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A survey of the highland grassland endemics in Mau Narok/Molo Important Bird Area, Kenya PDF

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A survey of the highland grassland endemics in Mau Narok/Molo Important Bird Area, Kenya KariukiNdanganga, RonaldMulwa andPatrick Gichuki L’etendue, larepartition etlaqualitedecequi reste de 1’habitat herbeuxdans les Mau Narok-Molograsslands. Zoned’ImportancepourlaConservationdesOiseaux(ZICO)auKenya,onteteevalueesdu 16au24septembre 2001. Les auteurs ont egalement estime la repartition et la densite de deux especesglobalement menac&set a repartition restreinte, laSentinelledeSharpeMacronyxsbarpeietlaCisticoledesAberdare Cisticolaaberdare. 1a plusgrandepartie(48%)delaZICOetaitconstitutedecultures,tandisqueleszonesherbeusesnecomprenaient que 33%, les plus importantes se trouvant dans la partie la plus meridionale, occupee principalement parla communautepastoraleMasai.LaSentinelledeSharpeavaitunedensitede 1,2individusparhaetetaitladeuxi&me especelaplus communementobservee. La Cisticole desAberdareaeteobservtedanstroisparcellesseulement, avec un total de sept individus. La conversion a grande echelle en cultures d'orge et de froment constitue une menacegravepourleszonesherbeuses.LaZICOenpossedetoutefoisencoredesetenduesconsiderablesdehaute qualiteetelleestainsi importante pourlaconservation desespecesendemiquesdecet habitat. Lesinitiativesde conservation devraient done se concentrersurces zones. T he Mau Narok/Molo Grasslands Important Bird MacronyxsharpeiandAberdareCisticolaCisticolaaberdare, Area(IBA) holdssignificantareasofKenya’sunique both classified as Endangered by BirdLife InternationaF. highland grasslands. This and Kinangop Grasslands IBA No adequate information concerning the status ofeither (Fig 1), eitherside ofthe central RiftValley, are the only species or their grassland habitat is available from Mau sitesthatholdsignificantareasofthishabitat,which lacks Narok/Molo Grasslands. Between 16 and 24 September any formal protection in Kenya and is rapidlyvanishing. 2001, wesurveyed the extent, distribution and condition Theyarehometoseveralmigratorybirdspeciesandvarious of the remaining grassland habitat, and estimated the specialised grassland birds, and are ofkey importance as distributionanddensityofthesespecies. Wealsousedthe they harbour the restricted-range Sharpe’s Longclaw surveyto(1)increaseawarenessamongthelocalcommunity oftheconservationvalueoftheIBA,(2)makeopportunistic contactswithinterestedmembersofthiscommunitywith the aim of initiating a local conservation group or Site Support Group (SSG), and (3) involve and train three members of the Kinangop Grasslands SSG in grassland surveymethods. Here, we present the basic results ofour work. Mau Narok/Molo Grasslands The Mau Narok/Molo Grasslands IBA is an extensive montane grassland situated on the crest of the Mau escarpment, which forms the western wall ofthe central RiftValleyinKenya.Thishigh,openplateauoccupiesc80 kmsouth-easttonorth-west,andisbounded(andpartially interrupted)bytheMauForestcomplex.Rainfalliscl,000 mm peryear,andtheoriginalvegetationisshortgrassland, with some heather and scrub on ridges where soils are deeper.Theareahashighpotentialforagriculture,andhas gradually been settled since the 1950s; it is now heavily populated,withalandscapeseverelymodifiedbycultivation. Cereals are themain crops. TheIBAissitedinNakuruand(asmallpartof)Narok Figure 1.TotalrangeofSharpe’sLongclawMacronyxsharpei districts, within RiftValley province. Population density (shadedarea)showingthelocationsofthestudyarea(MauNarok/ in Nakuru district is high (164 per km2)8. The main MoloGrasslandsIBA) andKinangopGrasslands (theprobable occupantsofthestudyareaaresmallholdersoftheKikuyu strongholdofthespecies). 