| WHSE_TERRESTRIAL_ECOLOGY.BIOT_OCCR_NON_SENS_AREA_SVW.fid-437d179c_19d5a692cbb_-5b11 | 29911934 | FF84660220 | 25530 | 6630 | <i>Fabronia pusilla</i> | Fabronia pusilla | silver hair moss | silver hair moss | Nonvascular Plant | PLANT | | N | G4G5 | S1S3 | E (MAY 2012) | Red | 1 | SUMAS MOUNTAIN, WEST END | From Trans Canada Highway at Abbotsford, travel north on Sumas Way to Old Clayburn Road. Turn right and follow Old Clayburn Road to McMillan Road. Turn right and follow McMillan Road to McKee Road where you turn left. Follow McKee Road around to the southwest slopes of Sumas Mountain. | 1968-03-10 | 1968-03-10 | This is the only known extant site for <i>Fabronia pusilla </i>in Canada. This species was not observed during surveys in 2001 and 2005. Last observed in 1968, when it was collected from a cranny on a dry vertical sandstone cliff and from a damp, shaded sandstone cliff (W. Schofield, pers. comm. 1968). | H | Historical | 1968-03-10 | <i>Fabronia pusilla</i> has not been observed at this location since 1968. Two recent surveys were unsuccessful in relocating plants. Because this plant is small and the site contains extensive suitable habitat, it is possible that <i>Fabronia pusilla </i>is still extant. | [No data provided.] | [No data provided.] | [No data provided.] | Exposed sandstone cliffs within a forested matrix near recent suburban housing developments. | Lowland | TERRESTRIAL: Cliff | | McIntosh, T.T. 2002. Assessment and status report on the silver hair moss Fabronia pusilla in Canada. Rep. submitted to the Comm. on the Status of Endangered Wildl. in Can. Ottawa. 17pp.<BR>McIntosh, T.T. Personal communication. Biospherics Environmental Inc.<BR>Schofield, W.B. Personal communication.<BR>University of British Columbia. Dep. Bot., Dep. Zool., Biol. Sci. Bldg., 6270 Univ. Blvd., Vancouver, BC. | 9/18/2008 12:00:00 AM | Donovan, M., S. Hartwell, and J. Penny | Low | ? | Uncertain whether full extent of EO is known | FRL | | | 200 | 440 | Y | Further surveys of Sumas Mountain are needed to determine if the species still exists at this site. According to the 2002 COSEWIC report, a search in Garry oak and open cliff habitats along the southwestern BC Coast is recommended. However, much of the potential habitat for this species (i.e., steep sandstone cliffs) is inaccessible (T. McIntosh, pers. comm. 2002). | | This EO was created from UTM coordinates collected during a 2005 transect survey. The species was not relocated during the survey but the original collector estimated the location of the original 1968 collection site (T. McIntosh, pers. comm. 2002; W.B. Schofield, pers. comm. 2002). The source polygon was extended to include additional potential habitat to the east. | Schofield, W.B. #35903 # b179761. UBC. | 1 | NBMUS2V030 | 14397 | | https://a100.gov.bc.ca/pub/eswp/search.do?searchType=COMBINED&method=process&esId=14397 | 293987.1485 | 4747.0776 | 26773235 | |
