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Associated Maps
Ecoregions of Texas...1
South Texas Plains.4
Associated Tables
The Texas Priority Species List.1
Priority Species
GroupSpecies NameCommon NameState/Federal StatusBirdsAimophila botteriiBotteri's SparrowSCAimophila cassiniiCassin's SparrowSCAimophila ruficepsRufous-crowned SparrowSCAmazilia yucatanensisBuff-bellied HummingbirdSCAmazona viridigenalisRed-crowned ParrotSCAmmodramus bairdiiBaird's Sparrow (42 accepted state records)SCAmmodramus maritimusSeaside SparrowSCAmmodramus savannarumGrasshopper SparrowSCAmphispiza bilineataBlack-throated SparrowSCAnas acutaNorthern PintailSCAnas fulvigulaMottled DuckSCAnthus spragueiiSprague's PipitSCAquila chrysaetos Golden EagleSCArenaria interpresRuddy TurnstoneSCAsio flammeusShort-eared OwlSCAsturina nitidusGray HawkSTAthene cuniculariaBurrowing OwlSCAythya affinisLesser ScaupSCAythya americanaRedheadSCAythya valisineriaCanvasbackSCBartramia longicaudaUpland Sandpiper SCBotaurus lentiginosusAmerican BitternSCButeo albicaudatusWhite-tailed HawkSTButeo albontatusZone-tailed HawkSTButeo lineatusRed-shouldered HawkSCButeo regalis Ferruginous HawkSCButeo swainsoniSwainson's HawkSCButeogallus anthracinusCommon Black-HawkSTCalcarius mccowniiMcCown's LongspurSCCalidris albaSanderlingSCCalidris canutusRed KnotSCCalidris himantopusStilt SandpiperSCCalidris mauriWestern SandpiperSCCallipepla squamataScaled QuailSCCamptostoma imberbeNorthern Beardless-TyrannuletSTCampylorhynchus brunneicapillusCactus WrenSCCaprimulgus carolinensisChuck-will's-widowSCCardinalis sinuatusPyrrhuloxiaSCChaetura pelagicaChimney SwiftSCCharadrius alexandrinusSnowy PloverSCCharadrius melodus**Piping PloverFT/STCharadrius montanus Mountain PloverSCCharadrius wilsoniaWilson's PloverSCChloroceryle americanaGreen KingfisherSCChondestes grammacusLark SparrowSCChondrohierax uncinatusHook-billed KiteSCChordeiles minorCommon NighthawkSCCircus cyaneusNorthern HarrierSCCistothorus platensisSedge WrenSCCoccyzus americanusYellow-billed CuckooSCColinus virginianusNorthern BobwhiteSCColumba flavirostris Red-billed PigeonSCContopus virensEastern Wood-PeweeSCCorvus imparatusTamaulipas CrowSCCoturnicops noveboracensisYellow RailSCCyanocorax morioBrown JaySCDendrocygna bicolorFulvous Whistling-DuckSCDendroica dominicaYellow-throated WarblerSCEgretta caeruleaLittle Blue HeronSCEgretta rufescensReddish EgretSTEgretta thulaSnowy EgretSCEgretta tricolorTricolored HeronSCElanoides forficatusSwallow-tailed KiteSTEremophila alpestrisHorned LarkSCFalco columbarius MerlinSCFalco femoralisAplomado FalconFE/SEFalco peregrinus tundriusArctic Peregrine FalconSTFalco sparveriusAmerican Kestrel (Southeastern)SCGallinago delicataWilson's Snipe (formerly Common Snipe)SCGeothlypis trichasCommon Yellowthroat (Brownsville)SCGlaucidium brasilianumFerruginous Pygmy-OwlSTHaematopus palliatusAmerican OystercatcherSCHimantopus mexicanusBlack-necked StiltSCHylocichla mustelinaWood ThrushSCIcterus cucullatusHooded Oriole (both Mexican & Sennett's)SCIcterus graduacaudaAudubon's OrioleSCIcterus gularisAltamira OrioleSCIcterus spuriusOrchard OrioleSCIctinia mississippiensisMississippi KiteSCIxobrychus exilisLeast BitternSCLanius ludovicianusLoggerhead ShrikeSCLaterallus jamaicensisBlack RailSCLimnodromus griseusShort-billed DowitcherSCLimosa fedoaMarbled GodwitSCLimosa haemasticaHudsonian GodwitSCMelanerpes aurifronsGolden-fronted WoodpeckerSCMicrathene whitneyi Elf OwlSCMycteria americana**Wood StorkSTMyiarchus crinitusGreat Crested FlycatcherSCNumenius americanusLong-billed CurlewSCNumenius phaeopusWhimbrelSCNyctanassa violaceaYellow-crowned Night-HeronSCOrtalis vetulaPlain ChachalacaSCPachyramphus aglaiaeRose-throated Becard (30 accepted state records)STParabuteo unicinctusHarris's HawkSCParula pitiayumiTropical ParulaSTParus atricristatus Black-crested TitmouseSCPasserina cirisPainted BuntingSCPasserina versicolorVaried BuntingSCPegadis chihiWhite-faced IbisSTPelecanus erythrorhynchosAmerican White PelicanSCPelecanus occidentalis**Brown PelicanFT/SEPlatalea ajajaRoseate SpoonbillSCPluvialis dominicaAmerican Golden-PloverSCPodiceps nigricollisEared GrebeSCPolioptila melanuraBlack-tailed GnatcatcherSCPorphyrio martinicaPurple GallinuleSCProtonotaria citreaProthonotary WarblerSCRallus elegansKing RailSCRallus limicolaVirginia RailSCRallus longirostrisClapper RailSCRecurvirostra americanaAmerican AvocetSCRynchops nigerBlack SkimmerSCScolopax minorAmerican WoodcockSCSpiza americanaDickcisselSCSpizella breweriBrewer's SparrowSCSpizella pusillaField SparrowSCSporophila torqueolaWhite-collared SeedeaterSCSterna forsteriForster's TernSCSterna niloticaGull-billed TernSCSturnella magnaEastern MeadowlarkSCSturnella neglectaWestern MeadowlarkSCToxostoma curvirostreCurve-billed ThrasherSCToxostoma longirostreLong-billed ThrasherSCToxostoma rufumBrown ThrasherSCTringa flavipesLesser YellowlegsSCTringa melanoleucaGreater YellowlegsSCTringa solitariaSolitary SandpiperSCTryngites subruficollisBuff-breasted SandpiperSCTyrannus forficatusScissor-tailed FlycatcherSCTyrannus tyrannusEastern KingbirdSCTyto albaBarn OwlSCVermivora pinusBlue-winged WarblerSCVireo atricapillus**Black-capped VireoFE/SEVireo belliiBell's VireoSCVireo flavifronsYellow-throated VireoSCVireo gilvusWarbling VireoSCWilson's PhalaropeWilson's PhalaropeSCZenaida macrouraMourning DoveSCMammalsFelis pardalis**Ocelot FE/SEGeomys attwateriAttwaters Pocket GopherSCGeomys personatusMaritime Pocket GopherSCGeomys streckeriiStrecker's Pocket GopherSCGeomys texensis bakeriFrio Pocket GopherSCHerpailurus yaguarondiJaguarundiFE/SELasiurus egaSouthern Yellow BatSTLasiurus xanthinusWestern Yellow BatSCMormoops megalophyllaGhost-faced BatSCMustela frenataLong-tailed WeaselSCMyotis veliferCave MyotisSCMyotis yumanensisYuma MyotisSCNasua naricaWhite-nosed CoatiSTNotisorex crawfordiiDesert Shrew SCNyctinomops macrotisBig Free-tailed BatSCOryzomys couesiCoues Rice RatSTPuma concolorMountain LionSCSpilogale gracilisWestern Spotted SkunkSCSpilogale putoriusEastern Spotted SkunkSCTadarida brasiliensisMexican Free-tailedSCTaxidea taxusAmerican Badger SCReptilesAlligator mississippiensisAmerican Alligator (4 sp.)SCCemophora coccineaScarlet Snake STCrotaphytus reticulatusReticulate Collared Lizard STDrymarchon coraisWestern Indigo Snake STDrymobius margaritiferusSpeckled Racer STGopherus berlandieriTexas TortoiseSTHeterodon nasicus gloydiDusty Hog-nosed Snake SCHolbrookia lacerataSpot-tailed Earless Lizard SCHolbrookia propinquaKeeled Earless LizardSCHypopachus variolosusSheep Frog STMacrochelys temminckiiAlligator Snapping Turtle STNotophthalmus meridionalisBlack-spotted Newt STOphisaurus attenuatusSlender Glass Lizard SCPhrynosoma cornutumTexas Horned LizardSTPhrynosoma modestumRound-tailed Horned Lizard SCScaphiopus hurteriiHurters Spadefoot SCSiren sp.Rio Grande (Lesser) Siren STSistrurus catenatusMassasaugaSCSyrrhophus cystignathoidesRio Grande Chirping FrogSCTerrapene spp.Box Turtles SC
