Historic, archived document Do not assume content reflects current scientific knowledge, policies, or practices. —— SS “22 4 9629 me? 2. | R2St2 SUSCEPTIBLE TO ATTACK BY THE SOUTHWESTERN PINE _ ~ f 3 ra PR h: oe AJBEETLE AND ASSOCIATED BARK BEETLES + / by Z a Donald A. Pierce ; " / SF AX \ ete Station Paper No. bay August 1961. — ws r / fo uf ROCKY MOUNTAIN FOREST AND RANGE EXPERIMENT STATION a" =< i —Z — —_ 2 = = Raymond Price, Director *_Fort Collins, Colora#de- fof ¢ TA = Ay, j $iD),.FOREST SERVICE, U. S. DEPARTMENT OF AGRICULTURE = United States Department of Agriculture NATIONAL AGRICULTURAL LIBRARY Advancing Access to Global Information for Agriculture ag \CLASSES OF PONDEROSA PINE IN NEW MEXICO AND ARIZONA SUSCEPTIBLE TO ATTACK BY THE SOUTHWESTERN PINE eat ual eae ASSOCIATED BARK BEETLES \v A poh >< by ae O Donald A. |Pierce, Entomologist Rocky Mountain Forest and Range Experiment Station! GlORNe aes N T S Page Methods of tests in Southwest MCC tE oe Meine = 02 ems 118) NO 4 Results e e e e } e e e e e ae e e es e e e e 4 Total mortality by tree class . . . . «6 « «© -« 7 Total mortality by vriskiclass. 3. «.« se. © « «) © aU Insect-caused mortality by tree classes oF Maret > 8 Insect-caused mortality by risk classes niet Mier tte 8 DISCUSS LON: 3) ie. aos Miowepyel Me one ele Osh UTIs Qe at. vero ine 8 cee mes, U.S.D.A.. NAL | Oy. | JUN 0 3 2008 | | CATAL OGING PREP | li Central headquarters maintained in cooperation with Colorado State University at Fort Collins. The study was completed at the Sta- tion's Forest Insect Laboratory at Albuquerque, New Mexico. CLASSES OF PONDEROSA PINE IN NEW MEXICO AND ARIZONA SUSCEPTIBLE TO ATTACK BY THE SOUTHWESTERN PINE BEETLE AND ASSOCIATED BARK BEETLES by Donald A. Pierce, Entomologist Bark beetle control in the United States is largely done by direct methods. These include: (1) Killing the overwintering brood by felling, peeling, and burn- ing the bark of infested trees; (2) salvage logging the infested trees from the woods, the wood is utilized, and the insects are killed in the refuse burner or mill pond; and (3) spraying either the standing or felled infested tree with insecticides. These methods are effective, but results may be temporary and not directed at the cause of the insect outbreak. An ideal way of keeping bark beetle populations under control would be by silvicultural methods based on a susceptibility classification system. The aim of the system is to sort the trees in a stand accorcing to their susceptibility to bark beetle attack. Trees classed as high-risk can be removed by a sanitation-salvage cutting that captures the loss and possibly prevents outbreaks. The success of the system is dependent on three things: (1) The species of bark beetles involved prefer trees of low vigor; (2) low-vigor trees can be recognized in the stand and their characteristics defined; and (3) the high-risk trees constitute a low percentage of the stand that can be removed without upsetting the ecology of the residual stand. Keen! in 1936 and Salman and Bongberg=! im 1942 developed systems that proved to be highly successful against the western pine beetle (Dendroctonus brevicomis Lec.) on the inland ponderosa pine stands of California and Oregon. Because of the similarity of the habits of the southwestern pine beetle (Dendroc- tonus barberi Hopk. ) to those of the western pine beetle, ind similarity of the pine stands, it was only natural that the methods be tested in the ponderosa pine stands of the Southwest. Such tests were started in 1952 when a Forest Insect Laboratory, a field unit of the Rocky Mountain Forest ge Range Experiment Station, was established at Albuquerque, New Mie sic or 2/ Keen, F. P. Relative susceptibility of ponderosa pines to bark-beetle attack. Jour. Forestry 34: 919-927, illus. 