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SUMMER HABITAT USE AND SELECTION BY FEMALE SAGE GROUSE (CENTROCERCUS UROPHASIANUS) IN OREGON PDF

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GreatBasinNaturalist53(3), pp.293-298 SUMMER HABITAT USE AND SELECTION BY FEMALE SAGE GROUSE {CENTROCERCUS UROPHASIANUS) IN OREGON Michael A. Cretig',John A. Crawford-, and Martin S. Dnit- — Abstr.\CT. Cover t\pes and \egetati\e characteristics (e.g., grasst's, rorl)s, sIuuIjn) used h\- female Sage (;r()use [Centrocercus urophasianus) during summerwere comparedwith a\ailal)le habitat on tsvo studyareas in southeastern Oregon. Broodlesshens,whichconstituted 114ofthe 125(91%)radio-markedhensstudied, selectedbig(Arteiimiatri- dentata subspp.) and low sagebrush (A. arbuscula) covertypes at both stuch- aieas. At Hart Mountain, broodless liens didnotselectspecificvegetativecharacteristics within covertypes. However, atJackass Creek, forbcoverwas greater (P = .004)atbroodlesshen sites than at random locations. Differences in habitat useb\ broodless hensbetween stud\- areas were associatedwith differences in torb availability. Broodless hens used agreaterdiversit\- ofcover types than hens \\'ith broods. Broodless hens gathered in flocks and remained separate from but near hens with broods during earl\ summer. Byearl\'Julyliroodlesshensnio\edtomeadowswhilehenswitli broodsriMuainedin u[)landhaliitats. Keywords: SageGroiLse. Centrocercus urophasianus, Oregon, fi'indli'. hnxxllesslien.s. Iiulntut. iiiorniwnts. .'unniner. broods, use,selection. Productivity of Sage Grouse {Centrocercus tions, and to assess habitat use by broodless urophasianus) is among the lowest of North hens in relation to hens with broods on two American grouse (Edminster 1954:130). stud)' areas. Reported nest failure ranged from 76% in Oregon (Batterson and Morse 1948) to 36% Study Ahea.s (Wallestad and Pyrah 1974) in Montana. Con- sequently, a relatively large percentage of The stud)' areas were located in southeast- summer Sage Grouse populations consists of ern Oregon at Hart Mountain National Ante- broodless hens. However, information on lope Refuge (Lake County) and at Jackass broodless hens is largely anecdotal. Only Creek (Harnc) County). Topography at both observations of the pro.ximity of broodless areas consists of flat sagebrush plains inter- hens to hens with broods (Dalke et al. 1963, rupted b)- rolling hills, ridges, and draws. Ele- Martin 1976) and chronology of summer vations range from 1500 to 2450 m at Hart movements by broodless hens (Petersen 1980, Mountain and from 1200 to 1700 ni at Jackass Conn(4K' et al. 1988) have been reported. No Creek. Vegetation at both areas is dominated stud)' has dealt specifically with habitat use by bv low sagebrush [Artemisia arbuscula), big broodless Sage Grouse. sagebrush (A. tridentata vaseijana, A. t. We investigated habitat use by broodless wijomingensis, andA. t. tridentata), green rab- hens on a hierarchical order of selection bitbrush {Chrysothamnus ciscidiflorus), and (Johnson 1980). We hypothesized that brood- western juniper ijuniperus occidentalis). less Sage Grouse selected cover types (third- Stands of cm-1-leaf mountaiii-niahogain- iCer- order selection) and vegetative characteristics cocarpus ledifolius) and (}uakiug aspen {Popii- within cover types (fourth-order selection) lus tremuhndes) occur onl)- at Hart Moiuitaiii. and that selection differed between broodless Conunon annual and perennial forbs include hens and hens with broods. Our objectives mountain-dandelion {Agoseris spp.), milk- were to identify cover types used by broodless vetch {Astragalus spp.), hawksbeard {Crepis hens in relation to availability, to identifv' veg- spp.), lupine {Lupinus spp.), and phlo.x {Phlox etative characteristics at broodless hen sites spp.). Grasses consist largely ofbluegrass {Poa and compare those to randomly selected loca- spp.), bluebunch wheatgrass {Agropijron 'U.S.FisliandWikllili-Si-nice,Bci\HI.Lakeview.Orfgon97630. -Dt-partnu-iitofFislu-riesandWildlilc.OirgonStateUni\ersit>,Conallis.Ori-goii973.31-3803. 