64-BullABC Vo! 10No 1 AsurveyofthehighlandgrasslandendemicsinMauNarok/MoloIBA:Ndangangaetal andKalenjincommunities(MoloandnorthernMauNarok) ened species, was the fifth most abundant species. The andtheMasaicommunity(whoaretraditionallylivestock longclawwasencounteredin 17outof37surveyplots,and herders) inthesouthernMauNarok. was thesecond most frequentlyencounteredspecies after Grassland Pipit,whichwas recordedin 22 plots. Methods Aberdare Cisticola was recorded in only three plots, Wecontinuouslymappedbroadland-usecategoriesovera withatotalofsevenindividuals,suggestingalowdensity. predeterminedroutethroughthegrasslandsbyestimating However,itisprobablethatthespecieswasunder-recorded the percentage cover of each habitat around points en duringthecountsasthetransectmethodusedwasdesigned route, at intervals of 1.5 km. Transects were conducted for surveying Sharpe’s Longclaw and may not be as every3kmtosurveygrasslandbirdsinselected 1-haplots appropriateforthecisticola,whichmayalsoutilisedifferent withinlargergrasslands.Thirty-sevenplotsweresurveyed. habitat. The few individuals to be locatedwere all on or Theareaofeachlargerpatchwasrecordedas <5, 5-20or close to slightly bushy grassland. Other commonly >20ha,andtheplotsweresurveyedbyateamofsixpeople encounteredspecies(andthenumberofplotsinwhichthey spreadacrossthewidthofthearea,walkingslowlyacrossit were recorded) were Common Fiscal Laniuscollaris (17), 10-20 m apart. All species and individuals flushed were Red-capped Lark (14), Stonechat Saxicola torquata (ten), recorded. Measures ofgrassland quality were also noted Baglafecht Weaver Ploceus baglafecht (nine) and Wing- within the plot using a system developed for monitoring snappingCisticola Cisticolaayresii (eight). grasslandhabitatinKinangop. Grassheightwas recorded Asgrasslandswereestimatedtocoverone-third(cl3,000 asG1(short),G2(mediumlength)andG3(tall).Percentage ha) ofthe IBA, the areasurveyedwas c0.3% ofthe IBA’s tussockcoverwasrecordedasT1 (noorjustafewscattered grassland area. The plots were, however, within patches tussocks), T2 (moderate tussock covering up to 30% of totallingapproximately2,150 ha (16.5%). area),T3 (considerabletussockcovering30-60%ofarea), andT4(densetussockcovering>60%ofarea).Thenumber Grassland cover oflivestockandotherbirdspecieswithin theentirepatch Grasslands covered only one-third ofthe estimated area were also recorded. (c40,000ha)1oftheentireIBA(Table1),whilecultivation covered approximately 50%. The spatial distribution of Results grasslandsvariedbetweentheMoloandMauNarokareas Sixtyspecieswererecordedinthegrasslandpatchessurveyed. of the IBA. Most (75%) of the 20 grassland patches Sharpe’s Longclaw occurred at a relatively high overall surveyedinNarokdistrict(southernMauNarok)were>20 density,of1.2individualsperha,throughoutthe37plots, ha. Only35%ofthe 17patchesinNakurudistrict (Molo i.e. slightlyhigherthan the0.85 perhafromsampleplots block and northern Mau Narok) were >20 ha in size. inKinangoprecordedbyMuchaietaP.However,theMau GrasslandsinMolooccurredaspatchesofvaryingsizesand Narok/Molodensitycompareswellwiththatnotedonlyin were mostly isolated by cultivation. The main crops in thoseplotswithshortgrassandtussocksatKinangop5.The Moloweremaizeandpyrethrum.Wheat,barleyandpotatoes speciesoccurredat2.2perhainplotswithingrasslandsof were also common. >20 