1936. 3/ Salman, K. A., and Bongberg, J. W. Logging high-risk trees to con- trol insects in the pine stands of northeastern California. Jour. Forestry 40: 533-539. 1942, 4/ Mortality plots were established by J. W. Bongberg and R. K. Bennett in 1953 and 1954. Keen's classification as modified by Thomeon for the Southwest used 4 age groups each of which is divided into 4 vigor classes resulting in a total of 16 age and vigor divisions (tables 1 and 2). The age groups are determined on the basis of d.b.h., bark color and surface texture, shape of the top, and the branching habit. The vigor classification groups trees into classes accord- ing to their relative rates of growth, from the best represented by A to the poorest represented by D. Size of crown and the abundance and condition of the needles are the best indicators of vigor. Table 1. --Description of Keen's age classes as modified by Thomson for the Southwest Character d Class 1 j Class 2 : Class 3 ; Class 4 Maturity Young Immature Intermediate - Mature -overmature mature Age Usually less than Usually less than Approximately 150- Approximately 225 75 years 150 years 225 years years and over Diameter breast Under 12 inches Seldom over 24 Usually less than Usually large high inches 36 inches Bark color Dark gray to Black to dark Reddish brown Reddish brown to black reddish brown shading to black yellow in the top Bark plates No plates, rough Ridges or very Moderately large Plates usually very bark, deeply narrow plates plates between wide, long and furrowed with between the the fissures smooth narrow ridges fissures between fissures Tops Usually pointed Pointed or slightly Usually pyramidal Usually flat and rounding; never flat or rounded, occa- making no further sionally pointed height Branches Upturned and Mostly upturned and Upturned in upper Mostly large whorls distinct whorls distinct for third of crown; drooping, gnarled upper half of crown, those in the middle or crooked; whorls flattening out with horizontal, and indistinct and less distinct whorls drooping in lower incomplete in lower half third of crown Salman and Bongberg defined four risk groups (table 3). Characters used in defining risk are concerned with the apparent health or vigor of the crown as evidenced by the foliage, twigs, and branches. Factors of age, crown form, and crown position do not enter into their appraisal of risk. As stated by Miller and Keene! the essential difference between the two systems is one of distinguishing inherent vigor (Keen's classes) from current health (risk ratings). 5/ Thomson, Walter G. A growth rate classification of southwestern ponderosa pine. Jour. Forestry 38: 547-553, illus. 1940. 6/ Miller, J. M., and Keen, F. P. Biology and control of the western pine beetle. U. S. Dept. Agr. Misc. Pub. 800, 381 pp., illus. 1960. Table 2. --Description of Keen's crown vigor classes as modified by Thomson for the Southwest Character Class A Class B Class C Class D Fair to moderately Fair to poor vigor vigorous Crown vigor Full, vigorous Crown length 55 percent or Less than 55 percent, Either short (from and width more of the but 35 percent or 20-25 percent of the total height more of height of the height of the tree, of the tree; tree, or a longer if foliage is of average width crown if narrow or average thrift) or or wider somewhat thin; either long, sparse and short wide crowns or narrow long narrow ones Foliage Usually very Usually thrifty, of Usually short and dense and full to medium from medium to thrifty, the density and of poor density; of