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"description": "Barren-ground caribou annual ranges and calving areas by herd (i.e. subpopulation). The supplementary table BIO_ENR_WFE_SARA_AttributeTable contains additional attribute information for this species and its status and range in the NWT. All barren-ground caribou subpopulations considered by COSEWIC (2016) as part of Designatable Unit 3 are included in this shapefile. See COSEWIC (2011) for details on the Designatable Unit. Subpopulation structure of caribou (Rangifer tarandusL.) is as described by Nagy et al. (2011) for the Qamanirjuaq, Ahiak (i.e. Queen Maud Gulf), Beverly, Bathurst, Bluenose-East, Bluenose-West, Cape Bathurst, Lorillard and Wager Bay subpopulations. Other types of caribou (e.g. Dolphin and Union, Peary, mountain woodland, boreal woodland) are not included. Their ranges are available as separate NWT species at risk range shapefiles. Some of their ranges overlap with the barren-ground caribou ranges in this shapefile.Important notes: There is year-to-year variation in the areas used by barren-ground caribou, and there has been range contraction for several herds as they have reached lower numbers. Range information is being updated and is subject to change.If shapefiles are being used to consider potential impacts of development on barren-ground caribou, Environment and Natural Resources recommends seeking further information on seasonal ranges.Polygons were derived using collar data from Government of Nunavut, Government of the Northwest Territories, Yukon Environment and United States Fish and Wildlife Service. “Collar data” provide information on range use by caribou that were collected over many years by remotely tracking locations of caribou fitted with radio-collars using satellite telemetry. Composite shapefile was developed by GNWT ENR, Yellowknife. Details on the origin of each polygon are provided in the table below:Herd (subpopulation)Annual rangeCalving areaPorcupineObtained from the Porcupine Caribou Technical Committee. As displayed on the Porcupine Caribou Management Board website (http://www.pcmb.ca/images/habitat/PCH-Rangemap2.jpg)Prepared by K. Poole (Poole 2011) for CARMA (2012). Cumulative extent of calving (1-21 June) from 1985 – 2010. 90% fixed kernel polygon using all available satellite collar data, obtained from Yukon Environment, combined among years.Tuktoyaktuk PeninsulaCreated byA. D'Hont, ENR in 2013. Produced using caribou collar telemetry data 2006-2012. Contours accumulate the number of unique marked individuals that visit within a 10x10km cell; The contour shown by this polygon is 5%. The percentages are based on the highest count (=100%) of unique collared individuals for that herd occurring within any 10km x 10km block, illustrating the relative degree of use of specific land areas over a defined period of time. Created byA. D'Hont, ENR in 2013.Cape BathurstGeneralized annual range polygon from Nagy et al. (2011) Fig. 3, based on mean 90% utilization distribution from accumulated collar data 1996-2008Calving ground A from Nagy et al. (2011) Fig. 1Bluenose-WestGeneralized annual range polygon from Nagy et al. (2011) Fig. 3, based on mean 90% utilization distribution from accumulated collar data 1996-2008Calving ground B from Nagy et al. (2011) Fig. 1Bluenose-EastGeneralized annual range polygon from Nagy et al. (2011) Fig. 3, based on mean 90% utilization distribution from accumulated collar data 1996-2008Calving ground C from Nagy et al. (2011) Fig. 1BathurstGeneralized annual range polygon from Nagy et al. (2011) Fig. 3, based on mean 90% utilization distribution from accumulated collar data 1996-2008Calving ground D from Nagy et al. (2011) Fig. 1BeverlyGeneralized annual range polygon from Nagy et al. (2011) Fig. 3, based on mean 90% utilization distribution from accumulated collar data 1995-2008There are 2 polygons, a northern and a southern calving ground. Based on BQCMB compilation of all data from government surveys (1957-2011) and telemetry (1996-2012). See Poole (2011) for details.Polygons are as displayed by BQCMB (2014) as well as Nagy et al. (2011, Fig. 1, calving grounds E-1 and F).AhiakGeneralized annual range polygon for ‘Queen Maud Gulf’ from Nagy et al. (2011) Fig. 3, based on mean 90% utilization distribution from accumulated collar data 1996-2008. In 2017, the Ahiak annual range was extended by B.Fournier (ENR) to cover the Queen Maud Gulf calving area produced by J.Nagy, when it was discovered that 2 areas in the northwest and northeast of the calving area were not covered by the annual range polygon.Calving ground E from Nagy et al. (2011) Fig. 1QamanirjuaqGeneralized annual range polygon from Nagy et al. (2011) Fig. 3, based on mean 90% utilization distribution from accumulated collar data 1993-2008Based on BQCMB compilation of all data from government surveys (1963-2008) and telemetry (1993-2012). See Poole (2011) for details.Polygons are as displayed by BQCMB (2014) as well as Nagy et al. (2011, Fig. 1, calving ground G).LorillardGeneralized annual range polygon from Nagy et al. (2011) Fig. 3, based on mean 90% utilization distribution from accumulated collar data 1998-2007Calving ground H from Nagy et al. (2011) Fig. 1Wager BayGeneralized annual range polygon from Nagy et al. (2011) Fig. 3, based on mean 90% utilization distribution from accumulated collar data 2000-2006Calving ground I from Nagy et al. (2011) Fig. 1Boothia PeninsulaAs shown in COSEWIC (2016) Fig. 2. Digitized by B. Fournier, ENR, as instructed by COSEWIC (J. Ray) in 2015.Polygon not availableSouthampton IslandAs shown in COSEWIC (2016) Fig. 2. Digitized by B. Fournier, ENR, as instructed by Mitch Campbell (Govt of NU) in 2014, for the COSEWIC report. Used entire island as there were no quantitative seasonal range data available.Polygon not availableCoats IslandAs shown in COSEWIC (2016) Fig. 2. Digitized by B. Fournier, ENR, as instructed by Mitch Campbell (Govt of NU) in 2014, for the COSEWIC report. Used entire island as there were no quantitative seasonal range data available.Polygon not availableBaffin IslandAs shown in COSEWIC (2016) Fig. 2. Digitized by B. Fournier, ENR, from an image provided by Troy Pretzlaw (Govt of NU) in 2014, for the COSEWIC report. Polygon not availableAcronyms:BQCMB = Beverly and Qamanirjuaq Caribou Management BoardCARMA = CircumArctic Rangifer Monitoring and Assessment NetworkCOSEWIC = Committee on the Status of Endangered Wildlife in CanadaReferences cited in table:BQCMB. 2014. Beverly and Qamanirjuaq Caribou Management Plan 2013-2022. Beverly and Qamanirjuaq Caribou Management Board, Stonewall, MB. Available at http://arctic-caribou.com/pdf/bqcmb_managementplan_detailed2014.pdfCARMA. 2012. Caribou herd information. CircumArctic Rangifer Monitoring and Assessment Network. Web site: http://www.caff.is/carmaherds[accessed December 2012]COSEWIC. 2011. Designatable Units for Caribou (Rangifer tarandus) in Canada. Committee on the Status of Endangered Wildlife in Canada, Ottawa, ON. 88 pp. Available at http://www.cosewic.gc.ca/D37AB818-5F3B-44DC-9D56-EE22C63F4512/COSEWIC_Caribou_DU_Report_23Dec2011.pdfCOSEWIC. 2016. COSEWIC Status Report on Barren-ground caribou Rangifer tarandus in Canada. Draft - 2-month interim status report. Committee on the Status of Endangered Wildlife in Canada.Nagy, J.A., D. L. Johnson, N. C. Larter, M. W. Campbell, A. E. Derocher, A. Kelly, M. Dumond, D. Allaire, and B. Croft. 2011. Subpopulation structure of caribou (Rangifer tarandusL.) in arctic and subarctic Canada. Ecological Applications 21:2334–2348. http://dx.doi.org/10.1890/10-1410.1Poole, K. 2011. Methodology and sources for preparing seasonal shape files for caribou herds for CARMA. Unpublished document, Aurora Wildlife Research. 11 pp.",
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"description": "Locations of globally rare plants and lichens(ranked G1 or G2 by Natureserve) in the Northwest Territories that are also ranked May Be at Risk by the NWT General Status Ranking program. Includes Drummond bluebell, Raup's willow, Banks Island alkali grass, and arctic orangebush lichen. Note that hairy braya (Braya pilosa) and Nahanni Aster (Symphotrichum nahanniense) are also ranked G1 but are not shown because they have been assessed as a Species at Risk in NWT and/or Canada and therefore have their own range maps. Developed for ENR/EC joint Species at Risk in the NWT booklet. Locations updated November 22, 2013 by Joanna Wilson. Shapefile modified to remove Nahanni Aster on February 19, 2015. One possible site for Mackenzie hairgrass (species identification requires verification) was added by Joanna Wilson on December 1, 2015. Four additional sites for Drummond Bluebell were added in November 2019.In January 2024, Mackenzie Hairgrass was removed from the dataset and points for Arctic orangebush lichen were addedby Joanna Wilson and Bonnie Fournier (GNWT ECC).DRUMMOND BLUEBELL (Mertensia drummondii) locations from: 1. Porsild AE, and Cody WJ . 1980 . Vascular Plants of Continental Northwest Territories, Canada. 2. McJannet CL, Argus GW and Cody WJ . 1995 . Rare Vascular Plants in the Northwest Territories. 3. Cody et al. 1992. CFN. 106(2):87-99. 4. Cody et al. 2003. CFN 117(3):448-465. 5. http://aknhp.uaa.alaska.edu/rareguide/md1.html. Four additional Drummond bluebell records in Nunavut were provided by Bruce Bennett in October 2019: Bluenose Lke area, Cape Young DEW Line site, Camp Necessity Clifton Point, and Wollaston Peninsula.RAUP'S WILLOW (Salix raupii) locations from: 1. McJannet CL, Argus GW and Cody WJ . 1995 . Rare Vascular Plants in the Northwest Territories. 2. Argus 1986. CFN 100(3):386-388. 3. Argus 1974. Can J Bot 52:1303-1304. BANKS ISLAND ALKALI GRASS (Puccinellia banksiensis) records were drawn from ENR's NWT Virtual Herbarium in November 2013. ARCTIC ORANGEBUSH LICHEN (Seirophora aurantiaca) locations from: Sokoloff, P. & McMullin, T. 2020. Seirophora aurantiaca. The IUCN Red List of Threatened Species 2020: e.T175710010A175710692. https://dx.doi.org/10.2305/IUCN.UK.2020-3.RLTS.T175710010A175710692.en.https://www.iucnredlist.org. Downloaded on 10 November 2023. Seirophora aurantiaca is endemic to the Inuvialuit Settlement Region in the Northwest Territories, Canada, where it occurs on Banks Island, Melville Island, Victoria Island, and the Cape Parry area of the Northwest Territories mainland. This species is only known from 12 sites in the Canadian Arctic, documented by 18 herbarium collections. (Sokoloff and McMullin 2020)MACKENZIE HAIRGRASS was removed from this dataset in January 2024. A single Canadian Museum of Nature specimen 310905, collected at Old Fort Reliance on Great Slave Lake in 1927, was labeled as Deschampsia mackenzieana . However, Jeff Saarela at Canadian Museum of Nature had studied this specimen in 2018 and compared its morphology to Mackenzie hairgrass from Saskatchewan; he determined the specimen fits D. cespitosa subsp. cespitosa better. (J. Saarela, pers. comm). Therefore the best available information at this point suggests the NWT specimen is likely not Mackenzie hairgrass.",
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"description": "Please refer to the following website for additional information including the reports for each Level II Ecoregion (i.e. Taiga Plains, Taiga Shield, Cordillera, Southern Arctic, Northern Arctic (coming soon)).http://www.enr.gov.nt.ca/_live/pages/wpPages/Ecosystem_Classification.aspxATTRIBUTESOne set of variables aggregated under climate data was derived from Level III ecoregion descriptions; the remainder of the attribute list information was derived from Level IV ecoregion descriptions. For non-climate information, the entire ecoregion description and all photos and captions were reviewed to develop the best abstraction of each attribute. Attribute abstraction was completed by the D.Downing (2013) who prepared all of the Level IV ecoregion descriptions and is familiar with the landscapes. 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The information presented for Level III ecoregions in the above-listed reports was largely derived from models produced at the national ecodistrict level by Agriculture and Agri-Food Canada, which are generalizations derived from very sparsely distributed long-term weather station data.Attribute values included under this general category are typically expressed as numeric ranges, reflecting the degree of inherent variability (geographic and year-to-year) within Level III ecoregions. Attributes include the following:CLIMATE ATTRIBUTESATTRIBUTEDESCRIPTIONMATMean annual temperature, expressed as degrees CelsiusMAPMean annual precipitation, expressed as mm of total rain and snowM_JANMean temperature in the coldest month, typically January (or February where designated by a value followed by (Feb)), expressed as degrees CelsiusM_JULMean temperature in the warmest month (July), expressed as degrees CelsiusSRAnnAverage annual solar radiation, expressed as megajoules per square metre per daySRJunSolar radiation in June (longest days), expressed as megajoules per square metre per daySRDecSolar radiation in December (shortest days), expressed as megajoules per square metre per day Surficial geologyThree dataset attributes (Surfgeo1, Surfgeo2, Surfgeo3) are included under the general category of surficial geology. The attribute values and their definitions are provided below and in the worksheet titled “surficial geology” in the Excel® workbook titled “NWT_ecoregion_searchable_attributes.xls”.Most of the attribute values and their definitions are as presented by Agriculture and Agri-foods Canada (website: http://sis.agr.gc.ca/cansis/nsdb/ecostrat/1999report/data_tables.html. Attribute value definitions for colluvium were augmented by adding a reference to highly weathered tills, mostly related to areas in the Northern and Southern Arctic considered by some researchers to be recently unglaciated. A variable referencing weathered rock (RW) was also added as it is a significant component in some areas. Changes are shown in italics and coloured red in the table below. The first and second variables (Surfgeo1, Surfgeo2) may be codominant or the second subordinate to the first. In most cases, Surfgeo3was a minor component of the ecoregion but some ecoregions were highly complex and all three variables were judged to be of equal importance. The written descriptions should be consulted in cases where analysis requires a more specific assessment of proportion.SURFICIAL GEOLOGYAttribute ValueDESCRIPTIONIGlaciers: Ice and minor morainal debris.AAlluvial Deposits: stratified silt, sand, clay, and gravel; floodplain, delta, and fan deposits; in places overlies and includes glaciofluvial deposits.mMMarine Mud: Fluid silty clay and clayey silt: deposited as quiet water sediments.sMMarine Sand: Sand and locally gravel; deposited as sheet sands, lags, and beaches.mLLacustrine Mud: Fluid silty clay and clayey silt: deposited as quiet water sediments.sLLacustrine Sand: Sand and locally gravel; deposited as sheet sands, lags, and beaches.EEolian Deposits: sand and minor silt: dunes, blowouts, and undulating plains: In most places overlies deltaic sediments, coarse lacustrine sediments, or glaciofluvial deposits.OOrganic deposits: peat, muck and minor inorganic sediments; large bog, fen, and swamp areas where organic fill masks underlying surficial materials; generally >2 m thickbCColluvial Blocks: Blocks, and rubble with sand and silt; derived from crystalline bedrock, medium grade metamorphic substrate, and cemented sandstone.rCColluvial Rubble:Rubble and silt; derived from carbonate and consolidated fine classic sedimentary rock substrate. Includes highly weathered tillsfCColluvial Fines: Silt, clay, and fine sand: derived from substrate weakly consolidated shale and siltstone substrate. Includes highly weathered tillssCColluvial Sand: Sand and gravel; derived from poorly lithified sandstone and conglomerate substrate. Includes highly weathered tills.L:fMLacustrine Fine Grained: Fine grained silt and clay, locally containing stones: deposited as quiet water sediments.L:cLLacustrine Coarse Grained: sand, silt, and gravel: deposited as deltas, sheet sands and lag deposits.M:fMMarine Fine Grained: Dominantly silt and clay, locally containing stones; deposited as a quiet water sediment.M:cMMarine Coarse Grained: Sand and gravel: deposited as sheet sands, deltas, and extensive flights of beaches.M:MvLag: Sand, gravel, and pockets of fine sediment; thin to discontinued sediment veneer and residual lag developed during marine submergence; includes areas of washed till and rock.GpGlaciofluvial Plain: Sand and gravel: deposited as outwash sheets, valley trains, and terrace deposits.GxGlaciofluvial Complex: Sand and gravel and locally diamicton: undifferentiated ice contact stratified drift, and outwash; locally includes till and rock.TbTill Blanket: Thick and continuous till.TvTill Veneer: Thin and discontinuous till: may include areas of rock outcrop.TvbTill veneer and blanket complex:VQuarternary Volcanics: consolidated lava, breccia and tephra: dominantly basaltic and andesitic in composition; includes flows, volcanic piles and cinder conesRaAlpine Complexes: rock, colluvium, and till: rock and Quarternary deposits complex in an area, characterized by alpine and glacial landforms.RUndivided: rock with minor Quaternary deposits. Includes unweathered and weathered rock.RWWeathered bedrock – usually shales and sandstones.Surface materialsTwo attribute