ha, compared to those of<20 ha where the species GrasslandextentanddistributioninMauNarokvaried occurredatdensitiesof0.2perha.Basedonoveralldensity, between that occupied by smallholders and that by the itwasthefourthmostabundantspeciesafterBlack-winged mainly pastoral Masai community. The north-west Mau Lapwing Vanellus melanopterus Red-capped Lark Narok was heavily cultivated and only 14.4% held , CalandrellacinereaandGrasslandPipitAnthuscinnamomeus. grasslands. Smallholders of the Kalenjin and Kikuyu Jackson’s Widowbird Euplectesjacksoni a Near-Threat- communities, who mainly cultivate maize, potatoes and , Table 1. Percentage land-usewithin Molo (n=30) and Mau Narok(n=55)areasofthe Mau Narok-MoloGrasslands ImportantBirdArea (IBA), Kenya. Estimatesfortheentire IBA(N=85)arealsopresented. Landuse Molo MauNarok EntireIBA Mean SD Mean SD Mean SD Grassland 33.3 23.6 33.2 19.7 33.3 21.0 Cultivation 45.1 22.6 49.2 18.9 47.8 20.3 Exotictreeplantations 14.0 8.4 6.2 5.6 9.0 7.6 Settlements 5.7 3.5 3.0 2.1 3.9 3.0 Indigenousforest 2.2 6.7 6.2 11.6 4.8 10.3 Dams/waterreservoirs 0.1 0.5 0.0 0.0 0.0 0.3 Woodland/thicket 0.0 0.0 2.0 9.0 1.3 7.3 AsurveyofthehighlandgrasslandendemicsinMauNarok/MoloIBA:Ndangangaetal BullABC Vol 10No 1-65 vegetables, occupied most ofthis area. Elsewhere in Mau nant grasslands at Mau Narok/Molo IBA were larger, Narok, where the Masai are the principal land-users, although isolated by large areas under cereals, probably grasslands covered 43.2%. In particular, more extensive because most land holdings are larger in Mau Narokand grasslandswerefoundin two regionsofMauNarok: west Molo than in Kinangop6. ofMauNaroktown aroundOlokurto, andsouthofMau Throughout the study area continuous grasslands Narok between Olorropil and south through 01 Chorro appear to survive mostly along shallow sloping valleys. and 01Joro. Seventeen (46%) of the surveyed grasslands were along Principal crops in cultivatedareasofMasai landwere watercourses and none was <5 ha. Most grasslands were barley and wheat, which mainly occurred on extensive heavilygrazedandhadshortgrass,astheMasaikeeplarge farms accessible to agricultural machinery (Fig 2). The herds ofcattle on these areas. We counted 2,351 cows, Masai communitytraditionallypractised pastoralism and 7,307 sheep and goats, and 42 donkeys within an areaof tended to abandon extensive pasture to their livestock c2,000ha,atagrazingintensityofninelargeanimal units (Fig3). This practice is, however, becoming rarer due to (LAU) perha. Weassumethatasingle LAU isequivalent theadventoflarge-scalecropcultivation.Barleyandwheat, to one cow or five sheep, and represents the metabolic whicharepotentiallymorelucrativethanlivestockfarming, equivalentofa454-kgcow7 arecurrentlybeingincreasinglycultivatedandposeamajor A higher proportion (15) ofthe plots had moderate threat, especially to large grasslands in southern Mau tussockcover. Onlytwo plots haddensetussock, whereas Narok.Theremaininggrasslandsarenowheavilygrazedas nine plots completely lacked or had just a few scattered the pastoralistsstill herdlarge numbers ofcattle. tussocks. Sharpes Longclaw strongly prefers short grass IncomparisontoKinangopGrasslands IBA, therem- with tussocks34. Mostofthesurveyplots (62%) hadshort grasswith tussocks. Most (20) of the surveyed grasslands were >20 ha, whereas 13were5-20ha.Onlyfourpatcheswere<5hain size.The82pointswhereland-usewassurveyedcovereda total areaof14,496 ha (c36% ofthe IBA). Training SSG members, awareness and contacts The three SSG members from Kinangop gained skills in grassland bird survey