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Query: Species and Ecosystems at Risk - Publicly Available Occurrences - CDC (ID: 1)

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    Species and Ecosystems at Risk - Publicly Available Occurrences - CDC (1)

    Species and Ecosystems at Risk - Publicly Available Occurrences - CDC (1)gml:idpub:OCCR_AREA_SP_IDpub:FEATURE_CODEpub:SHAPE_IDpub:OCCR_IDpub:SCI_NAME_Fpub:SCI_NAMEpub:ENG_NAME_Fpub:ENG_NAMEpub:EL_TYPEpub:EL_TYPE_CDpub:TAX_CLASSpub:DATA_SENSpub:GLOB_RANKpub:PROV_RANKpub:COSEWICpub:BC_LISTpub:SARA_SCHEDpub:SURV_SITEpub:DIRECTIONSpub:FIRST_OBSpub:LAST_OBSpub:OCCR_DATApub:RANKpub:RANK_DESCpub:RANK_DATEpub:RANK_COMpub:CONDITIONpub:OCCR_SIZEpub:LAND_CONTpub:GEN_DESCpub:VEG_ZONEpub:HABITATpub:BGCpub:REFERENCESpub:VERS_DATEpub:VERS_AUTHORpub:EST_RApub:CON_EXTENTpub:CON_EXTENT_DESCpub:ECOSECTIONSpub:ENVIRONMENT_COMpub:SOIL_COMpub:MIN_ELEV_METERSpub:MAX_ELEV_METERSpub:ADDITIONAL_INV_NEEDED_INDpub:ADDITIONAL_INV_NEEDED_COMpub:INVENTORY_COMpub:REP_ACCURACY_COMpub:SPECIMEN_DESCpub:EO_NUMpub:ELCODEpub:ELEMENT_SUBNATIONAL_IDpub:ECOSYSTEM_GRPpub:BCSEE_SPECIES_CODE_URLpub:FEATURE_AREA_SQMpub:FEATURE_LENGTH_Mpub:OBJECTIDpub:SE_ANNO_CAD_DATApub:GEOMETRY (Geometry)
    WHSE_TERRESTRIAL_ECOLOGY.BIOT_OCCR_NON_SENS_AREA_SVW.fid--31aa9699_196a7b0fa41_-65f125786497FF846601105202623<i>Ambystoma mavortium</i>Ambystoma mavortiumWestern Tiger SalamanderWestern Tiger SalamanderVertebrate AnimalANIMALamphibiansN G5S2E (NOV 2012)Red1 MYERS LAKE1990-08-131990-08-131990-08-13: 4 metamorphosed salamanders observed and one dead on the lake bottom. (Orchard 1991). Not surveyed in 2006 (Noble and Spendlow 2006).AExcellent estimated viability1990-08-13A large lake that is virtually undeveloped without predatory fish.A long, large, clear lake that is dammed at one end.LACUSTRINENoble, R. and I. Spendlow. 2006. South Okanagan, Similkameen and Kettle Valley Tiger Salamander (Ambystoma tigrinum) Inventory - 2006. BC Conservation Corps Project Completion Report prepared for the Ministry of Environment, Penticton , BC. 14 pp.<BR>Orchard, S.A. 1991. Provincial status report for the tiger salamander, Ambystoma tigrinum. Unpubl. rep., B.C. Environ., Wildl. Branch, Victoria.2/19/2007 12:00:00 AMRAMSAY, L.? Uncertain whether full extent of EO is knownSOH241Y16AAAAA0114233337https://a100.gov.bc.ca/pub/eswp/search.do?searchType=COMBINED&method=process&esId=33337160322.33853697.173622323297
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    WHSE_TERRESTRIAL_ECOLOGY.BIOT_OCCR_NON_SENS_AREA_SVW.fid--31aa9699_196a7b0fa41_-65f025789409FF84660110366957373<i>Megascops kennicottii kennicottii</i>Megascops kennicottii kennicottiiWestern Screech-Owl, <i>kennicottii</i> subspeciesWestern Screech-Owl, kennicottii subspeciesVertebrate AnimalANIMALbirdsN G4G5T4S2S3T (MAY 2012)Blue1 HORNBY ISLAND, FORD COVELocated at the southern end of Hornby Island.1992-02-191992-02-191992: Heard screech-owl calling here at about 1745 hrs (Innes 2000).EVerified extant (viability not assessed)1992-02-19TERRESTRIAL: woodland mixedInnes, Douglas W. 2000. Unpublished bird survey field notes: Rock Doves through Owls. Courtenay, BC.7/20/2007 12:00:00 AMStewart, ACMediumN Confident full extent of EO is NOT knownSOGY16ABNSB0104219173https://a100.gov.bc.ca/pub/eswp/search.do?searchType=COMBINED&method=process&esId=19173290579.32162440.587722326209
