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Ecological types of the upper Gunnison Basin : review draft PDF

548 Pages·1997·228.7 MB·English
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iin | LIBR Barry C. Johnston, Ecologist REVIEW DRAFT May 1, 1997 USDA Forest Service USDI Bureau of Land Management Grand Mesa-Uncompahgre-Gunnison National Forests Gunnison Resource Area 216 N. Colorado St. 216 N. Colorado St. Gunnison, Colorado 81230-2197 Gunnison, Colorado 81230-2197 (970) 641-0471 (970) 641-0471 Habitat Partnership Program Colorado Division of Wildlife Gunnison District 310 West New York Ave. Gunnison, Colorado 81230 (970) 641-0088 eeOel e ee AYO4IY fé)f rat ; Barry C. Johnston, Ecologist REVIEW DRAFT May 1, 1997 USDI Bureau of Land Management USDA Forest Service Grand Mesa-Uncompahgre-Gunnison National Forests Gunnison Resource Area 216 N. Colorado St. 216 N. Colorado St. Gunnison, Colorado 81230-2197 Gunnison, Colorado 81230-2197 (970) 641-0471 (970) 641-0471 Habitat Partnership Program Colorado Division of Wildlife Gunnison District 310 West New York Ave. Gunnison, Colorado 81239 (970) 641-0088 Let them read the titles! Every plant has a story to tell about its environment, Martin Luther’s lawyer, at the Diet of Worms ° especially soil conditions... This story or indicator significance, is of great help in As I did stand my watch upon the hill, interpreting conditions over an area I look’d towards Birnam, and anon, as well as in utilizing the land to its fullest extent. Methought, the wood began to move... Herbert C. Hanson, 1929 William Shakespeare, Macbeth, Act 5, Scene 5 Ecology is not to be regarded as a specialized field In the administration of the National Forests the aim is comparable to physiology or morphology or even zoology, to convey to the greatest possible number the full benefit of botany, or geology, but as a point of view and a plan of all the resources which the Forests contain and at the attack. same time to perpetuate those resources by regulating Frederic E. Clements, 1935 their use. James Jardine and Mark Anderson, 1919 The natural plant communities are not merely the best integrators of the effects of climate and soil, but Every plant is an indicator. This is an inevitable axiomatically they are also by far the best judges of these conclusion from the fact that each plant is the product of two complexes in terms of plant production. the conditions under which it grows, and is thereby a Frederic E. Clements, 1935 measure of these conditions. ... The question of species and community values is much simpler than appears at Who among these overland voyagers could have dreamed first. Itis not a matter of employing one to the exclusion that within a few short decades other settlers would of the other, but of taking advantage of their engage in fierce wars among themselves for possession of complementary relation. There can be no doubt that the this “desert” land; how could they have guessed that this community is a more reliable indicator than any single land would produce five times more wealth for the Nation species of it. ... The community not only affords a better through the pasturage of livestock than all the gold they norm for the major indications, but it is likewise, so to would dig out of the earth with their picks and shovels? speak, more finely graduated and hence more sensitive, Richard E. McArdle and David F. Costello, 1936 owing to the fact that no two of its dominants or subdominants are exactly equivalent. It is also a better The general correlation between indicator of the whole habitat, since it levels the plant succession stages and range condition would variations from one point to another. frequently not hold true were forage production Frederic E. Clements, 1920 (pp. 28-30) as reflected by floristic composition used as the sole criterion for determining condition. Each [geographical area] is a complex of climax and R. R. Humphrey, 1947 developmental habitats of varying rank and extent, each controlling a plant community which serves as the Since simple correlations [between climate, soils, and indicator of it. vegetation] in small areas are of little or no value for Frederic E. Clements, 1920 (p. 39) general use, it follows that vegetation and soil maps can be constructed only by direct observation. There are no It is a simple matter to trace the line of 20 inches of short cuts - unless one knows all