fields (Surfmat1, Surfmat2) are included under the general category of surface materials. This category is very general and reflects surficial geology categories. Refer to the table below.SURFACE MATERIALSAttribute ValueDESCRIPTIONICICE and SNOWGlacial ice and permanent snowORORGANIC SOILContains > 30% organic matter as measured by weightROROCKRock undifferentiatedSOMINERAL SOILPredominantly mineral particles: contains < 30% organic matter as measured by weightURURBANUrban areas. Note that only a few major urban area polygons are included on SLC source maps, therefore, do not use for tabulating total urban coverage. Not used in NWT attribute list. LandformOne attribute field (Landform) is included. This is the only attribute field that exceeds 8 alphanumeric characters (it is 10 characters in length). The landform reflects the predominant landscape feature within the ecoregion and is taken directly from the three-part name for the ecoregion, which reflects its geographic location, its major landform, and its affinity with climate(e.g., KellerPlainLSEcoregion). The attribute values used for this project are more comprehensive than the options provided under the CanSIS classification system. landformAttribute ValueDESCRIPTIONCoastlandsnarrow linear areas parallel to the seacoast that are influenced by both oceanic and terrestrial processes and that include a variety of landforms.Cst PlainCoastal Plain: see plain.Deltaan alluvial sediment deposit at the mouth of a river, often somewhat triangular in form, frequently flooded and nearly level. High water tables, abandoned channels and oxbow lakes and periodic nutrient-rich sediment deposition are important ecological factors.Foothillslow hills at the base of mountains. For purposes of delineation in the Northwest Territories, an arbitrary elevation range of 200-800 m ASL is used and is reasonably well correlated with breaks in slope between the valleys and the foothills and between the foothills and the mountains. Incised stream channels, uneven topography that creates variable microenvironments, and steeper slopes than the surrounding lowlands and plains are typical. Hillsprominences rising generally no more than about 500 m above the surrounding areas. They may have gentle to abrupt slopes; slope steepness and aspect along with bedrock substrates near or at the mineral soil surface can strongly influence vegetation development. Drainage patterns are well developed relative to those of the surrounding lower-lying areas. In the Northern Arctic, this term and highlands are used to name ecoregions with variable topography that are markedly higher than the surrounding terrain and that often have distinctive bedrock and surficial geology features. Islandsland masses completely surrounded by water.Lowlandan area of low relief at the lower ranges of regional elevation; it receives water inputs from adjacent higher terrain. It is typically imperfectly- to poorly-drained, has a higher proportion of wetlands than other landscape types and is nearly level. Drainage patterns are poorly defined.Mountainsareas that display large differences in relief, usually over 600 m. Bedrock exposures, steep slopes and deeply incised parallel river channels are characteristic, climatic zonation occurs as a result of elevation changes, and microenvironments are highly variable. A range is a row or chain of mountains separated from other mountain ranges by passes or rivers; a ridge is an elongate crest or a linear series of crests. Peninsulaa land mass surrounded on three sides by waterPlainan extensive area that is typically level, gently sloping or hummocky and that can occur at low to high elevations, the latter often as part of high elevation plateaus. It is referred to as a coastal plainwhen it borders the coastline and is influenced by marine and terrestrial factors.Plateauan extensive level to gently sloping upland area at a higher elevation than its surroundings, often underlain by horizontally-oriented bedrock strata. They can be deeply eroded by streams.Rangesee mountains.LANDFORM(cont.)Attribute ValueDESCRIPTIONSlopesareas with variable local relief underlain by a regionally inclined surfaceUplandgeneral term for an area that is higher than the surrounding area, sometimes several hundred metres higher, that are not plateaus or hills. Uplands usually have undulating to hummocky terrain, a higher proportion of moderately well- to well-drained sites than lowlands or plains and a lower proportion of wetlands. Drainage patterns tend to be dendritic (resembling tree roots).Valleyany low-lying area bounded by plateaus, mountains, foothills or plains and traversed by a river.Surface formTwo attribute fields (Surffrm1, Surffrm2) are provided. The table below summarizes 31 classes provided by Agriculture and Agri-foods Canada at the website address referenced above under Surficial Geology. As for surficial geology, the first and second attributes reflect the dominant surface forms referenced in the written descriptions. A one-to-one correspondence between the ecoregion description and the supplied list of surface forms was not always possible; these decisions were most challenging in mountainous areas, where the value for “ridged”was often used to capture the concept of rugged bedrock-controlled terrain in addition to the provided definition that mostly references glacial features. Wetland forms were sometimes included as the second component (Surffrm2) even if they did not cover a majority of the ecoregion because of their significance or uniqueness. For example, one wetland form (snowpatch fens) was added to the list of attributes provided by Agriculture and Agri-foods Canada and referenced in two High Arctic-oceanic ecoregions. The changes are shown in italics and coloured red in the table below. Many of the wetland forms (B04 and most of the entries below that value) were not present in the NWT, but are included here for completeness. SURFACE FORMAttribute ValueDESCRIPTIONDDissectedA dissected (or gullied) pattern providing external drainage for an area.HHummocky (or irregular)A very complex sequence of slopes extending from somewhat rounded concavities (or swales) of various sizes to irregular conical knolls (or knobs) and short discontinuous ridges; there is a general lack of concordance between knolls and swales. Slopes are generally 4-70%. Examples are hummocky moraines and hummocky fluvioglacial landforms.IInclinedA sloping, unidirectional surface with a generally constant slope unbroken by marked irregularity or gullies; a weakly developed dissected pattern provides external drainage for the local area. Slopes are 2-70%; the form of inclined slopes is not related to the initial mode of origin of the underlying material.KKnoll and kettleA chaotic sequence of knolls and kettles (or sloughs), which occupies 15-20% of an area and has no external drainage. Slopes are generally >3%. Examples are morainal plains and hill lands.LLevelA flat or very gently sloping, unidirectional surface with a generally constant slope unbroken by marked elevations and depressions. Slopes are generally <2%. Examples are floodplains and lake plains.MRollingA very regular sequence of moderate slopes extending from rounded and, in some places, confined concave depressions to broad, rounded convexities producing a wavelike pattern of moderate relief. Slope gradients are generally >5% but may be less. This surface form is usually controlled by the underlying bedrock.RRidgedA long, narrow elevation of the surface, usually sharp crested with steep sides; ridges may be parallel, subparallel, or intersecting. Examples are eskers, crevasse fillings, washboard moraines and some drumlins. Includes pronounced terrain associated with rugged bedrock-controlled hill and mountain systems.SSteepErosional slopes of greater than 70% (35°), present on both consolidated and unconsolidated materials. The form of a steep erosional slope on unconsolidated materials is not related to the initial mode of origin of the underlying material. An example is an escarpment.TTerracedScarp face and the horizontal or gently inclined surface (or tread) above it. An example is an alluvial terrace.SURFACE FORM(cont.)Attribute ValueDESCRIPTIONUUndulatingA very regular sequence of gentle slopes that extends from rounded and, in some places, confined concavities to broad, rounded convexities producing a wavelike pattern of low local relief. Slope length is generally less than 0.8 km and the dominant gradient of slopes is usually 2-5%. The terrain lacks an external drainage pattern. Examples are some ground moraines and lacustrine material of varying textures.B04Domed bogA large bog (diameter usually >500 m) with a convex surface rising several metres above the surrounding terrain. The centre usually drains in all directions; small crescentic pools commonly form around the highest point; a concentric pattern is formed if the highest point is in the centre, while an eccentric pattern is formed if the highest point is off-centre. Peat development is usually >3 m.B05Polygonal peat plateau bogA perennially frozen bog rising approximately 1 m above the surrounding fen. The surface is relatively flat, scored by a polygonal pattern of trenches that developed over ice wedges. The permafrost and ice wedges developed in peat originally deposited in a nonpermafrost environment.B07Peat plateau bogA bog composed of perennially frozen peat rising abruptly about 1 m from the surrounding unfrozen fen. The surface is relatively flat and even, and commonly covers large areas. The peat was originally deposited in a nonpermafrost environment and is associated in many places with collapse scar bogs or fens.B09Atlantic plateau bogA bog with a flat to undulating surface raised above the surrounding terrain. The bog edges commonly slope steeply downwards to the mineral soil terrain. Large pools scattered on the bog reach depths of 2-4 m.B13Basin bogA bog situated in a basin with essentially closed drainage which receives water from precipitation and runoff from the immediate surroundings. The surface of the bog is flat with peat generally deepest at the centre.B14Flat bogA bog having a flat, featureless surface and occurring in broad, poorly defined depressions. The depth of peat is generally uniform.B15String bogA pattern of narrow (2-3 m wide), low (<1 m high) ridges oriented at right angles to the direction of drainage; wet depressions or pools occur between the ridges. The water and peat are very low in nutrients because the water has been derived from other ombrotrophic wetlands. The peat thickness is >1 m.B16Blanket bogA bog consisting of extensive peat deposits that occur more or less uniformly over gently sloping hills and valleys. The peat thickness is usually < 2 m.B18Slope bogA bog occurring in areas of high rainfall on appreciably sloping land surfaces. The bog is fed by rainwater and by water draining from other nutrient-poor peatlands. The peat may exceed 1 m in thickness.B19Veneer bogA bog occurring on gently sloping terrain underlain by generally discontinuous permafrost. Although drainage is predominantly below the surface, overland flow occurs in poorly defined drainways during peak runoff. Peat thickness is usually <1.5 m.B20Lowland polygon bogA bog with flat-topped or convex peat surfaces (often referred to as 'high-centre polygons') separated by trenches over ice wedges that form a polygonal pattern when viewed from above. The peat was deposited in a permafrost environment as shown by internal structures.F01Northern ribbed fenA fen with parallel, low peat ridges ('strings') alternating with wet hollows or shallow pools, oriented across the major slope at right angles to water movement. The depth of peat is >1 m.F07Shore fenA fen with an anchored surface mat that forms the shore of a pond or lake. The rooting zone is affected by the water of the lake at both normal and flood levels.F11Slope fenA fen occurring mainly on slow-draining, nutrient-enriched seepage slopes. Pools are usually absent, but wet seepage tracks may occur. Peat thickness is usually <2 m.F13Horizontal fenA fen with a gently sloping, featureless surface. This fen occupies broad, often ill-defined depressions and may interconnect with other fens. Peat accumulation is generally uniform.F14Snowpatch fenFens that form below melting snowbanks in the Arctic or Alpine. Peat accumulation is very limited and thicknesses are usually less than 20 cm.SURFACE FORM(cont.)Attribute ValueDESCRIPTIONS01Stream swampA swamp occurring along the banks of permanent or semipermanent streams. The high water table is maintained by the level of water in the stream. The swamp is seasonally inundated with subsequent sediment deposition.S04Basin swampA swamp developed in a topographically defined basin where water derived locally may be augmented by drainage from other parts of the watershed. Accumulation of well-decomposed peat is shallow (< 0.5 m) at the edge but may reach 2 m at the centre.M06Stream marshA marsh occupying shorelines, bars, stream beds, or islands in continuously flowing watercourses. The marsh is subject to prolonged annual flooding and is commonly covered by thick layers of sediments.M11Shallow basin marshA marsh occurring in a uniformly shallow marsh depression or swale, having a gradual gradient from the edge to the deepest portion; the marsh edge may be poorly defined. Water levels fluctuate rapidly.M14Shore marshA marsh occupying the contact zone between high and low water marks bordering semipermanent or permanent lakes. The marsh, usually found along protected shorelines, behind barrier beaches in lagoons, on islands, or in embayments, is subject to flooding by a rise in lake levels, wind waves, or surface runoff.Permafrost formTwo attribute fields (Prmfrst1, Prmfrst2) capture the primary and secondary permafrost forms in each ecoregion. The documents were reviewed for all permafrost types and a list was compiled that is more comprehensive than that provided by Agriculture and Agri-foods Canada. The attribute values and definitions are provided below.Permafrost FORMAttribute ValueDESCRIPTIONEHEarth hummocks -A hummock having a core of silty and clayey mineral soil which may show evidence of cryoturbation. Earth hummocks are a type of non-sorted circle (see also patterned ground and turf hummock) commonly found in the zone of continuous permafrost. They develop in materials of a high silt and clay content and/or of high ice content.FRFrost heaved/shattered rock -rock that has been pushed to the surface or broken by freeze-thaw cyclesGIGround ice - Layers of segregated ice or ice-organic mixes or ice-mineral soil mixes that do not melt.GLGlacier - A mass of ice that develops as a result of snow and ice accumulation over a long period of time and that moves laterally from the centre of accumulation.HCHigh centre polygons (with low-centre polygons as subdominant) - see low-centre polygonIWIce wedge polygonsLCLow centre polygons (with high-centre polygons as subdominant): A feature of continuous permafrost in wet terrain (e.g., drained lakes). Ice wedges develop in cracks, pushing up soil ridges adjacent to the wedges and creating dams that trap water inside the resulting polygons. The features appear as high-rimmed ridges surrounding wet shallow central pools of water. Over hundreds or thousands of years, peat deposits build up and eventually create a dome-shaped surface; these features are referred to as high-centre polygons.NCNon-sorted circles, stripes - a non-sorted circle is a patterned ground form that is equidimensional in several directions, with a dominantly circular outline which lacks a well-defined border of stones and has a centre composed of a mixture of textures from fine through coarse mixed with gravels, cobbles and boulders. A network of non-sorted circles that meet is referred to as a non-sorted net. Non-sorted stripes form under the same influence of frost action as non-sorted circles, but because they form on slopes, they flow and elongate perpendicular to contour.PAPalsa -A peaty permafrost mound possessing a core of alternating layers of segregated ice and peat or mineral soil material. Palsas are typically between 1 and 7 metres in height and a few metres to 100 metres in diameter. PGPatterned ground - A general term for circles, polygons, stripes, nets and steps created by frost action.Permafrost FORM (cont.)Attribute ValueDESCRIPTIONPIPingo - A mound of earth-covered ice found in the Arctic, Subarctic and Antarctica that can reach up to 70 metres in height and up to 2 kilometres in diameter. The term originated as the Inuit word for a small hill. They are most common in Canada along the coastal plains of the Tuktoyaktuk Peninsula. They form in the former basins of drained lakes. PPPeat plateau - A bog composed of perennially frozen peat, rising abruptly about 1 m from the surrounding unfrozen fen. The surface is relatively flat and even and often covers very large areas. The peat was originally deposited in a non-permafrost environment and is often associated with collapse scars or fens.PPPPolygonal peat plateau - A perennially frozen bog, rising about 1 m above the surrounding fen. The surface is relatively flat, scored by a polygonal pattern of trenches that developed over ice wedges. The permafrost and ice wedges developed in peat originally deposited in a non-permafrost environment. Polygonal peat plateaus are commonly found near the boundary between the zones of discontinuous and continuous permafrost.RRunnels - A pattern of alternating flow channels and interchannel uplands perpendicular to contour. In permafrost-affected areas, light and dark-striped patterns on hill slopes are runnels; the light stripes are usually sparsely treed, lichen covered interchannel areas with permafrost close to the surface and the dark stripes are shallow drainage channels vegetated by dwarf birch, willow and other shrubs with a thicker active layer.RGRock glaciers - ice-cored, often lobe-shaped landforms covered by soil and rock.RTRetrogressive thaw (or flow) slides - A slide that consists of a headwall containing ice or ice-rich sediment, which retreats in a retrogressive fashion through melting, and a debris flow formed by the mixture of thawed sediment and ice that has slid down the failure surface to the base of the slope and frequently into a thermokarst depression, lake, or pond. SCSorted circles, stripes - a sorted circle is permafrost-related patterned ground that forms under extremely cold conditions when frost action pushes parent materials to the surface; the centre of the circle is occupied by sparsely vegetated finer-textured materials, with a ring of gravels, cobbles and boulders around the outside. A network of sorted circles that meet is referred to as a sorted net. Sorted stripes form under the same influence of frost action as sorted circles, but because they form on slopes, they flow and elongate perpendicular to contour.SOSolifluction - the downslope movement of water-saturated soil in a viscous or plastic state over an impermeable layer, often permafrost. The presence of an impermeable permafrost layer prevents the internal drainage of the soil, forcing the soil to flow down the slope. During warm periods the surface layer thaws and slides across the frozen layer, slowly moving downslope due to frost heave.TKThermokarst -The process by which characteristic landforms result from the thawing of ice-rich permafrost or the melting of massive ice. TUTurf hummocks - a permafrost-related northern Arctic landform generally less than 1m across and 50cm in height that is often associated with aeolian materials (sands, silts). It is more or less circular and is initially forced upward by frost action. It receives solar energy from all sides during the 24-hour days of the brief growing season, promoting plant growth which traps windborne silt and sand particles, resulting in the gradual accretion of materials and growth of the hummock.VBVeneer bog - A bog occurring on gently sloping terrain underlain by generally discontinuous permafrost. Although drainage is predominantly below the surface, overland flow occurs in poorly defined drainage ways during peak runoff. Peat thickness is generally less than 1.5 metres.Soil developmentThree dataset attribute fields (Soil1, Soil2, Soil3) capture soil information from the written ecoregion descriptions. A subset of the soil table provided by Agriculture and Agri-food Canada was used, as many of the soil types in the full table do not occur in the NWT. As for surficial geology, the first and second variables (Soil1, Soil2) may be codominant or the second subordinate to the first. In some cases, a value for Soil1and Soil3was provided, with no value for Soil2. This indicates that Soil1is dominant, and Soil3is only present over minor areas within the ecoregion. The written descriptions should be consulted in cases where analysis requires a more specific assessment of proportion.Attribute ValueDESCRIPTIONFGray LuvisolHGHumic GleysolHRHumic RegosolIBrunisol Gray LuvisolLGLuvic GleysolMEutric BrunisolOOrganic CryosolPDystric BrunisolRRegosolSStatic CryosolTTurbic CryosolUGleysolXFibrisolYMesisolZHumisol#Water, Rock or IceLand CoverThree attribute fields (Landcov1, Landcov2, Landcov3) capture vegetation information from the written descriptions. Because vegetation patterns are in part how ecoregions are described, there is considerable variation from one Level II ecoregion to another, and the 17 classes provided by Agriculture and Agri-food Canada were considered inadequate to represent significant vegetation trends. A review of all five documents consequently resulted in the establishment of specific attribute values for major vegetation types within the Taiga Plains, Taiga Shield, and Cordillera. The Southern Arctic and Northern Arctic classifications are based mainly upon the Circumpolar Arctic Vegetation Map community types (CAVM Team 2003) and are more consistently defined and described, but also had some unique values. Attribute values specific to each area are presented in tables below; to identify the types uniquely, they are prefaced with TP:(Taiga Plains), TS:(Taiga Shield), CO:(Cordillera), SA:(Southern Arctic) and NA:(Northern Arctic).Landcov1and Landcov2were generally used to capture the major vegetation types; if there was a significant vegetation type that did not occur over large areas but was considered diagnostic (e.g. alpine fir types in the southern mountains), it was included as Landcov3even if there were other vegetation communities that covered larger areas. The written descriptions should be consulted in cases where analysis requires a more specific assessment of proportion.LAND COVER (VEGETATION): TAIGA PLAINSAttribute ValueDESCRIPTIONTP:F1Fen: SedgeTP:F2Fen: shrub-sedgeTP:F3Fen or bog: Black spruce - shrub - mossTP:F4Fen: Black spruce - larchTP:FC1Forest: Jackpine - shrub - lichenTP:FC2Forest: Jackpine - tall shrub - lichenTP:FC3Forest: Lodgepole and jackpine X lodgepole hybridTP:FC4Forest: White spruce - jack pineTP:FC5Forest: Spruce - lichenTP:FC6Forest: spruce-shrub (includes both black and white spruce)TP:FC7Forest: white spruceTP:FC8Forest: black spruce - shrub - lichenTP:FD1Forest: Deciduous (aspen, balsam poplar, paper birch)TP:FD2Forest: Paper birchTP:FM1Forest: Mixedwood jackpine - aspenTP:FM2Forest: Spruce - paper birch (includes white and black spruce)TP:FM3Forest: Mixedwood aspen - paper birch - spruce - jackpineTP:M1Marsh: bulrush - sedgeTP:M2Meadow: herb-grass-shrubTP:S1Shrubland: dwarf birch - dryland sedge - lichenTP:S2Shrubland: dwarf birch - Labrador tea - peat moss TP:S3Shrubland: dwarf birch - paper birch (post-fire regeneration). May include white spruce and black spruce regeneration, and may be one or both deciduous species.TP:S4Shrubland: dwarf birch - willowTP:S5Shrubland: lichen - Labrador tea - dwarf birch (polygonal peat plateaus)TP:S6Shrubland: willow-alderTP:S6Shrubland: willowTP:S7Shrubland: dryTP:TSTundra: ShrubTP:W1Woodland: White spruce - shrub-lichen woodlandTP:W2Woodland: Black spruce - low shrub- lichenLAND COVER (VEGETATION): TAIGA SHELDAttribute ValueDESCRIPTIONTS:F1Fen: sedge (including a minor component of shrubs)TS:F2Fen: shrub (including a minor component of sedges)TS:FC1Forest: Jackpine (may include minor paper birch, white spruce, black spruce)TS:FC2Forest: Spruce - moss (undifferentiated white and black spruce)TS:FC3Forest: Spruce - shrub - lichen (undifferentiated white and black spruce)TS:FD1Forest: DeciduousTS:FM1Forest: Mixedwood (any combination of aspen, balsam poplar, and birch with white spruce, black spruce, and jackpine)TS:FM2Forest: Mixedwood white spruce - paper birchTS:FM3Forest: Mixedwood jackpine - paper birchTS:NFLLichen on rockTS:S1Shrubland: Dwarf birch - paper birch (post-fire regeneration)TS:S2Shrubland: lichen - Labrador tea - dwarf birch (peat plateaus)TS:T1Tundra: lichen - grass heathTS:T2Tundra: sedgeTS:T3Tundra: shrub heathTS:T4Tundra: lichen-sedge-shrub complexTS:W1Woodland: White spruce - shrub - lichen TS:W2Woodland: Spruce - shrub - lichenTS:W3Woodland: Black spruce - lichenLAND COVER (VEGETATION): CORDILLERAAttribute ValueDESCRIPTIONCO:F1Fen: Black spruce - (larch) - shrubCO:F2Fen: Sedge - cottongrass tussockCO:F3Fen: Shrub - sedgeCO:FC1Forest: JackpineCO:FC2Forest: lodgepole pineCO:FC3Forest: Spruce - shrubCO:FC4Forest: White spruceCO:FC5Forest: White spruce - alpine firCO:FD1Forest: Deciduous (aspen, balsam poplar, paper birch)CO:FM1Forest: Mixedwood (white spruce, aspen, jackpine, lodgepole pine)CO:FM2Forest: Mixedwood (spruce, balsam poplar, birch, tall shrub)CO:NFL1Lichen - RockCO:Rrock barrensCO:S1Shrubland: dwarf birch - willow - paper birch (post-fire regeneration)CO:S2Shrublands: Tall (alder, willow, birch)CO:S3Shrublands: DryCO:S4Shrublands: dwarf birch - willowCO:T1Tundra: herb (rich, diverse, Pacific-Cordilleran species)CO:T2Tundra: LichenLAND COVER (VEGETATION): CORDILLERA (cont.)Attribute ValueDESCRIPTIONCO:T3Tundra: Sedge - cottongrassCO:T4Tundra: sedge-shrubCO:T5Tundra: shrubCO:W1Woodland: alpine firCO:W2Woodland: black spruce - larch - mossCO:W3Woodland: black spruce - shrub - moss - lichenCO:W4Woodland: White spruce - alpine firCO:W5Woodland: White (black) spruce - shrub - lichenLAND COVER (VEGETATION): SOUTHERN ARCTIC*Attribute ValueDESCRIPTIONSA:B1Cryptogam –herb barren SA:B2Cryptogam –barren complex (bedrock) SA:CMCoastal MarshSA:G2Graminoid –prostrate dwarf-shrub –forb tundraSA:G3Nontussock sedge –dwarf-shrub –moss tundraSA:G4Tussock-sedge –dwarf-shrub –moss tundra SA:P1Prostrate dwarf-shrub –herb tundraSA:S1Erect dwarf-shrub tundra SA:S2Low-shrub tundraSA:T1Tundra: lichen - grass heath (continuation of Taiga Shield)SA:T2Tundra: sedge (continuation of Taiga Shield)SA:T3Tundra: shrub heath (continuation of Taiga Shield)SA:TGTree groves / sparse tree growthSA:W2Sedge –moss –dwarf-shrub wetland SA:W3Sedge –moss –low-shrub wetland LAND COVER (VEGETATION): NORTHERN ARCTIC*Attribute ValueDESCRIPTIONNA:B1Cryptogam –herb barren NA:B2Cryptogam –barren complex (bedrock) NA:B3b-cNon-carbonate mountain complex NA:B4bCarbonate mountain complex NA:G1Rush –grass–forb –cryptogam tundra NA:G2Graminoid –prostrate dwarf-shrub –forb tundra NA:G3Nontussock sedge –moss –dwarf-shrub tundraNA:P1Prostrate dwarf-shrub –herb tundra NA:P2Prostrate/hemiprostrate dwarf-shrub tundraNA:S2Low-shrub tundra NA:W1Sedge –grass –moss wetland * the code values following SA: and NA: are those defined by the Circumpolar Arctic Vegetation Map (CAVM Team 2003), except for SA:T1, SA:T2, SA:T3 (continuation of Taiga Shield vegetation to the north) and SA:CM (coastal marshes of Mackenzie Delta, too small to address in the circumpolarmap survey.REFERENCES CITEDCAVM Team. 2003. Circumpolar Arctic Vegetation Map. (1:7,500,000 scale), Conservation of Arctic Flora and Fauna (CAFF) Map No. 1. U.S. Fish and Wildlife Service, Anchorage, Alaska.",
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"description": "Please refer to the following website for additional information including the reports for each Level II Ecoregion (i.e. Taiga Plains, Taiga Shield, Cordillera, Southern Arctic, Northern Arctic (coming soon)).http://www.enr.gov.nt.ca/_live/pages/wpPages/Ecosystem_Classification.aspxATTRIBUTESOne set of variables aggregated under climate data was derived from Level III ecoregion descriptions; the remainder of the attribute list information was derived from Level IV ecoregion descriptions. For non-climate information, the entire ecoregion description and all photos and captions were reviewed to develop the best abstraction of each attribute. Attribute abstraction was completed by the D.Downing (2013) who prepared all of the Level IV ecoregion descriptions and is familiar with the landscapes. There is a certain amount of repetition between some of the categories e.g. glaciers may be represented under surficial geology and surface materials as ice and under permafrost as glaciers. Climate dataClimate information is derived from Level III ecoregion descriptions, specifically the descriptive section titled “Climate”,and assigned to all Level IV ecoregions nested within a Level III ecoregion. For example, the Taiga Plains Low Subarctic Level III ecoregion includes 14 Level IV ecoregions. All 14 of these ecoregions are assigned the same value or value range for mean annual temperature, precipitation and the other climatic variables listed below. Climate attributes are assigned in this manner because there is insufficient climatic information to describe individual climatic parameters for Level IV ecoregions. The information presented for Level III ecoregions in the above-listed reports was largely derived from models produced at the national ecodistrict level by Agriculture and Agri-Food Canada, which are generalizations derived from very sparsely distributed long-term weather station data.Attribute values included under this general category are typically expressed as numeric ranges, reflecting the degree of inherent variability (geographic and year-to-year) within Level III ecoregions. Attributes include the following:CLIMATE ATTRIBUTESATTRIBUTEDESCRIPTIONMATMean annual temperature, expressed as degrees CelsiusMAPMean annual precipitation, expressed as mm of total rain and snowM_JANMean temperature in the coldest month, typically January (or February where designated by a value followed by (Feb)), expressed as degrees CelsiusM_JULMean temperature in the warmest month (July), expressed as degrees CelsiusSRAnnAverage annual solar radiation, expressed as megajoules per square metre per daySRJunSolar radiation in June (longest days), expressed as megajoules per square metre per daySRDecSolar radiation in December (shortest days), expressed as megajoules per square metre per day Surficial geologyThree dataset attributes (Surfgeo1, Surfgeo2, Surfgeo3) are included under the general category of surficial geology. The attribute values and their definitions are provided below and in the worksheet titled “surficial geology” in the Excel® workbook titled “NWT_ecoregion_searchable_attributes.xls”.Most of the attribute values and their definitions are as presented by Agriculture and Agri-foods Canada (website: http://sis.agr.gc.ca/cansis/nsdb/ecostrat/1999report/data_tables.html. Attribute value definitions for colluvium were augmented by adding a reference to highly weathered tills, mostly related to areas in the Northern and Southern Arctic considered by some researchers to be recently unglaciated. A variable referencing weathered rock (RW) was also added as it is a significant component in some areas. Changes are shown in italics and coloured red in the table below. The first and second variables (Surfgeo1, Surfgeo2) may be codominant or the second subordinate to the first. In most cases, Surfgeo3was a minor component of the ecoregion but some ecoregions were highly complex and all three variables were judged to be of equal importance. The written descriptions should be consulted in cases where analysis requires a more specific assessment of proportion.SURFICIAL GEOLOGYAttribute ValueDESCRIPTIONIGlaciers: Ice and minor morainal debris.AAlluvial Deposits: stratified silt, sand, clay, and gravel; floodplain, delta, and fan deposits; in places overlies and includes glaciofluvial deposits.mMMarine Mud: Fluid silty clay and clayey silt: deposited as quiet water sediments.sMMarine Sand: Sand and locally gravel; deposited as sheet sands, lags, and beaches.mLLacustrine Mud: Fluid silty clay and clayey silt: deposited as quiet water sediments.sLLacustrine Sand: Sand and locally gravel; deposited as sheet sands, lags, and beaches.EEolian Deposits: sand and minor silt: dunes, blowouts, and undulating plains: In most places overlies deltaic sediments, coarse lacustrine sediments, or glaciofluvial deposits.OOrganic deposits: peat, muck and minor inorganic sediments; large bog, fen, and swamp areas where organic fill masks underlying surficial materials; generally >2 m thickbCColluvial Blocks: Blocks, and rubble with sand and silt; derived from crystalline bedrock, medium grade metamorphic substrate, and cemented sandstone.rCColluvial Rubble:Rubble and silt; derived from carbonate and consolidated fine classic sedimentary rock substrate. Includes highly weathered tillsfCColluvial Fines: Silt, clay, and fine sand: derived from substrate weakly consolidated shale and siltstone substrate. Includes highly weathered tillssCColluvial Sand: Sand and gravel; derived from poorly lithified sandstone and conglomerate substrate. Includes highly weathered tills.L:fMLacustrine Fine Grained: Fine grained silt and clay, locally containing stones: deposited as quiet water sediments.L:cLLacustrine Coarse Grained: sand, silt, and gravel: deposited as deltas, sheet sands and lag deposits.M:fMMarine Fine Grained: Dominantly silt and clay, locally containing stones; deposited as a quiet water sediment.M:cMMarine Coarse Grained: Sand and gravel: deposited as sheet sands, deltas, and extensive flights of beaches.M:MvLag: Sand, gravel, and pockets of fine sediment; thin to discontinued sediment veneer and residual lag developed during marine submergence; includes areas of washed till and rock.GpGlaciofluvial Plain: Sand and gravel: deposited as outwash sheets, valley trains, and terrace deposits.GxGlaciofluvial Complex: Sand and gravel and locally diamicton: undifferentiated ice contact stratified drift, and outwash; locally includes till and rock.TbTill Blanket: Thick and continuous till.TvTill Veneer: Thin and discontinuous till: may include areas of rock outcrop.TvbTill veneer and blanket complex:VQuarternary Volcanics: consolidated lava, breccia and tephra: dominantly basaltic and andesitic in composition; includes flows, volcanic piles and cinder conesRaAlpine Complexes: rock, colluvium, and till: rock and Quarternary deposits complex in an area, characterized by alpine and glacial landforms.RUndivided: rock with minor Quaternary deposits. Includes unweathered and weathered rock.RWWeathered bedrock – usually shales