GroupFamilySpecies NameFederal StatusInvertebratesStylommatophora (Gastropoda)PolygyridaeEuchemotrema leai cheatumiSCSchizomida (Myriapoda)Protoschizomidae?Agastoschizomus n.sp.SCPolydesmida (Myriapoda)PolydesmidaeSpeodesmus falcatusSCPolydesmidaeSpeodesmus ivyiSCPolydesmidaeSpeodesmus reddelliSCAraneae (Arachnida)DictynidaeCicurina baroniaFEDictynidaeCicurina gatitaSCDictynidaeCicurina madlaFEDictynidaeCicurina medinaSCDictynidaeCicurina minorata (Gersch and Davis)SCDictynidaeCicurina pabloSCDictynidaeCicurina pateiSCDictynidaeCicurina porteriSCDictynidaeCicurina riogrande (Gertsch and Mulaik)SCDictynidaeCicurina rudimentops (Chamberlin and Ivie)SCDictynidaeCicurina selectaSCDictynidaeCicurina serenaSCDictynidaeCicurina sintoniaSCDictynidaeCicurina uvaldeSCDictynidaeCicurina veniiFEDictynidaeCicurina vesperaFEDictynidaeCicurina watersiSCLeptonetidaeNeoleptoneta new speciesSCLeptonetidaeNeoleptoneta valverde (Gertsch)SCNesticidaeEidmannella nasuta (Gertsch)SCOpiliones (Arachnida)PhalangodidaeTexella homiSCPseudoscorpiones (Arachnida)Bochidae Leucohya texanaSCNeobisiidaeTartarocreagris cookeiSCNeobisiidaeTartarocreagris reyesiSCColeoptera (Insecta)AnobiidaePtinus tumidus (Fall)SCAnobiidaeTrichodesma pulchella (Schaeffer)SCAnobiidaeTrichodesma sordida (Horn)SCAnobiidaeTrichodesma texana (Schaeffer) SCAnobiidaeTricorynus texanus (White)SCAnthribidaeNeoxenus versicolor (Valentine)SCAnthribidaeOrmiscus albofasciatus (Schaeffer)SCAnthribidaeOrmiscus irroratus (Schaeffer)SCAnthribidaePhoenicobiella schwarzii (Schaeffer)SCAnthribidaeToxonotus penicellatus (Schaeffer)SCBrentidaeApion aculeatum (Fall)SCBrentidaeApion buchanani (Kissinger)SCBrentidaeHeterobrenthus texanus (Schaeffer)SCBuprestidaeAgrilus dollii (Schaeffer)SCBuprestidaeAgrilus subtropicus (Schaeffer)SCBuprestidaePachyschelus fisheri (Vogt)SCBuprestidaeSpectralia prosternalis (Schaeffer)SCBuprestidaeTrigonogya reticulaticollis (Schaeffer)SCCarabidaeAgra oblongopunctata oblongopunctata (Chevrolat)SCCarabidaeApenes sp. UASM 11 SCCarabidaeCalleida fimbriata (Bates)SCCarabidaeGalerita aequinoctialis (Chaudoir)SCCarabidaeNemotarsus rhombifer (Bates)SCCarabidaeRhadine exilisFECarabidaeRhadine infernalisFECerambycidaeAdetus sp. EGR 1 SCCerambycidaeAgallissus lepturoides (Chevrolat)SCCerambycidaeAtaxia tibialis (Schaeffer)SCCerambycidaeCacostola lineata (Hamilton)SCCerambycidaeCallipogonius cornutus (Linsley)SCCerambycidaeDesmiphora aegrota (Bates)SCCerambycidaeDihammaphora dispar (Chevrolat)SCCerambycidaeEcyrus penicillatus (Bates)SCCerambycidaeHemierana marginata suturalis (Linell)SCCerambycidaeSphaenothecus trilineatus (Dupont)SCChrysomelidaeBaliosus sp. EGR 1 SCChrysomelidaeBrucita marmorata (Jacoby)SCChrysomelidaeChaetocnema rileyi (White)SCChrysomelidaeChlamisus maculipes (Chevrolat)SCChrysomelidaeDibolia championi (Jacoby)SCChrysomelidaeDisonycha barberi (Blake)SCChrysomelidaeDisonycha stenosticha (Schaeffer)SCChrysomelidaeEpitrix sp. EGR 1 SCChrysomelidaeHeptispa sp. EGR 1 SCChrysomelidaeMalacorhinus acaciae (Schaeffer)SCChrysomelidaeMegascelis texana (Linell)SCChrysomelidaeOctotoma championi (Baly)SCChrysomelidaePachybrachis duryi (Fall)SCChrysomelidaePachybrachis sp. EGR 2 SCChrysomelidaePachybrachis sp. EGR 6 SCChrysomelidaeParchicola sp. EGR 1 SCChrysomelidaePentispa distincta (Baly)SCChrysomelidaePlagiodera thymaloides (Stal)SCCicindelidaeCicindela cazieriSCCoccinellidaeDiomus pseudotaedatus (Gordon)SCCoccinellidaeHyperaspis rotunda (Casey)SCCurculionidaeAllopentarthrum sp. TAC 1 SCCurculionidaeAllopentarthrum sp. TAC 2 SCCurculionidaeAndranthobius sp. TAC 1 SCCurculionidaeApteromechus texanus (Fall)SCCurculionidaeBrachystylus microphthalmus (Champion)SCCurculionidaeChalcodermus semicostatus (Schaeffer)SCCurculionidaeChalcodermus serripes (Fahraeus)SCCurculionidaeConotrachelus rubescens (Schaeffer)SCCurculionidaeElleschus sp. TAC 1 SCCurculionidaeEubulus sp. TAC 1 SCCurculionidaeHaplostethops sp. TAC 1SCCurculionidaeNotolomus sp. TAC 1 SCCurculionidaeNotolomus sp. TAC 2 SCCurculionidaePlatyomus flexicaulis (Schaeffer)SCCurculionidaePlocetes versicolor (Clark)SCElateridaeAnchastus augusti (Candeze)SCLanguriidaeHapalips texanus (Schaeffer)SCLanguriidaeLoberus ornatus (Schaeffer)SCLanguriidaeToramus chamaeropis (Schaeffer)SCMycetophagidaeBerginus sp. EGR 1 SCPhengodidaeCenophengus pallidus (Schaeffer)SCPtilodactylidaeLachnodactyla texana (Schaeffer)SCSalpingidaeDacoderus n. sp. (Aalbu & Andrews, ms.)SCScarabaeidaeDeltochilum scabriusculum scabriusculum (Bates)SCScarabaeidaeMalagoniella astyanax yucateca (Harold)SCScarabaeidaeOnthophagus batesi (Howden & Cartwright)SCScarabaeidaePhanaeus adonis (Harold)SCStaphylinidae (Pselaphinae)Batrisodes (Babnormodes) uncicornis (Casey)SCTenebrionidaeRhypasma sp. EGR 1 SCTenebrionidaeStrongylium aulicum (Maklin)SCTenebrionidaeStrongylium championi (Gebien)SCTenebrionidaeTalanus mecoselis (Triplehorn)SCLepidoptera (Insecta)HesperiidaeMegathymus streckeri texanusSCHesperiidaeStallingsia maculosusSCSaturniidaeAgapema galbinaSCSaturniidaeSphingicampa blanchardiSCHymenoptera (Insecta)ApoideaAndrena (Micrandrena) micheneri (Ribble)SCApoideaAndrena (Scrapteropsis) flaminea (LaBerge)SCApoideaAnthophorula (Anthophorisca) ignota (Timberlake)SCApoideaBrachynomada (Melanomada) sp. ASCApoideaCalliopsis (Verbenapis) michenerella (Shinn & Engel)SCApoideaCoelioxys (Xerocoelioxys) piercei (Crawford)SCApoideaColletes saritensis (Stephen)SCApoideaHolcopasites (Holcopasites) jerryrozeni (Neff)SCApoideaMacrotera (Cockerellula) lobata (Timberlake)SCApoideaMacrotera (Cockerellula) robertsi (Timberlake)SCApoideaMegachile (Megachiloides) parksi (Mitchell)SCApoideaOsmia (Diceratosmia) botitena (Cockerell)SCApoideaPerdita (Cockerellia) fraticincta (Timberlake)SCApoideaPerdita (Cockerellia) tricincta (Timberlake)SCApoideaPerdita (Epimacrotera) dolanensis (Neff)SCApoideaPerdita (Hexaperdita) agasta (Timberlake)SCApoideaPerdita (Perdita) fidissima (Timberlake)SCApoideaProtandrena (Heterosarus) subglaber (Timberlake)SC
Location and Condition of the South Texas Plains Ecoregion
Bounded on the west by the Rio Grande and Mexico, and on the north by the Balcones Escarpment, the South Texas Brush Country is vast, serene, and unpopulated (Winkler, 1982). Elevations range from sea level to 1,000 feet AMSL and rainfall varies from 30 inches in the east to 16 inches in the west. Soils are varied and highly complex. Generally extremely basic to slightly acidic, they range from deep sands to tight clays and clay loams. With average annual temperatures around 73F, the South Texas Plains boasts the longest growing season in Texas, lasting up to 365 days in some years at Brownsville (Simpson, 1988). This warm region is, however, a land of recurrent droughts, a factor which distinctly marks the landscape. Nearly everything that grows here is drought-tolerant, as rainfall is well below the amount needed for conventional forest trees (Wasowski, 1988). Sporadic rains, however, will trigger wildflowers to bloom unexpectedly at almost any time of year.
The South Texas region owes its diversity to the convergence of the Chihuahuan desert to the west, the Tamaulipan thornscrub and subtropical woodlands along the Rio Grande to the south and the coastal grasslands to the east. Essentially a gently rolling plain, the region is cut by arroyos and streams, and is blanketed with low-growing vegetation--mesquite, granjeno, huisache, catclaw, blackbrush, cenizo and guayacan. Wherever conditions are suitable, there is a dense understory of smaller trees and shrubs such as coyotillo, paloverde, Mexican olive, and various species of cacti. The woody vegetation of the South Texas Plains is so distinctive that the area is also referred to as the "brush country."