the independent rainfall, or the 60 per cent ratio of rainfall to evaporation variables. and to assume that it marks the line between prairies and N. C. W. Beadle, 1951 plains. Such an assumption reverses the proper procedure, in which the associations themselves must be permitted to indicate their respective climates. When this The most significant biogeographic classification of the has been done and the limits of the various communities land surface is that based on climax conditions established, it will be possible to determine the correlated exclusively. One important fact that supports this factors. conclusion is that seral communities are not well Frederic E. Clements, 1920 (p. 40) organized. Rexford Daubenmire, 1952 When the relation between the silvicultural characteristics and the physical factors which affect tree One can, with knowledge of the ecology of the plants growth and the correlation of increment with the which are growing there and the climate, make a good associated shrubby and herbaceous species are better estimate of the moisture regime. The correlation between understood, the different sites may be regarded as the vegetation and climate is generally pretty good. integral biological units which the administrator can use Guy Smith, 1981 an a basis for the rational organization of his forest. Clarence F. Korstian, 1920 A soil classification or map is not an ecological classification if the relationship of the classes to the vegetation of the area is unknown. Similarly, a vegetation map is not an ecological classification unless the interrelationships between the vegetation types and the environmental factors is known. Barnes, Pregitzer, Spies, and Spooner, 1982 il TABLE OF CONTENTS CHAPTER PAGE Ae EDA YG a aterscenel.. Gee eet Aaa MEME ee, Ee Mc PD Ini. sasscscorernsencscnesoieMitvncanseasennne l CE MANU CMAAUCT LONI Lae ee, UTM ate ee Eo Besa os cnc snsec annon nade ven iQdeeind heim, Meliat LBRUA varcee ee. 3 Dapuueory One colosical Classification.,..\..,.1.4 eure A 8s 4 PACINO OM ENG CaSO ASU Macs «1, ites sic ert re oott cee c ce eee 10 DY Coetaulon OMthie Gamison Basin 198... SERA lee cccearoceoe racseneteé povgteoelensonseseoanns ze Descriptowor Major Plant’ Species 3... Fi, AR, A eas AEE IN ne 21 BATRCES Wi ROT Me. 4. i a TE Ee MR 22 Joo) ee oi AG Oa RR LATE RR AR A nl a nee a 26 Ky STATE MO MO... achasedeates AMUSO ete NT, DUR Ie AE 44 LE POTS 2 25ic ceive <saden MO a. AIEEE, Ree eee ten ene) SIE 61 Weeds, Introduced Plants, and Poison Plants .................cccccccssecssssesseceesceeceseeseceeeecess 716 asuvasivePiants and Poison Plants). en ee eee ee ee vos PRL OOOO. PE secioas tone snnlsaiisbal sc vas mansnipreacamiiecaiian nicenimensioreesees 82 6. SoilstandGoil- Vegetation Correlation Cae a OG Wa atieledeaaabvecs oh. 7s Methods Used fo ield Data and-Analysis’.:... Seo aa a eM ne eee 94 8. Keys to the Ecological Types and Community Types ...............0ccccccccesssscceesseessssesseeees 98 mK ey loscolopical Types & .2.h R eR en e 98 OC OMIT TPTy pe Sy, rite ee. ee eee ee ve wag ne 106 OU oesctipUuol.ol the REGlopicadl TYPES ..2..4..20.5. 2: ee ee ee 139 DAR OCKky MOUT(aIPTUNIPer Series | ee ee rere ee veccsentesacsectercesns 146 PRP ONUCEOSA INCI CHICA IR ANH Lyon, skenacuslcosennessnr sonkguabeccagmssfpieniesoiarnnyeasnvbaetisen 150 SrBristiccone Pine Series ates... Peek Both i open EO dh) al Beene 165 a. Dlucwpruice Uplands Series 3 f.....20.).. 7: iy Bune Behe We 171 5 AOOUSIAS-FAPISCHICS te Me coh da Me tee eee eerie eth saetirttesen 178 DPLOASCDOIE PING SETICS i. oi. hisccstadc Pe oe LE APU en izes 204 faoubalpine-bir-Douglas-Fit Series |. 8.0 eee eee eee e eer ctsdsnsncepédcens 217 8a. Subalpine Fir-Engelmann Spruce Series (Tall Forests) ............000.ceccscsccseseeeeees get 8b. Subalpine Fir-Engelmann Spruce Series (Krummholz, Wind Deformed, Alpine Ecotone Forests) 27. Ne tetes iris cee- cs toteonersosscsteccseoees 243 SOSLAMPEE PING OCTICS 3h. Vas Gets ces eee re et crete hat miaetecu te teett erties. 