MULTIPOLYGON(((49.06347537 -122.21121294,49.06342172 -122.21193848,49.06315815 -122.21232042,49.06289669 -122.21276228,49.06259778 -122.2132674,49.06237156 -122.21358621,49.061948 -122.21392106,49.06165754 -122.2146658,49.06127768 -122.21511725,49.06089983 -122.21562861,49.06045158 -122.21638615,49.06015899 -122.21707081,49.05979178 -122.21788182,49.05934976 -122.21881905,49.05905935 -122.21956358,49.0587358 -122.22049117,49.05849952 -122.22165199,49.05857273 -122.22260746,49.05844015 -122.22333916,49.05894487 -122.22305793,49.05953264 -122.22289012,49.05992528 -122.2227982,49.05990268 -122.22328069,49.05996533 -122.22393664,49.05978907 -122.22455173,49.06020269 -122.22505909,49.06023428 -122.22595775,49.05984805 -122.2262295,49.05976545 -122.22725756,49.05975116 -122.22797983,49.0598949 -122.22868916,49.05927809 -122.22915979,49.05934702 -122.22999533,49.05952592 -122.2305818,49.05978165 -122.23110183,49.05986528 -122.2323569,49.05975786 -122.23380766,49.05971256 -122.23477275,49.05947996 -122.2349117,49.05895421 -122.23459371,49.05880218 -122.23364459,49.05873959 -122.23298878,49.05869754 -122.23179046,49.05847497 -122.23108738,49.05809865 -122.23051703,49.05737985 -122.23033487,49.05691407 -122.22947127,49.05698196 -122.22802378,49.057493 -122.22792233,49.05767138 -122.22736705,49.05772505 -122.22664177,49.05765188 -122.2256863,49.05751453 -122.22515673,49.05698929 -122.22598029,49.05669408 -122.22546351,49.05642357 -122.22452406,49.05639828 -122.22380505,49.0567529 -122.22263484,49.05704552 -122.22195013,49.05755015 -122.2216689,49.05780119 -122.22092746,49.05805425 -122.22024606,49.05816628 -122.21985077,49.05810997 -122.21958054,49.058332 -122.21914197,49.05858936 -122.21858036,49.05892978 -122.21813204,49.05915391 -122.21775336,49.05944017 -122.21688885,49.05965585 -122.21627053,49.06018945 -122.21568632,49.060594 -122.2148123,49.06104655 -122.21417456,49.06149478 -122.21341714,49.06194943 -122.21283929,49.06239342 -122.211962,49.06269232 -122.21145688,49.06310952 -122.21094226,49.06347537 -122.21121294)))
|
| WHSE_TERRESTRIAL_ECOLOGY.BIOT_OCCR_NON_SENS_AREA_SVW.fid-437d179c_19d5a692cbb_-5b10 | 29917072 | FF84660300 | 102044 | 12526 | <i>Schoenoplectus acutus </i>Deep Marsh | Schoenoplectus acutus Deep Marsh | hard-stemmed bulrush Deep Marsh | hard-stemmed bulrush Deep Marsh | Ecological Community | NPC | | N | G5 | S3 | | Blue | | JACK SMITH LAKE, 3.9 KM EAST OF | | 1994 | 2009/04/14 | This wetland element occurrence is based on Terrestrial Ecosystem Mapping but has not been confirmed by a field sample. The element occurrence occupies an estimated 8.7% (0.11 ha) of the area shown. Annual and seasonal fluctuations in water levels results in changes to the vegetation over time. The vegetation and ecological community on this site may have changed since mapping. | E | Verified extant (viability not assessed) | | | | 0.11 ha | | The occurrence is in a depression on the middle slopes of the Okanagan Valley. It is surrounded by upland coniferous forests upslope. It is associated with deciduous riparian forest and shallow open water. | | | IDF dm 1 | Cadrin, C.M., and K. Iverson. 2013. Element occurrence and element occurrence rank specifications for wet transition grasslands of British Columbia. Unpublished document. B.C. Minist. Environ., Conservation Data Centre, Victoria, B.C. 3 pp.<BR>Iverson, K., D. Curran, T. Fleming, and A. Haney. 2008. Sensitive Ecosystems Inventory: Okanagan Valley: Vernon to Osoyoos, 2000-2007. Methods, Ecological Descriptions, Results and Conservation Tools. Technical Report Series No. 495, Canadian Wildlife Service, Pacific and Yukon Region, British Columbia. 224pp.