The Lower Rio Grande Valley is a highly distinctive subregion of the South Texas Plains. Usually defined as Cameron, Willacy, Hidalgo, and Starr counties, it contains the only subtropical area in Texas. Once supporting majestic groves of Texas palmetto, Montezuma cypress, tall ebony-anaqua woodlands, and jungle-like expanses of Tamaulipan thorny shrubs, today much of it has been bulldozed, plowed or paved. In fact, the once extensive groves of the native Sabal palm which used to flourish here are now reduced to only a few stands near Brownsville. Soils in this subtropical region range from sands to heavy clays. Clays and extremely poor drainage dominate the resaca areas (old meandering paths of the Rio Grande) (Wasowski, 1988).
Despite a history of land use that is the oldest in the state, the Rio Grande Plain harbors many rare species of plants and animals (Texas General Land Office, 1984). It is here that a few wild tropical cats--ocelots and jaguarundis--still take refuge. Other special animals include ferruginous pygmy-owl, green jay, elf owl, Texas tortoise, indigo snake and Mexican burrowing toad. There are also a surprising number of plants that occur here and nowhere else, especially among the cactus family, like Albert's black lace cactus, star cactus, and Runyon's cory cactus.
This ecoregion can be broken down into eight main habitat classes consisting of brushland, forest, native and introduced grasses, parkland, woodland, woodland, forest and grassland mosaic, parkland woodland mosaic, and urban.
South Texas Plains Brushland
The South Texas Plains brushland consists of woody plants mostly less than nine feet tall which are dominant and growing as closely spaced individuals, clusters or closed canopied stands (greater than 10% canopy cover). Typically there is continuous, impenetrable cover of shrubs which are over 75% of the ground (McMahan et al. 1984, Bridges et al. 2002). Two plant associations dominate this habitat class.
The ceniza-blackbrush-creosote association is normally found on the slopes of the Rio Grande River basin, Stockton Plateau, and South Texas plains which occur from Val Verde County, in the city of Langtry, to Zapata County near San Ygnacio (McMahan et al. 1984, Diamond 1993). This community typically grows on shallow soils (Diamond 1993). Commonly associated plants include guajillo, lotebush, mesquite, guayacan, Texas pricklypear, paloverde, goatbush, yucca, sotol, desert yaupon, catclaw acacia, kidneywood, allthorn, curly mesquite, Texas grama, hairy tridens, slim tridens, pink pappusgrass, and two-leaved senna (McMahan et al. 1984). Cross-referenced communities: 1) ceniza series (Diamond 1993), 2) cenizo-blackbrush xerophytic brush (Bezanson 2000), and 3) blackbrush-cenizo-guajillo shrubland alliance (Weakley et al. 2000). The ceniza-blackbrush-creosote community is apparently secure within the state as well as globally (Diamond 1993). This community is common and widespread, therefore, it is considered a fairly low priority for further protection (Bezanson 2000).
The mesquite-blackbrush association comprises the following plants: lotebush, ceniza, guajillo, desert olive, allthorn, whitebrush, bluewood, granjeno, guayacan, leatherstem, Texas pricklypear, tasajillo, kidneywood, yucca, desert yaupon, goatbush, purple three-awn, pink pappusgrass, hairy tridens, slim tridens, hairy grama, mat euphorbia, coldenia, dogwood, knotweed leafflower, and two-leaved senna. This association is typically found on upland shallow, loamy or gravelly soils in the south Texas plains ecoregion (McMahan et al. 1984). Cross-referenced communities: 1) freer mixed brush (Davis and Spicer 1965), 2) barretal (USFWS 1983), 3) blackbrush-twisted acacia (McLendon 1991), 4) blackbrush series (Diamond 1993), 5) blackbrush xerophytic brush (Bezanson 2000), and 6) blackbrush-cenizo-guajillo shrubland alliance (Weakley et al. 2000). The mesquite-blackbrush association is demonstratably secure globally and within the state of Texas (Diamond 1933). As a whole, this community is stable and common, however, there are a few plants found within this association that are rare and should have selective protection (USWFS 1983, Weakley et al. 2000). This community is considered low priority for further protection, excluding the discriminatory protection of a few rare species (Bezanson 2000).
South Texas Plains Forest
The South Texas Plains forest consists of deciduous or evergreen trees that are dominant in the landscape. These species are mostly greater than 30 feet tall with closed crowns or nearly so (71-100% canopy cover). The midstory is generally apparent except in managed monocultures (McMahan et al. 1984, Bridges et al. 2002). Only one plant association dominates this habitat class.
American elm, cedar elm, cottonwood, sycamore, black willow, live oak, Carolina ash, bald cypress, water oak, hackberry, virgins bower, yaupon, greenbriar, mustang grape, poison oak, Johnsongrass, Virginia wildrye, Canada wildrye, rescuegrass, frostweed, and western ragweed are species commonly found in the pecan-elm association (McMahan et al 1984). This community is a broadly defined deciduous forest typically found along major rivers, bottomlands and mesic slopes where soils are often heavily textured and calcareous (Diamond 1993). This community is found along the Brazos, Colorado, Guadalupe, San Antonio, and Frio river basins as well as the areas of the Navidad, San Bernard, and Lavaca rivers (McMahan et al 1984). Cross-referenced communities: 1) sugarberry-elm series, pecan-sugarberry series (Diamond 1993), 2) sugarberry-elm floodplain forests (South Texas Plains) (Bezanson 2000), and 3) plateau oak-sugarberry woodland alliance, sugarberry-cedar elm temporarily flooded forest alliance, pecan-(sugarberry) temporarily flooded forest alliance (Weakley et al. 2000). The pecan-elm community is apparently secure within the state as well as globally (Diamond 1993). However, there are very few mature examples of the dominant plants in this community. The locations in south Texas that do exist are not very well protected but there are many examples of this community in other ecoregions. Due to this, Bezanson (2000) suggests to rank this community as a medium priority for further protection in south Texas.
South Texas Plains Native and Introduced Grasses
A mixture of native and introduced grasses which includes herbs (grasses, forbs, and grasslike plants) that are dominant with woody vegetation lacking or nearly so (generally 10% or less woody canopy cover). These associations typically result from the clearing of woody vegetation and can be easily associated with the early stages of a young forest. This community is located in northeast and east central Texas, the South Texas Plains, and the Gulf Coast Prairies and Marshes ecoregion. This community can quickly change as removed brush begins to regrow (McMahan et al. 1984, Bridges et al. 2002).
South Texas Plains Parkland
In the South Texas Plains parkland, a majority of the woody plants are equal to or greater than nine feet tall. They are generally dominant and grow as clusters, or as scattered individuals within continuous grass or forbs (11-70% woody canopy cover overall) (McMahan et al. 1984, Bridges et al. 2002). Two plant associations dominate this habitat class.
The mesquite-granejo association is found mainly on loamy or sandy upland soils in the South Texas Plains. Commonly associated plants include bluewood, lotebush, coyotillo, guayacan, Texas colubrina, tasajillo, Texas pricklypear, Pan American balsamscale, single-spike paspalum, hooded windmillgrass, tanglehead, Roemer three-awn, purple three-awn, tumble lovegrass, Lindheimer tephrosia, bullnettle, croton spp., slender evolvulus, Texas lantana, silverleaf nightshade, and firewheel. Cross-referenced communities: 1) mesquite-granjeno shrubland/dry woodland (McLendon 1991), 2) mesquite-granjeno series (Diamond 1993), 3) upland mesquite savannas (Bezanson 2000), and 4) honey mesquite woodland alliance (Weakley et al. 2000). The mesquite-granejo community is considered demonstrably secure globally and within the state of Texas (Diamond 1933). It is suggested that this community is of low priority for further protection (Bezanson 2000).
Huisache, huisachillo, whitebrush, granjeno, lotebush, Berlandier wolfberry, blackbrush, desert yaupon, Texas pricklypear, woollybucket bumelia, tasajillo, agarito, Mexican persimmon, purple three-awn, Roemer three-awn, pink pappusgrass, Halls panicum, slimlobe poppymallow, sensitive briar, two-leaved senna, and mat euphorbia are species commonly linked to the mesquite-live oak-bluewood association. Typically, this association is found on loamy or sandy upland soils in the South Texas Plains. Locations of this community are primarily found in Uvalde, Bee, and Medina counties in the South Texas Plains. Cross-referenced communities: 1) mesquite-granjeno shrubland/dry woodland (McLendon 1991), 2) mesquite-granjeno series (Diamond 1993), 3) upland mesquite savannas (Bezanson 2000), and 4) honey mesquite woodland alliance (Weakley et al. 2000). The mesquite-live oak-bluewood community is considered demonstrably secure globally and within the state of Texas (Diamond 1933). It is suggested that this community is of low priority for further protection (Bezanson 2000).
South Texas Plains Woodland
In the South Texas Plains woodland, a majority of the woody plants are mostly 9-30 feet tall with closed crowns or nearly so (71-100% canopy cover). Typically the midstory is usually lacking any vegetation (McMahan et al. 1984, Bridges et al. 2002). One plant association dominates this habitat class.
The mesquite-granejo association is located primarily in Jim Wells and Kleberg counties in the South Texas Plains. Commonly associated plants include whitebrush, virgins bower, desert olive, retama, Texas pricklypear, bluewood, lotebush, desert yaupon, tasajillo, guayacan, woollybucket bumelia, Berlandier wolfberry, catclaw acacia, Halls panicum, pink pappusgrass, purple three-awn, woodsorrel, and field ragweed. Typically, this association is found on loamy or sandy upland soils in the South Texas Plains. Cross-referenced communities: 1) mesquite-granjeno shrubland/dry woodland (McLendon 1991), 2) mesquite-granjeno series (Diamond 1993), 3) upland mesquite savannas (Bezanson 2000), and 4) honey mesquite woodland alliance (Weakley et al. 2000). The mesquite-granejo community is considered demonstrably secure globally and within the state of Texas (Diamond 1933). It is suggested that this community is of low priority for further protection (Bezanson 2000).