247 TOPASDEIVDCIIES cen rete cicks chat ve eee ne ttt tee Meee stat marc octecteattere nse. : 250 LlgNarrowleat Cottonwood Series: hc. nceterret ere es cecetetetenctrtetirettesssesestetseters 270 12. Blue & Engelmann Spruces-Subalpine Fir Riparian Series...............0....:cccccceees 279 DO MCLIOU MW TIO Wier icSe meri ey tteaek i tune ety Re ME a) ape waatu ate 292 14. Blue Willow-Serviceberry Willow-Booth Willow Series.................c.:ccccsesseeeees 303 15. Planeleaf Willow-Wolf Willow-Bog Birch Series ..................ccccessccccseesssseseeeees 315 16. Grayleaf Willow-Barrenground Willow Series .................ccccccsssccceeeeessssseeeeeeeees 329 MEW DIED EG CC CE IOSIM oun ate ene CG Dso o CUREN oat d) besub stodary doues head vationd albensuaas sna cima 333 18. Indian Ricegrass-Needle-and-thread Series ...............ccssccccccssessssccessessserseceseeses 340 RATIO Tea PIC SCUC SHC IICS er arn ent ain arcs den sks amredirty tek vexsecdsab cet cews ye sshth vesaee 346 See MULT eke COGIC SSET ICS arene ert MnP, Core cs tocthcucnstraes cca nerteapuoasinnsstnsvvetsen 355 SARL tee LLCS morad ens maNeRts GeO LL eth N uty Hol MEER AAS FN enascc iacusind Raubacuat nested 369 IAD OSC HerC LG etre eee ee Ray Bieeeatn en annie, ha Tle Sys ccatcaulies 374 Po eRA IDS rC IALP TASS SCL carr thse HURL et ies Hany Wide Vile aun ay Meu Gd ati ep iuaae s paceneats 37 DAPI DIE AERCT A GS SCEIOS Keres toy rt snes ens tne eeagact ra alney ocean <a hecde Saaenvpemmvereomes 380 25. Utah Serviceberry-Saskatoon Serviceberry Series ..................ccccessesssssssceeeeeeeees 382 POP ROCKY Valle MIOLAINS SOLHOS ey atl Nidan see tavi es aes nq oaticciaeXerteea lean seuneneornenndaYavuadts 407 Pe eA VOLT sS L APCOTUSH MCT ES ot coera tts ween sre cot acai s tersta nndaeSonadgnaonmi bneeeonnenkey « Sk4 10 AAR CRA IMC OPIGIL OCLICS Oy eer tactile ya shed. & ced aetna say aeousnuy aden ievovewsanbobcaavays aus4 21 29. Big Sagebrush-Antelope Bitterbrush Series ...........0:0.:ccccsssssssscsssoesnssnnseseceseenens 428 SU WIOUNtAIIY ELD PARCOLUSIE SETICS 0.5 ,cecssiosteus cs ieasae ied ie Wiech iacseeesede<ocsnarguecinsdtavaens 449 SOW I eCOLII SSCS tee iy tet yet rere tn scree surance taudliy baatndelesmaasasten sas 461 Gee MoU WEA ORIELISI D RTLO S carly scanietaiecs cane trvitas chee naan cea aN es Spasnacainteccestonldeanc e 468 Appendices ASPlaatspecies of the Upper Gunnison. Basin 2 c...cj2ii..sessnsieesiatessoravscnaseouseanssntens 472 B. Soils Mapped and Sampled by Ecological Type ...................ccccccccseeeesssessssereees 487 COONS VET As OTLE AAUIONIS ie Fae citn sey aesdey chgats Teiwrstat anes Meeroha abe tnduchud fesucutieakess 518 TARE LES ee eM aes Tene eeu, dak rsh bch Smastatk sskdend orc evs Mobiansanetecasintecanisemusciens 523 Bee Wicca LANL URECLICS yo phtea Leryn ss sou esdaterronp toast sek aniseidhescoiisdoikachcesiveawtoernhoden 538 ee Me EM er ae Ota cet cduic) 9 Coe Hint ka ecm oseandaas Module dadeles brokSuiuioa nviiewes 540 ili ACKNOWLEDGEMENTS My heartfelt thanks to those wise, visionary resource Special thanks to Gay Austin, Art Hayes, and Sandy Hayes, managers who were willing to allow the time and resources to my “techno” partners in this HPP project. They have done it all finish this: Steve Marquardt, Bob Storch, Jim Dawson, Miles — advise, counsel, procuring vehicles, selling the program to Hemstrom, Barry Tollefson, and Elizabeth Estill. Special thanks agency people and outsiders alike, coming up with funding have to go to Craig Whittekiend, whose idea this was all along — when most needed, helping with field sampling, it goes on and he guided it through the first, critical half. on. You three are the sine qua non of this classification, valued The partners in this project — Forest Service, Bureau of Land friends. Management, and Colorado Division of Wildlife — have stuck Technical advice was kindly given by Dave Wheeler, Terry with it to the end, and been most gracious in allowing me to Hughes, Floyd Reed, and Art Haines. finish this project. Arden Anderson set up and supported a trip into the The members of the Gunnison Habitat Partnership Powderhorn Wilderness that Joe and I will never forget. Beulah Committee had the foresight to support this classification. The (Kathy) Kelly, Peggy Dobie, and Peggy Schick have been non-agency people on the HPP committee have shown friends and helpers. remarkable foresight, even though they are ranchers and Vera Komarkova kindly allowed the use of a few of her sportsmen. Especially important to me were the agency samples from the early 1980’s. members of this committee, Bill Wallis, Mark Hatcher, and Joe The interagency-plus-the-public spirit, “we can get it Capodice. You have always been there for me, and I appreciate done if we work together for the good of the public” attitude it greatly. shows abundantly in the way all of