A Comparative Study of the Vegetation of Grazed and Ungrazed Canyons of the Wasatch Range, Utah Author(s): Walter P. Cottam and Frederick R. Evans Reviewed work(s): Source: Ecology, Vol. 26, No. 2 (Apr., 1945), pp. 171-181 Published by: Ecological Society of America Stable URL: http://www.jstor.org/stable/1930822 . Accessed: 06/07/2012 08:52 Your use of the JSTOR archive indicates your acceptance of the Terms & Conditions of Use, available at . http://www.jstor.org/page/info/about/policies/terms.jsp . JSTOR is a not-for-profit service that helps scholars, researchers, and students discover, use, and build upon a wide range of content in a trusted digital archive. We use information technology and tools to increase productivity and facilitate new forms of scholarship. For more information about JSTOR, please contact support@jstor.org. . Ecological Society of America is collaborating with JSTOR to digitize, preserve and extend access to Ecology. http://www.jstor.org A COMPARATIVE STUDY OF THE VEGETATION OF GRAZED AND UNGRAZED CANYONS OF THE WASATCH RANGE, UTAH 1 WALTER P. COTTAM AND FREDERICK R. EVANS Universityof Utah, Salt Lake City, Utah CLIMATIC, PHYSIOGRAPHIC, AND GEOLOGIC FEATUREIS INTRODUCTION' The past twodecades have beenmarked by intensifiedgovernmentaleffortsin rangerehabilitation. These efforts have been handicapped by lack of definiteinformationabout the pristinenature of grazed lands as well as about quantitative and qualitative changeswhichgrazing has doubtless induced in the plant cover. The meagernessof the historical recordconcerningthevegetationoverthe vast grazingareas ofthe West at the time of settlement,togetherwith the almost totalabsenceofpreservedprimitiveareas, makes the problemof reconstructing the originalplant cover difficultthough not impossibleto solve. In these problems ecologyfindsboth a duty and a privilege to serve the land-useprogram. The Wasatch Mountains east of Salt Lake City,Utah, affordedan opportunity to ascertainsomeoftheeffectsofnearlya centuryof intensive,unregulatedgrazing and otherhumaninfluenceson the native vegetationand soil of various elevations and slope exposures. This study was confined to vegetational problems of Emigration and Red Butte canyons, while the resultsof parallel but independent soil investigationswerereportedby Croftet al ('43) of the same and other areas of the Wasatch Mountains. Emigration and Red Butte canyons were selected forstudy because of theircomand parabilityin position,physiography, historicaluse. 1 Acknowledgmentsare due the Intermountain Forest and Range Experiment Station, Ogden, Utah, for valuable suggestionsand financialaid in the pursuit of this study. The WVasatchMountains constitute the northeasternrimof the Great Basin. They rise abruptly as an escarpment froma desert floorwith an elevation of 4500 feet up to altitudes of 12,000 feet. The range is deeply dissectedby numerous canyons having a general east-west direction,of which Red Butte and Emigrationcaynons are typical. These two canyons are parallel to each other with their mouths directlyeast of and adjacent to Salt Lake City and discharge their streams westward into Salt Lake Valley. Red Butte Canyon, which lies one mileto the northof EmigrationCanyon, drains an area of approximately25 square miles. EmigrationCanyondrains an area ofapproximately40 square miles. It is characteristicof the canyons of the Wasatch Mountains that the southfacing slopes are less precipitous than their north-facingcounterparts. Since the drainage area of Red Butte Canyon is less and its lengthshorterthan those of Emigration Canyon while both canyons at theirmouthsare approximately the same depth,both slopes of Red Butte Canyon are in generalsteeperthan those of EmigrationCanyon. In soil and geological features these two canyonsshow importantdifferences. EmigrationCanyon is composed principally of Jurassic limestone while Red Butte Canyon consistsin part of a complex mixtureofTriassic shale, sandstone, and