293 294 Ghi:at Basin Naturalist [Volume 53 spicatitm), needlegrass (Stipa spp.), fescue We characterized vegetation at sites used {Festuca spp.), giant wildrye {Elymu.s b\' broodless hens within two days after visual cinereiis), and bottlebrush squirreltail (Sitmi- locations were determined. Canopy cover (%) lon hystrix). Plant nomenclature from Hitch- of shrubs was measured by line intercept cockand Cronquist (1987)was used. (Canfield 1941) along two 10-m perpendicular transects intersecting at the broodless hen site. The position of the first transect was Mkthods determined from a randomb- selected com- pass bearing. Each shrub intercepted was Female Sage Grouse were captured (Giesen et al. 1982) during summer 1988, p(l<a4c0edcmi)n,tomoendeioufmth(r4e0e-8h0eicgmh)t,cloarssteasl:l (sh>o8r0t spring and summer 1989-90, and spring 1991. cm). Canopy cover of shrubs was recorded Kach hen was fitted with a numbered alu- separately for each height class. Cover (%) of minum leg band and a poncho-mounted, forbs and grasses was estimated in five 20 X solar-powered radio transmitter with a nickel- 50-cm plots equidistantly spaced along each cadmium l)attcry (Amstrup 1980). Radio- transect (Daubenmire 1959). Vegetation was marked hens were monitored during summer characterized at randomK' located points dur- (June-August) 1989-91 at an average rate of ing June and JuK with the same methods no more than twice monthly to minimize the used to measure variables at broodless hen problem associated with lack ofindependence sites. Random sites were located with a ran- oflocations. Furthermore, we recaptured and dom numbers table, which was used to deter- remoN(.'d radios from hens at the conclusion of mine starting point, compass bearing, and dis- each field season, and pre\'iousl\' unmarked tance traxeled. hens were fitted with radios for use in subse- We compared the use of cover types by {{uent \ears to maintain independence ofsam- broodless hens with availability ofcover types ples among years. Nevertheless, we acknowl- within study areas from June through August. edge there may be a potential bias in the use The proportions ofcover t\'pes available were of re-observations, even at a low rate of Ire- used to establish the expected \'alues for fre- (juency, of the same indixidiuils within a quency of bird observations occurring in breeding season. those cover types. We also compared cover All locations of radio-marked hens were t)pe use between broodless hens and hens mapped as Universal Transverse Mercator with broods. Chi-square analysis was used for coordinates. Visual locations of radio-marked these tests. Co\er t\pes with expected values broodless hens were marked and served as of <5 bird observations were combined and sites for vegetation sampling during Jime and analyzed collectively. If differences were July 1990. Date, location, and flock size of detected, confidence intenals were calculated broodless hens and hens with broods to identify cover tvpes that contributed to the observed on each study area were recorded. difference (Neu etal. 1974, Byers et al. 1984). Definitions of monthly time periods were We used a factorial analysis of variance early (first 10 days), mid (middle 10 da>s). and (ANOVA) (PROG GLM, SAS Institute, Inc. late (last 10 days). 1989) to compare \egetati\'e characteristics Eleven cover types were defined on the among plot types (broodless hen or random). basis ofdominant shrubs and grasses (Gregg Study area was an additional factor in the 1992). We used color infrared aerial pho- ANOVA model to account forvariation associ- tographs and topographic maps to delineate ated with spatial differences (Snedecor and co\er types on each stud\ area. Each hen Cochran 1967:339). A significant plot t\'pe location was classified into 1 of the 1 1 cover (hen use site or random location) X stud\ area t>pes. At each study area available habitat was