South Texas Plains Woodland, Forest, and Grassland Mosaic
The South Texas Plains woodland, forest, and grassland mosaic is a combination of a few characters from each individual habitat class. Woody plants that are mostly 9-30 feet tall are growing with deciduous or evergreen trees that are dominant and mostly greater than 30 feet tall. Between patches of woody vegetation grow herbs (grasses, forbs, and grasslike plants) where woody vegetation is lacking or nearly so (generally 10% or less woody canopy cover). In this mosaicked habitat, there is a mix between absent canopy cover and areas with closed crowns or nearly so (71-100% canopy cover). In the areas with canopy cover, there ranges a lack of midstory to a midstory that is generally apparent except in managed monocultures (McMahan et al. 1984, Bridges et al. 2002).
Blackjack oak, eastern red cedar, mesquite, black hickory, live oak, sandjack oak, cedar elm, hackberry, yaupon, poison oak, American beautyberry, hawthorn, supplejack, trumpet creeper, dewberry, coral-berry, little bluestem, silver bluestem, sand lovegrass, beaked panicum, tree-awn, spranglegrass, and tickclover are species commonly associated with the post oak association. This community is most commonly found in sandy soils in the Post Oak Savannah but is also found in the northeastern most portions of the South Texas Plains (McMahan et al 1984). Cross-referenced communities: 1) post oak-blackjack oak series (Diamond 1993), 2) post oak-blackjack oak upland forest and woodlands (Bezanson 2000), and 3) post oak-blackjack oak forest alliance, post oak-blackjack oak woodland alliance (Weakley et al. 2000). The post oak community is considered demonstrably secure globally and within the state of Texas (Diamond 1933). It is suggested that this community is of low priority for further protection (Bezanson 2000).
South Texas Plains Parkland Woodland Mosaic
The parkland woodland mosaic can be best described by pastures or fields with widely scattered vegetation (trees and/or shrubs) covering 10-25% of the ground (Bridges et al. 2002). There is only one plant association in this habitat class (McMahan et al. 1984, Bridges et al. 2002).
The live oak association is principally on sandy soils in Brooks and Kenedy counties. Commonly related plants include the following: Texas pricklypear, lime pricklyash, greenbriar, bushsunflower, tanglehead, crinkleawn, single-spike paspalum, fringed signalgrass, Lindheimer tephrosia, croton, silverleaf nightshade, bullnettle, Texas lantana, dayflower, silverleaf sunflower, and shrubby oxalis. Cross-referenced communities: 1) live oak savannas (South Texas Sand Sheet) (Bezanson 2000). The live oak community is stable, however it is considered a medium priority for further protection since this community it located on private lands (Bezanson 2000).
South Texas Plains Urban Community
Urban habitats are cities or towns which are areas dominated by human dwellings including the fences, shrub rows, windbreaks, and roads associated with their presence (Bridges at al. 2002). The two statistically important metropolitan areas of the Valley (Harlingen/San Benito/Brownsville, and McAllen/Mission/Edinburg) are amongst the 10 fastest growing in the country. Smaller, prominent cities include McAllen and surrounding suburbs, Kingsville, Laredo, Freer, Eagle Pass, Pleasanton, Del Rio, and Hondo. Economic development is a priority and urban sprawl continues being a major cause of habitat loss. The effect of non-native, invasive plants on wildlife (birds, butterflies, small reptiles) might be better understood by conducting science-based research and surveys.
As much as 97% of the native south Texas thorny brush ecosystem has been lost, primarily to agriculture and urban development. The urban landscape consists mainly of exotic, high maintenance plants that provide little or no habitat for both resident and migratory wildlife.
The remaining pockets of sabal palm trees and the abundance of other non-native palm trees are important elements of the urban landscape. Their importance resides in the fact that they provide roosting/nesting opportunities for birds (owls, orioles, etc), and at least two species of bats.
High Priority Communities
The Eocene sand barrens of the South Texas Plains are considered a critical habitat for further protection. This key community consists of deep, isolated sand dunes that occur on Eocene sandstone formations. Typically these outcrops are located in post oak woodlands in south and east Texas. These communities are known to support endangered plants such as the large-fruited sand verbena, one of the many rare endemic species located in these barrens (Bezanson and Wolfe 2001). According to Bezanson (2000) there are no known Eocene sand dune communities that are protected. Since these locations are small it would be very easy for conservation organizations to protect these key communities by buying land or through private landowner agreements.
The Lower Rio Grande valley brush habitat is considered an ecological transition zone between Mexico and the United States. This key community is not only home to many rare, threatened, and endangered species but it is also a stop-over for migrating Neotropical birds. This rare habitat only occurs in the southernmost portion of Texas and is found no where else in the nation (Bezanson and Wolfe 2001). It is a high priority to protect more of the Lower Rio Grande valley brush habitat community. Since 1970 this area has tripled in population and is expected to double again within 20 years. Presently, there are small conservation areas in this community but not enough continuous land to preserve wildlife species such as the endangered ocelot (Bezanson and Wolfe 2001).
Problems Affecting Habitat and Species
The Eocene sand dunes are most threatened from subdivision growth from an increase in the human population (Bezanson and Wolfe 2001).
In the Lower Rio Grande valley brush habitat there is significant growth in the human population. Approximately 90% of the Rio Grande Valley floodplain has been converted to agricultural land. General use, dams, and upstream diversions of the Rio Grande waters are reducing this river to a trickle in many points. Near the mouth of this river it is almost dry, especially during the summer months. It is a high priority that private landowner involvement and preservation of land by various organizations occur for the preservation of this key community. Education is also necessary to build public awareness and to involve them in the preservation of this rare and fragile community (Bezanson and Wolfe 2001).
Problems Affecting Habitat and Species
The common practice of trimming palm trees for aesthetical purposes effectively takes roosting/nesting opportunities away from the wildlife species found in the South Texas Plains ecoregion.
The demographic make-up of the area is predominantly Hispanic. Traditionally, Hispanics take less advantage of nature-related outdoor recreation.
Other Associated Problems and Threats to Species and Their Populations:
Improper Livestock GrazingDevelopment into intensive cropland, etc.Construction Activity (i.e. building roads, structures, hardscape)Modification of Natural Community with 110m of Population LocationUrbanization; Urban SprawlUtilitiesDirect Mortality with structuresCreation/Modification of large reservoirsInfrastructure (i.e. ditches, jetties collision structures, ship channels, navigation traffic)SiltationReservoirs and DamsFencingInhibited dispersal due to fragmentation Reduced genetic variability and reduced gene flow Foot trafficGarbageNoiseVegetation disturbancePopular with CollectorsDeforestation and Tree-harvestingFishing LineRecreationLand or Drainage Alteration; Land-use changes (i.e. draining, filling, bulkheading)Increased turbidityConflict with rookeriesDrainage of wetlandsGravel miningVandalismMine blasting; Cave ClosuresFood source is threatenedDisease and pathogens Forest pest epizootics (e.g., bark beetles, blister beetles, defoliating caterpillars, etc.) Animals (i.e. Feral goats, hogs, Big Game, Red Imported Fire Ants, carp, apple snails, E.Starling, poultry)Herbaceous Plants (i.e.Wild Mustard)Aquatic Plants (i.e. water hyacinth, hydrilla, cattail, giant salvinia, water trumpet)Grasses & Grass-like Plants (i.e. Fescue, Bahia, Bufflegrass, Bermudagrass, KR bluestem, Cogon grass)Woody Plants (i.e.coral bean, salt cedar, privet, ligustrum, Chinese tallow, Brazilian pepper)Brush eradicationFire suppressionLack of authority to manipulate water levels to improve bird habitatPlant successionGround-water PumpingSpecies or populations are considered destructiveHurricanesFlood EventsBrood parasitism (i.e. cowbirds, other brood parasites)Petroleum/Chemical spillsNon-point and point sourceContaminated water dischargeIndiscriminate Pesticide UseFragmentation due to tax policiesNative and non-native (i.e. coyote, feral cats, rats, feral dogs, racoon)Lack of ProtectionNaturally Limited RangeBeach CompactionNest DisturbanceEnergy ExpenditureDirect Mortality (i.e. road kill)Boat TrafficOff-roading
Priority Research and Monitoring Efforts
Identification of undisturbed palm tree sites or islands and an urban bat survey may help initiate a conservation plan.
Environmental education programs that address cultural/language barriers may assist in restoration and improved conservation.
Bat monitoring plan - Surveys could be conducted quarterly to capture presence/absence of resident and migratory species throughout the year and especially during spring and fall migration. In light of the recent incursion of neotropical birds to south Texas the documentation of accidental species, particularly those new to the United States, is especially important.
Educational materials - Simple, easy to read, bilingual brochures, presentations can be distributed to city planners, home builders, landscaping companies, nurseries, home improvement stores, etc.
Conservation and management workshops - Partnerships with local home/land owner organizations may assist in improved urban conservation.
Landowner incentive program - Urban landowners would be more likely to buy into urban conservation actions when technical/economic assistance is provided.
Promote outdoor recreational and educational opportunities that are family oriented. This would likely recruit more Hispanics into nature/wildlife conservation.