limestone. Considering the great differencein grazing use, it was suggested by Croft,Woodward,and Anderson ('43) that the soils of Red Butte 171 172 WALTER P. COTTAM AND FREDERICK Canyon erode much moreeasily than do thoseof EmigrationCanyon. It is generallyrecognizedalso thatsandstonesoils are basically less favorable for plant growththan are limestonesoils (Hilgard, '06). These factswould seem to favora moreabundantvegetationin Emigration Canyonand are importantin theanalysis of vegetationin this paper. The Wasatch front, because of its westernexposureand itsabruptrisefrom the desert, is considerably more xeric than the canyons that dissect it. Precipitation,which averages 16.13 inches annually at Salt Lake City, increases with elevation to a maximumof about 40 inches at 9000 feet. The growing season shortens with higher altitude; Salt Lake Valley has a frostlessperiodof about 160 days while BrightonCanyon, 10 miles south of Emigration Canyon, with an elevation of 8700 feet, has an averagegrowingseason ofabout 90 days. HISTORY OF RANGE USE ANDOWNERSHIP Soon afterthe settlementof Salt Lake Valley in 1847,both Red Butte and Emigrationcanyonscame underprivateownershipand both were utilizedforgrazing purposes. In 1888 the United States governmentbegan the purchase of Red Butte Canyon forthe purpose of establishingFort Douglas at its mouth,and by 1909 had acquired titleto the entirewatershed. Protectionfromgrazingprobably commencedwith the firstpurchase of the land. Even then,however,gully erosionwas manifestin the canyon. It is assumed that depletion of the plant coverwas responsiblebecause, underprotection,gullieshave become revegetated and severeerosionat presentis only half thatfoundin EmigrationCanyon. Ring counts fromtrees growingon these old erosionscars place theirage at approximately 40 years, a date which coincides with the purchaseof Red Butte Canyon by the War Department. As a result of a policy to protect its watershed,Salt Lake City has acquired R. EVANS Ecology, VTol,26, No. 2 title to most of the land in Emigration Canyon. However,some of the canyon is includedin the Wasatch National Forest, and a fewsectionsstillremainunder privateownership. Because the permanent stream in Emigration Canyon is small and uncertain,the water is not used by Salt Lake City fordomesticpurposes,and littleattentionhas been given to grazing or erosion problems. City propertyis still leased to private stockmen, and grazingin this canyon, therefore, has continued without regulation since the time of settlement. In addition to the grazing abuses alreadyrecounted,EmigrationCanyon for a distance of six miles is used as a stock trail to and from the higher summer rangesoftheWasatch and Uintah Mountains. The number of sheep passing over this trail varies fromyear to year. In thespringof 1935,forexample,97,550 sheepand 200 cattle used thistrail;in the fallof the same year 123,000sheep were herdeddown the canyon. By comparison, the spring drive of 1931 included 145,510sheep,and the fallflockstotaled 209,203 sheep. Trailing here is said to have begun in the early "fifties." Each flockhas the freedomofthecanyonup to the six-milepoint wherethe trail passes over Little Mountain into Parley's Canyon. It is not uncommonfor a single flockto remaina week withinthe lower reachesof EmigrationCanyon. Many summerhomeswith theirassociated fenced enclosures are located in Emigration Canyon along the stream course,and the canyon is much used for campingand generalsummerrecreation. On the other hand, civilians have been rigidlyexcludedfromRed Butte Canyon since the turnof this century. Fires at the mouths of both canyons are not uncommon. Especially is this trueof Red Butte Canyon wherevegetationis purposelyburnedto clear the land for target ranges. Both canyons have sufferedfrominadvertentburns at various places and timesat higherelevations. April, 1945 EARLY CANYON DESCRIPTIONS VEGETATION OF OF VEGETATION No recordsare extantwhichreferparticularlyto the