<BR>Terrestrial Ecosystem Mapping [TEM] of the Central Okanagan Valley: updated Mar. 2009c. Prepared for Okanagan Collaborative Conservation program by A. Haney and K. Iverson. 1:20,000 spatial data. | 10/23/2015 12:00:00 AM | Iverson, K. and A. Haney | Low | ? | Uncertain whether full extent of EO is known | NOH | The occurrence is mapped on a thin lacustrine deposit overlying a glaciofluvial plain. It is very poorly drained. | Bioterrain: /LG/FGp; drainage imperfect to very poorly. | | | Y | | This element occurrence is based on available ecosystem mapping. Many factors influence the reliability of an ecosystem map. Depending on the scale of aerial images used to capture the ecosystems, very small ecosystems and some types of disturbance may not be visible and will not be mapped. If the air photos are not current, new disturbance may have occurred since the time of mapping and the inventory may not accurately represent the current state of the landscape. Other factors, such as the skill and experience of the mapper within the study area, and the field survey intensity level will also influence the reliability of the map. | The element occupies 8.7% (0.11 ha) of this element occurrence. | | 51 | CEBC001044 | 20410 | Wetland Realm - Mineral Wetland Group: Marsh Wetland Class (Wm) | https://a100.gov.bc.ca/pub/eswp/search.do?searchType=COMBINED&method=process&esId=20410 | 12677.0198 | 435.2329 | 26778373 | |
MULTIPOLYGON(((49.79559159 -119.41099516,49.79555904 -119.4110304,49.79552293 -119.41105624,49.79544857 -119.41109764,49.79542864 -119.41110707,49.7953483 -119.41113915,49.79530162 -119.41114992,49.79525465 -119.41114539,49.79520921 -119.41112586,49.7951356 -119.41108097,49.79509429 -119.41104759,49.79505819 -119.41100175,49.79502913 -119.41094542,49.79500817 -119.41088108,49.79499619 -119.4108114,49.79499392 -119.41073949,49.79499474 -119.41071567,49.79498015 -119.41059226,49.79497647 -119.4105285,49.79498047 -119.41046475,49.79499192 -119.41040313,49.79501059 -119.41034591,49.79510183 -119.4101205,49.79512202 -119.41007812,49.79522851 -119.40988692,49.79524034 -119.40986736,49.79532371 -119.40973903,49.79535795 -119.40969588,49.79539693 -119.40966391,49.795478 -119.40961247,49.79551513 -119.40959457,49.79555358 -119.4095868,49.79564173 -119.40958078,49.79564272 -119.40958064,49.79582729 -119.40956937,49.79584308 -119.40956919,49.79600947 -119.409577,49.79601501 -119.40957745,49.79611052 -119.40958558,49.79614979 -119.40959428,49.79618737 -119.40961369,49.79627669 -119.40967334,49.79631257 -119.40970359,49.79634433 -119.40974336,49.79637089 -119.40979141,49.79639136 -119.40984605,49.79640508 -119.40990558,49.79641164 -119.40996781,49.79641603 -119.41006578,49.79641441 -119.41013769,49.79640327 -119.41020736,49.79638307 -119.41027205,49.79635472 -119.410329,49.79624788 -119.41050255,49.79621724 -119.41054392,49.79618225 -119.4105763,49.79609684 -119.41063951,49.7960594 -119.41066123,49.79602006 -119.41067234,49.79591475 -119.41068724,49.79588074 -119.41069549,49.79578517 -119.41078345,49.79577677 -119.41079094,49.79569844 -119.4108562,49.79565062 -119.41091832,49.79559159 -119.41099516)))
|