interaction (F = .02) was detected tor (orb determined with the mininuuu convex poly- cover. Consequently, differences among plot gon method (Odum and Kuenzler 1955) from t\pes for forb cover were reported by study telemetr\ locations obtained during summer. area. A single-factor ANOVA was used to Proportions of cover types within the avail- compare vegetative characteristics at random able habitat at each area were determined locations between study areas in co\er t\pes with adot grid s\stem (AveiT 1977). used bv broodless hens. We assumed our data 1993] HAiuTvr UsK BY Fkmai.e Sack Chol'se 295 MoTuanbtalien1.NaUtsieon(a7lf)AonitceloomptelR\epcf.usgdemi(nnt=;s6u7imhieKn-sr.(1Ji6i8iKl'o-Acuajtjiioinsst))aInndraJcalcikoa-isnsarCkrie'dekl)i((n)()=ilk4-s7s lSiaetnjsf,(;1n3)7iilsofcaltiii'oiinss)atsltluadr\l areas. LakeandHarne\ counties,Oregon, 1989-91. "IiK'ludfSbasinbigsagrlirusli.lakcluil.amitiioiintaiiislinili "UsfclillcTfil(/'<.0.5,fromavail.iliilitv. 296 Great Basin Naturalist [Volume 53 TvBLli2. Use(%)ofc()\crtvpes duringsummer(June-August)byradio-markedfemale SageGrouse at Hart Moun- tain NationalAntelope RefugeandJaekassCreekstudyareas. LakeandHarneycounties,Oregon, 1989-91. ; 1993] H \Hirvr I'si", by Fi:\iai.k Sack (^hoise 297 Table 4. \i'iii.tati\c iliaiacttrislics (/;? comt) at raiuloiii locations at Hart Mountain National Anti-IojH' Ht-I'imc and jackass(licck stntK areas. Lakeand Ilanic\ counties, Oici^on.JniicandJnly 1990. Hart Mountain JackassCrci'k in = 30) fii = 70) (iliaractcristic /'\ SD .SD Fori)co\'ei" .0001 Grasscover .0001 Shriihco\t'r Short. <4()cm .ooos 19 12 Medium.4()-S()ci .25 6 9 Tall. >S()cm .OOOfi 1 4 chroiioloiix of .sumnier niovemcnts 1)\ blood- ment, ihroiigli a research contract adiiiiiiis- less hens (Batterson and Morse 194.S, Dalke et tered 1)\ the Oregon Department ol l-1sh and al. 1963, Martin 1976, Connelly et al. 1988). Wildlife. Logistical support was supi)Iied l)\ Petersen (1980) reported that the early nio\e- the U.S. Fish and Wildlife Service. We thank ment to meadows bybroodless hens was relat- J. K. Barnett and .\. K. DeLong for assistance ed to nest loss and not desiceation of vegeta- with data collection. W". D. Fdge. S. L. Olson- tion in uplands. Contrastingly, Sehoenberg Edge, and R. L. Jarvis proxided ciitical (1982) noted that summer movements by reviews of the manuscript. broodless hens andhens with broods occurred simultaneousK' and were prol)ably a response Litkhatl Ki: Cited to \egetation desiccation in sagebrush uplands. .\\isiiup, S. C. 1980. \ radio-collarforgame liirds. Jour- Differences in summer habitat use nalofWildlife Manasiement44:214-217. between broodless hens and hens with broods .\\i;in. r. I". 1977. Interpretation ofaerial photographs. ma\- be attributed to specific dietary rec^uire- 3rd eil. Burgess Press, Minneapolis. .Minnesota. .391 ments ofjmenile Sage Grouse. Juvenile Sage BahikPIs).on, W, .\I.. and \V. B. .Mohsi:. 1948. Oregon Grouse consume primarily forbs and insects •Sage (irouse. Oregon Fauna Series 1. Oregon Stale during suiumer (Rasmussen and (iriner 1938, (^anieCommission.29pp. Patterson 1952:201, Peterson 1970). Johnson BvKKS, C. R., R. K. Steimiokst. and P. R. Khaiseman. and Boyce (1990) demonstrated that sur\'ival 1984. Clarification ofa techni(|ue foranaKsisofnti- ii/ation-a\ailal)ilit\ data. Journal ol W'ildlile Man- and growth of captive Sage Grouse chicks agement48: 10.50-1053. decreased as the quantity ofinsects in the diet C^ANFIEI.D, R. 1941. Application ofthe line interception decreased. Furthermore, hens with broods method in .sampling ofrange vegetation. Journal of selected areas with less sagebrush (Klel)enow Forestiy39:386-394. 1969, Dunn and Braun 1986) and greater Co.NNELLV, J. W., H. \\". BHOWKKS. AM) R. J. (IaTKS. 1988. Seasonal movementsofSage(irouse in south- availabilit)' offorbs (Klebenow 1969, Peterson eastern Idaho. Journal ofWildlife Management 52: 1970, W'allestad 1971). Presumably, hens with 11()-122. broods remained in uplands until succulent Dalke, P. D., D. B. P>kaii. D. C. Stanton. J. E. Ciuw- forbs were no longer available; the\ then l-ORn, AND E. F. Sc:ill-vnEHEK. 