vegetationof Red Butte Canyon, and but fewreferto the vegetation of Emigration Canyon in 1847. However, it is significantthat available referencesdescribe Emigration Canyon as denselyvegetated. William Clayton ('21), an early Mormon historian,stated that it was necessary, because of the dense growthof vegetation,forthe pioneersto reconstructa road throughEmigration Canyon which had apparently been used by the Donner partyonly the year previous. In July, 1847, Erastus Snow and Orson Pratt traveled through Emigration Canyon in advance of the main pioneer party. Snow said that "The thicketdown the narrowsat the mouth of the canyon was so dense that we could not penetrate through it. I crawled forsome distance on my hands and knees throughthis thicket until I l: WASATCH RANGE, UTAH 173 was compelledto return." (Quoted from Linn, '02.) Clayton ('21), in describing the pioneertrekdown EmigrationCanyon,said, "The grass on the creekgrows fromsix to twelvefeethighand appears veryrank." (Doubtless Elymuscondensatus.2) At theirlast encampment,a position six miles fromthe mouth of this canyon, he wrote, "The grass here appears even thickeron the ground than where we left this morning. The soil looks indeed rich, black and a little sandy. The grassis about fourfeethigh and very thick on the ground and well mixedwithrushes." At thepresenttime thevegetationin EmigrationCanyon has no suchappearance,but, in general,these 2 Authorityforplant names is Tidestrom,Flora of Utah and Nevada, with the followingexceptions: grasses, Hitchcock's Manual of the grasses of the United States; Populus tremuloidesvar. aurea, Pseudotsuga taxifolia,Berberisrepens,and Sisymbriumaltissimum, Kearney and Peebles, Floweringplants and fernsof Arizona. I FIG. 1. A typicalview midwayup Red Butte Canyon showingthe dense vegetationin the bottomof thecanyon. Note theabundanceofcow parsnip(Heracleum lanatum),a palatableweed rarelyseenin EmigrationCanyon. 174 FIG. 2. WALTER P. COTTAM AND FREDERICK R. EVANS Ecology, Vol. 26, No. 2 EmigrationCanyon contrastsunfavorablywithcorrespondingareas in Red Butte Canyon. Note the hedgednatureof the haw shrubs(Crataegus rivularis) and the low ruderalvegetationin the foreground. thecanyon,thoughits exact positionwas placed at random. From this point the centerofeach succeedingtransectwas establishedin the bottomof the canyon at exactlythree-mileintervalsby speedometerreading. Each transectconsistedof 40 plots evenlyspaced along a compass line and so distributedthat 20 plots lay on each hillside. The firstplot of each transectlay 100 feetfromthestreambed, and the twentiethplot lay on or near the canyonridgetops. Plots wereseparated by a distanceof 200 feet,makingthe entire transectof 40 plots 8000 feet long. Each plot was circularin shape and 100 square feetin area. FIELD PROCEDURE transectsand plotswere Corresponding The lengthof EmigrationCanyon to established for Red Butte Canyon, but the main tributariesof its drainage was since this canyon is not as long as Emifound by speedometermeasurementsto grationCanyon, altitudes at the stream be approximately12 miles. In orderto bed wererecordedby meansofan aneroid sample adequately the vegetationin this barometerforeach transectin Emigracanyon,fourtransectsdrawnat rightan- tion Canyon and the same altitude was gles to thedirectionofdrainageand equi- used to locate the correspondingtransect distantfromoneanotherwereestablished. in Red Butte Canyon. AltitudinalposiTransect I was located at the mouth of tionsforcorrespondingtransectsin each descriptionsapply to Red Butte Canyon as it appears today (figs.1, 2). Three moreor less distinctbeltsofvegetationhave been recognizedon the Wasatch front. A grass-sagebrushclimax extendsfromthe valley floorto an average elevation of 5000 feet. Above this to about 7500 feet scrub oak (Quercus gambeli)dominatesthe landscape, while stillhigherthereis a belt ofaspen (Populus tremuloides var. area) and conifers consistingof white fir (Abies concolor), Douglas fir (Pseudotsugataxifolia),and blue spruce (Picea pungens). April, 1945 CANYON VEGETATION OF WASATCH RANGE, UTAII 175 canyonat thestreambed wereas follows: 1, 5000 feet; Il, 5350 feet; 111, 5600 feet; IV, 6800 feet. The point-observationplot methodof vegetationalanalysis devised by Stewart and Hutchings ('36) was adopted forthis study. The surveywas made in thesummerof 1935 (late June, July). Each summer since then the authorshave made a cursory study of the two canyons. Conditions at presentare essentiallythe same as thoseat thetimeoftheoriginalsurvey. ANALYSIS OF VEGETATION Data gatheredin this study permita comparativeanalysisofthevegetationin Red Butte and Emigrationcanyonswith respectto the densityof the plant cover as a whole and of the individualspecies, and grazingcapacity. Comparativedensities: Graphic comparisonsof plant densitiesof Red Butte and Emigrationcanyonsare shownin figures 3 and 4. The densityof the plant cover of Red Butte Canyon is approximatelytwicethatofEmigrationCanyon. The distributionof plant densities by transectsin the two canyons (fig.4) presents several interestingfacts. (1) The canyons are nearly equal in the total amountof vegetationon transectI. (2) /5 k~~~~~~~~ ~~~~~~.04 n 0: .03 PO 0" Al.- .0/ FIG. 3. Comparison of the density of plant cover and forage acre factor of Red Butte and Emigration canyons. Solid bars = Red Butte Canyon; cross-hatchedbars = Emigration Canyon. rA7NSECrS 1II FIG. 4. Comparison of densities of all vegetation in each transect of Red Butte and Emigration canyons. Solid bars = Red Butte Canyon; cross-hatchedbars = Emigration Canyon. Except at the mouth,Red Butte Canyon shows plant densitiesfarin excess of the correspondingareas in EmigrationCanyon. (3) The vegetation midway up Red Butte Canyon (transectII1) is less dense than on adjacent areas below and above (transect II and IV) in the same canyon. Field observationsclearly reveal the reasonforthis in the prevalence of rockoutcroppingsand poorsoil chiefly on the south slope of the canyon. (4) Except at the mouth, EmigrationCanyon varies but slightlyin the densityof vegetationof all transects. Vegetation types:Red Butte and Emigrationcanyons are both dominatedby scrub oak (Quercusgambeli). Figure 5 gives a graphic comparisonof the two canyonswithrespectto total amountsof weeds,3shrubs,and grassesin each of the fourtransects. Some outstandingfacts are illustrated by these graphs. (1) Shrub densities exceed the combined densitiesofweeds and grassesin all areas above the mouth in both canyons. (2) The mouthof Red Butte Canyon has a grass-weedaspect, while the mouth of Emigration Canyon is dominated by 3 The Forest Service classificationof vegetation is used in this study. Weeds include all nongrassyherbaceous plants whilethe term"ruderal" is reserved for plants falling under the popular concept of "weed." 176 WALTER P. COTTAM AND FREDERICK R. EVANS Ecology,Vol. 26, No. 2 /4 _ i0 TRANSECTS: I H RED surrT T U II Zf EMICRAA KE r/Ov FIG. 5. Comparison of densities of shrubs, weeds, and grasses in each transect of Red Butte and Emigrationcanyons. Solid bars = shrubs; cross-hatchedbars = weeds; stippledbars = grasses. shrubs. The grassyslopes of Red Butte parison of the vegetation of these two Canyon are burned by firemuch more canyons. An analysis of the vegetation oftenthan are the correspondingslopes from the standpoint of livestock influof Emigration Canyon. (3) The pro- ences involved a re-examinationof the portionsof shrubs,weeds,and grasseson vegetation in each canyon on the basis the various transectsof each canyon are, of the palatability forsheep and cattle. in general,similar. Accordingto strati- In this analysis the authorsfollowedthe graphicmaps of the area, the portionof Forest Service practice of determining Red Butte Canyon in the vicinity of the forageacre factorforthe sectionsof transectIII possesses,in additionto lime- each canyon throughwhichthe transects stone, some shale and sandstone, prob- passed. The