| WHSE_TERRESTRIAL_ECOLOGY.BIOT_OCCR_NON_SENS_AREA_SVW.fid-437d179c_19d5a692cbb_-5b0f | 29911478 | FF84660210 | 24276 | 6519 | <i>Crassula connata</i> | Crassula connata | Erect Pigmyweed | Erect Pigmyweed | Vascular Plant | PLANT | dicots | N | G5 | S2S3 | | Blue | | RUM ISLAND | On cliffs on south side. | 1982-05-09 | 1982-05-09 | [No Data] | E | Verified extant (viability not assessed) | 1982-05-09 | There is no data available to aid in assigning a letter rank for this species at this site. | | | | | Lowland | TERRESTRIAL; ROCK OUTCROP | | Ceska, A. Personal communication. Geobotanical Consulting. | 7/12/2005 12:00:00 AM | JLP | Medium | | | SOG | | | | | N | | | | Ceska, A. (10193). 1982. V173656. V. | 12 | PDCRA02040 | 18644 | | https://a100.gov.bc.ca/pub/eswp/search.do?searchType=COMBINED&method=process&esId=18644 | 31214.5956 | 627.3112 | 26772779 | |
MULTIPOLYGON(((48.66269162 -123.27644833,48.66286791 -123.27646416,48.66303876 -123.27653143,48.6631976 -123.27664754,48.66333829 -123.2768081,48.66345552 -123.27700677,48.66354468 -123.27723608,48.6636024 -123.27748715,48.66362644 -123.27775034,48.66361591 -123.27801553,48.66357119 -123.27827253,48.663494 -123.27851134,48.66338726 -123.2787231,48.66325519 -123.27889931,48.66310275 -123.27903357,48.66293585 -123.27912039,48.66276089 -123.27915655,48.6625846 -123.27914071,48.66241375 -123.27907343,48.662255 -123.27895717,48.66211423 -123.27879675,48.66199709 -123.27859794,48.66190784 -123.27836878,48.66185012 -123.27811771,48.66182608 -123.27785453,48.66183661 -123.27758935,48.66188133 -123.27733236,48.66195861 -123.27709342,48.66206525 -123.2768818,48.66219741 -123.27670545,48.66234976 -123.27657133,48.66251666 -123.2764845,48.66269162 -123.27644833)))
|
| WHSE_TERRESTRIAL_ECOLOGY.BIOT_OCCR_NON_SENS_AREA_SVW.fid-437d179c_19d5a692cbb_-5b0e | 29919700 | FF84660120 | 147700 | 18928 | <i>Radiodiscus abietum</i> | Radiodiscus abietum | Fir Pinwheel | Fir Pinwheel | Invertebrate Animal | ANIMAL | gastropods | N | G4 | S2? | | Red | | KANE CREEK | North of Highway 31A, next to Kane Creek and the Kane Creek FSR at Three Forks. | 2013-09-22 | 2013-09-22 | One Fir Pinwheel was collected in 2013 (GBIF.org 2025s). | E | Verified extant (viability not assessed) | 2013-09-22 | | | | | Second-growth mixed-wood forest (70-80 years old) along fast-flowing tributary creek (Ovaska 2013). | | TERRESTRIAL: Forest Mixed | | GBIF.org. 2025s. Occurrence download for Radiodiscus abietum. Accessed 3 February 2025.<BR>Ovaska, K. 2013. Electronic database of Pygmy & Sheathed Slug & Banded Tigersnail records summary, Oct-13. | 2/3/2025 12:00:00 AM | Davis, H. | Medium | N | Confident full extent of EO is NOT known | CCM | | | 829 | 829 | Y | | | | | 3 | IMGAS49020 | 36935 | | https://a100.gov.bc.ca/pub/eswp/search.do?searchType=COMBINED&method=process&esId=36935 | 31215.678 | 627.322 | 26781001 | |
MULTIPOLYGON(((50.01617555 -117.28189534,50.01635174 -117.28188849,50.0165254 -117.28193512,50.01668987 -117.28203344,50.01683878 -117.28217973,50.0169665 -117.2823682,50.01706804 -117.28259178,50.01713952 -117.28284181,50.01717819 -117.28310868,50.01718261 -117.28338213,50.01715255 -117.28365166,50.0170892 -117.28390692,50.01699494 -117.28413802,50.0168735 -117.28433625,50.01672944 -117.28449382,50.01656834 -117.28460476,50.01639639 -117.28466477,50.01622019 -117.28467162,50.01604653 -117.28462497,50.01588206 -117.28452665,50.01573316 -117.28438035,50.01560544 -117.28419188,50.01550391 -117.2839683,50.01543243 -117.28371828,50.01539376 -117.28345142,50.01538934 -117.28317798,50.0154194 -117.28290846,50.01548274 -117.28265321,50.01557701 -117.28242211,50.01569844 -117.28222389,50.0158425 -117.28206631,50.0160036 -117.28195536,50.01617555 -117.28189534)))