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    WHSE_TERRESTRIAL_ECOLOGY.BIOT_OCCR_NON_SENS_AREA_SVW.fid--31aa9699_196a7b0fa41_-65ef25789411FF84660110367027375<i>Megascops kennicottii kennicottii</i>Megascops kennicottii kennicottiiWestern Screech-Owl, <i>kennicottii</i> subspeciesWestern Screech-Owl, kennicottii subspeciesVertebrate AnimalANIMALbirdsN G4G5T4S2S3T (MAY 2012)Blue1 TOQUART BAYLocated at access point to Toquart Bay.1996-03-311996-03-311996: Male and female Western Screech-owl heard calling (Innes 2000).EVerified extant (viability not assessed)1996-03-31TERRESTRIAL: forest needleleaf Innes, Douglas W. 2000. Unpublished bird survey field notes: Rock Doves through Owls. Courtenay, BC.7/20/2007 12:00:00 AMStewart, A.C.LowN Confident full extent of EO is NOT knownVIS;WIMY17ABNSB0104219173https://a100.gov.bc.ca/pub/eswp/search.do?searchType=COMBINED&method=process&esId=19173668908.96523951.308722326211
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    WHSE_TERRESTRIAL_ECOLOGY.BIOT_OCCR_NON_SENS_AREA_SVW.fid--31aa9699_196a7b0fa41_-65ee25789386FF84660220366397363<i>Bartramia halleriana</i>Bartramia hallerianaHaller's apple mossHaller's apple mossNonvascular PlantPLANTN G4G5S2S3T (NOV 2011)Blue1 MOUNT ROBSON PROVINCIAL PARK, 1.5 KM SOUTHWEST OF YELLOWHEAD PASSFitzwilliam Spur. Ca. 1 km west of the Alberta border, south of Highway 16 along the old road on the base of the north-trending spur of Mount Fitzwilliam.2004-07-122023-06-032023-06-03: 14 colonies over 242.5 square cm from the original ROW location. Northwest aspect (COSEWIC 2024a). 2023-05-26: 14 colonies observed over 956 square cm with 10.5 square cm mortality (Jacob 2023). 2022-09-30: 79 colonies observed over 4,675 square cm from 5 clusters that were originally found in 2011. North to northwest aspect (COSEWIC 2024a). 2021-SP: 15 colonies (Jacob 2023). 2020-08-23: Observed (iNaturalist 2022b; Fenneman 2021). 2020-06: 14 colonies with 3 new colonies and 2 colones were no longer present (Jacob 2023). 2019-05: 13 colonies with 3 new colonies (Jacob 2023). 2018-SP: 10 colonies (Jacob 2023). 2017-SP: 10 colonies (Jacob 2023). 2016-SP: 10 colonies with 1 new colony (Jacob 2023). 2015-SP: 9 colonies with 1 new colony (Jacob 2023). 2014-SP: 8 colonies with 1 new colony (Jacob 2023). 2013-05: 7 colonies with 1 new colony (Jacob 2023). 2012: 6 colonies. One colony displaced (Jacob 2023). 2011-09: 3 newly discovered clusters (COSEWIC 2024a). 2011: 7 mature individuals over 163 square cm (COSEWIC 2011o, Jacob 2023). 2010: 7 colonies (Jacob 2023). 2009: 7 individuals observed (Arthur 2009, Jacob 2023). 2004-07-12: One clump (10 cm x 10 cm) on siliceous cliff in <i>Picea engelmannii-Abies lasiocarpa-Pinus contorta</i> forest (P. Achuff, pers. comm.).CDFair or poor estimated viability2023-06-03Single individual in an area of imminent pipeline development, but mitigation is still possible. In the absence of direct destruction, the probability of this species persisting at this site over the next 20 years remains only fair to poor, because of the small population size.2004: With capsules (P. Achuff, pers. comm. 2007). 2009: 2 colonies with signs of stress (browning) post construction; 2010-2012: All patches were in a similar condition to 2009 except for one tuff had fallen in 2011 and one colony displaced in 2012; 2013: Colonies healthy overall and first sporophytes observed since construction; 2014: F7 almost totally removed and the other patches remain healthy; 2015: Sporophytes observed at 3 patches; 2016: Sporophytes at 1 patch. New stems at 2 patches, 1 patch less discoloured, and 1 patch more discoloured; 2017: Sporophytes at 1 patch. New stems at 2 patches, discolouration decreased at 3 patches and most patches increased in length/width; 2018: 1 patch with additional stems, 1 improved colour, 5 improved growth; 2019: 1 colony accidentally dislodged and replaced, 3 with worsening colour/mortality, and 7 with increased length; 2020: 3 colonies with sporophytes, 4 with worsening colour/mortality, and 3 increased in size; 2021: Sporophytes at 2 colonies, increase in size at 3, and discolouration at 3; 2023: Sporophytes at 1 colony, 2 increased in size, and 3 increased discolouration. Overall, colonies healthy (Jacobs 2023). 