forageacre factoris a fracably accounting in part for the fewer tional unit of measurementfromwhich shrubs on that transect. Other differ- actual stock-carrying capacity of a given ences in proportionsof the three plant rangeis estimated. The amount of fortypes (for example, on transect II of age on any given acre of range is depenEmigrationCanyon) may be accounted dent on two importantmeasurable facfor chieflyby the influenceof grazing, tors: first,the density of each forage although the greater excess of shrubs species, and second, the utility (palata(chieflyscruboak) overweedsand grasses bility)4of each foragespeciesto livestock. at the head of Red Butte Canyon is Many laymen and even stockmenare doubtless due to the fact that at this proneto accept quantityofvegetationas altitudeclimateand topography(steeper the sole criterionof grazing capacity. slopes) favor the maximum growth of The errorin not consideringquality of shrubs. vegetation as well as quantity is illusGRAZING CAPACITIES Differencesof grazing use to which Red Butte and Emigrationcanyonshave been subjected constitute a variable which should prove significantin a com- I Palatability tables used in this study were secured fromthe U. S. Forest Service. A palatability rating is given for each species of plant. Palatability is definedas the per cent of current growth of a given species of plant utilized by stock when the range is properlygrazed. April, 1945 CANYON VEGETATION OF WASATCH '.11 RANGE, UTAH 177 triplants as big sagebrush (Artemnisia dentata), rabbit brush (Chrysothamnus speciosus),and barberry(Berberisrepens), all oflow palatabilityto livestock. None of these plantswas encounteredin measurable quantities at the mouth of Red Butte Canyon. DISCUSSION rRANsrcrs 1 FIG. 6. Comparison of forage acre factors of each transectof Red Butte and Emigration canyons. Solid bars = Red Butte Canyon; crosshatched bars = Emigration Canyon. trated in figures3, 4, and 6. The total densityofvegetationof EmigrationCanyon is 55 per cent of that of Red Butte Canyon,but the actual amountof forage is only42 percentas much (fig.3). This fact stands out even more in comparing specificareas of the two canyons. The density of vegetation at the mouthof EmigrationCanyon is 87 per cent of that at the mouthof Red Butte Canyon (fig. 4). Owing to the quality of the plant cover,however,the amount of forageat the mouthof EmigrationCanyon is only 45 per cent of that at the mouthof Red Butte Canyon (fig.6). The difference betweenthe forageacre factorand the densityof plant cover in Red Butte and Emigration canyons is much greaterat the mouths than elsewhere. This may be explained by the fact that at the mouth of Emigration Canyon therehas been a greaterchange of vegetational types. It is here that the competitionbetweengrassand shrub types is in most delicate balance in the undisturbedrange. These facts would seemtosupporttheconclusionofPickford ('32) and theunpublishedobservationsof othersthat the foothillvegetationof the mountainson theeasternrimoftheGreat Basin at the timeof the firstwhitesettlementwasthegrasstype. Approximately one-thirdof the vegetationat the mouth of EmngrationCanyon consists of such In the absence of detailed historical data it was impossibleto ascertainwith accuracy the floristicchanges which occurred in the vegetation of Emigration Canyon (lue to grazingand otherfactors. That the vegetationin Red Butte Canyonwas richbothin quantityand quality offoragewas evidentto thewritersat the outset of this study, and the foregoing analysisgivessome numericalidea of the differencesbetween the two canyons. The followingmore detailed consideration of the data on grasses,weeds, and shrubs points to the great probability that grazingis chieflyresponsibleforthe impoverishmentand the retrogressive succession of vegetation which has occurredin EmigrationCanyon. Grasses: The density of palatable grasses, including Agropyronspicatum, A. pauciflorum,A. dasystachyum, BroB. carinatus,Poa