|
| WHSE_TERRESTRIAL_ECOLOGY.BIOT_OCCR_NON_SENS_AREA_SVW.fid-437d179c_19d5a692cbb_-5b0d | 29911450 | FF84660110 | 23915 | 6459 | <i>Rangifer tarandus</i> pop. 14 | Rangifer tarandus pop. 14 | Caribou (Boreal Population) | Caribou (Boreal Population) | Vertebrate Animal | ANIMAL | mammals | N | G5TNRQ | S2? | T (NOV 2014) | Red | 1 | ETTHITHUN LAKE - CHINCHAGA RIVER | | | 2004 | Current (2004) population estimate for the entire Chinchaga Range (which includes the Ethithum core) is 483 (433-533) (Culling et al. 2004). | D | Poor estimated viability | 2004 | The Chinchaga is a cross border herd with Alberta; it is declining on the Alberta side, so it is likely declining in BC as well (I.W. Hatter, pers. comm.) | | | | | | TERRESTRIAL; SUBALPINE; FOREST MIXED | | Culling, D.E., et al. 2004. Interim oil and gas industry guidelines for boreal caribou ranges in northeastern British Columbia. Prepared. for Oil and Gas Comm., Fort St. John, BC. 32pp.+ map.<BR>Hatter, I.W. Personal communication. | 10/15/2004 12:00:00 AM | French, L. | High | ? | Uncertain whether full extent of EO is known | CLH;FNL | | | | | N | | | | | 1 | AMALC0401E | 14385 | | https://a100.gov.bc.ca/pub/eswp/search.do?searchType=COMBINED&method=process&esId=14385 | 822228926.4182 | 119155.1714 | 26772751 | |
MULTIPOLYGON(((57.9691318 -120.00168572,57.96860017 -120.00992461,57.96627324 -120.01899525,57.96394561 -120.0280646,57.96390147 -120.04172377,57.96706805 -120.05307079,57.97483156 -120.0592627,57.98018547 -120.07111913,57.98125459 -120.08605973,57.9833774 -120.09954975,57.98931224 -120.1052189,57.99672666 -120.11213725,57.99970166 -120.11531463,58.00067324 -120.12617173,58.00049576 -120.13438728,58.00508772 -120.14495645,58.00961774 -120.15279881,58.01209575 -120.16627511,58.01312359 -120.17986717,58.0111015 -120.18686262,58.00756986 -120.19124143,57.99730625 -120.20297941,57.99556657 -120.22293173,57.99386806 -120.24492863,57.99397692 -120.26678539,57.99183586 -120.28539612,57.99170544 -120.31341848,57.99252703 -120.3352207,57.99688247 -120.3526633,58.00229405 -120.36866568,58.00782987 -120.39081536,58.01251219 -120.40688098,58.01494963 -120.41969388,58.01711987 -120.43731331,58.01841266 -120.44747646,58.01822817 -120.45637781,58.0161907 -120.46335904,58.01160323 -120.46983597,58.00610424 -120.48526035,58.00127431 -120.49789998,57.99536946 -120.5112938,57.98922034 -120.53084833,57.98460282 -120.53594746,57.97927378 -120.54177694,57.97414122 -120.55783395,57.96931696 -120.57113427,57.96445237 -120.58238582,57.95763156 -120.60536799,57.95071749 -120.62357092,57.94247761 -120.64867585,57.93653143 -120.66066055,57.92969692 -120.66383322,57.92204987 -120.66228461,57.91577693 -120.65655695,57.91015281 -120.64669917,57.90456593 -120.6388867,57.8957302 -120.63197157,57.88656987 -120.62712484,57.88060675 -120.61866403,57.86985568 -120.60643855,57.86022927 -120.59618719,57.8552994 -120.58494601,57.8464218 -120.57601487,57.83781468 -120.56230785,57.83196009 -120.54093874,57.82915971 -120.52752764,57.82291029 -120.50483633,57.8133421 -120.47966489,57.80550362 -120.4686577,57.7991135 -120.45755318,57.79408959 -120.44227914,57.79189322 -120.423411,57.79026558 -120.39703078,57.78658536 -120.37691598,57.78248306 -120.35411889,57.77988287 -120.33393287,57.77720757 -120.31035929,57.77703468 -120.28524297,57.78038046 -120.27208615,57.78201111 -120.24683004,57.78048068 -120.2265691,57.77923433 -120.20289166,57.78076052 -120.17356507,57.78281002 -120.15166687,57.78393953 -120.13556377,57.77985672 -120.11725296,57.7732461 -120.10307124,57.77022718 -120.08566402,57.76727374 -120.07119552,57.76586477 -120.05562313,57.76227068 -120.0363095,57.75988065 -120.02376207,57.76012707 -120.01197856,57.7562122 -120.00152016,57.9691318 -120.00168572)))
|
| WHSE_TERRESTRIAL_ECOLOGY.BIOT_OCCR_NON_SENS_AREA_SVW.fid-437d179c_19d5a692cbb_-5b0c | 29911455 | FF84660110 | 23943 | 6472 | <i>Rangifer tarandus</i> pop. 14 | Rangifer tarandus pop. 14 | Caribou (Boreal Population) | Caribou (Boreal Population) | Vertebrate Animal | ANIMAL | mammals | N | G5TNRQ | S2? | T (NOV 2014) | Red | 1 | CALENDAR CREEK; CALENDAR RANGE | | | 2004 | Current (2004) population estimate for the entire Calendar range (which includes the Calendar core) is 291 (range 154 - 429) (Culling et al. 2004).<br> | E | Verified extant (viability not assessed) | 2004 | | | | | | | TERRESTRIAL; MUSKEG; FOREST MIXED | | Culling, D.E., et al. 2004. Interim oil and gas industry guidelines for boreal caribou ranges in northeastern British Columbia. Prepared. for Oil and Gas Comm., Fort St. John, BC. 32pp.+ map. | 10/15/2004 12:00:00 AM | French, L. | High | ? | Uncertain whether full extent of EO is known | TLP;PEP;FNL | | | | | N | | | | | 15 | AMALC0401E | 14385 | | https://a100.gov.bc.ca/pub/eswp/search.do?searchType=COMBINED&method=process&esId=14385 | 4963894600.3413 | 350611.1171 | 26772756 | |
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| WHSE_TERRESTRIAL_ECOLOGY.BIOT_OCCR_NON_SENS_AREA_SVW.fid-437d179c_19d5a692cbb_-5b0b | 29913662 | FF84660120 | 122531 | 15317 | <i>Cercyonis pegala incana</i> | Cercyonis pegala incana | Common Wood-nymph, <i>incana </i>subspecies | Common Wood-nymph, incana subspecies | Invertebrate Animal | ANIMAL | insects | N | G5T4T5 | S2? | | Red | | SALTSPRING ISLAND, MOUNT TUAM | Southwest Saltspring Island, Mount Tuam. | 2014-08-12 | 2017-08 | Over 30 Common Wood-nymphs, incana subspecies, observed flying on the southwest side of Saltspring Island in 2017 (Ferguson 2017). Six observed flying in 2015 and three observed flying in 2014 (Griffiths 2016). | E | Verified extant (viability not assessed) | 2017-08 | | Observations occur on federal lands, ecological reserves and nature reserves. | Occurrence is comprised of six point features, each with one observation, and one polygon with multiple observations (Griffiths 2016). | | | | TERRESTRIAL: Savannah, Roadside, Grassland/Herbaceous | | Ferguson, R. 2017. Avian species at risk survey report. Transport Canada Property, Mt. Tuam. Prepared for the Salt Spring Island Conservancy. 14 pp.<BR>Griffiths, C. 2016. Electronic spreadsheet containing multi species data for the Saltspring Island Conservancy from April 2013 to December 2015. | 12/20/2018 12:00:00 AM | Davis, H. | High | N | Confident full extent of EO is NOT known | SGI | | | | | Y | | | | | 2 | IILEPN701G | 17064 | | https://a100.gov.bc.ca/pub/eswp/search.do?searchType=COMBINED&method=process&esId=17064 | 121962.2444 | 2287.9037 | 26774963 | |