2024: Colony numbers increased since last status report due to new the discovery of new subsites. At TMX ROW, there are more colonies and a slightly larger area of occupancy in comparison to 2011 but the health is poor and declining. One colony accounts for most of the area (153.0 square cm), and a second colony that appears to be half-deceased (45.0 square cm), whereas remaining colonies contain few shoots and are being overgrown or exhibit dieback, likely from suboptimal microclimate (COSEWIC 2024a).2004: One individual plant over 10 cm x 10 cm (P. Achuff, pers. comm. 2007). 2009: 7 individuals observed (Arthur 2009, Jacob 2023). 2010: 7 colonies (Jacob 2023). 2011: 7 mature individuals over 163 square cm (COSEWIC 2011o, Jacob 2023); 3 newly discovered clusters (COSEWIC 2024a). 2012: 6 colonies (Jacob 2023). 2013: 7 colonies (Jacob 2023). 2014: 8 colonies (Jacob 2023). 2015: 9 colonies (Jacob 2023). 2016: 10 colonies (Jacob 2023). 2017: 10 colonies (Jacob 2023). 2018: 10 colonies (Jacob 2023). 2019: 13 colonies (Jacob 2023). 2020: 14 colonies (Jacob 2023). 2021: 15 colonies (Jacob 2023). 2022: 79 colonies observed over 4,675 square cm from 5 clusters (COSEWIC 2024a). 2023: 14 colonies over 242.5 square cm (COSEWIC 2024a); 14 colonies over 956 square cm (Jacob 2023).2004: The original patch is in the middle of the Transmountain Pipeline Anchor Loop project. In August 2007, the area was flagged as a right-of-way and vegetation clearing began in the vicinity (P. Achuff, pers. comm. 2007). Habitat restoration and remediation from 2009 and 2010 included installation of a shade frame and planting trees and shrubs (Jacobs 2023). The colonies have been adversely affected by tree removal during pipeline construction in 2007-2008. Some colonies are declining and habitat quality may continue to decline in the future despite restoration and remediation efforts. Threats include wildfire due to close proximity to rail line and Highway 16, recreation as walking on the rocky outcrop can dislodge plants, and stochastic events due to small patch size. Mountain pine beetle infestation also threatens the moss as tree mortality wIn forest on shaded, saturated (wet-mesic) siliceous cliff.MontaneTERRESTRIAL: Cliff, Forest Needleleaf, On RockAchuff, P. Personal communication.Scientist Emeritus, Ecological Integrity Branch, Parks Canada, Waterton Lakes National Park, AB.<BR>Arthur, W. 2009. Shapefile of Hallers Apple Moss observations within the Omineca Forest Region.<BR>COSEWIC. 2011o. COSEWIC assessment and status report on the Haller's Apple Moss Bartramia halleriana in Canada. Committee on the Status of Endangered Wildlife in Canada. Ottawa. xi + 23 pp.<BR>COSEWIC. 2024a. Draft COSEWIC Status Report on Haller's Apple Moss Bartramia halleriana. Committee on the Status of Endangered Wildlife in Canada. Ottawa. xxii + 63 pp.<BR>Fenneman, J. 2021. Excel spreadsheet of iNaturalist records.<BR>Jacobs Consultancy Canada Inc. 2023. 2023 Haller's Apple Moss Monitoring Report. TMX - Achor Loop Project. 37pp.<BR>Stevenson, G. Personal communication. Environmental Monitor. Transmountain Pipeline Anchor Loop Project. <BR>Van Velzen, Wayne. Personal Communication. Area Supervisor. Mount Robson Park. <BR>iNaturalist. 