Historic, archived document Do not assume content reflects current scientific knowledge, policies, or practices. ~ Crrcular No. 804 { ; ee 7 April 1949 ¢ Washington, D.C. UNITED STATES DEPARTMENT OF AGRICULTURE Stocking Northern Great Plains Sheep Range for Sustained High Production By E. J. Woouro.k, forest ecologist, Northern Rocky Mountain Forest and Range Experiment Station, Forest Service } CONTENTS Page Page TT EROCTIGEIOM Me eee nite. pens oe Se od Le 1 Effects of heavy conservative, and light stock- How the problem was studied________________ 2 ing—Continued. Character of northern Great Plains range_____ 5 Effects on number and size of plants________ 24 (The forage and iis utilization. —-.-. _---.2_- ) Effects on height growth of blue grama and Growth and development of the forage_____ 9 bluestemiwiheatorasss ss eee 26 Relativevsrazine values. 922 =e 2 10 Effects on herbage production_____________- 28 How the forage was utilized___.___________- 12 Effects onthe sole: tees) 2 = ee eee 30 Habits of the yearling ewes_____-_--_« ____.. 14 Biitectsion) the sheepis=: 25 ee eee eee 30 MIN CHO AAC HIV LUeSee ees ee! 2 Sel eel ae hi 14 Degree of forage use recommended for northern Influence of natural factors_________________ 18 Great Plaims!sheep Trance ssa ee aR. mflienceyonfences: 222-2 2s 19 Recommended stocking rate for northern Great Infinence ofpredators=---- = 2. 20 Plains sheep range during average 8- to 9- Habits indicate desirable management sys- monthiseason se eee ee ee 34 TEST Seer mee ree er eta RSE os a a 20) SAS UMMA sees ey i ie ae ee eee at 35 Effects of heavy, conservative, and light stock- Common and botanical names of species men- LTT Oggpee ener ed Sap Oe eS is 21 HONE d Seok ae es ee ee E Lar aths Seneca 38 Effects on density of the vegetation_________ Jie Witerature cited =. ka ae ee ee eee 39 INTRODUCTION The northern Great Plains, which includes approximately the west- ern half of North and South Dakota, the northeast quarter of Wyo- ming, and the eastern two-thirds of Montana, constitutes one of the oO) largest and most important range-livestock areas in the United States. The major part produces nutritious native forage, the utilization of which determines the economic and social pattern of the region. Only a relatively small proportion is cultivated. 1JIn cooperation with the U. S. Bureau of Animal Industry and the Montana Agricultural Experiment Station. The author acknowledges the assistance and cooperation of several members of these agencies and of numerous employees of the Forest Service who assisted in conducting this experiment. Special acknowl- edgment is made to Martin J. Doyle, B. A. I. shepherd, who served faithfully and well throughout the experiment. 821193°—49—-—-1 1 2 CIRCULAR 804, U. S. DEPARTMENT OF AGRICULTURE Much of this range is grazed by cattle and horses, but sheep also use a considerable part of it. Although wool and feeder lambs are the chief market products of the local sheep industry, the development of ewe lambs and yearling ewes into breeding animals by grazing them for several months to a year on the range is becoming an increasingly maar ea type of range sheep husbandry in the northern Great ains. In this area the low production of supplemental hay and the high cost of imported feeds, plus generally open winters and the relatively good forage value of cured range herbage, encourage range grazing for long periods annually. It is a common practice to graze sheep on the range continuously for 9to11 months and even year long when forage is available and weather is not too severe. One of the major problems which northern Great Plains sheepmen face is how to stock their ranges to get the greatest possible production year after year without deterioration of the forage and soil upon which their continued and successful operation depends. ‘The effect of past grazing use and the frequent occurrence of severe drought contribute to the wide variations in stocking which occur in the region. It has been most difficult to determine the acreage of range per sheep per month; 1. e., the rate of stocking that will give best results over a long period. A common but questionable practice has been to stock heavily during favorable years and then attempt to adjust down- ward when unfavorable