pramus brizaeformis, tensis, and P. secunda, is five times greater in Red Butte Canyon than in Emigration Canyon. The density of an introducedspecies, Bromus tectorum, is one and one-halftimesgreaterin Red Butte Canyon than in EmigrationCanyon. This grass,thoughpalatable fora short time early in the growingseason, has a low palatabilityratingmost of the summer. The successfulinvasionofthis species in Red Butte Canyon (table I) is doubtlessdue to the frequentburningat is priits mouth. That Bromustectorum marilya grassofthefoothillenvironment oftheintermountain westis generallyobserved and specificallyshown for both Red Butte and Emigrationcanyons. are most Grasses (except B. tectorum) abundant at lower elevations in Red Butte Canyon, but in EmigrationCan- 178 WALTER P. COTTAM AND FREDERICK R. EVANS Ecology,Vol. 26, No. 2 TABLE I. A comparison of densities in per cent of Broiiius tectorum and combined native grasses in the various transectsof Red Butte and Emigrationcanyons gration Canyon is seen in the following significant data: (1) The densityof weed vegetationwith low palatabilityis twice as greatin EmigrationCanyon as in Red Red Butte Canyon Emigration Canyon Butte Canyon. The densityofmorepalatable species,on the otherhand, is only IralsectsBromus Brms Combined BromCsombined Brms native native one-fifth as great in EmigrationCanyon tectorum tectorum grasses grasses as in Red Butte Canyon. (2) HerbaceI 2.01 0.85 1.62 0.11 ous vegetationoflow palatabilityis twice II 0.86 0.66 0.08 0.09 as dense as palatable weeds in EmigraIII 0.21 0.18 0.25 0.01 tion Canyon; in Red Butte Canyon the IV 0.06 0.08 0.11 0.14 densityof palatable weeds is five times that of unpalatable weeds. (3) Highly yonthereverseis true(table I). Several palatable species of weed vegetation, factors are probably responsible. Red probably once abundant in Emigration Butte Canyon with its more precipitous Canyon, are on the verge of extinction slopes and its less open upperdrainageis (table II). morefavorableto shrubsand less favorable to grasses. This phenomenon is TABLE II. Percentagepalatabilityof important specieswithcomparative in per cent densities common to narrowcanyons of the Wain RedButteand Emigration canyons satch Mountains. The near absence of native grasses midway up Emigration Density PalataCanyon (table I, transectI I I) is explained bility Red Emiby the fact that the sheep trail passes Butte gratin over Little Mountain near this point, Grasses: and, consequently,grazingis heaviest in 80 0.23 Agropyron spicatum .......... 0.03 Bromus tectorum............. 15 0.78 0.50 this vicinity. Despite grazing, grasses Poa longiligula .............. 85 0.15 0.02 are moredense in theupperareas ofEmi- Weeds: Achillea lanulosa ............ 0.12 40 0.04 gration Canyon (table I, transect IV) Balsamorhiza sagittata........ 40 0.90 0.18 Geranium 45 0.22 fremoniii 0.04 .......... than at the correspondingelevation of 20 0.25 Lathyrus leucanthus .......... 0.14 50 0.25 0.07 Red Butte Canyon. This observation Leptotaenia multifida......... 15 1.11 Wyethia amplexicaulis ........ 0.28 gives credence to the probabilitythat grass was abundant in EmigrationCan- Shrubs: Amelanchier alnifolia ......... 75 0.39 0.19 Artemisia tridentala.......... 0 0.04 0.53 yon in pioneerdays. Berberis repens.............. 0 0.13 0.14 0 trace Chrysothamnus speciosus...... 0.55 Ten native grasseswere foundin Red 20 4.51 2.56 Quercus gambeli............. 50 Rosa spp ................... 