19fi3. EcoIog\. pro- ducti\it\,andmanagementofSageGrousein Idaho. moved to meadows later in summer (Petersen JournalofWildlife .Management27:811-841. 1980). Dietan- needs ofbroodless hens might Dal15ENMIRE, R. F. 1959. .\ canops-cwerage method of be less specific than those of hens with vegetationanalysis. NorthwestScience.3.3:224-227. broods; as a consetiiience, broodless hens DlNN, P. O.. AND C. E. BliAlN. 198fi. Summer hahitat moved from uplands to meadows earlier in WuisledlbivfefeMmaanlaegaenmdenjutve5n0i:l2e28S-a2g3e5.Grouse. Journal of summer and used a greater diversit) of co\er Ed.minstek, F.C. 1954..\mericangamebirdsoffieldand bi'pes than hens with broods. forest.CastleBooks, NewYork.490pp. GiESE.\, K. M., T. J. Sctioenheik:. and C. E. Brain. AcKNOwled(:;mfats o1r9a8d2o..MWieltdhliofdes.SfoocriettyraBpuplilnegtinSa1g0:e2(2;4r-o2n3s1e.in Col- Grecx:, M. a. 1992. Use and selection ofnesting habitat Fmids were provided b\ the I.S. Depart- by Sage Grouse in Oregon. Unpublished master's ment of Interior. Bureau of Land Manage- thesis.Oregon StateUni\ersit\.Cor\allis.46pp. 298 Ghkat Basin Naturalist [Volume 53 Hitchcock, C. L., andA. Cronquist. 1987. Floraofthe lUs.viussEN, D. I., AND L. A. Griner. 1938. Life liiston PacificNorthwest.6thed. Univer.sit>-ofWashington and management studies ofthe Sage Grouse in Press,Seattle.730pp. Utah, with special reference to nesting and feeding JOIIN.SON, D.A. 1980.Thecomparison ofiisasieanil avail- habits. Transactions ofthe NorthAmerican Wildlife ability measurements for evaluatinfi prelerence. Gonference3:852-S64. Ecolog> 61:65-71. S.\S Institute, Inc. 1989. SAS/STAT user's guide, ver- Johnson, C. D.. and M. S. Bovce. 1990. Feeding trials sion6. Volumes 1 and2. 4th ed. SAS Institute. Inc.. with insects in thedietofSageGrousechicks.Jour- Gaiy, NorthCarolina. 1686pp. nalofWildlife Management54:89-91. Schoenberc, T. J. 1982. Sage Grouse movements and KleBENOW, D. a. 1969. Sage (wouse nesting and brood habitat selection in North Park, Golorado. L'npub- habitat in Idaho. Journal ofWildlife Management lished masters thesis, Golorado State LIniversit\-, ,33:649-662. FortGollins.86pp. 1972. The habitat reciuirements ofSage Grouse Snedecor, G. W., and W. G. Gochran. 1967. Statistical an.d the role offire in management. Proceedings of methods.6thed. IowaState University Press,Ames. the Tall Timbers Fire Ecology Gonference 12: 507pp. 305-315. Wallestad, R. O. 1971. Summermovements and habitat Maktin, N. S. 1976. Life history and habitat require- use by Sage Grouse broods in central Montana. mentsofSageGrousein relation tosagebrush treat- JournalofWildlife Management35: 129-136. ment. ProceedingsoftheWestern Association State . 1975. Life history and habitat requirements of GameandFishGommission56:289-294. Sage Grouse in central Montana. Montana Depart- Nel-, G. W., G. R. Byeks, andJ. M. Peek. 1974. A tech- mentofFishandGame, Helena.65pp. nique for analysis ofutilization data. Journal of Wallestad, R. O.,J. G. Peterson, and R. L. Enc. 1975. WildlifeManagement38:541-545. Foods ofadidt Sage Grouse in central Montana. Odlm,terEr.itpo.r,\'.\aNDndE.hJo.mKel ErNaZnLgEeH.si1z9e55i.nMbeiardssu.reAmueknt72o:f WalleJsoutranda,loRf.WOi.l,dlaifnedMDa.naBg.emPyernath.39:1967248.-6M3o0.vement 128-137. and nesting ofSage Grouse hens in central Mon- P.ATTERSON, R. L. 1952. The Sage (irouse ofWyoming. tana.Journalof\\'ildlife Management38:6.30-633. SageBooks, Inc., Denver,Golorado.341 pp. Petersen, B. E. 1980. Breeding and nesting offemale SageGrouse in North Park, Colorado. Unpublished Received26June1992 master's thesis, Golorado State Uni\ersit\-, Fort Accepted22Vehruunj1993 Gollins.86pp. Peterson, G. 1970.The foodhabitatsandsummerdis- J. tribution ofjuvenile Sage Grouse in central Mon- tana.JournalofWildlileManagement34: 147-155.

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