weather and forage conditions occur. This has led many operators into financial ruin because, unfortunately, a crisis may develop more rapidly than adjustments can be made during unfavorable seasons. Furthermore, the range deteriorates severely under heavy stocking. On the other hand, stocking so light as to entirely avoid heavy sales of livestock during drought years is not practical because heavy carrying charges and other expenses make such a practice unprofitable. The urgent need for information on how to stock northern Great Plains sheep range for sustained production led to the study here reported. HOW THE PROBLEM WAS STUDIED The Northern Rocky Mountain Forest and Range Experiment Station in cooperation with the Bureau of Animal Industry and the Montana Agricultural Experiment Station conducted a study of sheep grazing from 1936 through 1941 to determine and develop guides to proper stocking of northern Great Plains range for sustained sheep production without deterioration of the forage and soil resource. The study centered on lands of the United States Range Livestock Experi- ment Station, about 10 miles southwest of Miles City, Mont. This location is typical of northern Great Plainsrange. Three experimental pastures (fig. 1) of 332, 476, and 847 acres were established and stocked with yearling ewes to provide 9.5, 13.6, and 24.2 acres of range per head in 1936, the first grazing season. During that first season, 1936, the range pastures received 0.48, 0.34, and 0.19 sheep-months of graz- ing use per acre, respectively. The smallest pasture was stocked heavily, the next larger one conservatively, and the largest pasture lightly throughout the entire test. Because of favorable weather after late 1937 and substantial re- covery of the range from the severe droughts of 1934 and 1936, it was necessary to increase the number of sheep in each pasture to maintain STOCKING NORTHERN GREAT PLAINS SHEEP RANGE STOCKED. CONSERVATIVELY STOCKED Custer Flot Wel/ ~ HEAVILY Eckel se 3 e oS = y LEGEND Sor ! ag oe \ \ w Reservoir w j Cm POS Ba tisie oe eae 158 Cie Broke’ ie 0 0 765 OS Oa ree nes | 300 14 | 290 PE) 3 1 | 635 OAS aes See | 545 205 Sos 60 | 5 4 798 LOANS a 765 30° | 55 90 | 6 15 961 19426 ao? 267. 38 36 139 || 4 30 1, 514 Conservative | | LOSSee a ere 96 18 683 12 | 0 0 809 L939 = s 2G. 23 418 18 | 2 (1) 678 ROA Q ee 8 eee 357 32 247 40 3 4 683 OAc eae 737 55) 99 Sie leowas 28 975 ROADS Sees 1, 427 50 35 104 | 4 38 1, 658 Light: | LOSS oe eee 100 29 630 4 0 | 0 776 NOS Ore: Sea 221 48 > 484 28 | 5 | 0 785 TOA OE ee PRS 44] 51} 382 AS 25 9 951 OAM Tne eee | 856 SS elSS 46 | 23 | 17 ASG NQAD ok eo 1, 612 13 {> 107 93 225) 12 1, 919 Ungrazed:? | | | | LOSSe= Sates 135 17 667 ol | 0 (1) 850 193 Oe eee 273 31 495 58 | 2 (1) 859 BGA see | 570 38 295 101 4 (1) 1, 008 OA eae eae | 949 CE 140 178 5 18 jo ele 19422 c2 tse = [Sale oe Den 73 62 345 4 26 2, 022 | | 1 Less than 1 Cm ? These areas were fenced in 1938 and thereafter entirely protected from sheep grazing. BLUE GRAMA In 1938, blue grama covered 1 to 2 percent of the ground surface on the average and composed 12 to 20 percent of the total perennial vegetative cover. There was a greater density of blue grama on plots in the heavily stocked pasture at that time than in any of the other pastures or the ungrazed areas. During the 4 years of grazing, 1938— 41, blue grama density increased through the establishment of new plants and the enlargement of old ones ‘by 814, 756, and 641 square centimeters per plot on the ungrazed, lightly, and conservatively stocked pastures, respectively, but under heavy stocking the increase was only 607 square centimeters per plot. In the relatively good rainfall year of 1942, when none of the pastures was grazed, blue grama made striking density increases on all plots; 502, 690, 756, and 563 STOCKING NORTHERN GREAT PLAINS SHEEP RANGE 23 square centimeters on the average on the heavily, conservatively, and lightly grazed, and ungrazed plots, respectively. For the 5 years 1938-42 , the greatest increase, 1,512 square centime- ters, occurred on the plots under hght stocking. These plots also had the highest final grama density. The total increase under conservative stocking was slightly smaller as was final density. On the protected plots, blue grama