Determine degree and result of competition with local flora and fauna
Determine associated population diseases and monitor spread
Determine how manmade alterations influence species or populations (i.e. roads, fire breaks, structures)
Determine if population is disjunct and/or genetically stable over whole range or isolate
Identify foraging habitat requirements
Identify and quantify diet
Identify and study environmental parameters required for species or populations (i.e. temperature, humidity, seasons, plants)
Identify and study possibilities for artificial habitats
Determine habitat availability and monitor locations
Survey and monitor affect of species or populations on the local habitat
Determine affects of various management practices on species, populations, and habitats (i.e. prescribed burning, discing)
Monitor size of population
Monitor seasonal fluctuations in population size
Monitor long term trends in population size
Determine date of most recent occurrence in the region
Determine and document incidental take
Estimate life history parameters (i.e. litter size, survival, age at first reproduction, reproductive behavior)
Determine minimum viable population
Determine habitat range of species or population
Determine dispersal and movement patterns
Determine historical range and monitor movements
Monitor successful survey techniques
Centralized collection point for road mortalities
Identify, map, and ground truth locations and habitats
Develop and monitor live-trapping technique or techniques that have low mortality
Develop and monitor deterrents (in place of killing the animals or transporting them elsewhere)
Conservation Actions
Conduct a systematic survey of urban bats.
Produce educational materials (brochure, presentations, etc) on pros and cons of palm tree trimming.
Promote urban/suburban land/wildlife conservation and management workshops.
Promote a landowner incentive program for urban landowners
Promote outdoor recreational and educational opportunities that are family oriented.
Encourage cities to modify mowing regimes and start prairie restoration projects. Currently we have proposed several prairie restoration projects. One involves training science teachers from the Dallas Independent School District about the importance of prairies, and basic restoration techniques.
Emphasize the importance of proper grazing. Work with state, federal, and private agencies to continue to develop cost-effective means to balance grazing and wildlife. Patch grazing appears to be very promising. Support Farm Bill programs which encourage proper grazing management.
Work with federal state and private organization to promote (incentives) leaving some cover for wildlife. The economic benefits of wildlife can sometimes equal or surpass the agricultural value of land.
Research on best class, stocking rate, season of use and measures of percent utilization to promote diversity of desirable plant and bird species (no more than 40% utilization - Saiwana (1990) but where some brush loafing and escape cover exists, high intensity, short duration grazing produces greater abundance of forb and grass cover favored by some birds especially critical during drought (Campbell-Kissock et al. 1984). Summer deferral and winter grazing appear most beneficial to some birds (NBQ).
Restore and protect of thornscrub by planting on both private and public lands and by purchase (fee title) or conservation easement, provide grants for reforestation with native species, priority should be the most threatened biotic communities with buffer zones and connected into corridors for movement, staging, and build energy reserves for migration
Maintain communication with farming community through the NRCS and FSA, Support conservation through Farm Bill Programs, and provide information concerning Landowner Incentive Program (LIP), Partners for Fish and Wildlife (PFW), and other landowner incentive/conservation programs.
Seek to prohibit or minimize grazing in riparian forests, fencing, and develop alternative water sources for livestock.
Fencing of sensitive areas (or portions of sensitive areas), when appropriate, for at least part of the year would keep out grazing animals and allow the understory to regenerate.
Research local species distributions by season, flight corridors and behavior; Develop site planning alternatives.
Research in Kansas indicates a negative effect of wind power (tall vertical structures) in lesser prairie chicken habitat. Proposed wind power in the Gulf Coast poses a potential threat to migrating birds, especially at one on the proposed sites in Kenedy County. Extensive pre-production EIS work is needed especially during peak hawk migration; FCC regulation, placement and design alteration as needed.
Land use planning and zoning to control urban sprawl and to conserve habitat corridors along streams and rivers (seek to minimize encroachment of urban development along riparian areas, including hike and bike trails); retro-active property tax penalties when agricultural land is sold for development.
Education and habitat preservation in areas undergoing urbanization.
Natural resource agencies and private landowners should make every effort to ensure that oil, gas, and wind power development proceed with as little impact as possible to native wildlife.
Continue to monitor Section 404 Permit Applications submitted through USACE and TCEQ, continue educating landowners concerning best management practices for construction activities, actively participate in planning meetings with local/municipal governments, provide information to landowners/public concerning utilization of native plants/ecosystems in landscaping, limit mining permits on state land, utilize GIS to analyze landscape to identify areas with critical conservation/corridor values, work with TxDOT, and the Public Utilities Commission to identify potential impacts to critical habitats from proposed new projects, and implement BMPs.
Identify opportunities to work with public utilities concerning conservation issues and provide information concerning best management practices to utilities.
Ensure that proper lighting is maintained on tall structures, and that regular monitoring for bird strikes is carried out
Continue to monitor Section 404 Permit Applications submitted through USACE and TCEQ, continue educating landowners concerning best management practices for agriculture/forest management/community planning, maintain communication with farming community through the NRCS and FSA, and support conservation through Farm Bill Programs.
Education through Technical Guidance - TAES/NRCS Seminars, Field Days, BW Brigade Summer Camps, 4-H Projects, literature on wind and water erosion control, mechanical and natural means to reduce head cutting.
Maintain wooded buffers between uplands and wetlands
Marsh creation with marsh mounds, terracing, etc., using dredge material.
Encourage broad coalition (environmental and agricultural) support for wetland favorable policies that have application in the restriction of what can be done on public lands with public resources.
Education through Technical Guidance - TAES/NRCS Range Mgmt Seminars, Field Days, literature on advantages and disadvantages of fencing, "too much of a good thing." This may include Natural resource agencies critically evaluating the need for additional cross-fencing when formulating cost-sharable practices, the removal of unnecessary fences and the marking of needed fences when appropriate.
Natural resource agencies should utilize GIS models to plan cooperative habitat restoration efforts for declining species.
Continue to monitor Section 404 Permit Applications submitted through USACE and TCEQ, participate in local levee and flood planning board meetings, work with local Water Planning Boards to emphasize use of water conservation and other measures rather than new reservoir construction, work with local conservation groups to seek alternatives to new reservoir construction, maintain contact with local legislators concerning biological/ecological impacts that will result from construction of new reservoirs, and restoration and conservation of large blocks of habitat.
The creation of new reservoirs is one of the most important conservation issues facing migratory birds. The destruction of large tracts BLH's will have detrimental affects to migratory bird species. The change in historic river flows will affect downstream wetlands and floodplains. Contiguous tracts of BLH is one of the most important habitat types in Texas when it comes to migrating neotropical migrants. Alternatives to reservoir constructions need to be explored. Examples of what is happening at Richland Creek WMA could be a modal for the future.
Study relationships of organisms
Determine taxonomic validity by modern methods
Systematically check for suitable habitat locations
Survey all known colonies of host vegetation and determine status of all host plant populations
Encourage small tract clear cuts rather than total area clear cuts.
Encourage the use of artificial habitats (i.e. artificial hollow trees, buildings, artificial reefs, bat houses, replica hollow trees and caves)
Encourage non-traditional forest management practices modeled after the South Georgia and North Florida quail hunting plantations (www.talltimbers.org) such as uneven-aged management, and singletree selection harvest methods that maintain southern pine stands in an open, park-like structure with less than 50% tree canopy cover.
Education through Technical Guidance - TAES/State Forestry Seminars, Field Days, literature on site planning.
Education through Technical Guidance - TAES/NRCS Seminars, Field Days, BW Brigade Summer Camps, 4-H Projects, literature on advantages of stock tanks and water for wildlife, offer SWG for challenge-cost share with NRCS for wetland reserve program, riparian buffers and other Farm Billing practices on private land.
Seek agreement with International Water and Boundary Commission and various water districts to limit brush eradication within floodways.
Education through Technical Guidance - TCEX/TAES/NRCS Seminars, Field Days, BW Brigade Summer Camps, 4-H Projects, literature on recreational value of land, property tax incentives, and qualifying wildlife management practices.
Continue to monitor Section 404 Permit Applications submitted through USACE and TCEQ, continue educating landowners concerning best management practices for forest management, maintain communication with farming community through the NRCS and FSA, and support conservation through Farm Bill Programs.
Continue to support scientific management of fisheries and establish and enforce appropriate fishing regulations.
Continue educating landowners concerning best management practices for forest management, work with Texas Forestry Association to communicate the value of bottomland hardwood forests both ecologically and economically, work with Texas Logging Council to continue improvement of logging operations in bottomland hardwoods, and continue to educate landowners concerning programs to restore bottomland hardwoods like LIP, PFW and Farm Bill programs.
Identify opportunities to obtain carbon sequestration funding, continue to provide opportunities to landowner for reforestation projects using LIP, PFW, Farm Bill and other programs, and utilize GIS to identify critical areas for reforestation, conservation, and mitigation projects.
For gravel mining: design alteration, restoration upon completion back to wetlands, and reduce permitting on state owned land.
Enforce Clean Water Act and restore hydrology.
Document resources that could be affected by disturbances at each location. Seasonal area closures and buffer zones could be implemented in areas where species are breeding or feeding. Any type of "unnatural" disturbance should not be allowed in these areas at fragile times. Provide recreational users with educational material that discusses the impact of disturbance on wildlife and provide them with alternative recreational suggestions.
Support and educate landowners concerning restoration of native wetlands, and programs that provide support to do so, continue to monitor Section 404 Permit Applications submitted through USACE and TCEQ, continue educating landowners concerning best management practices for forest management/agriculture/community planning, maintain communication with farming community through the NRCS and FSA, and support conservation through Farm Bill Programs.
Encourage and support the preservation and planting of limited and necessary food sources.
Education on proper bird feeder/bird house management for the prevention of avian diseases.
Reduce feral hogs and feral goats through education and control method; Feral animals destroy understory and ground plants. These animals should be removed, and the sensitive locations should be fenced when appropriate.
Support any research on improving control measures of invasive species. Educate and inform about the spreading of invasive species, its possible that certain habitat management techniques help spread the distribution of certain invasive species.
Work with state, federal, and private agencies to continue to develop cost-effective means of removal of invasive species.
Educate and inform landowners about the effects of exotics on wildlife.
Fund research on invasive species such as with the Texas invasive species monitoring committee to assess risks and recommend policies that regulate importation of exotics.