you have supported this I have had the pleasure of working with some excellent field classification. This surely is the future, working together for crew persons, from whom I have learned a great deal. The a common goal. Thanks very much! biggest credit goes to Joseph (Joe) Pecor, one of the best field God bless you all! people around — he’s an ecologist in the best sense of the word. His commitment, hard work, humble attitude combined with a high degree of technical ability, and ability to think critically about science, makes him a special person. Thanks, Joe! Kim Parker deserves special credit for commitment way beyond what was needed, quality work, and a lot of sweat and extra time, during the critical 1994 year. Other field people have been Les Choy, Ed Mauch, Suzanne Parker, and Duane (Ken) Kenlon. iv Chapter 1. Summary 1. A classification of the ecological types of the Upper 4. The potential riparian types in the Upper Gunnison Basin Gunnison Basin has been completed. Between 1982 and 1995, are: we took data about the vegetation and soils at 978 points yellow willow, Salix lutea throughout the Upper Gunnison Basin. The result is a blue-serviceberry-Booth willows, S. drummondiana-monticola-boothii classification of 74 Ecological Types grouped into 33 Series. In planeleaf-Wolf willows, S. planifolia-wolfii some cases, the Ecological Types were subdivided into Phases; grayleaf-barrenground willows, S. glauca-brachycarpa water sedge, Carex aquatilis there are 148 of those. Each Ecological Type represents a blue spruce, Picea pungens! balanced combination of potential vegetation, soil, landform, subalpine fir-Engelmann spruce, Abies bifolia-Picea engelmannii' geology, climate, and water. Each Ecological Type is mappable. narrowleaf cottonwood, Populus angustifolia* Therefore, each Ecological Type is a significantly different 5. The non-riparian potential grassland and forbland types in regime for natural resource managers. the Upper Gunnison Basin are: 2. Each Ecological Type is represented by one to many Indian ricegrass-needle-and-thread, Stipa hymenoides-Stipa comata Community Types, which are groupings of current vegetation Arizona fescue, Festuca arizonica Thurber fescue, Festuca thurberi within the limits of that Ecological Type. osha, Ligusticum porteri 3. The potential forest types in the Upper Gunnison Basin are Idaho fescue, Festuca idahoensis (plant species names are listed in Appendix A): timber oatgrass, Danthonia intermedia Rocky Mountain juniper, Juniperus scopulorum purple pinegrass, Calamagrostis purpurascens ponderosa pine, Pinus ponderosa 6. The non-riparian potential shrubland types in the Upper bristlecone pine, Pinus aristata Gunnison Basin are: blue spruce, Picea pungens' Utah-Saskatoon serviceberries, Amelanchier utahensis-alnifolia Douglas-fir, Pseudotsuga menziesii rocky tall shrublands, dominated by Holodiscus dumosus, for example lodgepole pine, Pinus contorta Wyoming big sagebrush, Artemisia tridentata ssp. wyomingensis subalpine fir-Douglas-fir, Abies bifolia-Pseudotsuga menziesii black sagebrush, Artemisia nova subalpine fir-Engelmann spruce, Abies bifolia-Picea engelmannii' big sagebrush-antelope bitterbrush, A. tridentata-Purshia tridentata subalpine fir-Engelmann spruce timberline Krummholz mountain big sagebrush, Artemisia tridentata ssp. vaseyana limber pine, Pinus flexilis low sagebrush, Artemisia arbuscula aspen, Populus tremuloides silver sagebrush, Artemisia cana narrowleaf cottonwood, Populus angustifolia” 1. Includes both riparian and upland types. 2. Riparian types only. e mY >V Redstone Nae | o ee al : | oe x ie Py Ge . i To| amasLs ,i ice § P“a- N raned)i waleagy ALUN ese a tee 14265 ; Fissidies( slhee? , otn e gasm a trQetsy “uAtaC r ‘ HoK Napes T : de ar aTAaYRL OR PARR aia . aDC atT—onePoades s. 14196 : 2 , <P) Sse GN] ae ; ( . at Ww He RSIS -. A iB —< l fi Trias WA : | ee ales ineB OO Peu ai se ate Map I. The Upper Gunnison Basin (UGB). Chapter 2. Introduction The geographical scope of this classification is the area in the Goals of this classification include: upper main (south) fork of the Gunnison River, bounded on the 1. Construct a classification based on a limited number of samples of south and east by the Continental Divide, on the north and vegetation and soils, to meet resource management needs at the northwest by the hydrographic divide with tributaries of the project level. Project level includes activities