density increased 1,377 square centimeters per plot and the 1942 density was intermediate between the lightly and con- servatively stocked levels for that year. Under heavy stocking the increase in blue grama density between 1938 and 1942 was only 1,109 square centimeters per plot. In 1942, when none of the pastures was grazed, plots on range that had previously been heavily stocked had the lowest density of all situations. BLUESTEM WHEATGRASS The density of bluestem increased each year from 1938 through 1941 under all intensities of stocking and under protection. The greatest increase over the 4 years, 60 square centimeters per plot, occurred on the ungrazed areas. Under heavy stocking, the increase was 23 square centimeters compared with 37 and 52 per plot under conservative and light stocking. Thus, recovery of this valuable forage species was directly related to the rate of stocking; least where erazing use was heaviest, and progressively more through conservative and light erazing to protection. In 1942, when rainfall was relatively good, bluestem density actu- ally decreased on the plots that were conservatively and lightly stocked even though grazing was not permitted that year. At the same time, it continued to recover from past grazing use and drought on the plots that were heavily grazed. For the 5 years 1938-42, the greatest total increase in bluestem density occurred on the plots protected from sheep grazing since 1938. The fact that bluestem density continued to increase on the heavily erazed plots after grazing ceased but actually declined on areas pre- viously grazed lighter and protected, illustrates how much heavy erazing delayed the natural tendency of this range to reach a balance following a major drought disturbance. By 1942 the lightly grazed and ungrazed plots had equal densities of bluestem. Plots on the conservatively erazed area had only two- thirds as much bluestem density and the heavily grazed plots only about half as much as those protected and lightly grazed. LITTLE BLUEGRASS Largely because of its ability to grow early in spring when moisture is available and then lie dormant during the dry summer, little blue- grass increased during and immediately after the drought when later starting species were losing density. By 1938 it composed 75 to 85 percent of the vegetative cover exclusive of cactus and browse on plots in the sheep pastures. From 1938 through 1942 it declined steadily under all three intensities of grazing and even with protection from sheep grazing. This steady decline just about offset the increase in density of other perennial species in 1939 under light grazing and protection and caused a decline in total density under conservative . and heavy stocking. Under heavy stocking the loss in little bluegrass density in the 4 years 1938-41 was 91 percent as compared with 86 24. CIRCULAR 804, U. S. DEPARTMENT OF AGRICULTURE percent on the conservatively grazed pasture, and only 79 percent with light stocking and protection. By 1942 little bluegrass made up only 2 to 6 percent of the vegetative cover on the plots. OTHER PERENNIAL GRASSES AND GRASSLIKE PLANTS The group of other perennial grasses and grasslike plants, composed of species such as sand dropseed, needle-and-thread, and threadleaf sedge, recovered very slowly under all degrees of stocking. Greater competition from the principal perennial species which were recover-_ ing rapidly under conservative and light stocking retarded recovery of this group more than did heavy grazing and somewhat less competi- tion in the small pasture. By late 1942, the density of this group had just about doubled as compared with the 1941 level on plots in the areas previously stocked conservatively and lightly. On the heavily grazed plots the increase after grazing was slightly more than 50 percent above the 1941 level. The trend under protection was comparable with that on the conserva- tively and lightly stocked plots. PERENNIAL FORBS AND BROWSE Browse species and perennial forbs, although common on the ex- perimental range, were very sparse or entirely absent from all plots in 1938. They increased slowly under all situations throughout the study but none became important constituents of the plots. EFFECTS ON NUMBER AND SIZE OF PLANTS Under average weather and with good grazing management, the principal clump-forming forage species in the northern Great Plains are vigorous and well-spaced, but they seldom form a complete cover. Severe drought in 1934 and 1936 greatly reduced the stand of perennial forage plants in the northern Great Plains (6) and it is evident from TABLE 6.