Altamont Clay Loam Location: On a hillside a few feet above the Cahuenga Pass (Burbank road), near Oak Crest, Los Angeles County. _Just a few feet from the U. 8. Bureau of Soils station for the type in the San Fernando area. (For map, see the map under sample no. 25.) Soil: 0-14 inches—A dark brown clay loam. 14-36 inches—A yellowish brown loam, grading into the weathered, thin bed- ded shales at about 36 inches. History: Roadside, above the big cut on the road, probably never tilled. The sur- face is not so steep but that it could be well tilled; some of the soil in the immediate vicinity is cultivated to grain. Sample collected August 21, 1915. Depths of horizons: 4—A 0-12 inches. 4-B 12-24 inches. 4-C 24-36 inches. No. 5—Diablo Clay Adobe Location: About % a mile north of Calabasas, San Fernando Valley, Los Angeles County. The station is some distance up the hill to the west of the road running north from the Calabasas store. The sample was collected near the top of the hill, to the northeast of the oak tree. Soil: A dark gray to black typical clay adobe. Distinctly heavy. Digging was very difficult, the soil coming up in large, very hard clods. The soil was of about the same color and texture down to the bedrock at 26 inches. The bedrock is a heavy claystone or shale. History: John Grant, Calabasas P. O., owner. The land has been dry farmed to grain. Presumably there had been no additions of fertilizing materials to the soil. Sample collected August 21, 1915. Depths of horizons: 5-A 0-14 inches. 5-B 14-26 inches. 26 inches. Parent rock. No. 6—Diablo Clay Adobe Location: In Contra Costa County, % mile west of Tassajero; 6 miles east and a little south of Danville. Station about 150 feet up the hill to the south of the road, that is, about one-third of the way up the hill. Soil: 0-34 inches—A black or dark gray clay adobe, moist at 10 inches. 34-72 inches—A dark grayish brown subsoil, becoming lighter below the third foot. No bedrock within the 6 foot section, nor was there any sign of any outcrop in the vicinity. The slope of the hill moderate, the exposure north. The sample was collected with the assistance of Mr. L. C. Holmes and Mr. E. C. Eckman, both of the U. S. Bureau of Soils. They pro- nounced the station typical. 492 University of California Publications in Agricultural Sciences [ Vol. 3 History: Property owned by J. J. Johnson. The field has been farmed to grain for probably 60 years. Formerly the rotation was pasture one year, and grain one year; now the practice is grain two years, and pasture one year, Sample collected September 2, 1915. Depths of horizons: 6-A O-12 inches. 6-B 12-24 inches. 6-C 24-36 inches. No, 7—Altamont Clay Loam Location: On the Mission Pass road, a little less than 2 miles south and a little west of Sunol, Alameda County. About 100 feet above the road, between wooden electric power poles nos. 92/30 and 92/31. Soil: 0-34 inches—A medium brown clay loam, considered typical by Mr. L, C. Holmes and Mr, E. C.:Eckman of the U. 8. Bureau of Soils. There were slight changes in texture. | 34 inches—A stiff clay horizon. | Inspection of a deep cut on the roadside near the location of the sample station showed that at 6 feet and deeper there existed a heavy reddish clay. In the immediate locality the road sections showed that the parent rock was deeper than the 6 foot section. The slope of the land at the sample station was quite steep. History: Tom Burns, Irvington, owner. Field has been in pasture for the past 3 years at least, and probably for a much longer time. Sample collected September 2, 1915. Depths of horizons: 7T-A 0-12 inches. 7-B 12-24 inches. 7-C =. 