and sandstones.Surface materialsTwo attribute fields (Surfmat1, Surfmat2) are included under the general category of surface materials. This category is very general and reflects surficial geology categories. Refer to the table below.SURFACE MATERIALSAttribute ValueDESCRIPTIONICICE and SNOWGlacial ice and permanent snowORORGANIC SOILContains > 30% organic matter as measured by weightROROCKRock undifferentiatedSOMINERAL SOILPredominantly mineral particles: contains < 30% organic matter as measured by weightURURBANUrban areas. Note that only a few major urban area polygons are included on SLC source maps, therefore, do not use for tabulating total urban coverage. Not used in NWT attribute list. LandformOne attribute field (Landform) is included. This is the only attribute field that exceeds 8 alphanumeric characters (it is 10 characters in length). The landform reflects the predominant landscape feature within the ecoregion and is taken directly from the three-part name for the ecoregion, which reflects its geographic location, its major landform, and its affinity with climate(e.g., KellerPlainLSEcoregion). The attribute values used for this project are more comprehensive than the options provided under the CanSIS classification system. landformAttribute ValueDESCRIPTIONCoastlandsnarrow linear areas parallel to the seacoast that are influenced by both oceanic and terrestrial processes and that include a variety of landforms.Cst PlainCoastal Plain: see plain.Deltaan alluvial sediment deposit at the mouth of a river, often somewhat triangular in form, frequently flooded and nearly level. High water tables, abandoned channels and oxbow lakes and periodic nutrient-rich sediment deposition are important ecological factors.Foothillslow hills at the base of mountains. For purposes of delineation in the Northwest Territories, an arbitrary elevation range of 200-800 m ASL is used and is reasonably well correlated with breaks in slope between the valleys and the foothills and between the foothills and the mountains. Incised stream channels, uneven topography that creates variable microenvironments, and steeper slopes than the surrounding lowlands and plains are typical. Hillsprominences rising generally no more than about 500 m above the surrounding areas. They may have gentle to abrupt slopes; slope steepness and aspect along with bedrock substrates near or at the mineral soil surface can strongly influence vegetation development. Drainage patterns are well developed relative to those of the surrounding lower-lying areas. In the Northern Arctic, this term and highlands are used to name ecoregions with variable topography that are markedly higher than the surrounding terrain and that often have distinctive bedrock and surficial geology features. Islandsland masses completely surrounded by water.Lowlandan area of low relief at the lower ranges of regional elevation; it receives water inputs from adjacent higher terrain. It is typically imperfectly- to poorly-drained, has a higher proportion of wetlands than other landscape types and is nearly level. Drainage patterns are poorly defined.Mountainsareas that display large differences in relief, usually over 600 m. Bedrock exposures, steep slopes and deeply incised parallel river channels are characteristic, climatic zonation occurs as a result of elevation changes, and microenvironments are highly variable. A range is a row or chain of mountains separated from other mountain ranges by passes or rivers; a ridge is an elongate crest or a linear series of crests. Peninsulaa land mass surrounded on three sides by waterPlainan extensive area that is typically level, gently sloping or hummocky and that can occur at low to high elevations, the latter often as part of high elevation plateaus. It is referred to as a coastal plainwhen it borders the coastline and is influenced by marine and terrestrial factors.Plateauan extensive level to gently sloping upland area at a higher elevation than its surroundings, often underlain by horizontally-oriented bedrock strata. They can be deeply eroded by streams.Rangesee mountains.LANDFORM(cont.)Attribute ValueDESCRIPTIONSlopesareas with variable local relief underlain by a regionally inclined surfaceUplandgeneral term for an area that is higher than the surrounding area, sometimes several hundred metres higher, that are not plateaus or hills. Uplands usually have undulating to hummocky terrain, a higher proportion of moderately well- to well-drained sites than lowlands or plains and a lower proportion of wetlands. Drainage patterns tend to be dendritic (resembling tree roots).Valleyany low-lying area bounded by plateaus, mountains, foothills or plains and traversed by a river.Surface formTwo attribute fields (Surffrm1, Surffrm2) are provided. The table below summarizes 31 classes provided by Agriculture and Agri-foods Canada at the website address referenced above under Surficial Geology. As for surficial geology, the first and second attributes reflect the dominant surface forms referenced in the written descriptions. A one-to-one correspondence between the ecoregion description and the supplied list of surface forms was not always possible; these decisions were most challenging in mountainous areas, where the value for “ridged”was often used to capture the concept of rugged bedrock-controlled terrain in addition to the provided definition that mostly references glacial features. Wetland forms were sometimes included as the second component (Surffrm2) even if they did not cover a majority of the ecoregion because of their significance or uniqueness. For example, one wetland form (snowpatch fens) was added to the list of attributes provided by Agriculture and Agri-foods Canada and referenced in two High Arctic-oceanic ecoregions. The changes are shown in italics and coloured red in the table below. Many of the wetland forms (B04 and most of the entries below that value) were not present in the NWT, but are included here for completeness. SURFACE FORMAttribute ValueDESCRIPTIONDDissectedA dissected (or gullied) pattern providing external drainage for an area.HHummocky (or irregular)A very complex sequence of slopes extending from somewhat rounded concavities (or swales) of various sizes to irregular conical knolls (or knobs) and short discontinuous ridges; there is a general lack of concordance between knolls and swales. Slopes are generally 4-70%. Examples are hummocky moraines and hummocky fluvioglacial landforms.IInclinedA sloping, unidirectional surface with a generally constant slope unbroken by marked irregularity or gullies; a weakly developed dissected pattern provides external drainage for the local area. Slopes are 2-70%; the form of inclined slopes is not related to the initial mode of origin of the underlying material.KKnoll and kettleA chaotic sequence of knolls and kettles (or sloughs), which occupies 15-20% of an area and has no external drainage. Slopes are generally >3%. Examples are morainal plains and hill lands.LLevelA flat or very gently sloping, unidirectional surface with a generally constant slope unbroken by marked elevations and depressions. Slopes are generally <2%. Examples are floodplains and lake plains.MRollingA very regular sequence of moderate slopes extending from rounded and, in some places, confined concave depressions to broad, rounded convexities producing a wavelike pattern of moderate relief. Slope gradients are generally >5% but may be less. This surface form is usually controlled by the underlying bedrock.RRidgedA long, narrow elevation of the surface, usually sharp crested with steep sides; ridges may be parallel, subparallel, or intersecting. Examples are eskers, crevasse fillings, washboard moraines and some drumlins. Includes pronounced terrain associated with rugged bedrock-controlled hill and mountain systems.SSteepErosional slopes of greater than 70% (35°), present on both consolidated and unconsolidated materials. The form of a steep erosional slope on unconsolidated materials is not related to the initial mode of origin of the underlying material. An example is an escarpment.TTerracedScarp face and the horizontal or gently inclined surface (or tread) above it. An example is an alluvial terrace.SURFACE FORM(cont.)Attribute ValueDESCRIPTIONUUndulatingA very regular sequence of gentle slopes that extends from rounded and, in some places, confined concavities to broad, rounded convexities producing a wavelike pattern of low local relief. Slope length is generally less than 0.8 km and the dominant gradient of slopes is usually 2-5%. The terrain lacks an external drainage pattern. Examples are some ground moraines and lacustrine material of varying textures.B04Domed bogA large bog (diameter usually >500 m) with a convex surface rising several metres above the surrounding terrain. The centre usually drains in all directions; small crescentic pools commonly form around the highest point; a concentric pattern is formed if the highest point is in the centre, while an eccentric pattern is formed if the highest point is off-centre. Peat development is usually >3 m.B05Polygonal peat plateau bogA perennially frozen bog rising approximately 1 m above the surrounding fen. The surface is relatively flat, scored by a polygonal pattern of trenches that developed over ice wedges. The permafrost and ice wedges developed in peat originally deposited in a nonpermafrost environment.B07Peat plateau bogA bog composed of perennially frozen peat rising abruptly about 1 m from the surrounding unfrozen fen. The surface is relatively flat and even, and commonly covers large areas. The peat was originally deposited in a nonpermafrost environment and is associated in many places with collapse scar bogs or fens.B09Atlantic plateau bogA bog with a flat to undulating surface raised above the surrounding terrain. The bog edges commonly slope steeply downwards to the mineral soil terrain. Large pools scattered on the bog reach depths of 2-4 m.B13Basin bogA bog situated in a basin with essentially closed drainage which receives water from precipitation and runoff from the immediate surroundings. The surface of the bog is flat with peat generally deepest at the centre.B14Flat bogA bog having a flat, featureless surface and occurring in broad, poorly defined depressions. The depth of peat is generally uniform.B15String bogA pattern of narrow (2-3 m wide), low (<1 m high) ridges oriented at right angles to the direction of drainage; wet depressions or pools occur between the ridges. The water and peat are very low in nutrients because the water has been derived from other ombrotrophic wetlands. The peat thickness is >1 m.B16Blanket bogA bog consisting of extensive peat deposits that occur more or less uniformly over gently sloping hills and valleys. The peat thickness is usually < 2 m.B18Slope bogA bog occurring in areas of high rainfall on appreciably sloping land surfaces. The bog is fed by rainwater and by water draining from other nutrient-poor peatlands. The peat may exceed 1 m in thickness.B19Veneer bogA bog occurring on gently sloping terrain underlain by generally discontinuous permafrost. Although drainage is predominantly below the surface, overland flow occurs in poorly defined drainways during peak runoff. Peat thickness is usually <1.5 m.B20Lowland polygon bogA bog with flat-topped or convex peat surfaces (often referred to as 'high-centre polygons') separated by trenches over ice wedges that form a polygonal pattern when viewed from above. The peat was deposited in a permafrost environment as shown by internal structures.F01Northern ribbed fenA fen with parallel, low peat ridges ('strings') alternating with wet hollows or shallow pools, oriented across the major slope at right angles to water movement. The depth of peat is >1 m.F07Shore fenA fen with an anchored surface mat that forms the shore of a pond or lake. The rooting zone is affected by the water of the lake at both normal and flood levels.F11Slope fenA fen occurring mainly on slow-draining, nutrient-enriched seepage slopes. Pools are usually absent, but wet seepage tracks may occur. Peat thickness is usually <2 m.F13Horizontal fenA fen with a gently sloping, featureless surface. This fen occupies broad, often ill-defined depressions and may interconnect with other fens. Peat accumulation is generally uniform.F14Snowpatch fenFens that form below melting snowbanks in the Arctic or Alpine. Peat accumulation is very limited and thicknesses are usually less than 20 cm.SURFACE FORM(cont.)Attribute ValueDESCRIPTIONS01Stream swampA swamp occurring along the banks of permanent or semipermanent streams. The high water table is maintained by the level of water in the stream. The swamp is seasonally inundated with subsequent sediment deposition.S04Basin swampA swamp developed in a topographically defined basin where water derived locally may be augmented by drainage from other parts of the watershed. Accumulation of well-decomposed peat is shallow (< 0.5 m) at the edge but may reach 2 m at the centre.M06Stream marshA marsh occupying shorelines, bars, stream beds, or islands in continuously flowing watercourses. The marsh is subject to prolonged annual flooding and is commonly covered by thick layers of sediments.M11Shallow basin marshA marsh occurring in a uniformly shallow marsh depression or swale, having a gradual gradient from the edge to the deepest portion; the marsh edge may be poorly defined. Water levels fluctuate rapidly.M14Shore marshA marsh occupying the contact zone between high and low water marks bordering semipermanent or permanent lakes. The marsh, usually found along protected shorelines, behind barrier beaches in lagoons, on islands, or in embayments, is subject to flooding by a rise in lake levels, wind waves, or surface runoff.Permafrost formTwo attribute fields (Prmfrst1, Prmfrst2) capture the primary and secondary permafrost forms in each ecoregion. The documents were reviewed for all permafrost types and a list was compiled that is more comprehensive than that provided by Agriculture and Agri-foods Canada. The attribute values and definitions are provided below.Permafrost FORMAttribute ValueDESCRIPTIONEHEarth hummocks -A hummock having a core of silty and clayey mineral soil which may show evidence of cryoturbation. Earth hummocks are a type of non-sorted circle (see also patterned ground and turf hummock) commonly found in the zone of continuous permafrost. They develop in materials of a high silt and clay content and/or of high ice content.FRFrost heaved/shattered rock -rock that has been pushed to the surface or broken by freeze-thaw cyclesGIGround ice - Layers of segregated ice or ice-organic mixes or ice-mineral soil mixes that do not melt.GLGlacier - A mass of ice that develops as a result of snow and ice accumulation over a long period of time and that moves laterally from the centre of accumulation.HCHigh centre polygons (with low-centre polygons as subdominant) - see low-centre polygonIWIce wedge polygonsLCLow centre polygons (with high-centre polygons as subdominant): A feature of continuous permafrost in wet terrain (e.g., drained lakes). Ice wedges develop in cracks, pushing up soil ridges adjacent to the wedges and creating dams that trap water inside the resulting polygons. The features appear as high-rimmed ridges surrounding wet shallow central pools of water. Over hundreds or thousands of years, peat deposits build up and eventually create a dome-shaped surface; these features are referred to as high-centre polygons.NCNon-sorted circles, stripes - a non-sorted circle is a patterned ground form that is equidimensional in several directions, with a dominantly circular outline which lacks a well-defined border of stones and has a centre composed of a mixture of textures from fine through coarse mixed with gravels, cobbles and boulders. A network of non-sorted circles that meet is referred to as a non-sorted net. Non-sorted stripes form under the same influence of frost action as non-sorted circles, but because they form on slopes, they flow and elongate perpendicular to contour.PAPalsa -A peaty permafrost mound possessing a core of alternating layers of segregated ice and peat or mineral soil material. Palsas are typically between 1 and 7 metres in height and a few metres to 100 metres in diameter. PGPatterned ground - A general term for circles, polygons, stripes, nets and steps created by frost action.Permafrost FORM (cont.)Attribute ValueDESCRIPTIONPIPingo - A mound of earth-covered ice found in the Arctic, Subarctic and Antarctica that can reach up to 70 metres in height and up to 2 kilometres in diameter. The term originated as the Inuit word for a small hill. They are most common in Canada along the coastal plains of the Tuktoyaktuk Peninsula. They form in the former basins of drained lakes. PPPeat plateau - A bog composed of perennially frozen peat, rising abruptly about 1 m from the surrounding unfrozen fen. The surface is relatively flat and even and often covers very large areas. The peat was originally deposited in a non-permafrost environment and is often associated with collapse scars or fens.PPPPolygonal peat plateau - A perennially frozen bog, rising about 1 m above the surrounding fen. The surface is relatively flat, scored by a polygonal pattern of trenches that developed over ice wedges. The permafrost and ice wedges developed in peat originally deposited in a non-permafrost environment. Polygonal peat plateaus are commonly found near the boundary between the zones of