Education through Technical Guidance - TAES/NRCS Seminars, Field Days, BW Brigade Summer Camps, 4-H Projects, literature on value of native grasses and disadvantages of exotic grasses in holistic range management.
Native plantings should be required for all Conservation Reserve Program contract.
Educate boaters concerning the transport of aquatic invasives on boat trailers, boat motors and fishing equipment, support additional research on management techniques for invasive species, and actively apply control measures.
Continue the use of cowbird traps, issue more depredation plans, and educate the public.
Monitoring, regionally and within each ecoregion, insect-pathogen epizootics and develop/implement appropriate response strategies to insect-pathogen epizootics.
Research on response of production and species diversity by season, frequency and environmental conditions (soil moisture, humidity, temperature, etc) of most effective prescribed fire.
Emphasize the importance of periodic prescribed fire and adopt/implement fire policies that mimic natural fire regimes in frequency, size, intensity, etc. Work with and support the Texas Forest Service and the National Forest Service in their prescribed burning programs. Support legislation that facilitates prescribed burning on private lands. Support private prescribed burning associations (i.e.Hill Country Coop)
Educate youth through primary and secondary curriculums regarding ecological succession and biodiversity effects on plant and animal community health, and ultimately human health and need for balance in amount of landscape in various seral stages
Development of landowner-based management cooperatives, where landowners join forces to manage for habitat at more than just a 20-acre basis; support Audubon's quail cooperative efforts.
Fund broad coalition (environmental and agricultural, industry and private foundations) support for ground water quality and conservation policies that may take form in statutory restrictions on 'right of capture.' Fund Joint Ventures and other partners that leverage resources to purchase or obtain conservation easements on surface and ground water rights that are most vulnerable to loss or degradation.
Education through Technical Guidance - TAES/NRCS Brush Sculpting Seminars, Field Days, literature, Realistic water conservation policy and practice - 100% eradication not economically or ecologically sound.
Natural resource agencies should fully consider the needs of declining wildlife species when formulating brush managed contracts as well as sponsoring research on the response of avifauna to brush control efforts.
Lake management is a something historically biologist have had little influence over but which has a lot of potential for migratory bird management. For example, Lake Texoma has a plan in place that allows for some water level manipulations to encourage wetland vegetation to germinate that will provide a forage base for waterfowl in winter. A similar management plan could be negotiated with other reservoir management organizations to provide new mudflats during shorebird migration or time specific water levels to coincide when rookeries are active.
Controlled burning, discing, tilling, herbicide, spoil deposition, Beneficial Use sites
Survey abandoned mines before closure
Use specially designed gates that do not interfere with airflow or the passage of bats to protect roosts in abandoned mines and important caves
Natural resource agencies need to take a more active role in promoting and holding conservation easements.
Educate landowners about indiscriminate pesticide use.
Reduction of non-point pollutants and the monitoring of air, soil, water, and plant and animal tissues for trends in non-point pollutants; Better monitoring of discharge permit conditions, BMP during construction, maintaining buffers to prevent direct runoff.
Increase awareness of the effects of groundwater and hydrocarbon pumping along the Upper Texas Coast.
Prevention, Rapid Cleanup, Proper preparation/drills, develop innovative cleanup techniques.
Determine the distribution and abundance to yield a final species status
Reintroduce populations
Survey and search for populations to determine/refine knowledge of their biology
Reduce feral cat population through education and control methods.
Trapping, animal control, educate public about keeping cats indoors.
Protection of fragile locations from various forms of habitat destruction
Protection extant populations from various forms of habitat destruction
Fund broad coalition (environmental and agricultural, industry and private foundations) support for water conservation policies that have application to insure instream flows to coastal estuaries and bays and healthy riparian ecosystems. Fund Joint Ventures and other partners that leverage resources to purchase or obtain conservation easements on critical or high priority sites (surface or water rights) vulnerable to loss or degradation.
State protection for isolated wetlands.
Using current GIS; analyze the landscape and identify critical corridors with high conservation needs, continue to participate in West Gulf Coastal Plain, and other similar initiatives, support additional acquisition of lands for conservation, continue to promote LIP and PFW programs for private landowners and actively pursue identification of funding sources for these conservation purchases.
Delimit range
Identify critical bird-use areas, and mark them as no wake zones and enact new or enforce existing regulations.
Reduce impacts to seagrasses (scarring), impacts to waterfowl esp. redhead ducks where a majority of the North American population winters.
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ƕ Ǖ 4 j F kd9 $$If l - --6 4 4
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$If gdZ F kd9 $$If l - --6 4 4
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4 5 H I a j F kd: $$If l - --6 4 4
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$If gdZ F kdZ: $$If l - --6 4 4
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a b s t j F kd; $$If l - --6 4 4
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$If gdZ F kd4; $$If l - --6 4 4
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j F kd{< $$If l - --6 4 4
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$If gdZ F kd< $$If l - --6 4 4
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$If gdZ F kd< $$If l - --6 4 4
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l al p
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& F dh gdZ v w " # R ] Y e P q | Y Z [ \ ] ^ _ º hw h= 5hw hTXO 5hI h= 5hl5 h= 5hZ hJq hZ B*ph hJq hzBr hJq hZ 6 hJq hZ A $ } ~ u 0 n L P ^ v
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1h / =!"#$% $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 / /
a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 / a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 / a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 / a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 9/ a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 / a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 9/ a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 / a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 / a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 / a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 9/ a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 / a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 / a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 9/ a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 / a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 / a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 9/ a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 / a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 / a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 9/ a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 / a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 / a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 9/ a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 9/ a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 9/ a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 / a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 9/ a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 / a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 9/ a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 / a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 / a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 / a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 / a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 / a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 9/ a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 9/ a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 / a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 / a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 / a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 / a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 9/ a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 / a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 9/ a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 / a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 / a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 / a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 9/ a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 / a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 9/ a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 / a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 / a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 / a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 / a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 / a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 / a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 / a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 9/ a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 9/ a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 / a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 / a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 9/ a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 / a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 / a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 9/ a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 / a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 9/ a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 / a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 9/ a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 / a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 / a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 / a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 9/ a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 9/ a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 / a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 / a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 / a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 9/ a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 / a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 / a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 / a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 / a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 9/ a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 9/ a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 / a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 / a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 9/ a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 / a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 9/ a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 9/ a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 / a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 9/ a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 / a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 / a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 9/ a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 9/ a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 9/ a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 9/ a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 / a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 / a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 / a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 9/ a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 9/ a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 / a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 / a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 / a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 / a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 / a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 / a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 / a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 / a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 / a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 / a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 / a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 / a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 9/ a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 / a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 / a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 / a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 9/ a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 / a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 / a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 / a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 / a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 / a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 / a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 / a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 / a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 / a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 / a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 9/ a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 / a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 / a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 / a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 / a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 / a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 / a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 / a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 / a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 / a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 / a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 / a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 / a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 / a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 / a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 / a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 / a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 / a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 / a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 / a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 / a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 / a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 / a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 / a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 / a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 / a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 / a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 / a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 / a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 / a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 / a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 / a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 / a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 / a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 / a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 / a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 / a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 / a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 / a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 / a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 / a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 / a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 / a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 / a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 / a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 / a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 / a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 / a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 / a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 / a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 / a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 / a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 / a] p( $$If ] !v h5 ;5 5_5#v ;#v #v_#v:V l $6 , 5 ;5 5_59 / a] p( $$If ] !v h5 5,5 5}5#v #v,#v #v}#v:V l .&6 , 5 5,5 5}59 / /
a] p2 $$If ] !v h5 %5}5#v %#v}#v:V l .&6 , 5 %5}59 / a] p $$If ] !v h5 5 5#v #v #v:V l .&6 , 5 5 59 / a] p $$If ] !v h5 5,5 5}5#v #v,#v #v}#v:V l .&6 , 5 5,5 5}59 / a] p2 $$If ] !v h5 5 5}5#v #v #v}#v:V l .&6 , 5 5 5}59 / a] p( $$If ] !v h5 5,5 5}5#v #v,#v #v}#v:V l .&6 , 5 5,5 5}59 / a] p2 $$If ] !v h5 5 5}5#v #v #v}#v:V l .&6 , 5 5 5}59 / a] p( $$If ] !v h5 5,5 5}5#v #v,#v #v}#v:V l .&6 , 5 5,5 5}59 / a] p2 $$If ] !v h5 5,5 5}5#v #v,#v #v}#v:V l .&6 , 5 5,5 5}59 / a] p2 $$If ] !v h5 5,5 5}5#v #v,#v #v}#v:V l .&6 , 5 5,5 5}59 / a] p2 $$If ] !v h5 5 5}5#v #v #v}#v:V l .&6 , 5 5 5}59 / a] p( $$If ] !v h5 5,5 5}5#v #v,#v #v}#v:V l .&6 , 5 5,5 5}59 / a] p2 $$If ] !v h5 5,5 5}5#v #v,#v #v}#v:V l .&6 , 5 5,5 5}59 / a] p2 $$If ] !v h5 5,5 5}5#v #v,#v #v}#v:V l .&6 , 5 5,5 5}59 / a] p2 $$If ] !v h5 5,5 5}5#v #v,#v #v}#v:V l .&6 , 5 5,5 5}59 / a] p2 $$If ] !v h5 5,5 5}5#v #v,#v #v}#v:V l .&6 , 5 5,5 5}59 / a] p2 $$If ] !v h5 5,5 5}5#v #v,#v #v}#v:V l .&6 , 5 5,5 5}59 / a] p2 $$If ] !v h5 5,5 5}5#v #v,#v #v}#v:V l .&6 , 5 5,5 5}59 / a] p2 $$If ] !v h5 5,5 5}5#v #v,#v #v}#v:V l .&6 , 5 5,5 5}59 / a] p2 $$If ] !v h5 5,5 5}5#v #v,#v #v}#v:V l .&6 , 5 5,5 5}59 / a] p2 $$If ] !v h5 5,5 5}5#v #v,#v #v}#v:V l .&6 , 5 5,5 5}59 / a] p2 $$If ] !v h5 5,5 5}5#v #v,#v #v}#v:V l .&6 , 5 5,5 5}59 / a] p2 $$If ] !v h5 5,5 5}5#v #v,#v #v}#v:V l .&6 , 5 5,5 5}59 / a] p2 $$If ] !v h5 5,5 5}5#v #v,#v #v}#v:V l .&6 , 5 5,5 5}59 / a] p2 $$If ] !v h5 5,5 5}5#v #v,#v #v}#v:V l .