individual average length normal length and leaves being density when of average confined to top length or longer third of tree Position Usually Usually codominant Usually inter - isolated or but often isolated mediate or some- dominant or dominant times codominant, but rarely isolated Diameter Large for age Above average for Usually below age average Usually of very poor vigor Less than 20 percent of the total height of tree; often quite thin and sickly Usually short and of poor to very poor density, very sparse and scattered or only partially developed Usually suppressed or intermediate or if dominant or codominant it is suffering from some vigor=-reducing ailment such as severe insect attack, lightning strike, or very old age Usually decidedly subnormal, but very old and damaged trees are often of large diameter Table 3. --Descriptions of Salman and Bongberg's risk ratings Risk rating Symptoms Risk I--Low risk Risk II--Moderate risk Risk III--High risk Risk IV--Very high risk Full-foliaged, healthy-appearing crowns. Foliage of healthy appearance, needles usually long and coarse, color good dark green. Practically all twigs with normal foliage complement. No weakened parts of crown. Fair to moderately healthy crowns, imperfect in spots. Foliage mostly healthy, needle length average or better, color fair to good. Some twigs or branches may lack foliage, but such injur, should not be localized to form definite ''weak'"' spots in crown. Crowns of fair to poor health, somewhat ragged or thin in parts of crown. Foliage in parts of crown thin, bunchy, or unhealthy; needles average to shorter than average in length; color fair to poor. Some to many twigs or branches lacking foliage, some to many twigs or branches fading or dead. Small localized weakened parts of crown usually present. Crowns in poor condition, ragged or thin, often showing evidence of active insect infestations in upper parts. Foliage thin or bunchy, needles short or sparse, color poor. Twigs and branches dead or dying, parts of crown definitely weakened. Active top-killing or partial infestations often present. METHODS OF TESTS IN SOUTHWEST During the 1953 and 1954 field seasons, forty 10-acre plots were estab- lished in virgin ponderosa pine stands in Arizona and New Mexico. Table 4 gives the plot locations and information on the stands. Figure 1 shows a typical plot and how the trees were numbered. Table 4. --Summary of plot locations and stand characteristics beehin toare 3 lOwaere Volume per acre Trees per acre plote Lowest i Highest : Average : Lowest : Highest : Average Number ---- Boardfeet ---- = ----- Number - - - - - Navajo Indian Reservation 20 4,197 16, 067 8,914 9.9 40.2 21.4 National forests: Apache 7 5,451 11, 966 8,429 15.5 39.3 26.4 Kaibab 4 17, 293 19, 274 18, 225 37.0 46.0 39.5 Santa Fe 3 4, 828 22,521 13, 496 24.8 33.6 30.0 Sitgreaves 4 6,765 17,955 12, 388 17.4 34.9 26.6 Coconino 2 9, 684 12, 243 10, 963 24.9 36.2 30.5 Plot boundaries were marked with aluminum paint and each ponderosa pine tree 11.6 inches d.b.h. and over was numbered. Each tree was rated by Keen's Tree Classification System and also by Salman and Bongberg's Risk- Rating System. In addition, the d.b.h. height and volume were obtained for each tree. The plots were examined each year from 1956-59 by a crew of three men to determine the amount of mortality caused by the southwestern pine beetle and associated bark beetles. RESULTS During the 5-year period of the study, 223 trees died on the plots. Bark beetles alone killed 126 trees (tables 5 and 6); lightning, wind, and pathological agents accounted for the remainder. In volume, total loss amounted to approximately 119, 000 