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| WHSE_TERRESTRIAL_ECOLOGY.BIOT_OCCR_NON_SENS_AREA_SVW.fid-437d179c_19d5a692cbb_-5b0a | 29913789 | FF84660210 | 65397 | 9254 | <i>Alopecurus magellanicus</i> | Alopecurus magellanicus | alpine meadow-foxtail | alpine meadow-foxtail | Vascular Plant | PLANT | monocots | N | G5 | SU | | Unknown | | PINK MOUNTAIN | Approximately 3 km northwest of the summit of Pink Mountain. | 1992-08-10 | 2014-07 | 2014-07: Observed (Long 2016). 2013-07-21: In alpine zone, wet depression close to the road on the mountaintop (University of British Columbia Herbarium). 2010-SU: Observed (R. Long, pers. comm. 2010). 1992-08-10: In a wet alpine meadow on the summit of Pink Mountain (University of British Columbia Herbarium). | CD | Fair or poor estimated viability | 2014-07 | Construction of communication antennas and 2 gas wells on the summit has destroyed habitat. If further industrial development occurs (e.g. additional gas wells, proposed wind turbines, transmission lines to service an existing gas extraction plant), the viability of existing rare plant populations over the next 20 years is expected to be fair to poor. | [No data provided.] | [No data provided.] | Construction of communication antennas and 2 gas wells on the summit, north of the main plant concentrations resulted in the destruction of several hectares of fragile alpine habitat. Heavy trucks carrying fuel are destroying the road in places. Construction of additional wells and/or transmission lines to service the existing the gas extraction plant will likely also impact plants, especially if lines follow the existing road off the mountain. If a plan to erect 40 wind turbines on the summit moves forward, existing plant populations may be destroyed. There are also threats from off road vehicle use (R. Long, pers. comm. 2014).<br /> | | Alpine | TERRESTRIAL: Alpine; PALUSTRINE: Temporary Pool | | Long, R. 2016. The unique biodiversity of Pink Mountain. Unpublished report. 44 pages.<BR>Long, R. Personal communication.<BR>University of British Columbia. Dep. Bot., Dep. Zool., Biol. Sci. Bldg., 6270 Univ. Blvd., Vancouver, BC. | 3/29/2017 12:00:00 AM | Cook, J.B. and P. Chytyk | High | ? | Uncertain whether full extent of EO is known | MUF | | | 1774 | 1784 | Y | To determine full extent and viability of population. | | | Csergo, A.M. and R. Long. (4). 2013. UBC.; Lomer, F. (92-154). 1992. #V206495. UBC. | 2 | PMPOA07020 | 18097 | | https://a100.gov.bc.ca/pub/eswp/search.do?searchType=COMBINED&method=process&esId=18097 | 1404.616 | 188.1909 | 26775090 | |
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| WHSE_TERRESTRIAL_ECOLOGY.BIOT_OCCR_NON_SENS_AREA_SVW.fid-437d179c_19d5a692cbb_-5b09 | 29908730 | FF84660300 | 123848 | 15452 | <i>Amelanchier alnifolia</i> - <i>Shepherdia canadensis</i> - <i>Juniperus communis</i> | Amelanchier alnifolia - Shepherdia canadensis - Juniperus communis | saskatoon - soopolallie - common juniper | saskatoon - soopolallie - common juniper | Ecological Community | NPC | | N | GNR | S3? | | Blue | | DALZELL CREEK / ELK RIVER, 3.6 KM EAST OF | | 2010 | 