24-36 inches. No. 10—San Joaquin Sandy Loam Location: North Sacramento, Sacramento County; 144 mile east of tile factory, across the road; opposite poles 57/32 and 57/33, 75 feet southeast from the State Highway. Soil: 0-26 inches—A brownish red sandy loam, slightly hog wallowed, and very slightly rolling. 26-36 inches—A sandy clay loam. 36 inches—A hard hardpan. History: Owner not known, the district now being subdivided, the property being a portion of the old ‘‘ Hagan Grant.’’ A near-by resident gave the following information: ‘‘The land has not been cultivated for the past 15 years or more. The land is said to have been farmed to grain at one time for a few years, but the ‘soil is too light for wheat, it grows nothing but filaree.’ ’’ The principal use has been for cattle and sheep pasture. Sample collected March 28, 1916. Depths of horizons: 10-A 0-12 inches. 10-B 12-24 inches. 10-C 24-36 inches. No. 11—San Joaquin Sandy Loam Location: Four miles west of Lincoln, Placer County, at the ‘‘Road Corners,’’ in the southeast field, 10 feet east of the west fence and 60 feet south of the north fence. 1919 | Pendleton: A Study of Soil Types 493 Soil: A gently hog wallowed, sandy loam, with some deeper depressions, prob- ably stream channels, Sample slightly gravelly. 0-12 inches—Brownish or reddish brown sandy loam. 12-17 inches—Sandy clay loam or clay, color the same. 17-23 inches—A stiff reddish brown clay. 23 inches—A hard hardpan. History: Mr. Frank Dowd, owner. The land has been planted to wheat for the past 20 or 25 years; previous to that time it was used for pasture. Six to 10 or 12 bushels of wheat, and 8 to 20 bushels of barley is the production of this soil in the locality. The soil is usually fallowed on alternate years. Land held at from $30 to $50 per acre. Sample collected March 28, 1916. Depths of horizons: 11-A 0-11 inches. 11-B~ 11-17 inches. 11-C 17-23 inches. No. 12—San Joaquin Sandy Loam Location: About 6 miles west of Wheatland, Sutter County. Near a road corner, in a little swale west of a knoll, 15 feet east of the westerly fence of field, and 150 feet south of the north line of the westerly road. Soil: Texture slightly heavy, and barely enough sand for a sandy loam, but the best found for several miles. Color brownish red, the same throughout the entire depth. 0-18 inches—Light, fine textured, sandy loam. 18-31 inches—Heavy sandy clay loam, running into a stiff clay. 31 inches—Hardpan, sandy and somewhat soft. The ground was very moist at this time. History: Very evidently pasture for sheep and cattle. No signs of having been cultivated for several years, at least. The cover is of a number of low annuals—Orthocarpus, Trifolium, Centaurea, and others. Sample collected March 29, 1916. Depths of horizons: 12-A 0-12 inches. 12-B 12-18 inches. 12-C 18-31 inches. No. 183—San Joaquin Sandy Loam Location: Three and three-quarters miles east of Elk Grove, Sacramento County. On the Sheldon road, about 30 feet northwest from the fence on the north side of the road. About 200 feet southwest from where a house formerly stood. Soil: A reddish brown sandy loam, approaching a loam; becoming redder in color with increasing depth. 0-14 inches—Heavy sandy loam. 14-22 inches—Clay loam. 22-29 inches—Heavy clay loam. 29 inches—Compact hardpan. History: Wackman Brothers, Elk Grove, owners. The land has not been plowed or farmed for at least 15 years. The land is held at about $50 per acre. Sample collected March 30, 1916. Depths of horizons: 13-A 0-12 inches. 13-B 12-22 inches. 13-C 22-29 inches. 494 University of California Publications in Agricultural Sciences [ Vol. 3 No. 14—Hanford Fine Sandy Loam Location: One mile southeast of the Sheldon road, 34% miles east of Elk Grove, Sacramento County. On the southwest side of the secondary road, in al- falfa field, about 25 feet from the fence. Station on a little rise. Soil; 0-11 inches—A medium brown micaceous heavy fine sandy loam, 11-24 inches—A dark gray to black fine sandy loam, grading into the fol- lowing. 