&6 , 5 5,5 5}59 / a] p2 $$If ] !v h5 5,5 5}5#v #v,#v #v}#v:V l .&6 , 5 5,5 5}59 / a] p2 $$If ] !v h5 5,5 5}5#v #v,#v #v}#v:V l .&6 , 5 5,5 5}59 / a] p2 $$If ] !v h5 5,5 5}5#v #v,#v #v}#v:V l .&6 , 5 5,5 5}59 / a] p2 $$If ] !v h5 5,5 5}5#v #v,#v #v}#v:V l .&6 , 5 5,5 5}59 / a] p2 $$If ] !v h5 5,5 5}5#v #v,#v #v}#v:V l .&6 , 5 5,5 5}59 / a] p2 $$If ] !v h5 5,5 5}5#v #v,#v #v}#v:V l .&6 , 5 5,5 5}59 / a] p2 $$If ] !v h5 5 5}5#v #v #v}#v:V l .&6 , 5 5 5}59 / a] p( $$If ] !v h5 5,5 5}5#v #v,#v #v}#v:V l .&6 , 5 5,5 5}59 / a] p2 $$If ] !v h5 5 5#v #v #v:V l .&6 , 5 5 59 / a] p $$If ] !v h5 5,5; 55#v #v,#v; #v#v:V l .&6 , 5 5,5; 559 / a] p2 $$If ] !v h5 5,5; 55#v #v,#v; #v#v:V l .&6 , 5 5,5; 559 / a] p2 $$If ] !v h5 5,5; 55#v #v,#v; #v#v:V l .&6 , 5 5,5; 559 / a] p2 $$If ] !v h5 5g 55#v #vg #v#v:V l .&6 , 5 5g 559 / a] p( $$If ] !v h5 5,5; 55#v #v,#v; #v#v:V l .&6 , 5 5,5; 559 / a] p2 $$If ] !v h5 5,5; 55#v #v,#v; #v#v:V l .&6 , 5 5,5; 559 / a] p2 $$If ] !v h5 5,5; 55#v #v,#v; #v#v:V l .&6 , 5 5,5; 559 / a] p2 $$If ] !v h5 5,5; 55#v #v,#v; #v#v:V l .&6 , 5 5,5; 559 / a] p2 $$If ] !v h5 5,5; 55#v #v,#v; #v#v:V l .&6 , 5 5,5; 559 / a] p2 $$If ] !v h5 5,5; 55#v #v,#v; #v#v:V l .&6 , 5 5,5; 559 / a] p2 $$If ] !v h5 5,5; 55#v #v,#v; #v#v:V l .&6 , 5 5,5; 559 / a] p2 $$If ] !v h5 5,5; 55#v #v,#v; #v#v:V l .&6 , 5 5,5; 559 / a] p2 $$If ] !v h5 5,5; 55#v #v,#v; #v#v:V l .&6 , 5 5,5; 559 / a] p2 $$If ] !v h5 5,5; 55#v #v,#v; #v#v:V l .&6 , 5 5,5; 559 / a] p2 $$If ] !v h5 5,5; 55#v #v,#v; #v#v:V l .&6 , 5 5,5; 559 / a] p2 $$If ] !v h5 5,5; 55#v #v,#v; #v#v:V l .&6 , 5 5,5; 559 / a] p2 $$If ] !v h5 5,5; 55#v #v,#v; #v#v:V l .&6 , 5 5,5; 559 / a] p2 $$If ] !v h5 5,5; 55#v #v,#v; #v#v:V l .&6 , 5 5,5; 559 / a] p2 $$If ] !v h5 5,5; 55#v #v,#v; #v#v:V l .&6 , 5 5,5; 559 / a] p2 $$If ] !v h5 5,5; 55#v #v,#v; #v#v:V l .&6 , 5 5,5; 559 / a] p2 $$If ] !v h5 5,5; 55#v #v,#v; #v#v:V l .&6 , 5 5,5; 559 / a] p2 $$If ] !v h5 5,5; 55#v #v,#v; #v#v:V l .&6 , 5 5,5; 559 / a] p2 $$If ] !v h5 5,5; 55#v #v,#v; #v#v:V l .&6 , 5 5,5; 559 / a] p2 $$If ] !v h5 5,5; 55#v #v,#v; #v#v:V l .&6 , 5 5,5; 559 / a] p2 $$If ] !v h5 5,5; 55#v #v,#v; #v#v:V l .&6 , 5 5,5; 559 / a] p2 $$If ] !v h5 5,5; 55#v #v,#v; #v#v:V l .&6 , 5 5,5; 559 / a] p2 $$If ] !v h5 5,5; 55#v #v,#v; #v#v:V l .&6 , 5 5,5; 559 / a] p2 $$If ] !v h5 5,5; 55#v #v,#v; #v#v:V l .&6 , 5 5,5; 559 / a] p2 $$If ] !v h5 5,5; 55#v #v,#v; #v#v:V l .&6 , 5 5,5; 559 / a] p2 $$If ] !v h5 5,5; 55#v #v,#v; #v#v:V l .&6 , 5 5,5; 559 / a] p2 $$If ] !v h5 5,5; 55#v #v,#v; #v#v:V l .&6 , 5 5,5; 559 / a] p2 $$If ] !v h5 5,5; 55#v #v,#v; #v#v:V l .&6 , 5 5,5; 559 / a] p2 $$If ] !v h5 5,5; 55#v #v,#v; #v#v:V l .&6 , 5 5,5; 559 / a] p2 $$If ] !v h5 5,5; 55#v #v,#v; #v#v:V l .&6 , 5 5,5; 559 / a] p2 $$If ] !v h5 5,5; 55#v #v,#v; #v#v:V l .&6 , 5 5,5; 559 / a] p2 $$If ] !v h5 5,5; 55#v #v,#v; #v#v:V l .&6 , 5 5,5; 559 / a] p2 $$If ] !v h5 5,5; 55#v #v,#v; #v#v:V l .&6 , 5 5,5; 559 / a] p2 $$If ] !v h5 5,5; 55#v #v,#v; #v#v:V l .&6 , 5 5,5; 559 / a] p2 $$If ] !v h5 5,5; 55#v #v,#v; #v#v:V l .&6 , 5 5,5; 559 / a] p2 $$If ] !v h5 5,5; 55#v #v,#v; #v#v:V l .&6 , 5 5,5; 559 / a] p2 $$If ] !v h5 5,5; 55#v #v,#v; #v#v:V l .&6 , 5 5,5; 559 / a] p2 $$If ] !v h5 5,5; 55#v #v,#v; #v#v:V l .&6 , 5 5,5; 559 / a] p2 $$If ] !v h5 5,5; 55#v #v,#v; #v#v:V l .&6 , 5 5,5; 559 / a] p2 $$If ] !v h5 5,5; 55#v #v,#v; #v#v:V l .&6 , 5 5,5; 559 / a] p2 $$If ] !v h5 5,5; 55#v #v,#v; #v#v:V l .&6 , 5 5,5; 559 / a] p2 $$If ] !v h5 5,5; 55#v #v,#v; #v#v:V l .&6 , 5 5,5; 559 / a] p2 $$If ] !v h5 5,5; 55#v #v,#v; #v#v:V l .&6 , 5 5,5; 559 / a] p2 $$If ] !v h5 5,5; 55#v #v,#v; #v#v:V l .&6 , 5 5,5; 559 / a] p2 $$If ] !v h5 5,5; 55#v #v,#v; #v#v:V l .&6 , 5 5,5; 559 / a] p2 $$If ] !v h5 5,5; 55#v #v,#v; #v#v:V l .&6 , 5 5,5; 559 / a] p2 $$If ] !v h5 5,5; 55#v #v,#v; #v#v:V l .&6 , 5 5,5; 559 / a] p2 $$If ] !v h5 5,5; 55#v #v,#v; #v#v:V l .&6 , 5 5,5; 559 / a] p2 $$If ] !v h5 5,5; 55#v #v,#v; #v#v:V l .&6 , 5 5,5; 559 / a] p2 $$If ] !v h5 5,5; 55#v #v,#v; #v#v:V l .&6 , 5 5,5; 559 / a] p2 $$If ] !v h5 5,5; 55#v #v,#v; #v#v:V l .&6 , 5 5,5; 559 / a] p2 $$If ] !v h5 5,5; 55#v #v,#v; #v#v:V l .&6 , 5 5,5; 559 / a] p2 $$If ] !v h5 5,5; 55#v #v,#v; #v#v:V l .&6 , 5 5,5; 559 / a] p2 $$If ] !v h5 5,5; 55#v #v,#v; #v#v:V l .&6 , 5 5,5; 559 / a] p2 $$If ] !v h5 5,5; 55#v #v,#v; #v#v:V l .&6 , 5 5,5; 559 / a] p2 $$If ] !v h5 5,5; 55#v #v,#v; #v#v:V l .&6 , 5 5,5; 559 / a] p2 $$If ] !v h5 5,5; 55#v #v,#v; #v#v:V l .&6 , 5 5,5; 559 / a] p2 $$If ] !v h5 5,5; 55#v #v,#v; #v#v:V l .&6 , 5 5,5; 559 / a] p2 $$If ] !v h5 5,5; 55#v #v,#v; #v#v:V l .&6 , 5 5,5; 559 / a] p2 $$If ] !v h5 5,5; 55#v #v,#v; #v#v:V l .&6 , 5 5,5; 559 / a] p2 $$If ] !v h5 5,5; 55#v #v,#v; #v#v:V l .&6 , 5 5,5; 559 / a] p2 $$If ] !v h5 5,5; 55#v #v,#v; #v#v:V l .&6 , 5 5,5; 559 / a] p2 $$If ] !v h5 5,5; 55#v #v,#v; #v#v:V l .&6 , 5 5,5; 559 / a] p2 $$If ] !v h5 5,5; 55#v #v,#v; #v#v:V l .&6 , 5 5,5; 559 / a] p2 $$If ] !v h5 5,5; 55#v #v,#v; #v#v:V l .&6 , 5 5,5; 559 / a] p2 $$If ] !v h5 5,5; 55#v #v,#v; #v#v:V l .&6 , 5 5,5; 559 / a] p2 $$If ] !v h5 5,5; 55#v #v,#v; #v#v:V l .&6 , 5 5,5; 559 / a] p2 $$If ] !v h5 5,5; 55#v #v,#v; #v#v:V l .&6 , 5 5,5; 559 / a] p2 $$If ] !v h5 5,5; 55#v #v,#v; #v#v:V l .&6 , 5 5,5; 559 / a] p2 $$If ] !v h5 5,5; 55#v #v,#v; #v#v:V l .&6 , 5 5,5; 559 / a] p2 $$If ] !v h5 5,5; 55#v #v,#v; #v#v:V l .&6 , 5 5,5; 559 / a] p2 $$If ] !v h5 5,5; 55#v #v,#v; #v#v:V l .&6 , 5 5,5; 559 / a] p2 $$If ] !v h5 5,5; 55#v #v,#v; #v#v:V l .&6 , 5 5,5; 559 / a] p2 $$If ] !v h5 5,5; 55#v #v,#v; #v#v:V l .&6 , 5 5,5; 559 / a] p2 $$If ] !v h5 5,5; 55#v #v,#v; #v#v:V l .&6 , 5 5,5; 559 / a] p2 $$If ] !v h5 5,5; 55#v #v,#v; #v#v:V l .&6 , 5 5,5; 559 / a] p2 $$If ] !v h5 5,5; 55#v #v,#v; #v#v:V l .&6 , 5 5,5; 559 / a] p2 $$If ] !v h5 5,5; 55#v #v,#v; #v#v:V l .&6 , 5 5,5; 559 / a] p2 $$If ] !v h5 5,5; 55#v #v,#v; #v#v:V l .&6 , 5 5,5; 559 / a] p2 $$If ] !v h5 5,5; 55#v #v,#v; #v#v:V l .&6 , 5 5,5; 559 / a] p2 $$If ] !v h5 5,5; 55#v #v,#v; #v#v:V l .&6 , 5 5,5; 559 / a] p2 $$If ] !v h5 5,5; 55#v #v,#v; #v#v:V l .&6 , 5 5,5; 559 / a] p2 $$If ] !v h5 5,5; 55#v #v,#v; #v#v:V l .&6 , 5 5,5; 559 / a] p2 $$If ] !v h5 5,5; 55#v #v,#v; #v#v:V l .&6 , 5 5,5; 559 / a] p2 $$If ] !v h5 5,5; 55#v #v,#v; #v#v:V l .&6 , 5 5,5; 559 / a] p2 $$If ] !v h5 5,5; 55#v #v,#v; #v#v:V l .&6 , 5 5,5; 559 / a] p2 $$If ] !v h5 5,5; 55#v #v,#v; #v#v:V l .&6 , 5 5,5; 559 / a] p2 $$If ] !v h5 5,5; 55#v #v,#v; #v#v:V l .&6 , 5 5,5; 559 / a] p2 $$If ] !v h5 5g 55#v #vg #v#v:V l .&6 , 5 5g 559 / a] p( $$If ] !v h5 5,5; 55#v #v,#v; #v#v:V l .&6 , 5 5,5; 559 / a] p2 $$If ] !v h5 5,5; 55#v #v,#v; #v#v:V l .&6 , 5 5,5; 559 / a] p2 $$If ] !v h5 5,5; 55#v #v,#v; #v#v:V l .&6 , 5 5,5; 559 / a] p2 $$If ] !v h5 5,5; 55#v #v,#v; #v#v:V l .&6 , 5 5,5; 559 / a] p2 $$If ] !v h5 5g 55#v #vg #v#v:V l .&6 , 5 5g 559 / a] p( $$If ] !v h5 5,5; 55#v #v,#v; #v#v:V l .&6 , 5 5,5; 559 / a] p2 $$If ] !v h5 5,5; 55#v #v,#v; #v#v:V l .&6 , 5 5,5; 559 / a] p2 $$If ] !v h5 5,5; 55#v #v,#v; #v#v:V l .&6 , 5 5,5; 559 / a] p2 $$If ] !v h5 5,5; 55#v #v,#v; #v#v:V l .&6 , 5 5,5; 559 / a] p2 $$If ] !v h5 5,5; 55#v #v,#v; #v#v:V l .&6 , 5 5,5; 559 / a] p2 $$If ] !v h5 5,5; 55#v #v,#v; #v#v:V l .&6 , 5 5,5; 559 / a] p2 $$If ] !v h5 5,5; 55#v #v,#v; #v#v:V l .&6 , 5 5,5; 559 / a] p2 $$If ] !v h5 5,5; 55#v #v,#v; #v#v:V l .&6 , 5 5,5; 559 / a] p2 $$If ] !v h5 5,5; 55#v #v,#v; #v#v:V l .&6 , 5 5,5; 559 / a] p2 $$If ] !v h5 5,5; 55#v #v,#v; #v#v:V l .&6 , 5 5,5; 559 / a] p2 $$If ] !v h5 5,5; 55#v #v,#v; #v#v:V l .&6 , 5 5,5; 559 / a] p2 $$If ] !v h5 5,5; 55#v #v,#v; #v#v:V l .&6 , 5 5,5; 559 / a] p2 $$If ] !v h5 5,5; 55#v #v,#v; #v#v:V l .&6 , 5 5,5; 559 / a] p2 $$If ] !v h5 5,5; 55#v #v,#v; #v#v:V l .&6 , 5 5,5; 559 / a] p2 $$If ] !v h5 5,5; 55#v #v,#v; #v#v:V l .&6 , 5 5,5; 559 / a] p2 $$If ] !v h5 5,5; 55#v #v,#v; #v#v:V l .&6 , 5 5,5; 559 / a] p2 $$If ] !v h5 5,5; 55#v #v,#v; #v#v:V l .&6 , 5 5,5; 559 / a] p2 $$If ] !v h5 5,5; 55#v #v,#v; #v#v:V l .&6 , 5 5,5; 559 / a] p2 k $$If l !v h5 -#v -:V l -6 , 5 -/ al p
k $$If l !v h5 -#v -:V l -6 , 5 -/ al p
k $$If l !v h5 -#v -:V l -6 , 5 -/ al p
k $$If l !v h5 -#v -:V l -6 , 5 -/ al p
k $$If l !v h5 -#v -:V l -6 , 5 -/ al p
k $$If l !v h5 -#v -:V l -6 , 5 -/ al p
k $$If l !v h5 -#v -:V l -6 , 5 -/ al p
k $$If l !v h5 -#v -:V l -6 , 5 -/ al p
k $$If l !v h5 -#v -:V l -6 , 5 -/ al p
k $$If l !v h5 -#v -:V l -6 , 5 -/ al p
k $$If l !v h5 -#v -:V l -6 , 5 -/ al p
k $$If l !v h5 -#v -:V l -6 , 5 -/ al p
k $$If l !v h5 -#v -:V l -6 , 5 -/ al p
k $$If l !v h5 -#v -:V l -6 , 5 -/ al p
k $$If l !v h5 -#v -:V l -6 , 5 -/ al p
k $$If l !v h5 -#v -:V l -6 , 5 -/ al p
k $$If l !v h5 -#v -:V l -6 , 5 -/ al p
k $$If l !v h5 -#v -:V l -6 , 5 -/ al p
k $$If l !v h5 -#v -:V l -6 , 5 -/ al p
k $$If l !v h5 -#v -:V l -6 , 5 -/ al p
k $$If l !v h5 -#v -:V l -6 , 5 -/ al p
k $$If l !v h5 -#v -:V l -6 , 5 -/ al p
k $$If l !v h5 -#v -:V l -6 , 5 -/ al p
k $$If l !v h5 -#v -:V l -6 , 5 -/ al p
k $$If l !v h5 -#v -:V l -6 , 5 -/ al p
k $$If l !v h5 -#v -:V l -6 , 5 -/ al p
k $$If l !v h5 -#v -:V l -6 , 5 -/ al p
k $$If l !v h5 -#v -:V l -6 , 5 -/ al p
k $$If l !v h5 -#v -:V l -6 , 5 -/ al p
k $$If l !v h5 -#v -:V l -6 , 5 -/ al p
k $$If l !v h5 -#v -:V l -6 , 5 -/ al p
e $$If l !v h5 -#v -:V l -6 5 -/ al p
k $$If l !v h5 -#v -:V l -6 , 5 -/ al p
k $$If l !v h5 -#v -:V l -6 , 5 -/ al p
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