2010-07-04 | This brushland occurrence is based on grassland exceptions mapping for a Predictive Ecosystem Mapping project but has not been confirmed by a field sample. The ecological community occupies up to 33.1 percent (1.03 ha) of the area shown. Mapping did not estimate the proportion of each polygon with the target element, thus the amount of ecological community in the occurrence is not known at this time. | E | Verified extant (viability not assessed) | | | | Up to 1.03 ha | | The occurrence is located on a south-facing slope on gently, rolling hills in the bottom of the Elk Valley adjacent to the Rocky Mountains. It is surrounded by forest with a mine 1.0 km to the south of the occurrence. | | | ESSFdk 1;MS dk 1 | Grasslands exception mapping in the Elk Valley for Predictive Ecosystem Mapping [PEM] of Cranbrook TSA. DRAFT from November 2015. Grasslands, brushlands, and alpine grasslands were delineated on orthophotos. Prepared by Kristi Iverson, Lac la Hache, B.C. for Deb MacKillop, regional ecologist, Nelson, BC. 1:20 000 spatial data.<BR>K. Iverson. 2019. Element occurrence specifications for Amelanchier alnifolia - Shepherdia canadensis - Juniperus communis of the southern interior of British Columbia. Unpublished document. Version March 31, 2019. B.C. Minist. Environ., Conservation Data Centre, Victoria, B.C. 7 pp. | 2/27/2019 12:00:00 AM | Iverson, K. and A. Haney | Medium | ? | Uncertain whether full extent of EO is known | ELV | Reviewed information did not include additional environmental information. | | | | Y | | | The Amelanchier alnifolia - Shepherdia canadensis - Juniperus communis ecological community occupies up to 33.1 percent (1.03 ha) of the mapped occurrence. Mapping did not estimate the proportion of polygon(s) with the target element, thus the amount of ecological community in the element occurrence is not known at this time. | | 76 | CEBC003138 | 316203 | Terrestrial Realm - Grassland Group (G): Grassland Brushland Class (Gb) | https://a100.gov.bc.ca/pub/eswp/search.do?searchType=COMBINED&method=process&esId=316203 | 31092.4846 | 843.8821 | 26770031 | |
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| WHSE_TERRESTRIAL_ECOLOGY.BIOT_OCCR_NON_SENS_AREA_SVW.fid-437d179c_19d5a692cbb_-5b08 | 29908421 | FF84660110 | 106617 | 13817 | <i>Accipiter atricapillus laingi</i> | Accipiter atricapillus laingi | American Goshawk, <i>laingi</i> subspecies | American Goshawk, laingi subspecies | Vertebrate Animal | ANIMAL | birds | N | G5T2 | S2 | T (APR 2013) | Red | 1 | FROST LAKE, 1.5 KM NORTHWEST OF | Along Back Road, southeast of Woss. | 2010 | 2011 | 2010 and 2011: nests located within mapped occurrence (Sinclair 2016). | E | Verified extant (viability not assessed) | 2011 | | | | | | | TERRESTRIAL: Forest needleleaf | | Sinclair, L. 2016. Ministry of Forests, Lands and Natural Resources Operations. Electronic database containing Northern Goshawk, laingi nest records. Submitted to CDC February, 2016. | 8/27/2016 12:00:00 AM | Shepard, M.G. | High | N | Confident full extent of EO is NOT known | NIM | | | | | Y | | | | | 148 | ABNKC12062 | 19381 | | https://a100.gov.bc.ca/pub/eswp/search.do?searchType=COMBINED&method=process&esId=19381 | 1404.616 | 188.1909 | 26769722 | |
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