24-36 inches—Brown fine sandy loam. Water table at 32 inches. History: Mrs. A. C, Freeman, Elk Grove, owner. Land planted to alfalfa. Good growth. No irrigation. Willows as well as alders and river ash along the sloughs. Many scattering valley oaks. The land is subject to overflow from the Cosumnes River, as it lies low in the river bottom, and shallow stream channels and sloughs are frequent. Sample collected March 30, 1916. Depths of horizons: 14-A 0-12 inches. 14-B-_- 12-24 inches. 14-C 24-36 inches. No. 15—Hanford Fine Sandy Loam Location: North of Woodbridge, San Joaquin County, along the State Highway, less than 4 mile south of the road running westerly from Acampo to the highway. Station in a vineyard, with almond trees along the roadside, 20 feet northeast of ‘‘change telephone pole,’’ 200 feet north of pine tree at the gateway on the opposite side of the highway. (For map, see under sample 16.) Soil: Texture a rather coarse fine sandy loam; it was hard to find a good fine sandy loam. Color when moist was a medium brown throughout the 3 foot section; the field color was a light grayish brown. History: Mike Nolan estate, owner. The vineyard is of Tokay grapes, 10 to 12 years old. The land is held at $300 to $400 per acre. It is said to be a losing game to farm this land to grapes at this valuation. Sample col- lected March 30, 1916. Depths of horizons: 15—A 0-12 inches. 15-B 12-24 inches. 15-C 24-36 inches. No. 16—Hanford Fine Sandy, Loam Location: Along the road north of Woodbridge, San Joaquin County. In a young pear orchard about 65 feet west of the highway, and about 95 feet north » of the north abutments of the bridge over Mokelumne River. Soil: A medium brown fine sandy loam, similar throughout the soil column of three feet. This soil is of the recent, flood-plain phase of the type, though this station is not known to have been under water for a number of years, at least. There is only a comparatively narrow shelf of this phase between the older, higher phase, and the river. History: A. Perrin, Woodbridge, owner. The land had always been in brush and pasture until it was cleared and planted to pears in 1911. Value about $500 per acre. Sample collected March 30, 1916. Depths of horizons: i 16-A 0-12 inches. 16-B =: 12-24 inches. 16-C 24-36 inches. 1919 | Pendleton: A Study of Soil Types 495 No. 17—San Joaquin Sandy Loam Location: A short distance south of the east and west road that runs east to Thalheim, San Joaquin County. The station was on a slight knoll 75 feet south of a canal, and the same distance east of the secondary road running north and south; not far from a vacant barn. Soil: 0-12 inches—Reddish brown. 12-24 inches—Slightly redder. 24 inches—Hardpan. The surface had the characteristic hog wallows, and the usual scant vegeta- tion of grasses and herbs, ‘‘filaree’’ being abundant; yet all vegetation was more abundant than that in pastured fields. History: Rey. Frank Hoffman, Acampo, owner. Apparently, the land has not been cultivated in recent years. Sample collected March 31, 1915, Depths of horizons: 17-A 0-12 inches. 17-B = 12-24 inches. No. 18—San Joaquin Sandy Loam Location: Two and one-half miles northwest of Madera, Madera County. Along State Highway, 75 to 100 feet southwest of the paved road, at telephone pole 92/29; across the highway from the driveway to the house. Soil: 0-5 inches—A light reddish brown sandy loam. A noticeable plow pan at 5 inches. 5-24 inches—A light brownish red sandy loam, becoming heavier below. 