—Average number of plants, by species, on 2 by 5 decimeter plots randomly located in 1942, after 6 years of sheep grazing at various stocking rates Con- , Heavily | serva- | Lightly Un- Species stocked | tively stocked grazed stocked Clump-forming: Number | Number | Number | Number IB UND Key on zy 00k: Weemmneeth Catia are tAwe) ES 8 i als} 0. 75 0. 81 0. 47 ihreadleatisedse ss. 02 eas as eee 2. 66 Us, US 5. 20 1. 02 bittlesbluegrasss «= ae a= = yee el . 43 aro 1. 19 Needle-and-thread ____=__-.---2-=- . 16 68 . 41 gal. PROG AVES 2 pel es 2 RPS say ae eae ee 4, 71 9. 59 6. 79 2. 80 Single stem: Blwestemawheaterass == eee 8. 73 8. 19 13. 82 21. 36 Dhireadleat sed gess 23 3a 20. a een . 87 . 40 . 24 2. 93 A ter ae Bes yoo nee tee, See 9. 60 8. 59 14. 06 24. 29 AUT UAC SHE CLES ee eee eee ee en 64, 74 13. 65 34. 17 67. 53 “pln tae eee a ee STOCKING NORTHERN GREAT PLAINS SHEEP RANGE 25 the vegetative-density record in table 5 that the stand was still at a low level in 1938. In 1942, the first season after grazing was terminated in the pastures, and following the good growing season of 1941, there were fewer plants of the 4 major clump-forming species per unit of area on the heavily stocked range than on the other grazed areas (table 6). Collectively, blue grama, threadleaf sedge, little bluegrass, and needle-and-thread averaged about 10 and 7 plants per plot on the conservatively and lightly stocked pastures but only about 5 plants on the area heavily stocked. Also, the average size of plants of these 4 clump-forming species was less per plot under heavy stocking than under conservative or light (table 7). On plots ungrazed after early 1938, the plants of these 4 species combined were the fewest in number and the smallest in size of those in all situations. TABLE 7.—Average area of plants, by species, on 2 by 5 decimeter plots randomly located in 1942, after 6 years of sheep grazing at various stocking rates Con- : Heavily | serva- | Lightly Un- Species stocked | tively | stocked | grazed | stocked Cm2 Cm.2 Cm.2 Cm.2 LEAS (Giera tit poe ae Sa eS eee ee en 11. 97 12. 30 12. 47 on iiTReAeaTeNCOU Rs. 2 aS ee ee 2. 21 1. 62 ie yea 2a LLTES {lel Of Cover ea hSTS TR Sean hg ane ae ama ee 1. 53 1. 33 1. 66 1. 89 Meedic-and-thread—_ =) See ee Bgl 5. 16 7. 30 6. 56 LOGUE ak Bae Fo ad a ee ee 18. 82 20. 41 23. 14 18. 09 BLUE GRAMA Individual plants of blue grama were more numerous in 1942 on heavily stocked range than on conservatively and lightly stocked range by 57 and 46 percent, respectively (table 6). The areas pro- tected from sheep grazing from 1938 to the end of the experiment had fewer blue grama plants than any of the grazed pastures. Although most numerous on plots heavily grazed, the plants were slightly smaller than those on lighter grazed plots (table 7). The closer erazing and more severe trampling associated with heavy stocking prevented small blue grama mats from merging into compact clumps. Heavy stocking also apparently retarded the enlargement of indi- vidual established clumps of blue grama. On protected areas both numbers and size of blue grama plants were restricted by competition with other species for soil moisture and nutrients. THREADLEAF SEDGE In 1942 the pasture heavily stocked previously had less than three plants or clumps of threadleaf sedge per plot in comparison with nearly eight for the conservatively stocked and five for the lightly stocked (table 6). Even though the plants were slightly larger on the area heavily stocked than elsewhere (table 7), this difference was sufficient to account in part for the 1942 plot densities summarized in table 5. Since threadleaf sedge plants were less numerous but slightly 26 CIRCULAR 804, U. S. DEPARTMENT OF AGRICULTURE larger on the heavily stocked pasture than elsewhere in 1942, after 6 years of sheep grazing, heavy stocking evidently had such effects as killing the small plants that survived the drought or preventing the establishment of new