such as wildlife habitat improvement, range allotment planning, management, and upper Colorado River. The western boundary is drawn to include improvement, timber sales, wildlife-livestock habitat analysis, the whole watersheds of Big Blue Creek and Curecanti Creek, road and trail management, and dispersed recreation tributaries of the Gunnison River below Blue Mesa Dam. This management. area includes most of Gunnison County (County Seat in . Classify all Ecological Types in the area covered, including Gunnison), and parts of Saguache County (Saguache) and riparian areas and wetlands, grasslands, shrublands, coniferous Hinsdale County (Lake City). This area includes all of the forests, deciduous forests, and cultivated areas. The only areas not following watersheds (see Map 1): yet classified are alpine areas, above timberline. ’ East River . Enough ecological types will be described to meet normal project Taylor River needs. Quartz Creek . The classification is to meet the needs of the Gunnison Basin Tomichi, Quartz, and Cochetopa Creeks Habitat Partnership (HPP) Committee. The classification is to Ohio Creek provide information that will assist the HPP in resolving several Beaver, Steuben, East Elk, Red, West Elk, and Soap Creeks key questions: South Beaver Creek a. What action should the HPP Committee take to resolve Willow Creek livestock—big game conflicts? Cebolla Creek b. What action should the HPP Committee take to reverse the Lake Fork of the Gunnison River downward trend in sage grouse populations? Big Blue and Pine Creeks . The classification is to sample relatively few sites. The Curecanti Creek classification is to be coordinated with an independent inventory The area covered by the classification includes about 2.5 effort, which will be focused on areas of priority concern to the million acres, of which about 1,280,000 acres (51%) is National HPP Committee. Forest, about 585,000 acres (24%) is Public Lands administered . The classification is to cover all lands within the Upper Gunnison Basin, insofar as permission and cooperation permit. by the Bureau of Land Management, and about 40,000 acres . The classification is to produce a published product that can be (2%) is in the National Park System. Private lands, State lands, used by all those engaged in natural resource management in the tribal lands, and municipal lands make up the rest, about 23%. Upper Gunnison Basin, whether they are public or private. . The classification is to use standard, interagency sampling methods. . The Ecological Types will be designed to meet the following criteria: a. Ecological type definitions and descriptions will be balanced among the primary ecosystem components: potential (climax) vegetation, soils, geology, water, and landform. Other components, such as climate and animal populations have been added as needed. b. Each ecological type will represent significant differences in management potentials, responses, and effects, from other ecological types. c. Potential vegetation is classified using climax concepts (Daubenmire 1952-1976, Meeker and Merkel 1984). Ecological Classification Chapter 3. Theory of Ecological Classification 1. Classification Classification is the process of putting objects into classes. 1982, Moir and Ludwig 1983). The habitat type method uses The process of classification is usually logical, sequential, and (and further refines) concepts of dominance, climax, and the yields classes that are discrete, that is, non-overlapping. A indicator plant method developed by the great American classification can be artificial or natural. ecologist, Frederic Clements (1916, 1920). The habitat type Each class is defined by stated key characteristics; the key method is a vegetation classification, from which conclusions characteristics may well be different for each class. Thus, the are then inferred about soils, landforms, and management process of classification can be broken into several subprocesses, implications for each of the defined classes (habitat types). that may nonetheless be going on at the same time: Soil Survey classifies land according to the soils currently 1. Selection of objects for classification found there, by designing soil map units. These soil map units 2. Delimitation of outer boundaries of classification are made up of combinations of soil taxa that usually are defined (geographical, taxonomic, etc.) according to the standard