discontinuous and continuous permafrost.RRunnels - A pattern of alternating flow channels and interchannel uplands perpendicular to contour. In permafrost-affected areas, light and dark-striped patterns on hill slopes are runnels; the light stripes are usually sparsely treed, lichen covered interchannel areas with permafrost close to the surface and the dark stripes are shallow drainage channels vegetated by dwarf birch, willow and other shrubs with a thicker active layer.RGRock glaciers - ice-cored, often lobe-shaped landforms covered by soil and rock.RTRetrogressive thaw (or flow) slides - A slide that consists of a headwall containing ice or ice-rich sediment, which retreats in a retrogressive fashion through melting, and a debris flow formed by the mixture of thawed sediment and ice that has slid down the failure surface to the base of the slope and frequently into a thermokarst depression, lake, or pond. SCSorted circles, stripes - a sorted circle is permafrost-related patterned ground that forms under extremely cold conditions when frost action pushes parent materials to the surface; the centre of the circle is occupied by sparsely vegetated finer-textured materials, with a ring of gravels, cobbles and boulders around the outside. A network of sorted circles that meet is referred to as a sorted net. Sorted stripes form under the same influence of frost action as sorted circles, but because they form on slopes, they flow and elongate perpendicular to contour.SOSolifluction - the downslope movement of water-saturated soil in a viscous or plastic state over an impermeable layer, often permafrost. The presence of an impermeable permafrost layer prevents the internal drainage of the soil, forcing the soil to flow down the slope. During warm periods the surface layer thaws and slides across the frozen layer, slowly moving downslope due to frost heave.TKThermokarst -The process by which characteristic landforms result from the thawing of ice-rich permafrost or the melting of massive ice. TUTurf hummocks - a permafrost-related northern Arctic landform generally less than 1m across and 50cm in height that is often associated with aeolian materials (sands, silts). It is more or less circular and is initially forced upward by frost action. It receives solar energy from all sides during the 24-hour days of the brief growing season, promoting plant growth which traps windborne silt and sand particles, resulting in the gradual accretion of materials and growth of the hummock.VBVeneer bog - A bog occurring on gently sloping terrain underlain by generally discontinuous permafrost. Although drainage is predominantly below the surface, overland flow occurs in poorly defined drainage ways during peak runoff. Peat thickness is generally less than 1.5 metres.Soil developmentThree dataset attribute fields (Soil1, Soil2, Soil3) capture soil information from the written ecoregion descriptions. A subset of the soil table provided by Agriculture and Agri-food Canada was used, as many of the soil types in the full table do not occur in the NWT. As for surficial geology, the first and second variables (Soil1, Soil2) may be codominant or the second subordinate to the first. In some cases, a value for Soil1and Soil3was provided, with no value for Soil2. This indicates that Soil1is dominant, and Soil3is only present over minor areas within the ecoregion. The written descriptions should be consulted in cases where analysis requires a more specific assessment of proportion.Attribute ValueDESCRIPTIONFGray LuvisolHGHumic GleysolHRHumic RegosolIBrunisol Gray LuvisolLGLuvic GleysolMEutric BrunisolOOrganic CryosolPDystric BrunisolRRegosolSStatic CryosolTTurbic CryosolUGleysolXFibrisolYMesisolZHumisol#Water, Rock or IceLand CoverThree attribute fields (Landcov1, Landcov2, Landcov3) capture vegetation information from the written descriptions. Because vegetation patterns are in part how ecoregions are described, there is considerable variation from one Level II ecoregion to another, and the 17 classes provided by Agriculture and Agri-food Canada were considered inadequate to represent significant vegetation trends. A review of all five documents consequently resulted in the establishment of specific attribute values for major vegetation types within the Taiga Plains, Taiga Shield, and Cordillera. The Southern Arctic and Northern Arctic classifications are based mainly upon the Circumpolar Arctic Vegetation Map community types (CAVM Team 2003) and are more consistently defined and described, but also had some unique values. Attribute values specific to each area are presented in tables below; to identify the types uniquely, they are prefaced with TP:(Taiga Plains), TS:(Taiga Shield), CO:(Cordillera), SA:(Southern Arctic) and NA:(Northern Arctic).Landcov1and Landcov2were generally used to capture the major vegetation types; if there was a significant vegetation type that did not occur over large areas but was considered diagnostic (e.g. alpine fir types in the southern mountains), it was included as Landcov3even if there were other vegetation communities that covered larger areas. The written descriptions should be consulted in cases where analysis requires a more specific assessment of proportion.LAND COVER (VEGETATION): TAIGA PLAINSAttribute ValueDESCRIPTIONTP:F1Fen: SedgeTP:F2Fen: shrub-sedgeTP:F3Fen or bog: Black spruce - shrub - mossTP:F4Fen: Black spruce - larchTP:FC1Forest: Jackpine - shrub - lichenTP:FC2Forest: Jackpine - tall shrub - lichenTP:FC3Forest: Lodgepole and jackpine X lodgepole hybridTP:FC4Forest: White spruce - jack pineTP:FC5Forest: Spruce - lichenTP:FC6Forest: spruce-shrub (includes both black and white spruce)TP:FC7Forest: white spruceTP:FC8Forest: black spruce - shrub - lichenTP:FD1Forest: Deciduous (aspen, balsam poplar, paper birch)TP:FD2Forest: Paper birchTP:FM1Forest: Mixedwood jackpine - aspenTP:FM2Forest: Spruce - paper birch (includes white and black spruce)TP:FM3Forest: Mixedwood aspen - paper birch - spruce - jackpineTP:M1Marsh: bulrush - sedgeTP:M2Meadow: herb-grass-shrubTP:S1Shrubland: dwarf birch - dryland sedge - lichenTP:S2Shrubland: dwarf birch - Labrador tea - peat moss TP:S3Shrubland: dwarf birch - paper birch (post-fire regeneration). May include white spruce and black spruce regeneration, and may be one or both deciduous species.TP:S4Shrubland: dwarf birch - willowTP:S5Shrubland: lichen - Labrador tea - dwarf birch (polygonal peat plateaus)TP:S6Shrubland: willow-alderTP:S6Shrubland: willowTP:S7Shrubland: dryTP:TSTundra: ShrubTP:W1Woodland: White spruce - shrub-lichen woodlandTP:W2Woodland: Black spruce - low shrub- lichenLAND COVER (VEGETATION): TAIGA SHELDAttribute ValueDESCRIPTIONTS:F1Fen: sedge (including a minor component of shrubs)TS:F2Fen: shrub (including a minor component of sedges)TS:FC1Forest: Jackpine (may include minor paper birch, white spruce, black spruce)TS:FC2Forest: Spruce - moss (undifferentiated white and black spruce)TS:FC3Forest: Spruce - shrub - lichen (undifferentiated white and black spruce)TS:FD1Forest: DeciduousTS:FM1Forest: Mixedwood (any combination of aspen, balsam poplar, and birch with white spruce, black spruce, and jackpine)TS:FM2Forest: Mixedwood white spruce - paper birchTS:FM3Forest: Mixedwood jackpine - paper birchTS:NFLLichen on rockTS:S1Shrubland: Dwarf birch - paper birch (post-fire regeneration)TS:S2Shrubland: lichen - Labrador tea - dwarf birch (peat plateaus)TS:T1Tundra: lichen - grass heathTS:T2Tundra: sedgeTS:T3Tundra: shrub heathTS:T4Tundra: lichen-sedge-shrub complexTS:W1Woodland: White spruce - shrub - lichen TS:W2Woodland: Spruce - shrub - lichenTS:W3Woodland: Black spruce - lichenLAND COVER (VEGETATION): CORDILLERAAttribute ValueDESCRIPTIONCO:F1Fen: Black spruce - (larch) - shrubCO:F2Fen: Sedge - cottongrass tussockCO:F3Fen: Shrub - sedgeCO:FC1Forest: JackpineCO:FC2Forest: lodgepole pineCO:FC3Forest: Spruce - shrubCO:FC4Forest: White spruceCO:FC5Forest: White spruce - alpine firCO:FD1Forest: Deciduous (aspen, balsam poplar, paper birch)CO:FM1Forest: Mixedwood (white spruce, aspen, jackpine, lodgepole pine)CO:FM2Forest: Mixedwood (spruce, balsam poplar, birch, tall shrub)CO:NFL1Lichen - RockCO:Rrock barrensCO:S1Shrubland: dwarf birch - willow - paper birch (post-fire regeneration)CO:S2Shrublands: Tall (alder, willow, birch)CO:S3Shrublands: DryCO:S4Shrublands: dwarf birch - willowCO:T1Tundra: herb (rich, diverse, Pacific-Cordilleran species)CO:T2Tundra: LichenLAND COVER (VEGETATION): CORDILLERA (cont.)Attribute ValueDESCRIPTIONCO:T3Tundra: Sedge - cottongrassCO:T4Tundra: sedge-shrubCO:T5Tundra: shrubCO:W1Woodland: alpine firCO:W2Woodland: black spruce - larch - mossCO:W3Woodland: black spruce - shrub - moss - lichenCO:W4Woodland: White spruce - alpine firCO:W5Woodland: White (black) spruce - shrub - lichenLAND COVER (VEGETATION): SOUTHERN ARCTIC*Attribute ValueDESCRIPTIONSA:B1Cryptogam –herb barren SA:B2Cryptogam –barren complex (bedrock) SA:CMCoastal MarshSA:G2Graminoid –prostrate dwarf-shrub –forb tundraSA:G3Nontussock sedge –dwarf-shrub –moss tundraSA:G4Tussock-sedge –dwarf-shrub –moss tundra SA:P1Prostrate dwarf-shrub –herb tundraSA:S1Erect dwarf-shrub tundra SA:S2Low-shrub tundraSA:T1Tundra: lichen - grass heath (continuation of Taiga Shield)SA:T2Tundra: sedge (continuation of Taiga Shield)SA:T3Tundra: shrub heath (continuation of Taiga Shield)SA:TGTree groves / sparse tree growthSA:W2Sedge –moss –dwarf-shrub wetland SA:W3Sedge –moss –low-shrub wetland LAND COVER (VEGETATION): NORTHERN ARCTIC*Attribute ValueDESCRIPTIONNA:B1Cryptogam –herb barren NA:B2Cryptogam –barren complex (bedrock) NA:B3b-cNon-carbonate mountain complex NA:B4bCarbonate mountain complex NA:G1Rush –grass–forb –cryptogam tundra NA:G2Graminoid –prostrate dwarf-shrub –forb tundra NA:G3Nontussock sedge –moss –dwarf-shrub tundraNA:P1Prostrate dwarf-shrub –herb tundra NA:P2Prostrate/hemiprostrate dwarf-shrub tundraNA:S2Low-shrub tundra NA:W1Sedge –grass –moss wetland * the code values following SA: and NA: are those defined by the Circumpolar Arctic Vegetation Map (CAVM Team 2003), except for SA:T1, SA:T2, SA:T3 (continuation of Taiga Shield vegetation to the north) and SA:CM (coastal marshes of Mackenzie Delta, too small to address in the circumpolarmap survey.REFERENCES CITEDCAVM Team. 2003. Circumpolar Arctic Vegetation Map. (1:7,500,000 scale), Conservation of Arctic Flora and Fauna (CAFF) Map No. 1. U.S. Fish and Wildlife Service, Anchorage, Alaska.",
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"name": "Level IV EcoRegions",
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"description": "Please refer to the following website for additional information including the reports for each Level II Ecoregion (i.e. Taiga Plains, Taiga Shield, Cordillera, Southern Arctic, Northern Arctic (coming soon)).http://www.enr.gov.nt.ca/_live/pages/wpPages/Ecosystem_Classification.aspxATTRIBUTESOne set of variables aggregated under climate data was derived from Level III ecoregion descriptions; the remainder of the attribute list information was derived from Level IV ecoregion descriptions. For non-climate information, the entire ecoregion description and all photos and captions were reviewed to develop the best abstraction of each attribute. Attribute abstraction was completed by the D.Downing (2013) who prepared all of the Level IV ecoregion descriptions and is familiar with the landscapes. There is a certain amount of repetition between some of the categories e.g. glaciers may be represented under surficial geology and surface materials as ice and under permafrost as glaciers. Climate dataClimate information is derived from Level III ecoregion descriptions, specifically the descriptive section titled “Climate”,and assigned to all Level IV ecoregions nested within a Level III ecoregion. For example, the Taiga Plains Low Subarctic Level III ecoregion includes 14 Level IV ecoregions. All 14 of these ecoregions are assigned the same value or value range for mean annual temperature, precipitation and the other climatic variables listed below. Climate attributes are assigned in this manner because there is insufficient climatic information to describe individual climatic parameters for Level IV ecoregions. The information presented for Level III ecoregions in the above-listed reports was largely derived from models produced at the national ecodistrict level by Agriculture and Agri-Food Canada, which are generalizations derived from very sparsely distributed long-term weather station data.Attribute values included under this general category are typically expressed as numeric ranges, reflecting the degree of inherent variability (geographic and year-to-year) within Level III ecoregions. Attributes include the following:CLIMATE ATTRIBUTESATTRIBUTEDESCRIPTIONMATMean annual temperature, expressed as degrees CelsiusMAPMean annual precipitation, expressed as mm of total rain and snowM_JANMean temperature in the coldest month, typically January (or February where designated by a value followed by (Feb)), expressed as degrees CelsiusM_JULMean temperature in the warmest month (July), expressed as degrees CelsiusSRAnnAverage annual solar radiation, expressed as megajoules per square metre per daySRJunSolar radiation in June (longest days), expressed as megajoules per square metre per daySRDecSolar radiation in December (shortest days), expressed as megajoules per square metre per day Surficial geologyThree dataset attributes (Surfgeo1, Surfgeo2, Surfgeo3) are included under the general category of surficial geology. The attribute values and their definitions are provided below and in the worksheet titled “surficial geology” in the Excel® workbook titled “NWT_ecoregion_searchable_attributes.xls”.Most of the attribute values and their definitions are as presented by Agriculture and Agri-foods Canada (website: http://sis.agr.gc.ca/cansis/nsdb/ecostrat/1999report/data_tables.html. Attribute value definitions for colluvium were augmented by adding a reference to highly weathered tills, mostly related to areas in the Northern and Southern Arctic considered by some researchers to be recently unglaciated. A variable referencing weathered rock (RW) was also added as it is a significant component in some areas. Changes are shown in italics and coloured red in the table below. The first and second variables (Surfgeo1, Surfgeo2) may be codominant or the second subordinate to the first. In most cases, Surfgeo3was a minor component of the ecoregion but some ecoregions were highly complex and all three variables were judged to be of equal importance. The written descriptions should be consulted in cases where analysis requires a more specific assessment of proportion.SURFICIAL GEOLOGYAttribute ValueDESCRIPTIONIGlaciers: Ice and minor morainal debris.AAlluvial Deposits: stratified silt, sand, clay, and gravel; floodplain, delta, and fan deposits; in places overlies and includes glaciofluvial deposits.mMMarine Mud: Fluid silty clay and clayey silt: deposited as quiet water sediments.sMMarine Sand: Sand and locally gravel; deposited as sheet sands, lags, and beaches.mLLacustrine Mud: Fluid silty clay and clayey silt: deposited as quiet water sediments.sLLacustrine Sand: Sand and locally gravel; deposited as sheet sands, lags, and beaches.EEolian Deposits: sand and minor silt: dunes, blowouts, and undulating plains: In most places overlies deltaic sediments, coarse lacustrine sediments, or glaciofluvial deposits.OOrganic deposits: peat, muck and minor inorganic sediments; large bog, fen, and swamp areas where organic fill masks underlying surficial materials; generally >2 m thickbCColluvial Blocks: Blocks, and rubble with sand and silt; derived from crystalline bedrock, medium grade metamorphic substrate, and cemented sandstone.rCColluvial Rubble:Rubble and silt; derived from carbonate and consolidated fine classic sedimentary rock substrate. Includes highly weathered tillsfCColluvial Fines: Silt, clay, and fine sand: derived from substrate weakly consolidated shale and siltstone substrate. Includes highly weathered tillssCColluvial Sand: Sand and gravel; derived from poorly lithified sandstone and conglomerate substrate. Includes highly weathered tills.L:fMLacustrine Fine Grained: Fine grained silt and clay, locally containing stones: deposited as quiet water sediments.L:cLLacustrine Coarse Grained: sand, silt, and gravel: deposited as deltas, sheet sands and lag deposits.M:fMMarine Fine Grained: Dominantly silt and clay, locally containing stones; deposited as a quiet water sediment.M:cMMarine Coarse Grained: Sand and gravel: deposited as sheet sands, deltas, and extensive flights of beaches.M:MvLag: Sand, gravel, and pockets of fine sediment; thin to discontinued sediment veneer and residual lag developed during marine submergence; includes areas of washed till and rock.GpGlaciofluvial Plain: Sand and gravel: deposited as outwash sheets, valley trains, and terrace deposits.GxGlaciofluvial Complex: Sand and gravel and locally diamicton: undifferentiated ice contact stratified drift, and outwash; locally includes till and rock.TbTill Blanket: Thick and continuous till.TvTill Veneer: Thin and discontinuous till: may include areas of rock outcrop.TvbTill veneer and blanket complex:VQuarternary Volcanics: consolidated lava, breccia and tephra: dominantly basaltic and andesitic in composition; includes flows, volcanic piles and cinder conesRaAlpine Complexes: rock, colluvium, and till: rock and Quarternary deposits complex in an area, characterized by alpine and glacial