board feet of ponderosa pine timber on 400 acres during the 5-year period, an average of nearly 60 board feet per acre per year. The bark beetle-caused loss amounted to approximately 66, 000 board feet (tables 5 and 6). The basis for the susceptibility of a class is the percent of trees killed in the class. In making a selective cut to remove expected mortality from a stand, it would be best to select trees in classes that sustain a high percent of loss and contain a small percentage of the total living stand. Navajo --A typical plot with trees numbered with aluminum paint. Figure 1 Indian Reservation, Arizona. Table 5. --Insect-caused mortality over 5-year period grouped by tree classes Portion of ' : Portion of ; * Portion vol- * Portion of 1 Live and : Q pri * : Volume : : Tree class stand by Dead trees © risk class ume loss total vol- :deadtrees : .. : 3 : Ios £5 : risk class ; i dead i . inclass _ ume loss Number Percent Number Percent M b.m. Percent Percent HIGH RISK: 4D 90 0.9 14 15.6 8.2 14.8 12.4 3D 405 39 26 6.4 O5 9.4 14,4 2D 152 Wee} 4 2.6 1.0 6.4 ile 5 1D 7 sol 1 14, 3 0 0 0 4C 461 4.4 14 3.0 iG 3.4 17.0 3C 1, 658 15.9 Sil 1.9 14.8 Coe 22.4 LOW RISK: 2C 1, 187 11.4 10 0.8 1.3 of 2.0 1C 78 8 1 1.3 20 6 ol 4B 731 7.0 9 aye, 9.6 1.4 14.5 3B 1, 868 17.9 8 4 5.8 oy) 8.8 2B 1,475 14.2 3 674 6 G2 09) 1B 180 Ie 0 0 0 0 0 4A 347 S68 2 55 2.6 3.9 3A 704 6.8 3 4 1.4 a8} Po i 2A 923 8.9 0 0 0 0 0 1A 146 1.4 0 0 0 0 0 a ee Total or average 10, 412 100.0 126 U2 66.0 Ne '7e 100.0 rr rrr 1 Categories of high and low risk as defined by Keen (see footnote 7). 2 50 bd. ft. loss in this class. Table 6. --Insect-caused mortality over 5-year period grouped by risk classes 2 Portion of ' * Portion of * ; Portion vol-' Portion of 3 : Live and : : Eee : Volume =: : Risk class stand by Dead trees risk class ume loss total vol- : dead trees : 3 g : : loss So ers B risk class © ‘ dead ; . in class , ume loss Number Percent Number Percent M b.m. Percent Percent 4 241 Zed 38 15.8 18.3 17.9 Cithetts 3 817 7.8 24 2.9 16.0 4.6 24.3 2 3, 183 30.6 41 1.3 20.2 5) 30.6 1 6,171 59.3 23 4 Niles) 68) 17.4 Total or average 10, 412 100.0 126 liv 66.0 Ned 100. 0 Cumulative risk class 4 241 Ze3) 38 15.8 18.3 17.9 27.7 4+ 3 1, 058 10.1 62 5.9 34.3 (uskO 52.0 4+ 342 4,241 40.7 103 2.4 54.5 25 JI 82.6 TOTAL MORTALITY BY TREE CLASSES Table 7 is a summary of the total mortality data by each tree class. Classes 1C and 4B were placed in the low-risk category even though they showed a fairly high percentage of class killed. Had the study been more extensive and continued several more years, these classes would probably have been in the low-risk group. Table 7. --Mortality by all causes over 5-year period grouped by tree classes * Portion of ' * Portion of * beorton vol="" Portion of Q F : : 7 wWolume a: : Tree class! Eivevends stand by ~~ Deadtrees ~ risk class 1 ume loss ~ total vol- si ideaiditrees! js!) os 5 : : Oss Bg 8 ‘ riskclass | “dead : . inclass ~ ume loss Number Percent Number Percent Mb.m. Percent Percent HIGH RISK: 4D 90 0.9 22 24.4 14.9 27.0 W255 3D 405 3.9 41 10. 1 12.4 L204 10.4 2D 152 Nas) 7 4.6 M74 fiche: 1.0 1D 7 5 il 1 14, 3 20 Bi3 0 4C 461 4.4 30 655 24.7 7.6 20.8 3C 1, 658 NEG) Bi) Saul fail best 3.03 18, LOW RISK: 2C Ly LS 7; 11.4 16 IN} 4.0 ey 3.4 1c 78 at Zi 6 wl Meal ae) 4B 731 to) 20 enh 20.4 Sa trees 3B 1, 868 17.9 15 8 10.3 1.6 8.7 2B 1,475 14.2 6 4 4 aie oie 1B 180 tent! 1 ots .6 4.8 ce) 4A 347 353 6 EAT? 6.9 1.8 5.8 3A 704 6.8 3 4 1.0 oo .8 2A 923 8.9 1 6 dl se are 5 1A 146 1.4 0 0 0 0 0 ee ee Se ee ee ee ed ee Total or average 10,412 100.0 213) Zak 118.8 360 100.0 1 Categories of high and low risk as defined by Keen (see footnote