2022b. Bartramia halleriana observation. Accessed January 31, 2022 at https://www.inaturalist.org/observations/5741418510/23/2024 12:00:00 AMDonovan, M., I. Anderson, and E. BarnewallHigh? Uncertain whether full extent of EO is knownNPK10561171Y2004: Area 50 m x 50 m was searched extensively and no other plants were found. However, other potential habitat may be present at this site (P. Achuff, pers. comm.).Achuff, P. (31133). 2004. ALTA.4NBMUS0R02013959https://a100.gov.bc.ca/pub/eswp/search.do?searchType=COMBINED&method=process&esId=139591124.2992208.792422326186
    MULTIPOLYGON(((52.88663587 -118.48106375,52.88663571 -118.48103458,52.886639 -118.48100584,52.88664565 -118.48097875,52.88665527 -118.48095444,52.88666755 -118.48093369,52.88668209 -118.48091719,52.8866983 -118.48090578,52.88671551 -118.48089989,52.88673307 -118.48089962,52.88675037 -118.4809051,52.88676668 -118.48091614,52.88678131 -118.48093211,52.8867938 -118.48095251,52.88680374 -118.48097666,52.8868106 -118.4810036,52.88681415 -118.48103218,52.88681431 -118.48106135,52.88681323 -118.48107074,52.88682478 -118.4810896,52.88683471 -118.48111375,52.88684158 -118.48114069,52.88684513 -118.48116926,52.88684529 -118.48119844,52.88684199 -118.48122717,52.88683535 -118.48125426,52.88682573 -118.48127858,52.88681345 -118.48129932,52.88679891 -118.48131582,52.88678269 -118.48132723,52.88676549 -118.48133312,52.88674793 -118.48133339,52.88673063 -118.48132791,52.88671432 -118.48131687,52.88669968 -118.4813009,52.88668719 -118.4812805,52.88667726 -118.48125635,52.88667039 -118.48122941,52.88666685 -118.48120083,52.88666669 -118.48117166,52.88666776 -118.48116227,52.88665622 -118.48114341,52.88664628 -118.48111926,52.88663942 -118.48109232,52.88663587 -118.48106375)),((52.88391781 -118.48396785,52.88391766 -118.48393868,52.88392095 -118.48390994,52.8839276 -118.48388286,52.88393722 -118.48385854,52.8839495 -118.4838378,52.88396404 -118.4838213,52.88398025 -118.48380989,52.88399746 -118.483804,52.88401502 -118.48380374,52.88403232 -118.48380921,52.88404862 -118.48382025,52.88406326 -118.48383623,52.88407575 -118.48385663,52.88408569 -118.48388078,52.88409255 -118.48390772,52.8840961 -118.48393629,52.88409626 -118.48396546,52.88409296 -118.4839942,52.88408632 -118.48402128,52.8840767 -118.4840456,52.88406441 -118.48406634,52.88404988 -118.48408284,52.88403366 -118.48409425,52.88401646 -118.48410014,52.88399889 -118.4841004,52.88398159 -118.48409493,52.88396529 -118.48408389,52.88395065 -118.48406791,52.88393816 -118.48404751,52.88392823 -118.48402336,52.88392136 -118.48399642,52.88391781 -118.48396785)),((52.88684418 -118.4807513,52.88684402 -118.48072213,52.88684731 -118.48069339,52.88685396 -118.48066631,52.88686358 -118.48064199,52.88687586 -118.48062124,52.88689039 -118.48060474,52.88690661 -118.48059333,52.88692381 -118.48058744,52.88694138 -118.48058717,52.88695868 -118.48059265,52.88697498 -118.48060369,52.88698962 -118.48061966,52.88700211 -118.48064007,52.88701204 -118.48066421,52.88701891 -118.48069115,52.88702246 -118.48071973,52.88702262 -118.4807489,52.88701932 -118.48077764,52.88701268 -118.48080473,52.88700306 -118.48082904,52.88699078 -118.48084979,52.88697624 -118.48086629,52.88696002 -118.4808777,52.88694282 -118.48088359,52.88692526 -118.48088386,52.88690796 -118.48087838,52.88689165 -118.48086734,52.88687701 -118.48085137,52.88686453 -118.48083096,52.88685459 -118.48080682,52.88684772 -118.48077988,52.88684418 -118.4807513)))