landforms.RUndivided: rock with minor Quaternary deposits. Includes unweathered and weathered rock.RWWeathered bedrock – usually shales and sandstones.Surface materialsTwo attribute fields (Surfmat1, Surfmat2) are included under the general category of surface materials. This category is very general and reflects surficial geology categories. Refer to the table below.SURFACE MATERIALSAttribute ValueDESCRIPTIONICICE and SNOWGlacial ice and permanent snowORORGANIC SOILContains > 30% organic matter as measured by weightROROCKRock undifferentiatedSOMINERAL SOILPredominantly mineral particles: contains < 30% organic matter as measured by weightURURBANUrban areas. Note that only a few major urban area polygons are included on SLC source maps, therefore, do not use for tabulating total urban coverage. Not used in NWT attribute list. LandformOne attribute field (Landform) is included. This is the only attribute field that exceeds 8 alphanumeric characters (it is 10 characters in length). The landform reflects the predominant landscape feature within the ecoregion and is taken directly from the three-part name for the ecoregion, which reflects its geographic location, its major landform, and its affinity with climate(e.g., KellerPlainLSEcoregion). The attribute values used for this project are more comprehensive than the options provided under the CanSIS classification system. landformAttribute ValueDESCRIPTIONCoastlandsnarrow linear areas parallel to the seacoast that are influenced by both oceanic and terrestrial processes and that include a variety of landforms.Cst PlainCoastal Plain: see plain.Deltaan alluvial sediment deposit at the mouth of a river, often somewhat triangular in form, frequently flooded and nearly level. High water tables, abandoned channels and oxbow lakes and periodic nutrient-rich sediment deposition are important ecological factors.Foothillslow hills at the base of mountains. For purposes of delineation in the Northwest Territories, an arbitrary elevation range of 200-800 m ASL is used and is reasonably well correlated with breaks in slope between the valleys and the foothills and between the foothills and the mountains. Incised stream channels, uneven topography that creates variable microenvironments, and steeper slopes than the surrounding lowlands and plains are typical. Hillsprominences rising generally no more than about 500 m above the surrounding areas. They may have gentle to abrupt slopes; slope steepness and aspect along with bedrock substrates near or at the mineral soil surface can strongly influence vegetation development. Drainage patterns are well developed relative to those of the surrounding lower-lying areas. In the Northern Arctic, this term and highlands are used to name ecoregions with variable topography that are markedly higher than the surrounding terrain and that often have distinctive bedrock and surficial geology features. Islandsland masses completely surrounded by water.Lowlandan area of low relief at the lower ranges of regional elevation; it receives water inputs from adjacent higher terrain. It is typically imperfectly- to poorly-drained, has a higher proportion of wetlands than other landscape types and is nearly level. Drainage patterns are poorly defined.Mountainsareas that display large differences in relief, usually over 600 m. Bedrock exposures, steep slopes and deeply incised parallel river channels are characteristic, climatic zonation occurs as a result of elevation changes, and microenvironments are highly variable. A range is a row or chain of mountains separated from other mountain ranges by passes or rivers; a ridge is an elongate crest or a linear series of crests. Peninsulaa land mass surrounded on three sides by waterPlainan extensive area that is typically level, gently sloping or hummocky and that can occur at low to high elevations, the latter often as part of high elevation plateaus. It is referred to as a coastal plainwhen it borders the coastline and is influenced by marine and terrestrial factors.Plateauan extensive level to gently sloping upland area at a higher elevation than its surroundings, often underlain by horizontally-oriented bedrock strata. They can be deeply eroded by streams.Rangesee mountains.LANDFORM(cont.)Attribute ValueDESCRIPTIONSlopesareas with variable local relief underlain by a regionally inclined surfaceUplandgeneral term for an area that is higher than the surrounding area, sometimes several hundred metres higher, that are not plateaus or hills. Uplands usually have undulating to hummocky terrain, a higher proportion of moderately well- to well-drained sites than lowlands or plains and a lower proportion of wetlands. Drainage patterns tend to be dendritic (resembling tree roots).Valleyany low-lying area bounded by plateaus, mountains, foothills or plains and traversed by a river.Surface formTwo attribute fields (Surffrm1, Surffrm2) are provided. The table below summarizes 31 classes provided by Agriculture and Agri-foods Canada at the website address referenced above under Surficial Geology. As for surficial geology, the first and second attributes reflect the dominant surface forms referenced in the written descriptions. A one-to-one correspondence between the ecoregion description and the supplied list of surface forms was not always possible; these decisions were most challenging in mountainous areas, where the value for “ridged”was often used to capture the concept of rugged bedrock-controlled terrain in addition to the provided definition that mostly references glacial features. Wetland forms were sometimes included as the second component (Surffrm2) even if they did not cover a majority of the ecoregion because of their significance or uniqueness. For example, one wetland form (snowpatch fens) was added to the list of attributes provided by Agriculture and Agri-foods Canada and referenced in two High Arctic-oceanic ecoregions. The changes are shown in italics and coloured red in the table below. Many of the wetland forms (B04 and most of the entries below that value) were not present in the NWT, but are included here for completeness. SURFACE FORMAttribute ValueDESCRIPTIONDDissectedA dissected (or gullied) pattern providing external drainage for an area.HHummocky (or irregular)A very complex sequence of slopes extending from somewhat rounded concavities (or swales) of various sizes to irregular conical knolls (or knobs) and short discontinuous ridges; there is a general lack of concordance between knolls and swales. Slopes are generally 4-70%. Examples are hummocky moraines and hummocky fluvioglacial landforms.IInclinedA sloping, unidirectional surface with a generally constant slope unbroken by marked irregularity or gullies; a weakly developed dissected pattern provides external drainage for the local area. Slopes are 2-70%; the form of inclined slopes is not related to the initial mode of origin of the underlying material.KKnoll and kettleA chaotic sequence of knolls and kettles (or sloughs), which occupies 15-20% of an area and has no external drainage. Slopes are generally >3%. Examples are morainal plains and hill lands.LLevelA flat or very gently sloping, unidirectional surface with a generally constant slope unbroken by marked elevations and depressions. Slopes are generally <2%. Examples are floodplains and lake plains.MRollingA very regular sequence of moderate slopes extending from rounded and, in some places, confined concave depressions to broad, rounded convexities producing a wavelike pattern of moderate relief. Slope gradients are generally >5% but may be less. This surface form is usually controlled by the underlying bedrock.RRidgedA long, narrow elevation of the surface, usually sharp crested with steep sides; ridges may be parallel, subparallel, or intersecting. Examples are eskers, crevasse fillings, washboard moraines and some drumlins. Includes pronounced terrain associated with rugged bedrock-controlled hill and mountain systems.SSteepErosional slopes of greater than 70% (35°), present on both consolidated and unconsolidated materials. The form of a steep erosional slope on unconsolidated materials is not related to the initial mode of origin of the underlying material. An example is an escarpment.TTerracedScarp face and the horizontal or gently inclined surface (or tread) above it. An example is an alluvial terrace.SURFACE FORM(cont.)Attribute ValueDESCRIPTIONUUndulatingA very regular sequence of gentle slopes that extends from rounded and, in some places, confined concavities to broad, rounded convexities producing a wavelike pattern of low local relief. Slope length is generally less than 0.8 km and the dominant gradient of slopes is usually 2-5%. The terrain lacks an external drainage pattern. Examples are some ground moraines and lacustrine material of varying textures.B04Domed bogA large bog (diameter usually >500 m) with a convex surface rising several metres above the surrounding terrain. The centre usually drains in all directions; small crescentic pools commonly form around the highest point; a concentric pattern is formed if the highest point is in the centre, while an eccentric pattern is formed if the highest point is off-centre. Peat development is usually >3 m.B05Polygonal peat plateau bogA perennially frozen bog rising approximately 1 m above the surrounding fen. The surface is relatively flat, scored by a polygonal pattern of trenches that developed over ice wedges. The permafrost and ice wedges developed in peat originally deposited in a nonpermafrost environment.B07Peat plateau bogA bog composed of perennially frozen peat rising abruptly about 1 m from the surrounding unfrozen fen. The surface is relatively flat and even, and commonly covers large areas. The peat was originally deposited in a nonpermafrost environment and is associated in many places with collapse scar bogs or fens.B09Atlantic plateau bogA bog with a flat to undulating surface raised above the surrounding terrain. The bog edges commonly slope steeply downwards to the mineral soil terrain. Large pools scattered on the bog reach depths of 2-4 m.B13Basin bogA bog situated in a basin with essentially closed drainage which receives water from precipitation and runoff from the immediate surroundings. The surface of the bog is flat with peat generally deepest at the centre.B14Flat bogA bog having a flat, featureless surface and occurring in broad, poorly defined depressions. The depth of peat is generally uniform.B15String bogA pattern of narrow (2-3 m wide), low (<1 m high) ridges oriented at right angles to the direction of drainage; wet depressions or pools occur between the ridges. The water and peat are very low in nutrients because the water has been derived from other ombrotrophic wetlands. The peat thickness is >1 m.B16Blanket bogA bog consisting of extensive peat deposits that occur more or less uniformly over gently sloping hills and valleys. The peat thickness is usually < 2 m.B18Slope bogA bog occurring in areas of high rainfall on appreciably sloping land surfaces. The bog is fed by rainwater and by water draining from other nutrient-poor peatlands. The peat may exceed 1 m in thickness.B19Veneer bogA bog occurring on gently sloping terrain underlain by generally discontinuous permafrost. Although drainage is predominantly below the surface, overland flow occurs in poorly defined drainways during peak runoff. Peat thickness is usually <1.5 m.B20Lowland polygon bogA bog with flat-topped or convex peat surfaces (often referred to as 'high-centre polygons') separated by trenches over ice wedges that form a polygonal pattern when viewed from above. The peat was deposited in a permafrost environment as shown by internal structures.F01Northern ribbed fenA fen with parallel, low peat ridges ('strings') alternating with wet hollows or shallow pools, oriented across the major slope at right angles to water movement. The depth of peat is >1 m.F07Shore fenA fen with an anchored surface mat that forms the shore of a pond or lake. The rooting zone is affected by the water of the lake at both normal and flood levels.F11Slope fenA fen occurring mainly on slow-draining, nutrient-enriched seepage slopes. Pools are usually absent, but wet seepage tracks may occur. Peat thickness is usually <2 m.F13Horizontal fenA fen with a gently sloping, featureless surface. This fen occupies broad, often ill-defined depressions and may interconnect with other fens. Peat accumulation is generally uniform.F14Snowpatch fenFens that form below melting snowbanks in the Arctic or Alpine. Peat accumulation is very limited and thicknesses are usually less than 20 cm.SURFACE FORM(cont.)Attribute ValueDESCRIPTIONS01Stream swampA swamp occurring along the banks of permanent or semipermanent streams. The high water table is maintained by the level of water in the stream. The swamp is seasonally inundated with subsequent sediment deposition.S04Basin swampA swamp developed in a topographically defined basin where water derived locally may be augmented by drainage from other parts of the watershed. Accumulation of well-decomposed peat is shallow (< 0.5 m) at the edge but may reach 2 m at the centre.M06Stream marshA marsh occupying shorelines, bars, stream beds, or islands in continuously flowing watercourses. The marsh is subject to prolonged annual flooding and is commonly covered by thick layers of sediments.M11Shallow basin marshA marsh occurring in a uniformly shallow marsh depression or swale, having a gradual gradient from the edge to the deepest portion; the marsh edge may be poorly defined. Water levels fluctuate rapidly.M14Shore marshA marsh occupying the contact zone between high and low water marks bordering semipermanent or permanent lakes. The marsh, usually found along protected shorelines, behind barrier beaches in lagoons, on islands, or in embayments, is subject to flooding by a rise in lake levels, wind waves, or surface runoff.Permafrost formTwo attribute fields (Prmfrst1, Prmfrst2) capture the primary and secondary permafrost forms in each ecoregion. The documents were reviewed for all permafrost types and a list was compiled that is more comprehensive than that provided by Agriculture and Agri-foods Canada. The attribute values and definitions are provided below.Permafrost FORMAttribute ValueDESCRIPTIONEHEarth hummocks -A hummock having a core of silty and clayey mineral soil which may show evidence of cryoturbation. Earth hummocks are a type of non-sorted circle (see also patterned ground and turf hummock) commonly found in the zone of continuous permafrost. They develop in materials of a high silt and clay content and/or of high ice content.FRFrost heaved/shattered rock -rock that has been pushed to the surface or broken by freeze-thaw cyclesGIGround ice - Layers of segregated ice or ice-organic mixes or ice-mineral soil mixes that do not melt.GLGlacier - A mass of ice that develops as a result of snow and ice accumulation over a long period of time and that moves laterally from the centre of accumulation.HCHigh centre polygons (with low-centre polygons as subdominant) - see low-centre polygonIWIce wedge polygonsLCLow centre polygons (with high-centre polygons as subdominant): A feature of continuous permafrost in wet terrain (e.g., drained lakes). Ice wedges develop in cracks, pushing up soil ridges adjacent to the wedges and creating dams that trap water inside the resulting polygons. The features appear as high-rimmed ridges surrounding wet shallow central pools of water. Over hundreds or thousands of years, peat deposits build up and eventually create a dome-shaped surface; these features are referred to as high-centre polygons.NCNon-sorted circles, stripes - a non-sorted circle is a patterned ground form that is equidimensional in several directions, with a dominantly circular outline which lacks a well-defined border of stones and has a centre composed of a mixture of textures from fine through coarse mixed with gravels, cobbles and boulders. A network of non-sorted circles that meet is referred to as a non-sorted net. Non-sorted stripes form under the same influence of frost action as non-sorted circles, but because they form on slopes, they flow and elongate perpendicular to contour.PAPalsa -A peaty permafrost mound possessing a core of alternating layers of segregated ice and peat or mineral soil material. Palsas are typically between 1 and 7 metres in height and a few metres to 100 metres in diameter. PGPatterned ground - A general term for circles, polygons, stripes, nets and steps created by frost action.Permafrost FORM (cont.)Attribute ValueDESCRIPTIONPIPingo - A mound of earth-covered ice found in the Arctic, Subarctic and Antarctica that can reach up to 70 metres in height and up to 2 kilometres in diameter. The term originated as the Inuit word for a small hill. They are most common in Canada along the coastal plains of the Tuktoyaktuk Peninsula. They form in the former basins of drained lakes. PPPeat plateau - A bog composed of perennially frozen peat, rising abruptly about 1 m from the surrounding unfrozen fen. The surface is relatively flat and even and often covers very large areas. The peat was originally deposited in a non-permafrost environment and is often associated with collapse scars or fens.PPPPolygonal peat plateau - A perennially frozen bog, rising about 1 m above the surrounding fen. The surface is relatively flat, scored by a polygonal pattern of trenches that developed over ice wedges. The permafrost and ice wedges developed in peat originally