plants following the drought. The important point is that threadleaf sedge was only about half as abundant on the small pasture after 6 years of heavy stocking as on other pastures stocked more lightly. On the area protected after early 1938, the plants were intermediate in size between those on heavily and con- servatively stocked range but were very sparse. NEEDLE-AND-THREAD Needle-and-thread grass, another important clump-forming species and one of the most sensitive to grazing, was by 1942 very sparse in the heavily stocked pasture. Plants on the sample plots averaged only about one-fourth and one-half as numerous, respectively, as on the conservatively and lightly stocked pastures (table 6). Besides being much less numerous, needle-and-thread clumps were less than half as large on the heavily stocked pasture as in the lightly stocked and unstocked areas (table 7). The plants were somewhat smaller on the conservatively stocked than on the protected and lightly grazed areas but still considerably larger than under heavy stocking. Heavy grazing and trampling retarded the recovery from drought of surviving needle-and-thread plants and limited the establishment of new plants from seed. These findings strengthen the plot-den- sity data and help explain the sparser stand of vegetation on the heavily stocked pasture. . BLUESTEM WHEATGRASS In 1942 there was nearly twice as many stems of bluestem per plot on the lightly stocked range and more than twice as many on areas protected since 1938 as on the heavily stocked. There was little differ- ence in the stand of bluestem on conservatively and heavily stocked areas. Because of its single-stemmed growth habit, bluestem does not form a sod but by means of underground rootstocks increases rapidly in the stand when relieved from grazing. The large number of stems per plot on the lightly stocked and protected areas undoubtedly helps to account for the greater total density on these areas in 1942. ALL ANNUAL SPECIES Low-value annual species such as woolly Indianwheat and sixweeks fescue were five and two times more abundant in the heavily stocked pasture by 1942 than in the other two grazed pastures, respectively (table 6). By retarding the recovery of palatable perennial species, heavy stocking permitted an increase in annual species (fig. 10) which at best are only temporary and provide a limited amount of forage. EFFECTS ON HEIGHT GROWTH OF BLUE GRAMA AND BLUESTEM WHEATGRASS Height growth of blue grama leaves and seedstalks was greater in 1942 on the conservatively stocked pasture by 22 and 3 percent, respectively, than on the heavily stocked pasture (table 8). On the protected areas the leaves and seedstalks were 55 and 10 percent taller than on areas stocked heavily during 6 previous years. The propor- eee ee ee ee STOCKING NORTHERN GREAT PLAINS SHEEP RANGE 27 F-415227 FicurE 10.—Six years of heavy sheep grazing and trampling changed the vege- tative composition of typical northern Great Plains range to a dense stand of low-value annual plants mostly woolly Indianwheat except in the protection of pricklypear clumps. tion of plants producing seedstalks was very similar in the ungrazed areas and the conservatively stocked pasture. In the heavily stocked pasture, however, about 10 percent more of the plants produced seed stalks than in the conservatively stocked pasture and 5 percent more than in the ungrazed areas. Although heavy stocking retarded height growth, it stimulated the production of seedstalks in blue TABLE 8.—Average maximum length of leaves and height of seedstalks, and proportion of plants that produced seedstalks, by rate of stocking and species, 1942 : Plants . . Length | Height of a Stocking rate and species ‘ ane with of leaves | seedstalks seadsuallea Heavy: Cm. Cm. Percent Peers Ora iy Staeen. 0 8 Ee 9 30 91 Piueastem wheaterass. 2. 2 -=-L 2. 28 56 17 Conservative: BRreeeNa ee: Mal. Net ie ns NEOs i Lt 31 83 imestem-wheaterass_ ..-_..-.-=22-.2- 30 60 13 Ungrazed: Pere EDITED = sen eee ek Ce 14 33 87 iwestem. wheatgrass... <__--...----..