techniques. Posters have been developed by the Friends of Kinangop Plateau to raise awareness concerning the importance of conserving Kinangop Grassland IBA, which faces similar threats to MauNarok/Molo.Thirteenofthelatterposters,22national posterswithinformationconcerningall Kenyan IBAsand Figure2. Largebarleyandwheatplantationsarereplacing grasslands,withsmallgrasslandstripsbeingleftalongwatercourses 25 Kenyan IBAfactsheetsweredistributed. Talksoutlin- (Kariuki Ndang’ang’a) Figure3. RemnantareasofthepreferredhabitatofSharpe’s Figure4.Asurveymemberpresentsanawarenesstalktopupilsat LongclawMacronyxsharpei(shortgrasswithtussocks) inthe alocalprimaryschoolinMolo (KariukiNdang’ang’a) Masai-occupiedareaofOlokurtoarea,MauNarok(Kariuki Ndang’ang’a) 66-BullABC Vol 10No 1 AsurveyofthehighlandgrasslandendemicsinMauNarok/MoloIBA:Ndangangaetal ingtheconservationimportanceoftheIBAweremadeto References children and teachers at two schools (By-Gum and 1. Bennun,L.andNjoroge,P.1999.ImportantBirdAreasin Segututou primary schools), and informative material Kenya. Nairobi: NatureKenya. presented to a student and headmaster at two additional 2. BirdLife International. 2000. Threatened Birds ofthe schools(Fig4).SevencontactskeentoformaSiteSupport World. Cambridge, UK: BirdLife International & Groupweremade. Barcelona: LynxEdicions. 3. Lens, L., Muchai, M., Bennun, L.A. andDuchateau, L. Recommendations 2000.Conservationplanninginanagriculturallandscape: thecaseofSharpe’s Longclaw. Ostrich71: 300-303. • Initiate Site Support Group(s) for the IBA, based on 4. Muchai, S.M. 1998. Some aspects ofthe conservation existingandother, strategicallysoughtcontacts. biologyofSharpe’sLongclaw(MacronyxsharpeiJackson • Identify landowners and/or community leaders who 1904): a Kenyan grassland endemic bird. MSc. thesis. controlthemanagementoflargeareasofland,anduse Eldoret: Moi University. themasfocalpointstoinfluencemanagementofsuch 3. Muchai, M., Lens, L. and Bennun, L. 2002. Habitat areas to the benefitofconservation. selectionandconservationofSharpe’sLongclaw(.Macronyx • Determine those grasslandmanagementpractices (eg sharpei), a threatened Kenyan grassland endemic. Biol. stockinglevels) thatarecompatiblewithconservation Conserv. 103: 271-277. ofkey bird species, and the economic costs oftheir 6. Ndang’ang’a, P.K., du Plessis, M.A., Ryan, P.G. and Bennun, L.A. 2002. Grassland decline in Kinangop adoption, throughwell-focused research. Plateau,Kenya.ImplicationsforconservationofSharpe’s LongclawMacronyxsharpei.Biol. Conserv.107:341-350. Acknowledgements 7. Owen-Smith,N.andDanckwerts,J.E. 1997.Herbivory. WearegratefultotheFriendsofKinangopPlateau(FoKP), In: Cowling R.M., Richardson, D.M. and Pierce, S.M. in particular Andrew Mwangi, Jacob Njoroge and Pius (eds) Vegetation ofSouthern Africa. Cambridge, UK: Njoroge for their immense contribution in the field, and Cambridge UniversityPress. thosefarmerswhopermittedaccesstotheirland. Funding 8. Republic of Kenya. 2001. The 1999 Population and for the fieldworkwas provided byAfrican Bird Club to HousingCensus1999.Vol 1.Nairobi: CentralBureauof & Nature Kenya and the Ornithology Department of the Statistics, MinistryofFinance Planning. NationalMuseumsofKenya.TheOrnithologyDepartment OrnithologyDepartment,NationalMuseumsofKenya,P.O.Box providedequipmentusedduringthe survey. 40658, 00100 GPO Nairobi, Kenya. E-mail: [email protected]. Supported by ABC ConservationFund AsurveyofthehighlandgrasslandendemicsinMauNarok/MoloIBA:Ndang’ang’aetal BullABCVol 10No 1-67

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