deposited in a non-permafrost environment. Polygonal peat plateaus are commonly found near the boundary between the zones of discontinuous and continuous permafrost.RRunnels - A pattern of alternating flow channels and interchannel uplands perpendicular to contour. In permafrost-affected areas, light and dark-striped patterns on hill slopes are runnels; the light stripes are usually sparsely treed, lichen covered interchannel areas with permafrost close to the surface and the dark stripes are shallow drainage channels vegetated by dwarf birch, willow and other shrubs with a thicker active layer.RGRock glaciers - ice-cored, often lobe-shaped landforms covered by soil and rock.RTRetrogressive thaw (or flow) slides - A slide that consists of a headwall containing ice or ice-rich sediment, which retreats in a retrogressive fashion through melting, and a debris flow formed by the mixture of thawed sediment and ice that has slid down the failure surface to the base of the slope and frequently into a thermokarst depression, lake, or pond. SCSorted circles, stripes - a sorted circle is permafrost-related patterned ground that forms under extremely cold conditions when frost action pushes parent materials to the surface; the centre of the circle is occupied by sparsely vegetated finer-textured materials, with a ring of gravels, cobbles and boulders around the outside. A network of sorted circles that meet is referred to as a sorted net. Sorted stripes form under the same influence of frost action as sorted circles, but because they form on slopes, they flow and elongate perpendicular to contour.SOSolifluction - the downslope movement of water-saturated soil in a viscous or plastic state over an impermeable layer, often permafrost. The presence of an impermeable permafrost layer prevents the internal drainage of the soil, forcing the soil to flow down the slope. During warm periods the surface layer thaws and slides across the frozen layer, slowly moving downslope due to frost heave.TKThermokarst -The process by which characteristic landforms result from the thawing of ice-rich permafrost or the melting of massive ice. TUTurf hummocks - a permafrost-related northern Arctic landform generally less than 1m across and 50cm in height that is often associated with aeolian materials (sands, silts). It is more or less circular and is initially forced upward by frost action. It receives solar energy from all sides during the 24-hour days of the brief growing season, promoting plant growth which traps windborne silt and sand particles, resulting in the gradual accretion of materials and growth of the hummock.VBVeneer bog - A bog occurring on gently sloping terrain underlain by generally discontinuous permafrost. Although drainage is predominantly below the surface, overland flow occurs in poorly defined drainage ways during peak runoff. Peat thickness is generally less than 1.5 metres.Soil developmentThree dataset attribute fields (Soil1, Soil2, Soil3) capture soil information from the written ecoregion descriptions. A subset of the soil table provided by Agriculture and Agri-food Canada was used, as many of the soil types in the full table do not occur in the NWT. As for surficial geology, the first and second variables (Soil1, Soil2) may be codominant or the second subordinate to the first. In some cases, a value for Soil1and Soil3was provided, with no value for Soil2. This indicates that Soil1is dominant, and Soil3is only present over minor areas within the ecoregion. The written descriptions should be consulted in cases where analysis requires a more specific assessment of proportion.Attribute ValueDESCRIPTIONFGray LuvisolHGHumic GleysolHRHumic RegosolIBrunisol Gray LuvisolLGLuvic GleysolMEutric BrunisolOOrganic CryosolPDystric BrunisolRRegosolSStatic CryosolTTurbic CryosolUGleysolXFibrisolYMesisolZHumisol#Water, Rock or IceLand CoverThree attribute fields (Landcov1, Landcov2, Landcov3) capture vegetation information from the written descriptions. Because vegetation patterns are in part how ecoregions are described, there is considerable variation from one Level II ecoregion to another, and the 17 classes provided by Agriculture and Agri-food Canada were considered inadequate to represent significant vegetation trends. A review of all five documents consequently resulted in the establishment of specific attribute values for major vegetation types within the Taiga Plains, Taiga Shield, and Cordillera. The Southern Arctic and Northern Arctic classifications are based mainly upon the Circumpolar Arctic Vegetation Map community types (CAVM Team 2003) and are more consistently defined and described, but also had some unique values. Attribute values specific to each area are presented in tables below; to identify the types uniquely, they are prefaced with TP:(Taiga Plains), TS:(Taiga Shield), CO:(Cordillera), SA:(Southern Arctic) and NA:(Northern Arctic).Landcov1and Landcov2were generally used to capture the major vegetation types; if there was a significant vegetation type that did not occur over large areas but was considered diagnostic (e.g. alpine fir types in the southern mountains), it was included as Landcov3even if there were other vegetation communities that covered larger areas. The written descriptions should be consulted in cases where analysis requires a more specific assessment of proportion.LAND COVER (VEGETATION): TAIGA PLAINSAttribute ValueDESCRIPTIONTP:F1Fen: SedgeTP:F2Fen: shrub-sedgeTP:F3Fen or bog: Black spruce - shrub - mossTP:F4Fen: Black spruce - larchTP:FC1Forest: Jackpine - shrub - lichenTP:FC2Forest: Jackpine - tall shrub - lichenTP:FC3Forest: Lodgepole and jackpine X lodgepole hybridTP:FC4Forest: White spruce - jack pineTP:FC5Forest: Spruce - lichenTP:FC6Forest: spruce-shrub (includes both black and white spruce)TP:FC7Forest: white spruceTP:FC8Forest: black spruce - shrub - lichenTP:FD1Forest: Deciduous (aspen, balsam poplar, paper birch)TP:FD2Forest: Paper birchTP:FM1Forest: Mixedwood jackpine - aspenTP:FM2Forest: Spruce - paper birch (includes white and black spruce)TP:FM3Forest: Mixedwood aspen - paper birch - spruce - jackpineTP:M1Marsh: bulrush - sedgeTP:M2Meadow: herb-grass-shrubTP:S1Shrubland: dwarf birch - dryland sedge - lichenTP:S2Shrubland: dwarf birch - Labrador tea - peat moss TP:S3Shrubland: dwarf birch - paper birch (post-fire regeneration). May include white spruce and black spruce regeneration, and may be one or both deciduous species.TP:S4Shrubland: dwarf birch - willowTP:S5Shrubland: lichen - Labrador tea - dwarf birch (polygonal peat plateaus)TP:S6Shrubland: willow-alderTP:S6Shrubland: willowTP:S7Shrubland: dryTP:TSTundra: ShrubTP:W1Woodland: White spruce - shrub-lichen woodlandTP:W2Woodland: Black spruce - low shrub- lichenLAND COVER (VEGETATION): TAIGA SHELDAttribute ValueDESCRIPTIONTS:F1Fen: sedge (including a minor component of shrubs)TS:F2Fen: shrub (including a minor component of sedges)TS:FC1Forest: Jackpine (may include minor paper birch, white spruce, black spruce)TS:FC2Forest: Spruce - moss (undifferentiated white and black spruce)TS:FC3Forest: Spruce - shrub - lichen (undifferentiated white and black spruce)TS:FD1Forest: DeciduousTS:FM1Forest: Mixedwood (any combination of aspen, balsam poplar, and birch with white spruce, black spruce, and jackpine)TS:FM2Forest: Mixedwood white spruce - paper birchTS:FM3Forest: Mixedwood jackpine - paper birchTS:NFLLichen on rockTS:S1Shrubland: Dwarf birch - paper birch (post-fire regeneration)TS:S2Shrubland: lichen - Labrador tea - dwarf birch (peat plateaus)TS:T1Tundra: lichen - grass heathTS:T2Tundra: sedgeTS:T3Tundra: shrub heathTS:T4Tundra: lichen-sedge-shrub complexTS:W1Woodland: White spruce - shrub - lichen TS:W2Woodland: Spruce - shrub - lichenTS:W3Woodland: Black spruce - lichenLAND COVER (VEGETATION): CORDILLERAAttribute ValueDESCRIPTIONCO:F1Fen: Black spruce - (larch) - shrubCO:F2Fen: Sedge - cottongrass tussockCO:F3Fen: Shrub - sedgeCO:FC1Forest: JackpineCO:FC2Forest: lodgepole pineCO:FC3Forest: Spruce - shrubCO:FC4Forest: White spruceCO:FC5Forest: White spruce - alpine firCO:FD1Forest: Deciduous (aspen, balsam poplar, paper birch)CO:FM1Forest: Mixedwood (white spruce, aspen, jackpine, lodgepole pine)CO:FM2Forest: Mixedwood (spruce, balsam poplar, birch, tall shrub)CO:NFL1Lichen - RockCO:Rrock barrensCO:S1Shrubland: dwarf birch - willow - paper birch (post-fire regeneration)CO:S2Shrublands: Tall (alder, willow, birch)CO:S3Shrublands: DryCO:S4Shrublands: dwarf birch - willowCO:T1Tundra: herb (rich, diverse, Pacific-Cordilleran species)CO:T2Tundra: LichenLAND COVER (VEGETATION): CORDILLERA (cont.)Attribute ValueDESCRIPTIONCO:T3Tundra: Sedge - cottongrassCO:T4Tundra: sedge-shrubCO:T5Tundra: shrubCO:W1Woodland: alpine firCO:W2Woodland: black spruce - larch - mossCO:W3Woodland: black spruce - shrub - moss - lichenCO:W4Woodland: White spruce - alpine firCO:W5Woodland: White (black) spruce - shrub - lichenLAND COVER (VEGETATION): SOUTHERN ARCTIC*Attribute ValueDESCRIPTIONSA:B1Cryptogam –herb barren SA:B2Cryptogam –barren complex (bedrock) SA:CMCoastal MarshSA:G2Graminoid –prostrate dwarf-shrub –forb tundraSA:G3Nontussock sedge –dwarf-shrub –moss tundraSA:G4Tussock-sedge –dwarf-shrub –moss tundra SA:P1Prostrate dwarf-shrub –herb tundraSA:S1Erect dwarf-shrub tundra SA:S2Low-shrub tundraSA:T1Tundra: lichen - grass heath (continuation of Taiga Shield)SA:T2Tundra: sedge (continuation of Taiga Shield)SA:T3Tundra: shrub heath (continuation of Taiga Shield)SA:TGTree groves / sparse tree growthSA:W2Sedge –moss –dwarf-shrub wetland SA:W3Sedge –moss –low-shrub wetland LAND COVER (VEGETATION): NORTHERN ARCTIC*Attribute ValueDESCRIPTIONNA:B1Cryptogam –herb barren NA:B2Cryptogam –barren complex (bedrock) NA:B3b-cNon-carbonate mountain complex NA:B4bCarbonate mountain complex NA:G1Rush –grass–forb –cryptogam tundra NA:G2Graminoid –prostrate dwarf-shrub –forb tundra NA:G3Nontussock sedge –moss –dwarf-shrub tundraNA:P1Prostrate dwarf-shrub –herb tundra NA:P2Prostrate/hemiprostrate dwarf-shrub tundraNA:S2Low-shrub tundra NA:W1Sedge –grass –moss wetland * the code values following SA: and NA: are those defined by the Circumpolar Arctic Vegetation Map (CAVM Team 2003), except for SA:T1, SA:T2, SA:T3 (continuation of Taiga Shield vegetation to the north) and SA:CM (coastal marshes of Mackenzie Delta, too small to address in the circumpolarmap survey.REFERENCES CITEDCAVM Team. 2003. Circumpolar Arctic Vegetation Map. (1:7,500,000 scale), Conservation of Arctic Flora and Fauna (CAFF) Map No. 1. U.S. Fish and Wildlife Service, Anchorage, Alaska.",
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"description": "Direct human disturbance footprint refers to the area directly affected by human activities, such as mine sites, roads or airstrips. These human disturbance features directly affect caribou habitat. The direct human disturbance footprint mapping formed the basis for the Bathurst Caribou Range Plan disturbance assessment, with estimated zones of influence applied to each feature. The human land use feature mapping was developed iteratively between 2014 to 2016 by compiling and merging available GIS information including the Government of Northwest Territories Cumulative Impact and Monitoring Program (CIMP) database, the National Road Network, and mineral industry-provided information used to support project assessment and permitting activities. The human feature mapping database includes both existing and future potential human features based on three potential land use scenarios. 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Many Camp features are also associated with Mineral Exploration activities.MINE_ACTIVMinesite (Active)Minesites under construction or in production.CIMP Feature Class: Selected Mining Explorationand Mining and Milling – Waterfeatures to represent active mines (i.e., Ekati, Diavik, and Gahcho Kué).Note: Several other data sources were used to supplement the CIMP features, as required.MINE_PASTMinesite (Past or Closed)Past or closed minesites, either abandoned or under active reclamation.CIMP Feature Class: Closed or past mines are represented by selected Mining Explorationor Miscellaneousfeatures from the CIMP database (e.g., Lupin, Jericho, Tundra, Rayrock, etc.).Note: In CIMP database, many past mine footprints were classified as Miscellaneous features; where known, they have been re-classified as MINE_PAST.MISCMiscellaneousA variety of industrial and non-industrial surface disturbances or infrastructure.CIMP Feature Class: Miscellaneous features are represented by several CIMP feature classes, including Miscellaneous, Research Projects, and Unknown.Note: Some Miscellaneous features in CIMP database are old mine sites, quarries, mineral exploration, communications, etc. Where possible, obvious features were classified as a more accurate feature category. 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In GIS mapping, ZOI is estimated as a spatial buffer of a defined distance around a human development feature.The amount of direct and indirect human-caused disturbance in the Bathurst range planning area was calculated from an integrated GIS data set of human land use features/surface disturbances developed as part of the range planning exercise. The human land use feature mapping was created by compiling and merging available GIS information, with the Government of NWT Cumulative Impact Monitoring Program (CIMP) database (CIMP 2015) being the main input, supplemented and modified where necessary by the National Road Network and mineral industry-provided information used to support project assessment and permitting activities. Detailed mapping methods are described in Appendix A of the Caribou Range Assessment and Technical Information report developed in support of the Bathurst Caribou Range Planning process. 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(2011) Fig. 3, based on mean 90% utilization distribution from accumulated collar data 1996-2008Calving ground D from Nagy et al. (2011) Fig. 1BeverlyGeneralized annual range polygon from Nagy et al. (2011) Fig. 3, based on mean 90% utilization distribution from accumulated collar data 1995-2008There are 2 polygons, a northern and a southern calving ground. Based on BQCMB compilation of all data from government surveys (1957-2011) and telemetry (1996-2012). See Poole (2011) for details.Polygons are as displayed by BQCMB (2014) as well as Nagy et al. (2011, Fig. 1, calving grounds E-1 and F).AhiakGeneralized annual range polygon for ‘Queen Maud Gulf’ from Nagy et al. (2011) Fig. 3, based on mean 90% utilization distribution from accumulated collar data 1996-2008. In 2017, the Ahiak annual range was extended by B.Fournier (ENR) to cover the Queen Maud Gulf calving area produced by J.Nagy, when it was discovered that 2 areas in the northwest and northeast of the calving area were not covered by the annual range polygon.Calving ground E from Nagy et al. (2011) Fig. 1QamanirjuaqGeneralized annual range polygon from Nagy et al. (2011) Fig. 3, based on mean 90% utilization distribution from accumulated collar data 1993-2008Based on BQCMB compilation of all data from government surveys (1963-2008) and telemetry (1993-2012). See Poole (2011) for details.Polygons are as displayed by BQCMB (2014) as well as Nagy et al. (2011, Fig. 1, calving ground G).LorillardGeneralized annual range polygon from Nagy et al. (2011) Fig. 3, based on mean 90% utilization distribution from accumulated collar data 1998-2007Calving ground H from Nagy et al. (2011) Fig. 1Wager BayGeneralized annual range polygon from Nagy et al. (2011) Fig. 3, based on mean 90% utilization distribution from accumulated collar data 2000-2006Calving ground I from Nagy et al. (2011) Fig. 1Boothia PeninsulaAs shown in COSEWIC (2016) Fig. 2. Digitized by B. Fournier, ENR, as instructed by COSEWIC (J. Ray) in 2015.Polygon not availableSouthampton IslandAs shown in COSEWIC (2016) Fig. 2. Digitized by B. Fournier, ENR, as instructed by Mitch Campbell (Govt of NU) in 2014, for the COSEWIC report. Used entire island as there were no quantitative seasonal range data available.Polygon not availableCoats IslandAs shown in COSEWIC (2016) Fig. 2. Digitized by B. Fournier, ENR, as instructed by Mitch Campbell (Govt of NU) in 2014, for the COSEWIC report. Used entire island as there were no quantitative seasonal range data available.Polygon not availableBaffin IslandAs shown in COSEWIC (2016) Fig. 2. Digitized by B. Fournier, ENR, from an image provided by Troy Pretzlaw (Govt of NU) in 2014, for the COSEWIC report. Polygon not availableAcronyms:BQCMB = Beverly and Qamanirjuaq Caribou Management BoardCARMA = CircumArctic Rangifer Monitoring and Assessment NetworkCOSEWIC = Committee on the Status of Endangered Wildlife in CanadaReferences cited in table:BQCMB. 2014. Beverly and Qamanirjuaq Caribou Management Plan 2013-2022. Beverly and Qamanirjuaq Caribou Management Board, Stonewall, MB. Available at http://arctic-caribou.com/pdf/bqcmb_managementplan_detailed2014.pdfCARMA. 2012. Caribou herd information. CircumArctic Rangifer Monitoring and Assessment Network. Web site: http://www.caff.is/carmaherds[accessed December 2012]COSEWIC. 2011. Designatable Units for Caribou (Rangifer tarandus) in Canada. Committee on the Status of Endangered Wildlife in Canada, Ottawa, ON. 88 pp. Available at http://www.cosewic.gc.ca/D37AB818-5F3B-44DC-9D56-EE22C63F4512/COSEWIC_Caribou_DU_Report_23Dec2011.pdfCOSEWIC. 2016. COSEWIC Status Report on Barren-ground caribou Rangifer tarandus in Canada. 