    WHSE_TERRESTRIAL_ECOLOGY.BIOT_OCCR_NON_SENS_AREA_SVW.fid--31aa9699_196a7b0fa41_-65ed25793921FF84660110305707012<i>Brachyramphus marmoratus</i>Brachyramphus marmoratusMarbled MurreletMarbled MurreletVertebrate AnimalANIMALbirdsN G3S3T (MAY 2012)Blue1 GOAT ISLAND (POWELL LAKE)Located about 1.5 km north of Frogpond Lake on Goat Island.20012001Nest found using radio telemetry. Ground survey determined that nest was successful (CWE 2003).EVerified extant (viability not assessed)2001TERRESTRIAL: Forest Needleleaf, Old ForestCentre for Wildlife Ecology (CWE). 2003. Marbled Murrelet Project: nest site descriptions for all nests found by radio telemetry, Simon Fraser University, Burnaby. Last Update March 2003 Online. Available: http://www.sfu.ca/biology/wildberg/mamuweb/welcome.htm#<BR>Centre for Wildlife Ecology (CWE). 2006. Marbled Murrelet nest site locations for all nests found by radio telemetry in the Desolation Sound area. Simon Fraser University, Burnaby.<BR>Deal, J. and L. Waterhouse. 2013. Spreadsheet and geodatabase showing ortho-rectified Marbled Murrelet nest locations in Desolation Sound and Clayoquot Sound.8/9/2006 12:00:00 AMStewart, ACMediumN Confident full extent of EO is NOT knownSPRY5ABNNN0601014153https://a100.gov.bc.ca/pub/eswp/search.do?searchType=COMBINED&method=process&esId=1415331213.3427627.298622330721
    MULTIPOLYGON(((50.07578169 -124.3972816,50.07595742 -124.39730224,50.07612718 -124.39737578,50.07628445 -124.39749938,50.07642313 -124.39766834,50.07653802 -124.39787602,50.07662458 -124.3981146,50.07667953 -124.39837484,50.07670075 -124.39864674,50.07668746 -124.39891986,50.07664014 -124.39918369,50.07656061 -124.39942797,50.07645189 -124.39964365,50.07631826 -124.39982205,50.07616475 -124.39995657,50.0759973 -124.40004211,50.07582235 -124.40007509,50.07564662 -124.40005443,50.07547695 -124.39998074,50.07531968 -124.39985714,50.07518091 -124.39968831,50.07506612 -124.39948049,50.07497957 -124.39924206,50.07492461 -124.39898183,50.0749033 -124.39870994,50.07491668 -124.39843683,50.074964 -124.39817301,50.07504353 -124.39792859,50.07515216 -124.39771306,50.07528587 -124.39753451,50.07543938 -124.39739999,50.07560674 -124.39731458,50.07578169 -124.3972816)))
    WHSE_TERRESTRIAL_ECOLOGY.BIOT_OCCR_NON_SENS_AREA_SVW.fid--31aa9699_196a7b0fa41_-65ec25789293FF84660110284956813<i>Eumetopias jubatus</i>Eumetopias jubatusSteller Sea LionSteller Sea LionVertebrate AnimalANIMALmammalsN G3S3S4B,S4NSC (NOV 2013)Blue1 GARCIN ROCKSApproximately 2.5 kilometres southeast of Benjamin Point off of Moresby Island.2002-07-062010-07-03Garcin Rocks was a year round haulout until 2006, but has since been reclassified as a rookery. The first survey occurred in July of 2002, when 329 adults were observed (COSEWIC 2003m). Surveys in 2008 were the first to discover the site was a rookery and numbers of pups increased from 104 pups in 2008 to 217 in 2010 (COSEWIC 2013). Over this time, the number of adults increased to a high of 565 in 2010 (COSEWIC 2013).CFair estimated viability2002-07-02Based on EO rank specificationsMARINE; INTERTIDAL; ROCKY; EXPOSED; BARE ROCKCOSEWIC. 2003m. COSEWIC assessment and update status report on the Steller sea lion Eumetopias jubatus in Canada. Committee on the Status of Endangered Wildlife in Canada. Ottawa. vii + 47 pp.<BR>COSEWIC. 2013. DRAFT COSEWIC Status Report Update on Steller Sea Lion Eumetopias jubatus in Canada. Committee on the Status of Endangered Wildlife in Canada. Ottawa, ON. 40 pp + appendices.3/7/2006 12:00:00 AMFrench, L.Low? Uncertain whether full extent of EO is knownQCSN53AMAJC0301018180https://a100.gov.bc.ca/pub/eswp/search.do?searchType=COMBINED&method=process&esId=1818026420.18471665.762322326093