- 35 61 15 28 CIRCULAR 804, U. S. DEPARTMENT OF AGRICULTURE erama. It is not inferred that greater seedstalk production as a result of heavy stocking means greater production of viable seed. Although data are not available, heavy grazing may have actually reduced the quantity of good seed produced even though more seed- stalks appeared on the heavily than on lighter stocked areas. Leaves of bluestem grew tailer on the conservatively stocked pas- ture and the ungrazed areas in 1942 by 7 and 25 percent, respectively, than on the heavily stocked pasture, and seedstalks were 7 and 9 percent taller (table 8). However, the plants on the heavily stocked pasture produced more seedstalks that year by 31 and 13 percent than plants on the conservatively stocked and ungrazed areas. Thus, as with blue grama, heavy stocking retarded the height growth but stimulated seedstalk production. Again, however, the effect on pro- duction of viable seed is not known, but heavy stocking may well have caused the production to decline. EFrFrects ON HERBAGE PRODUCTION Where intensive use of range vegetation retards its recovery from drought, the result is less herbage production, less usable forage, and lower grazing capacity. Taste 9.—Production of air-dry herbage per acre and estimated usable forage per acre* under various stocking rates, by species, 1942 } | : Conserva- . Heavily Lightly $ tively 2S Ungrazed stocked stocked stocked Species = rs "8 “= © =a 2) a © = 2 © aes = = 6 OQ |-60 = = 6 2 |-=6 ® ‘ws @= ea eso a S ass oy ea cr is) a0 SS ry je) Perennial grasses: | Lbs. | Lbs. | Lbs. | Lbs. | Lbs. | Lbs. | Lbs. | Lbs. Blucwrama os 1232s | 149 66 250 @ | 279 |--59 |: Sts) is Bluestem wheatgrass_| 110 50 245 49°| 445. | 98-)" i5acbeetcee Threadleaf sedge_____| 124 | 43 | 365 | 69| 204 | 24) 39 7 Other perennial | STASSESt eee | = “875| 52) 1983-419 109 65 108 65 opie eee cS Cee | 470 | 211 |1, 058 | 310 |1, 037 |'246 [1,315 | 352 Perennial forbs" — 2-2 < 143 29 94 | 19 93 19 40 8 STO WSe Sees Ae ee (2) =|) 50e=5 te] 2@). le S45 2 33 2 Potash es 613 | 240 |1, 153 | 329 |1, 175 | 267 |1,388 | 362 PRTERTU AIS 28 Oo we Set 815 | 163 79 16 306 | 61) 437) 87 Total, all species_________ 1,428 | 403 |1, 232 | 345 1, 481 | 328 |1,825 | 449 ' 1 Estimates of usable forage for blue grama, bluestem, and threadleaf sedge derived by applying utilization figures in table 4 to pounds of air-dry herbage per acre. For other species the following factors were used for all stocking intensities: other perennial grasses, 60 percent; perennial forbs, 20 percent; browse, 5 percent; annuals, 20 percent. 2 Less than 1 pound. STOCKING NORTHERN GREAT PLAINS SHEEP RANGE 29 Not all herbage, even of the most palatable species, can be con- sidered as usable for age. Of the many factors involved, the necessity of leaving considerable herbage to protect the soil and insure regr owth of the range vegetation is most important. Since grazing capacity is based only on herbage that should properly be used instead of total herbage produced, a conversion is necessary. To make this conver- sion, total pounds of air-dry herbage for each key species were weighted by the aver age percentage grazing use obtained during 3 years (table 4, p. 13) in the sheep pastures under each intensity of stocking. For other species or groups of species for which average use per centages were not available, weighting was done by applying estimated factors for all areas regardless of degree of stocking. These data (table 9) indicate the proportionate part of total herbage that was considered to be usable forage on the differently stocked areas. In 1942, when the pastures were not grazed, the pasture that had been heavily stocked for 6 years pr oduced less perennial-type herbage per acre, based on samples hand-clipped to a 1-centimeter stubble, than either of the other pastures (table 9). Even when the yields of blue grama, bluestem, and threadleaf sedge were mathematically converted into usable forage, the advantage was still with the con- servative and light stocking rates. With the addition of annual-type herbage, however, the area that was heavily stocked showed greater production in total herbage than the conservative and in usable forage than all but the ungrazed area. The fact that the annual type forage is nutritious only when lush and green and that it dries and weathers away quickly, offsets any advantage the greater quantity might appear to have. Year-long sheep operations in the northern Great F-415238 Figure 11.