24-30 inches—Quite compact heavy sandy loam. 30 inches and deeper—A very compact hardpan. Topography very gently rolling, hog wallows well developed, though consider- ably degraded by cultivation. Barley grain not growing well in the lower spots. History: Cropped for probably 20 years to grains; barley at present. Land used for pasture previous to grain farming. e nd ; Peo = : = . ats me } ] ] J >] » oO, soil 25, pot 1. HANFORD FINE SANDY LOAM—FIRST CROP Pots of same and different representatives of a given soil type compared. Fig. 2. Dwarf milo A. Left to right—Soil 15, pot 1; soil 15, pot 2; soil 15, pot 3; soil 20, pot 1; soil 20, pot 2; soil 20, pot 3; soil 23, pot 1; soil 23, pot 2; soil 23, pot 3 UNIV: GALIE. PUBL. AGR, SCI, VOL. S { PENDLE TON] PLATE 64 HANFORD FINE SANDY LoAM—FIrst Crop Pots of same and different representatives of a given soil type compared. Fig. 1. Dwarf milo B. Left to right—Soil 14, pot 3; soil 15, pot 2 2: soil 16, pot 1; so1 19, pot 3; soil 20, pot 2; soil 22, pot 3; soil 23, pot 3; soil 24, pot 2; ; soil 25, pot 3. SSR HANFORD FINE SANDY LOAM—F IRST CROP Pots of same and different representatives of a given soil type compared. Fig. 2. Dwarf milo B. Left to right—Soil 14, pot 1; soil 14, pot 2; soil 14, pot 3; soil 22, pot 1; soil 22, pot 2; soil 22, pot 3; soil 23, pot 1; soil 23, pot 2; soil 23, pot 3. UNIV. CALIF. PUBL, AGR. SCI, VOL. S [ PENOLETON ] PLATE wie, ‘te. P =Ty , iV ae ae Bai HANFoRD FINE SANDY LoAM—Fi1rst Crop Pots of same and different representatives of a given soil type compared. Fig. 1. Soy beans. Left to right—Soil 14, pot 1; soil 15, pot 1; soil 16, pot se) soil 19, pot 2; soil 20, pot 3; soil 22, pot 1; soil 23, pot 3; soil 24, pot 1; soil 25, pot 3. Pe - b ee : Sian: ae, su - She lo, "14 see First Crop HANFORD FINE SANDY LOAM Pots of same and different representatives of a given soil type compared. Fig. 2. Soy beans. Left to right—Soil 14, pot 1; soil 14, pot 2; soil 14, D> . b] ] ] pot 3; soil 16, pot 1; soil 16, pot 2; soil 16, pot 3; soil 25, pot 1; soil 23, pot 2 soil 23, pot 3. UNIVe GALI PUBL, AGA, SCl. VOL. s [PENDLETON ] PLATE 56 i Penn aname se ~~ HANFORD FINE SANDY LOAM—FiIrRST Crop Pots of same and different representatives of a given soil type compared. Fig. 1. Cowpeas B. Left. to right—Soil 14, pot 1; soil 14, pot 2; soil 14, pot 3; soil 22, pot 1; soil 22, pot 2; soil 22, pot 3; soil 23, pot 1; soil 23, pot 2; soil 23, pot 3. - ae 1 , 6 44 =e F HANFORD FINE SANDY LOAM—FIRST CROP Pots of same and different representatives of a given soil type compared. Fig. 2. Cowpeas B. Left to right—Soil 14, pot 3; soil 15, pot 2; soil 16, pot 2; soil 19, pot 2; soil 20, pot 2; soil 22, pot 2; soil 23, pot 2; soil 24, pot 1; soil 25, pot 3. UNIV... CALIF, PUBL. AGR. SCI. VOL..s [f PENDLETON ] PEATE 6&7 \ bei 1 \ Ly ? hi : ' i 4 | \" .y \ 7 1 fee By : | \ —f — / j —_ 14 eS ow oe =< " a ‘ \ / : ’ } ; - wide 3 \ /t sl \ at t/ Vinee ap \W ; \ x HANFORD FINE SANDY LOAM—SECOND CROP Pots of same and different representatives of a given soil type compared. Fig. 1. Barley, following soy beans. Left to right—Soil 14, pot 2; soil 15, pot 1; soil 16, pot 3; soil 19, pot 3; soil 20, pot 1; soil 22, pot 2; soil 23, pot soil 24, pot 3; soil 25, pot 1. 43 me Fes as, am He publications in agricultural sciences Biological & Medical Serials PLEASE DO NOT REMOVE CARDS OR SLIPS FROM THIS POCKET eh eae UNIVERSITY OF TORONTO LIBRARY STORAGE PR A IO Sn Se re ee . * eo oes ee ee ee ae) oe = 0 . Se. = ee ene elas arms . OK DST Fay Sib rok ares ao ere oe pe ee a . rer oe 7 a ee eee ae . Sy . i es ~-6 2 Sr te be . Bs 2a32: Ee Rape ein. - <5 + 8 ee OA ere ome ww a Sobuba a cee OPT TA eee ee ee : : > = > RS, Fede B.S. 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