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    WHSE_TERRESTRIAL_ECOLOGY.BIOT_OCCR_NON_SENS_AREA_SVW.fid--31aa9699_196a7b0fa41_-65eb25788613FF84660110336247220<i>Plestiodon skiltonianus</i>Plestiodon skiltonianusWestern SkinkWestern SkinkVertebrate AnimalANIMALreptilesN G5S3S4SC (NOV 2014)Blue1 SHUSWAP RIVERLocated aong the north side of the Shuswap River valley about 7 km west of Cherryville.2004-04-252004-09-292004: 3 western skinks, 1 adult and 2 juveniles found during surveys (Davis 2007).EVerified extant (viability not assessed)2004-09-29TERRESTRIAL: Forest Needleleaf, Fine Talus/scree, Grassland/herbaceousDavis, H. 2007. Collection of miscellaneous red and blue-listed vertebrate sightings for the mid-Sushwap River region: 2001-2006.2/14/2007 12:00:00 AMStewart, ACMediumN Confident full extent of EO is NOT knownSRHY32ARACH0111014690https://a100.gov.bc.ca/pub/eswp/search.do?searchType=COMBINED&method=process&esId=1469083065.70571485.694522325413
    MULTIPOLYGON(((50.26442133 -118.73847346,50.2645592 -118.73861589,50.26468427 -118.73880946,50.26478278 -118.73903748,50.26485092 -118.73929111,50.26488612 -118.73956061,50.26488682 -118.73983566,50.26485321 -118.74010564,50.26478651 -118.7403602,50.26468932 -118.74058947,50.26456524 -118.74078485,50.26441916 -118.74093863,50.26425677 -118.74104496,50.26408411 -118.74109977,50.26390793 -118.741101,50.26373497 -118.74104853,50.2635719 -118.74094441,50.26342501 -118.74079256,50.26329986 -118.74059901,50.26320134 -118.740371,50.26313322 -118.74011737,50.2630981 -118.73984787,50.26309739 -118.73958496,50.26295953 -118.73944267,50.26283437 -118.73924898,50.26273585 -118.73902097,50.26266773 -118.73876749,50.26263261 -118.73849799,50.26263182 -118.73822297,50.26266542 -118.73795301,50.26273212 -118.73769845,50.26282939 -118.73746916,50.26295338 -118.7372738,50.26309945 -118.73712002,50.26326193 -118.73701366,50.26343458 -118.73695883,50.26361077 -118.73695759,50.26378363 -118.73701006,50.26394671 -118.73711416,50.26409369 -118.73726598,50.26421876 -118.73745955,50.26431728 -118.73768756,50.26438542 -118.73794119,50.26442063 -118.73821069,50.26442133 -118.73847346)),((50.25763749 -118.71303775,50.25781369 -118.71303656,50.25798665 -118.71308891,50.25814976 -118.71319291,50.25829667 -118.71334451,50.25842188 -118.71353811,50.25852045 -118.71376604,50.25858863 -118.71401946,50.25862381 -118.71428892,50.25862466 -118.71456391,50.25859112 -118.71483387,50.25852447 -118.71508844,50.25842725 -118.71531775,50.2583033 -118.71551316,50.25815726 -118.71566699,50.2579948 -118.71577342,50.25782215 -118.71582832,50.25764596 -118.71582964,50.257473 -118.71577727,50.2573099 -118.71567326,50.25716297 -118.71552152,50.25703778 -118.71532806,50.25693921 -118.71510013,50.25687102 -118.71484658,50.25683584 -118.71457713,50.25683499 -118.71430215,50.25686855 -118.71403234,50.25693519 -118.71377778,50.2570324 -118.71354833,50.25715636 -118.71335307,50.2573024 -118.71319923,50.25746486 -118.7130928,50.25763749 -118.71303775)))
    WHSE_TERRESTRIAL_ECOLOGY.BIOT_OCCR_NON_SENS_AREA_SVW.fid--31aa9699_196a7b0fa41_-65ea25787392FF8466011074162590<i>Melanerpes lewis</i>Melanerpes lewisLewis's WoodpeckerLewis's WoodpeckerVertebrate AnimalANIMALbirdsN G4S2S3BT (NOV 2024)Blue1 VASEUX LAKE, SOUTH OFVaseux Lake nest: private property.19622003-05-13Vaseux Lake nest: 2003: Pair entering cavity in dead topped ponderosa pine (Dawe <i>et al.</i> 2004); 1992: 2 birds. There has been a nest on the property for 20-30 years (B.C. Environ., Fish and Wildl. Program 1992). Vaseux-Bighorn NWA nest 1989: Nesting in area. 5 birds seen (B.C. Environ., Fish and Wildl. Program 1992).BGood estimated viability2003-05-13Nesting in this area known for 30+ years.TERRESTRIAL: Suburban/Orchard; Woodland NeedleafB.C. Environ., Fish and Wildl. Program, Penticton. 