0.64 0.16 Butte Canyon whichwere not observed 50 0.80 0.21 Symphoricarpos vaccinioides. .. in EmigrationCanyon (table III). Conversely,all but one of the native grasses Mule's ear ( Wyethiaamplexicaulis),an encounteredin the plots of Emigration Canyon appeared in Red Butte Canyon. herb of low palatability(15 per cent), is These factswould seem to emphasizethe much moreabundant in Red Butte Canof rare yon than in EmigrationCanyon (table dangerof completeextermination and highlypalatable speciesinovergrazed II). A possibleexplanationis that stock areas. A comparisonof the palatability in EmigrationCanyon is forcedto suband density of three principal grasses siston plantsof low palatabilityand that (table II) leaves little doubt as to the sheep are fond of the seed heads and with the natural reprodamaging influenceof severe grazingon therebyinterfere ductive processesof the plant. palatable grasses. Shrubs: Scrub oak is by far the most Weeds:The-influenceof heavy grazing on the native herbaceousflora5 of Emi- common shrub in both canyons. Dei All species of weeds whichaveraged in density at least one-eighthof one per cent per plot and whichweregiven palatability ratingsby the U. S. Forest Service are included in the data. CANYON April, 1945 TABLE III. RANGE, 179 UTAH List of grasses occurringin plots of Red Butte and Emigrationcanyons. Presence of a species is indicatedby a plus sign and absence by a zero sign Species Species | Agropyrondasystachyum A gropyronpauciflorum Agropyronsmithiimolle Agropyronspicatum . ..... Agropyronsubsecundum+.. *Agrostisalba .+ Agrostisexarata.+ Agrostisidahoensis. *Agrostisverticillata. Aristida longisetarobusta . + *Bromusbrizaeformis .+ Bromus carinatus.+ *Bromustectorum .+ Catabrosaaquatica .+ .0 *Dactylisglomerata Deschampsia caespitosa ..+ Elymus condensatus.+ * OF WASATCH VEGETATION Red Butte + + + 4-I 0 + ?+ ?+ Emigration + + 0 + 0 + 0 + 0 Q + + + 0 + + + SeisRed Species Festuca kingii. Festuca subulata. Glyceriaelata.+ Glyceriastriata. Hordeumjubatum.+ Koeleria cristata.+ Melica bulbosa.+ *Munroa squarrosa.0 Oryzopsishymenoides. *Phleum pratense. *Poa annua .0 *Poa compressa.+ Poa longiligula.+ *Poa pratensis.+ Poa secunda.+ *Setaria viridis. Stipa columbiana.+ Butte + + + + + 0 Emigration + 0 0 0 + 0 + + 0 + + 0 + + + + + Introducedspecies spite the fact that this shrubhas a palatabilityrating of only 20 per cent, the densityof scrub oak in EmigrationCanyon is but half of that in Red Butte Canyon. The densityofotherspecies of shrubswithhighpalatabilityis less than one-thirdas muchin EmigrationCanyon as in the other. Sagebrush and rabbitbrushwithlittleforagevalue have a density 13 timesgreaterin EmigrationCanyon than in Red Butte Canyon. Ruderals: The ruderal flora of Red Butte and Emigrationcanyons includes the followingspecies: Ambrosia psilostachya,Asclepias speciosa,Bromustectorum, Caulanthushastatus,Camelina microcarpa,Chenopodium album,Helianthus annuus, Lactuca scariola,Lepidium apetalum,Lepidiumperfoliatum, Marrubium vulgare,Polygonumdouglasii,Salsola pestifer,Sisymbrium altissimum,Sophia parviflora,and Zygadenuspaniculatus. Most ruderalsare practicallyvalueless as forageand many are exotic annuals. They appear either as pioneers on denuded areas or as the last stage in retrogressivesuccession. In Red Butte Canyon, with the exception of Bromus tectorum, they are confinedto the lower elevations of the canyon where fireor disturbedsoil about Fort Douglas permit their growth. In Emigration Canyon, however,a major highway,a long-used sheep trail, heavy grazing,and summer homesall contributeto conditionsfavorable to an abundant ruderalflora. The densityof ruderalsin Red Butte Canyon is 12 per cent less than in Emigration Canyon (fig.7). ExceptingBromustectorum,the densityof ruderalsin Emigration Canyon is seven timesas greatas in Red Butte Canyon. These ruderalsare most abundant in burnedareas on transect I, along the denuded sheep trail,and in fencedareas nearsummerhomeswhere Z.00 - 100 k.50 rRA NS ECTs I FIG. 7. Comparison ofdensitiesofruderalsin each transectof Red Butteand Emigration canyons. Solid bars = Red Butte Canyon; crosshatchedbars = EmigrationCanyon. 