USDA soil taxonomy (Soil Survey . Determination of goals and priorities for classification Staff 1975-1996). The soil survey method is a soil inventory S.W D etermination of necessary facts to know about each based on a soil classification, from which conclusions are then object inferred about vegetation that occurs on the land, and am Gathering data about objects, field sampling, interpretations for management for each of the defined classes measurements (soil map units). . Mathematical analysis of data The habitat type classification and the soil survey are . Inferring key and diagnostic characteristics for classes different classifications and inventories, which often are applied loao n . yD efinition and design of classes based on data and to the same areas of land, but for different purposes. Both analysis of data methods work within limits (the contexts and assumptions 9. Description of classes within which they were done). Both methods are special purpose Inventory has the task of finding out quantities of resources methods. Both methods make claims to validity as being that are present at each location within an area. Therefore, ‘ecological,’ but both fall short of being an all-purpose tool for inventory, which often includes mapping, is different from resource management. I will give a few examples of how these Classification. Classification samples from a small fraction of fall short: sites, then defines classes based on that limited sample. 1. Habitat type classifications usually do not have enough Predictions are made about what future sites, yet to be sampled, management information for soil-based resource management, might contain. Inventory, on the other hand, deals with reality such as amount of coarse material in the soil or interpretations more directly, and deals with every site in the area being for road cuts or other constructed facilities. inventoried. Some kind of inventory is usually necessary for 2. Normal soil surveys usually are insufficient for predicting almost every resource management project. However, inventory timber site quality for normal silvicultural activities (Carmean 1961). is relatively expensive, because every site must be looked at; so 3. Habitat type classifications typically do not sample soil the amount of inventory must be kept to a minimum to be characteristics sufficiently to allow resource managers to make efficient. I hope that, with this classification in hand, resource their own interpretations. Some habitat type classifications do managers will be enabled to restrict the amount of direct not sample soils at all. inventory they must do, and so save money and time. 4. Soil surveys usually contain little or no information on certain Taxonomy is the process of defining classes and naming critical factors to resource management, such as tree them. Taxa (singular, taxon) are the classes themselves in regeneration or community succession. general. Examples of common taxonomic classifications include 5. The productivity estimates in soil surveys (both for forage and plant species classifications (for example, Barneby 1964), trees) are not specific enough for many resource management projects. animal species classifications (Armstrong 19xx), soil 6. Most of the older habitat type classifications do not have classifications (Soil Survey Staff 1975, 1994), habitat type information about riparian areas, or else it is insufficient for classifications (Pfister and others 1977, Hess and Wasser 1982). modern management. The last two classifications focus on classification of land for 7. Most of the older soil surveys do not have information about management — also the focus of this project. riparian areas, or else it is insufficient for modern management. Habitat Type Classification is fundamentally a vegetation With these failings in mind, I believe that what is needed is a Classification, that classifies land according to the several general-purpose classification based on ecological principles. dominant species on the land at the last seral stage — climax, Ecosystem components (such as potential vegetation and soils) that is, the last progressive stage in natural vegetation should be weighted equally and given equivalent roles in development (Daubenmire 1952-1970, Poulton and Tisdale constructing the classification. 1961, Daubenmire and Daubenmire 1968, Pfister and Amo

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