1992. Database of wildlife observations in the Okanagan.<BR>Dawe, N.K., Buechert, R., Steward, A.C., Penny, J., Brock, K.A., and F. Russell. 2004. Some aspects of the ecology of Vaseux-Bighorn National Wildlife Area with emphasis on species at risk. Unpublished report. Can. Wildl. Serv., Pacific and Yukon Reg., Delta, British Columbia.3/26/2007 12:00:00 AMWestereng, L.MediumN Confident full extent of EO is NOT knownSOB101YThese records are prior to 1992 and so this area needs to be re-inventoried.17ABNYF0401020006https://a100.gov.bc.ca/pub/eswp/search.do?searchType=COMBINED&method=process&esId=200063121454.7566273.106622324192
    MULTIPOLYGON(((49.26950045 -119.52517441,49.27126468 -119.52519241,49.27299267 -119.52573524,49.27461809 -119.52678191,49.27607841 -119.52829226,49.27731743 -119.53020841,49.27828761 -119.53245661,49.27895164 -119.53495037,49.27928389 -119.53759394,49.27927175 -119.54028563,49.27891551 -119.54292191,49.278229 -119.54540152,49.2772386 -119.54762906,49.27598229 -119.54951883,49.27450844 -119.55099832,49.27287376 -119.5520107,49.27114099 -119.55251695,49.26937677 -119.55249791,49.2676489 -119.55195412,49.26602371 -119.55090673,49.26456369 -119.54939599,49.26332498 -119.54747986,49.2623551 -119.54523207,49.26169128 -119.54273905,49.26135915 -119.54009644,49.26137129 -119.5374058,49.2617274 -119.53477047,49.26241368 -119.53229158,49.26340379 -119.53006442,49.26465978 -119.52817464,49.26613334 -119.52669475,49.2677678 -119.52568162,49.26950045 -119.52517441)))
    WHSE_TERRESTRIAL_ECOLOGY.BIOT_OCCR_NON_SENS_AREA_SVW.fid--31aa9699_196a7b0fa41_-65e925788324FF84660110341747298<i>Sphyrapicus thyroideus</i>Sphyrapicus thyroideusWilliamson's SapsuckerWilliamson's SapsuckerVertebrate AnimalANIMALbirdsN G5S3BE (DEC 2017)Blue1 ROCKY CREEK, LAKE KOOCANUSANone provided. <br>It is south of Rocky Creek (~2.8 km), east of Lake Koocanusa (~2.3 km) and north of the USA border ~5 km.2006-06-172006-06-172006: Active nest in a larch tree. A bird was also observed foraging ~ 150 m to the east of the nest (Ohanjanian et. al. 2006). EVerified extant (viability not assessed)2006-06-17Larch seed tree cut. Larch and Douglas-fir; seed tree cut. TERRESTRIAL; Forest NeedleleafGyug, L. 2007. Electronic database containing WISA records from 1995 to 2007 (includes East Kootenays).<BR>Ohanjanian, I., I. Manley and P. Davidson. 2006. Williamson's Sapsucker in the East Kootenay region of British Columbia: Results of 2006 Inventory. Prepared for Tembec Industries Inc., Forest Investment Account and Ministry of Environment. 23 pp.3/6/2007 12:00:00 AMRamsay, L.R.High? Uncertain whether full extent of EO is knownEKTYCall playbacks were done in the area but no more were detected; single year survey.11ABNYF0503015025https://a100.gov.bc.ca/pub/eswp/search.do?searchType=COMBINED&method=process&esId=150257803.32313.64922325124
    MULTIPOLYGON(((49.34494834 -115.40649842,49.3450364 -115.40649162,49.34512368 -115.406511,49.34520676 -115.40655611,49.34528255 -115.40662514,49.34534807 -115.40671546,49.34540077 -115.40682346,49.34543862 -115.40694518,49.34546033 -115.40707577,49.34546479 -115.40721046,49.34545211 -115.40734382,49.34542259 -115.40747077,49.34537741 -115.40758659,49.3453183 -115.4076867,49.34524762 -115.40776723,49.34516796 -115.40782507,49.34508249 -115.40785811,49.34499436 -115.40786506,49.34490708 -115.40784567,49.344824 -115.40780056,49.34474821 -115.40773153,49.3446827 -115.40764121,49.34463 -115.40753321,49.34459214 -115.40741149,49.34457051 -115.40728075,49.34456597 -115.40714622,49.34457866 -115.40701286,49.34460818 -115.40688591,49.34465335 -115.4067701,49.34471246 -115.40666999,49.34478314 -115.40658946,49.3448628 -115.40653161,49.34494834 -115.40649842)))