180 WALTER P. COTTAM AND FREDERICK R. EVANS Ecology, \Tol. 26, No. 2 .. .. . FIG. 8. Barren areas along the sheep trail in Emigration Canyon constitute a flood hazard to Salt Lake City thenativevegetationhas been destroyed. Owing to the decrease of native vegetation on heavily grazed slopes, ruderals occur in all areas of EmigrationCanyon in contrastto the very small amount of these plants in the miidand upper areas ofRed Butte Canyon. Only one ruderal was found in species, Bromus tectorum, plots on transects III and IV of -Red Butte Canyon. EROSION alarming impoverishmentof the plant cover, and sheet erosion is generallyin evidence. Advanced gullyerosionis especiallynoticeableon the slopes of Little Mountain where the trail passes out of EmigrationCanyon. Here barrenareas (fig. 8) more than ten acres in extent furnishrunoffwhich reaches flood proportions when snows melt and heavy rains fall. A cloudburstin this vicinity mightresultin a floodthatwoulddestroy homes of Salt Lake City lying directly in its path. That this menace is a very real one is evidenced by the fact that such a floodhas already occurredin Dry Canyon which lies about one and onehalf miles to the north (Alter, '21). There the drainage area is not nearlyas largeas that in EmigrationCanyon, and the plant cover is considerably more dense. For more than half a century,from 100,000 to 200,000 sheep have trailed throughEmigrationCanyonto themountain summerrangeseach springand have returnedthroughthiscanyon to the desert winterranges each fall. Each herd leisurelygrazes in the canyonforseveral days in transit. Besides thisabuse, private flocksgraze on the upper areas of EmigrationCanyon duringthe summer. SUMMARY Cattle also graze in the canyon during 1. Two canyons,Red Butte and Emithe summermonths. Such overuse of thesegrazinglands in gration,extendingparallelto each other, Emigration Canyon has resulted in an adjacent and generallysimilarin geogra- April, 1945 CANYON VEGETATION OF phy,slope exposure,and elevation,were compared in respect to quantity and quality of plant cover. 2. In theirpristinecondition,because of morefavorablesoil types,Emigration Canyon probablycontaineda vegetation equal to or surpassingthat which now existsin Red Butte Canyon. 3. For a periodofat least 40 yearsRed Butte Canyon has been protectedagainst grazing. EmigrationCanyon has been grazed heavilysince settlementin 1847. 4. Palatable vegetation has probably decreased, and unpalatable vegetation has probably increased in Emigration Canyon. Only 42 per cent as much forage is producedhere as in equal areas in Red Butte Canyon. 5. Ten native grasses found in Red Butte Canyon were not encounteredin EmigrationCanyon, suggestingthe danger of completeexterminationof highly palatable species throughgrazingabuse. 6. Evidence points to the probability of the completesubstitutionof the original grass type with unpalatable shrubs plus Bromus tectorumat the mouth of EmigrationCanyon. 7. Some highly palatable shrubs in EmigrationCanyon have a density less than one-thirdthat in Red Butte Canyon. Othershrubsoflow palatabilityin WASATCHI RANGE, 181 UTAII Emigration Canyon have 13 times the densityof the same shrubsin Red Butte Canyon. 8. The densityof ruderalsin EmigrationCanyon is 12 percentgreaterthanin Red Butte Canyon. ExceptingBromus the densityof ruderalsin Emitectorum, grationCanyon is morethan seven times greaterthan in Red Butte Canyon. 9. Sheet erosionis generalthroughout EmigrationCanyon and advanced gully erosionis commonalong a sheep trail. LITERATURE CITED Alter,J. Cecil. 1921. Forests in relationto cli- mate and water supply. Trans. Utah Acad. Sci. 2: 195-198. Clayton, William. 1921. Journal of William Clayton. Deseret News, Salt Lake City, Utah. Croft, A. R., Lowell Woodward, and Dean A. Anderson. 1943. Measurements of accelerated erosion on range-watershed land. Jour. Forestry41: 112-116. Hilgard, E. W. 1906. Soils. 593 pp. The Macmillan Co., New York. Linn, W. A. 1902. Story of the Mormons. The Macmillan Co., New York. Pickford, G. D. 1932. The influenceof continued heavy grazing and promiscuous burning on spring-fallranges in Utah. Ecology 13: 159-171. Stewart,George,and S. S. Hutchings. 1936. The point-observation-plot(square-foot-density) method of vegetation surveys. Jour. Anmer.Soc. Agron. 28: 714-722.