—Six years of conservative sheep grazing did not materially change this typical northern Great Plains range. Palatable perennial grasses are abundant but low-value annuals very inconspicuous. 30 CIRCULAR 804, U. S. DEPARTMENT OF AGRICULTURE Plains are dependent upon adequate range forage at all seasons. The perennial species, which in 1942 produced more herbage and more usable forage on areas that had been conservatively and lightly stocked than on the heavier stocked pasture, are the only ones that can be depended upon to provide forage at all seasons of the year (fig. 11). Individual perennial species show in general the same comparisons as the entire group of perennial plants. The lower production both of herbage and usable forage for all perennial species on the heavily stocked area confirms the lower density, smaller size, and shorter height growth of plants already mentioned as evidence that heavy stocking retarded recovery. EFFECTS ON THE SOIL Heavy stocking removed too much herbage from the range and reduced the accumulation of litter on the soil surface, thereby exposing’ the soil surface to washing and blowing. Trampling on these barren, unlittered surfaces lossened the topsoil for easy removal by the wind and exposed the roots of the plants. On flat or level sites, some of the most persistent plants survived on pedestals a few inches higher than the surrounding surfaces. On slopes in the sandy loam soil type, heavy grazing and trampling loosened the soil and coarser subsoil materials which were moved down the slopes by gravity (fig. 12, A). Under conservative and light stocking there was little evidence of accelerated erosion or soil move- ment due to grazing even on the steepest slopes (fig. 12, B). EFFECTS ON THE SHEEP Heavy stocking affected the grazing habits of yearling ewes by forcing them to return to areas already too heavily grazed more often than they naturally would have done. This caused extremely heavy use on certain areas because there were fewer favored places to return to in the smaller pasture. Also, with less forage in the heavily stocked area, the yearling ewes necessarily spent considerably more time searching for forage than those on conservatively and lightly stocked range. Seasonal gains in weight averaged 32 and 33 pounds per head on the conservatively and lightly stocked ranges, and 31 pounds on the heavily stocked range. These differences were statistically significant when corrected for age and initial weight of the ewes. At the start of the grazing season the yearling ewes weighed from 70 to 77 pounds. Carry-over forage, together with a little green growth, was sufficient in all pastures to permit some gain during the first few weeks of each season, beginning in late March. This carry- over was confined to limited areas on the heavily stocked pasture but was available over most of the conservatively and lightly stocked pastures. An apparent loss of weight occurred at shearing time, usually during the third 28-day period, but this was followed by another period of rapid gain (table 10). By midsummer the choice forage was usually gone from the heavily stocked range and the yearling ewes gained less rapidly than earlier. The weight trends for the sheep grazed at the heavy intensity were similar to the trends for the others, but the tendency to lag at a somewhat lighter weight after midseason was noticeable. Weight gains usually continued with a —— — STOCKING NORTHERN GREAT PLAINS SHEEP RANGE 4 F-415231, 41524 FicureE 12.—A, This bank and talus deposit in the head of a small drainage in the sandy loam soil type resulted from too heavy grazing and trampling. B, Natural erosion, though evident on this steep heavy clay soil, was not noticeably accelerated by grazing and trampling under conservative stocking. some variations until late August or early September. After this date, a period of leveling off or even of slight decline in weight extended largely throughout September, but when there was ample green fall growth after late September or October rains, a noticeable gain occurred in all lots through late October or early November. Average final weights ranged from 101 to 109 pounds during the 5 years. CIRCULAR 804, U. S. DEPARTMENT OF AGRICULTURE o2 ‘potmod ABP-8z YAINOJ LO pALY OY} SULINp suUOp A[[BNsN sBM Sulresyg ‘