    WHSE_TERRESTRIAL_ECOLOGY.BIOT_OCCR_NON_SENS_AREA_SVW.fid--31aa9699_196a7b0fa41_-65e825789801FF84660220367317379<i>Bartramia halleriana</i>Bartramia hallerianaHaller's apple mossHaller's apple mossNonvascular PlantPLANTN G4G5S2S3T (NOV 2011)Blue1 HOLMES RIVER, CA. 6 KM WEST OF ALBERTA/BC BORDEREast of McBride, on Holmes River Forestry Road, ca. Kilometre 49. Upslope south of road, adjacent to creek falls.2005-08-2120112024: Site not visited and presumed to be extant (COSEWIC 2024a). 2011: 50 mature individuals over 5,526 square cm (COSEWIC 2011o). 2009: 39 individuals observed (Arthur 2009). 2005-08-21: 33 individuals over 600 square m. Shaded by forest of <i>Picea engelmannii-Abies lasiocarpa</i>. With understory of <i>Oplopanax horridus, Menziesia ferruginea, Phegopteris connectilis, Hylocomium splendens, Ptilium crista-castrensis, Pleurozium schreberi </i>and <i>Plagiopus oederiana </i>(P. Achuff, pers. comm.)<i>. </i>BGood estimated viability2011Moderately-sized population. In the absence of competition from <i>Bartramia pomiformis</i>, Haller's apple moss may be able to spread at this site.2005: With capsules (P. Achuff, pers. comm.). 2011: With sporophytes. Colony numbers appear stable (COSEWIC 2011o).2005: 33 individuals over 600 square m (P. Achuff, pers. comm.). 2009: 39 individuals observed (Arthur 2009). 2011: 50 mature individuals over 5,526 square cm (COSEWIC 2011o).Competition from <i>Bartramia pomiformis </i>may be an important factor in the limited occurrence of <i>B. halleriana</i>. However, as the latter species does not appear to be present at this site, conditions may be more favorable for the persistence of <i>B. halleriana</i> (Belland 2001). 2011: The proposed Holmes River project is the most serious plausible threat. Diversion of water from a stream and loss of tree cover can both alter the microhabitat. The site is in a leave strip adjacent to a harvest block (COSEWIC 2011o). 2024: Colonies are within a deep ravine, making the threat of wildfire, drought, and climate change less severe due to the moderating influence of the topography and waterbody (COSEWIC 2024a).In forest on shaded, saturated (wet-mesic) cliff adjacent to waterfalls.MontaneTERRESTRIAL: Cliff, Forest NeedleleafAchuff, P. Personal communication.Scientist Emeritus, Ecological Integrity Branch, Parks Canada, Waterton Lakes National Park, AB.<BR>Arthur, W. 2009. Shapefile of Hallers Apple Moss observations within the Omineca Forest Region.<BR>Belland, R. 2001. COSEWIC status report on Haller's Apple Moss Bartramia halleriana in Canada. Comm. on the Status of Endangered Wildl. in Can. Ottawa. 1-17 pp.<BR>COSEWIC. 2011o. COSEWIC assessment and status report on the Haller's Apple Moss Bartramia halleriana in Canada. Committee on the Status of Endangered Wildlife in Canada. Ottawa. xi + 23 pp.<BR>COSEWIC. 2024a. Draft COSEWIC Status Report on Haller's Apple Moss Bartramia halleriana. Committee on the Status of Endangered Wildlife in Canada. Ottawa. xxii + 63 pp.10/9/2024 12:00:00 AMDonovan, M. and E. BarnewallHigh? Uncertain whether full extent of EO is knownNPK1170YTo determine full extent and viability of population.Achuff, P. (7617). 2005. ALTA.; Achuff, P. (7619). 2005. ALTA.6NBMUS0R02013959https://a100.gov.bc.ca/pub/eswp/search.do?searchType=COMBINED&method=process&esId=13959702.30894.095522326601
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