ti) g & Yi 2 50 bd. ft. loss in this class. Of the total stand involved in the study, 26.7 percent fell into the high- risk category. During a 5-year interval, approximately 74.9 Mb.m. or 63.0 percent of the total volume loss occurred in this group. TOTAL MORTALITY BY RISK CLASSES Table 8 is a presentation of the total mortality data by the risk-rating system. Risk class 4 contained only 2.3 percent of the green stand, but 25.6 per- cent of the volume loss, amounting to approximately 30.4 Mb.m., which occurred during the 5-year period. Risk classes 4 and 3 combined contained 47.6 percent of the total volume loss or approximately 56.6 Mb.m. in only 10.1 percent of the living stand. Table 8.--Mortality by all causes over 5-year period grouped by risk classes Li Be ; Portion of : ; Portion of d Valurse ‘ Portion vol- * Portion of Risk class i Be “standby ‘ Deadtrees * riskclass ° “ume loss ~~ total vol- :deadtrees : _. fs g is loss Abas . i * risk class A a dead i . in class _ ume loss Number Percent Number Percent Mb.m. Percent Percent 4 241 2.3 BM 23.7 30.4 29.8 25.6 3 817 7.8 47 5.8 26.2 To 22.0 2 3, 183 30.6 67 (oi ° 36.9 2.8 Shale al 1 6,171 59.3 52 8 25153. ere (Alles) Total or average 10, 412 100.0 223 Zeid 118.8 3.0 100.0 Cumulative risk class 4 241 2 57 OSS 1 30.4 29.8 25.6 4+ 3 1, 058 10.1 104 9.8 56.6 12.7 47.6 4+34+2 4, 241 40.7 171 4.0 93:5 5.3 78.7 INSECT-CAUSED MORTALITY BY TREE CLASSES Arranging the insect-caused mortality by tree classes (see table 5), 44.7 Mb.m. of the volume loss fell in the high-risk category. These classes would isolate 67.7 percent of the volume loss caused by bark beetles from 26.7 per- cent of the stand in the 5-year period. INSECT-CAUSED MORTALITY BY RISK CLASSES Risk class 4, with 2.3 percent of the living stand, sustained a loss of 17.9 percent of its volume and 27.7 percent of the total volume loss due to bark beetles (see table 6). Risk classes 4 and 3 combined accounted for 52.0 per- cent of the volume loss (34.3 Mb.m.) in 10.1 percent of the living stand. DISCUSSION cen tested the two methods of tree selection in a study in Oregon. The results of the present study were similar to those reported by Keen. In the following tabulation the two studies are compared on the basis of bark beetle-caused mortality only. The comparison shows the percentage of trees killed and percentage of the living stand in the high-risk category: 7/ Keen, F. P. Ponderosa pine tree characteristics indicative of high risk to pine beetle attack. U. S. Forest Serv., Calif. Forest and Range Expt. Sta., Prog. Rpt. (1938-52). 50 pp. 1954. [Unpublished report. ] Portion of tree Portion of green in high tand in high Rating method joss ip beh as ee 8 risk classes risk classes (Percent) (Percent) 8 Keen's tree classes:— Oregon 66.8 34.8 Arizona and New Mexico 9/ (ot Zoe Salman and Bongberg's risk classes 3 and 4: Oregon 65.5 19516 Arizona and New Mexico 52.0 OER It appears the identification of susceptible trees was better in the Arizona and New Mexico study than in the Oregon study. It must be kept in mind, how- ever, that the Oregon study lasted 10 years. If the Arizona and New Mexico studies were continued, a larger percentage of the mortality would come from the lower risk classes. It appears from the data obtained in the foregoing study that both methods -- a marking system based on Keen's Tree Classification as modified by Thomson, and Salman and Bongberg's Risk-Rating System--can be adapted to marking ponderosa pine stands in the Southwest. g/ All D crowns and classes 4C and 3C. 9/ This study used Keen's tree classes as modified by Thomson (see footnote 5). Agriculture --- CSU, Ft. Collins a 9 2 10225 00833