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"description": "Barren-ground caribou annual ranges and calving areas by herd (i.e. subpopulation). The supplementary table BIO_ENR_WFE_SARA_AttributeTable contains additional attribute information for this species and its status and range in the NWT. All barren-ground caribou subpopulations considered by COSEWIC (2016) as part of Designatable Unit 3 are included in this shapefile. See COSEWIC (2011) for details on the Designatable Unit. Subpopulation structure of caribou (Rangifer tarandusL.) is as described by Nagy et al. (2011) for the Qamanirjuaq, Ahiak (i.e. Queen Maud Gulf), Beverly, Bathurst, Bluenose-East, Bluenose-West, Cape Bathurst, Lorillard and Wager Bay subpopulations. Other types of caribou (e.g. Dolphin and Union, Peary, mountain woodland, boreal woodland) are not included. Their ranges are available as separate NWT species at risk range shapefiles. 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Details on the origin of each polygon are provided in the table below:Herd (subpopulation)Annual rangeCalving areaPorcupineObtained from the Porcupine Caribou Technical Committee. As displayed on the Porcupine Caribou Management Board website (http://www.pcmb.ca/images/habitat/PCH-Rangemap2.jpg)Prepared by K. Poole (Poole 2011) for CARMA (2012). Cumulative extent of calving (1-21 June) from 1985 – 2010. 90% fixed kernel polygon using all available satellite collar data, obtained from Yukon Environment, combined among years.Tuktoyaktuk PeninsulaCreated byA. D'Hont, ENR in 2013. Produced using caribou collar telemetry data 2006-2012. Contours accumulate the number of unique marked individuals that visit within a 10x10km cell; The contour shown by this polygon is 5%. The percentages are based on the highest count (=100%) of unique collared individuals for that herd occurring within any 10km x 10km block, illustrating the relative degree of use of specific land areas over a defined period of time. Created byA. D'Hont, ENR in 2013.Cape BathurstGeneralized annual range polygon from Nagy et al. (2011) Fig. 3, based on mean 90% utilization distribution from accumulated collar data 1996-2008Calving ground A from Nagy et al. (2011) Fig. 1Bluenose-WestGeneralized annual range polygon from Nagy et al. (2011) Fig. 3, based on mean 90% utilization distribution from accumulated collar data 1996-2008Calving ground B from Nagy et al. (2011) Fig. 1Bluenose-EastGeneralized annual range polygon from Nagy et al. (2011) Fig. 3, based on mean 90% utilization distribution from accumulated collar data 1996-2008Calving ground C from Nagy et al. (2011) Fig. 1BathurstGeneralized annual range polygon from Nagy et al. (2011) Fig. 3, based on mean 90% utilization distribution from accumulated collar data 1996-2008Calving ground D from Nagy et al. (2011) Fig. 1BeverlyGeneralized annual range polygon from Nagy et al. (2011) Fig. 3, based on mean 90% utilization distribution from accumulated collar data 1995-2008There are 2 polygons, a northern and a southern calving ground. Based on BQCMB compilation of all data from government surveys (1957-2011) and telemetry (1996-2012). See Poole (2011) for details.Polygons are as displayed by BQCMB (2014) as well as Nagy et al. (2011, Fig. 1, calving grounds E-1 and F).AhiakGeneralized annual range polygon for ‘Queen Maud Gulf’ from Nagy et al. (2011) Fig. 3, based on mean 90% utilization distribution from accumulated collar data 1996-2008. In 2017, the Ahiak annual range was extended by B.Fournier (ENR) to cover the Queen Maud Gulf calving area produced by J.Nagy, when it was discovered that 2 areas in the northwest and northeast of the calving area were not covered by the annual range polygon.Calving ground E from Nagy et al. (2011) Fig. 1QamanirjuaqGeneralized annual range polygon from Nagy et al. (2011) Fig. 3, based on mean 90% utilization distribution from accumulated collar data 1993-2008Based on BQCMB compilation of all data from government surveys (1963-2008) and telemetry (1993-2012). See Poole (2011) for details.Polygons are as displayed by BQCMB (2014) as well as Nagy et al. (2011, Fig. 1, calving ground G).LorillardGeneralized annual range polygon from Nagy et al. (2011) Fig. 3, based on mean 90% utilization distribution from accumulated collar data 1998-2007Calving ground H from Nagy et al. (2011) Fig. 1Wager BayGeneralized annual range polygon from Nagy et al. (2011) Fig. 3, based on mean 90% utilization distribution from accumulated collar data 2000-2006Calving ground I from Nagy et al. (2011) Fig. 1Boothia PeninsulaAs shown in COSEWIC (2016) Fig. 2. Digitized by B. Fournier, ENR, as instructed by COSEWIC (J. Ray) in 2015.Polygon not availableSouthampton IslandAs shown in COSEWIC (2016) Fig. 2. Digitized by B. Fournier, ENR, as instructed by Mitch Campbell (Govt of NU) in 2014, for the COSEWIC report. Used entire island as there were no quantitative seasonal range data available.Polygon not availableCoats IslandAs shown in COSEWIC (2016) Fig. 2. Digitized by B. Fournier, ENR, as instructed by Mitch Campbell (Govt of NU) in 2014, for the COSEWIC report. Used entire island as there were no quantitative seasonal range data available.Polygon not availableBaffin IslandAs shown in COSEWIC (2016) Fig. 2. Digitized by B. Fournier, ENR, from an image provided by Troy Pretzlaw (Govt of NU) in 2014, for the COSEWIC report. Polygon not availableAcronyms:BQCMB = Beverly and Qamanirjuaq Caribou Management BoardCARMA = CircumArctic Rangifer Monitoring and Assessment NetworkCOSEWIC = Committee on the Status of Endangered Wildlife in CanadaReferences cited in table:BQCMB. 2014. Beverly and Qamanirjuaq Caribou Management Plan 2013-2022. Beverly and Qamanirjuaq Caribou Management Board, Stonewall, MB. Available at http://arctic-caribou.com/pdf/bqcmb_managementplan_detailed2014.pdfCARMA. 2012. Caribou herd information. CircumArctic Rangifer Monitoring and Assessment Network. Web site: http://www.caff.is/carmaherds[accessed December 2012]COSEWIC. 2011. Designatable Units for Caribou (Rangifer tarandus) in Canada. Committee on the Status of Endangered Wildlife in Canada, Ottawa, ON. 88 pp. Available at http://www.cosewic.gc.ca/D37AB818-5F3B-44DC-9D56-EE22C63F4512/COSEWIC_Caribou_DU_Report_23Dec2011.pdfCOSEWIC. 2016. COSEWIC Status Report on Barren-ground caribou Rangifer tarandus in Canada. Draft - 2-month interim status report. Committee on the Status of Endangered Wildlife in Canada.Nagy, J.A., D. L. Johnson, N. C. Larter, M. W. Campbell, A. E. Derocher, A. Kelly, M. Dumond, D. Allaire, and B. Croft. 2011. Subpopulation structure of caribou (Rangifer tarandusL.) in arctic and subarctic Canada. Ecological Applications 21:2334–2348. http://dx.doi.org/10.1890/10-1410.1Poole, K. 2011. Methodology and sources for preparing seasonal shape files for caribou herds for CARMA. Unpublished document, Aurora Wildlife Research. 11 pp.",
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In 2017, the Ahiak annual range was extended by B.Fournier (ENR) to cover the Queen Maud Gulf calving area produced by J.Nagy, when it was discovered that 2 areas in the northwest and northeast of the calving area were not covered by the annual range polygon.Calving ground E from Nagy et al. (2011) Fig. 1QamanirjuaqGeneralized annual range polygon from Nagy et al. (2011) Fig. 3, based on mean 90% utilization distribution from accumulated collar data 1993-2008Based on BQCMB compilation of all data from government surveys (1963-2008) and telemetry (1993-2012). See Poole (2011) for details.Polygons are as displayed by BQCMB (2014) as well as Nagy et al. (2011, Fig. 1, calving ground G).LorillardGeneralized annual range polygon from Nagy et al. (2011) Fig. 3, based on mean 90% utilization distribution from accumulated collar data 1998-2007Calving ground H from Nagy et al. (2011) Fig. 1Wager BayGeneralized annual range polygon from Nagy et al. (2011) Fig. 3, based on mean 90% utilization distribution from accumulated collar data 2000-2006Calving ground I from Nagy et al. (2011) Fig. 1Boothia PeninsulaAs shown in COSEWIC (2016) Fig. 2. Digitized by B. Fournier, ENR, as instructed by COSEWIC (J. Ray) in 2015.Polygon not availableSouthampton IslandAs shown in COSEWIC (2016) Fig. 2. Digitized by B. Fournier, ENR, as instructed by Mitch Campbell (Govt of NU) in 2014, for the COSEWIC report. Used entire island as there were no quantitative seasonal range data available.Polygon not availableCoats IslandAs shown in COSEWIC (2016) Fig. 2. Digitized by B. Fournier, ENR, as instructed by Mitch Campbell (Govt of NU) in 2014, for the COSEWIC report. Used entire island as there were no quantitative seasonal range data available.Polygon not availableBaffin IslandAs shown in COSEWIC (2016) Fig. 2. Digitized by B. Fournier, ENR, from an image provided by Troy Pretzlaw (Govt of NU) in 2014, for the COSEWIC report. Polygon not availableAcronyms:BQCMB = Beverly and Qamanirjuaq Caribou Management BoardCARMA = CircumArctic Rangifer Monitoring and Assessment NetworkCOSEWIC = Committee on the Status of Endangered Wildlife in CanadaReferences cited in table:BQCMB. 2014. Beverly and Qamanirjuaq Caribou Management Plan 2013-2022. Beverly and Qamanirjuaq Caribou Management Board, Stonewall, MB. Available at http://arctic-caribou.com/pdf/bqcmb_managementplan_detailed2014.pdfCARMA. 2012. Caribou herd information. CircumArctic Rangifer Monitoring and Assessment Network. Web site: http://www.caff.is/carmaherds[accessed December 2012]COSEWIC. 2011. Designatable Units for Caribou (Rangifer tarandus) in Canada. Committee on the Status of Endangered Wildlife in Canada, Ottawa, ON. 88 pp. Available at http://www.cosewic.gc.ca/D37AB818-5F3B-44DC-9D56-EE22C63F4512/COSEWIC_Caribou_DU_Report_23Dec2011.pdfCOSEWIC. 2016. COSEWIC Status Report on Barren-ground caribou Rangifer tarandus in Canada. Draft - 2-month interim status report. Committee on the Status of Endangered Wildlife in Canada.Nagy, J.A., D. L. Johnson, N. C. Larter, M. W. Campbell, A. E. Derocher, A. Kelly, M. Dumond, D. Allaire, and B. Croft. 2011. Subpopulation structure of caribou (Rangifer tarandusL.) in arctic and subarctic Canada. Ecological Applications 21:2334–2348. http://dx.doi.org/10.1890/10-1410.1Poole, K. 2011. Methodology and sources for preparing seasonal shape files for caribou herds for CARMA. Unpublished document, Aurora Wildlife Research. 11 pp.",
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(2011) Fig. 3, based on mean 90% utilization distribution from accumulated collar data 1996-2008Calving ground D from Nagy et al. (2011) Fig. 1BeverlyGeneralized annual range polygon from Nagy et al. (2011) Fig. 3, based on mean 90% utilization distribution from accumulated collar data 1995-2008There are 2 polygons, a northern and a southern calving ground. Based on BQCMB compilation of all data from government surveys (1957-2011) and telemetry (1996-2012). See Poole (2011) for details.Polygons are as displayed by BQCMB (2014) as well as Nagy et al. (2011, Fig. 1, calving grounds E-1 and F).AhiakGeneralized annual range polygon for ‘Queen Maud Gulf’ from Nagy et al. (2011) Fig. 3, based on mean 90% utilization distribution from accumulated collar data 1996-2008. In 2017, the Ahiak annual range was extended by B.Fournier (ENR) to cover the Queen Maud Gulf calving area produced by J.Nagy, when it was discovered that 2 areas in the northwest and northeast of the calving area were not covered by the annual range polygon.Calving ground E from Nagy et al. (2011) Fig. 1QamanirjuaqGeneralized annual range polygon from Nagy et al. (2011) Fig. 3, based on mean 90% utilization distribution from accumulated collar data 1993-2008Based on BQCMB compilation of all data from government surveys (1963-2008) and telemetry (1993-2012). See Poole (2011) for details.Polygons are as displayed by BQCMB (2014) as well as Nagy et al. (2011, Fig. 1, calving ground G).LorillardGeneralized annual range polygon from Nagy et al. (2011) Fig. 3, based on mean 90% utilization distribution from accumulated collar data 1998-2007Calving ground H from Nagy et al. (2011) Fig. 1Wager BayGeneralized annual range polygon from Nagy et al. (2011) Fig. 3, based on mean 90% utilization distribution from accumulated collar data 2000-2006Calving ground I from Nagy et al. (2011) Fig. 1Boothia PeninsulaAs shown in COSEWIC (2016) Fig. 2. Digitized by B. Fournier, ENR, as instructed by COSEWIC (J. Ray) in 2015.Polygon not availableSouthampton IslandAs shown in COSEWIC (2016) Fig. 2. Digitized by B. Fournier, ENR, as instructed by Mitch Campbell (Govt of NU) in 2014, for the COSEWIC report. Used entire island as there were no quantitative seasonal range data available.Polygon not availableCoats IslandAs shown in COSEWIC (2016) Fig. 2. Digitized by B. Fournier, ENR, as instructed by Mitch Campbell (Govt of NU) in 2014, for the COSEWIC report. Used entire island as there were no quantitative seasonal range data available.Polygon not availableBaffin IslandAs shown in COSEWIC (2016) Fig. 2. Digitized by B. Fournier, ENR, from an image provided by Troy Pretzlaw (Govt of NU) in 2014, for the COSEWIC report. Polygon not availableAcronyms:BQCMB = Beverly and Qamanirjuaq Caribou Management BoardCARMA = CircumArctic Rangifer Monitoring and Assessment NetworkCOSEWIC = Committee on the Status of Endangered Wildlife in CanadaReferences cited in table:BQCMB. 2014. Beverly and Qamanirjuaq Caribou Management Plan 2013-2022. Beverly and Qamanirjuaq Caribou Management Board, Stonewall, MB. Available at http://arctic-caribou.com/pdf/bqcmb_managementplan_detailed2014.pdfCARMA. 2012. Caribou herd information. CircumArctic Rangifer Monitoring and Assessment Network. Web site: http://www.caff.is/carmaherds[accessed December 2012]COSEWIC. 2011. Designatable Units for Caribou (Rangifer tarandus) in Canada. Committee on the Status of Endangered Wildlife in Canada, Ottawa, ON. 88 pp. Available at http://www.cosewic.gc.ca/D37AB818-5F3B-44DC-9D56-EE22C63F4512/COSEWIC_Caribou_DU_Report_23Dec2011.pdfCOSEWIC. 2016. COSEWIC Status Report on Barren-ground caribou Rangifer tarandus in Canada. Draft - 2-month interim status report. Committee on the Status of Endangered Wildlife in Canada.Nagy, J.A., D. L. Johnson, N. C. Larter, M. W. Campbell, A. E. Derocher, A. Kelly, M. Dumond, D. Allaire, and B. Croft. 2011. Subpopulation structure of caribou (Rangifer tarandusL.) in arctic and subarctic Canada. Ecological Applications 21:2334–2348. http://dx.doi.org/10.1890/10-1410.1Poole, K. 2011. Methodology and sources for preparing seasonal shape files for caribou herds for CARMA. Unpublished document, Aurora Wildlife Research. 11 pp.",
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The percentages are based on the highest count (=100%) of unique collared individuals for that herd occurring within any 10km x 10km block, illustrating the relative degree of use of specific land areas over a defined period of time. Created byA. D'Hont, ENR in 2013.Cape BathurstGeneralized annual range polygon from Nagy et al. (2011) Fig. 3, based on mean 90% utilization distribution from accumulated collar data 1996-2008Calving ground A from Nagy et al. (2011) Fig. 1Bluenose-WestGeneralized annual range polygon from Nagy et al. (2011) Fig. 3, based on mean 90% utilization distribution from accumulated collar data 1996-2008Calving ground B from Nagy et al. (2011) Fig. 1Bluenose-EastGeneralized annual range polygon from Nagy et al. (2011) Fig. 3, based on mean 90% utilization distribution from accumulated collar data 1996-2008Calving ground C from Nagy et al. (2011) Fig. 1BathurstGeneralized annual range polygon from Nagy et al. (2011) Fig. 3, based on mean 90% utilization distribution from accumulated collar data 1996-2008Calving ground D from Nagy et al. (2011) Fig. 1BeverlyGeneralized annual range polygon from Nagy et al. (2011) Fig. 3, based on mean 90% utilization distribution from accumulated collar data 1995-2008There are 2 polygons, a northern and a southern calving ground. Based on BQCMB compilation of all data from government surveys (1957-2011) and telemetry (1996-2012). See Poole (2011) for details.Polygons are as displayed by BQCMB (2014) as well as Nagy et al. (2011, Fig. 1, calving grounds E-1 and F).AhiakGeneralized annual range polygon for ‘Queen Maud Gulf’ from Nagy et al. (2011) Fig. 3, based on mean 90% utilization distribution from accumulated collar data 1996-2008. In 2017, the Ahiak annual range was extended by B.Fournier (ENR) to cover the Queen Maud Gulf calving area produced by J.Nagy, when it was discovered that 2 areas in the northwest and northeast of the calving area were not covered by the annual range polygon.Calving ground E from Nagy et al. (2011) Fig. 1QamanirjuaqGeneralized annual range polygon from Nagy et al. (2011) Fig. 3, based on mean 90% utilization distribution from accumulated collar data 1993-2008Based on BQCMB compilation of all data from government surveys (1963-2008) and telemetry (1993-2012). See Poole (2011) for details.Polygons are as displayed by BQCMB (2014) as well as Nagy et al. (2011, Fig. 1, calving ground G).LorillardGeneralized annual range polygon from Nagy et al. (2011) Fig. 3, based on mean 90% utilization distribution from accumulated collar data 1998-2007Calving ground H from Nagy et al. (2011) Fig. 1Wager BayGeneralized annual range polygon from Nagy et al. (2011) Fig. 3, based on mean 90% utilization distribution from accumulated collar data 2000-2006Calving ground I from Nagy et al. (2011) Fig. 1Boothia PeninsulaAs shown in COSEWIC (2016) Fig. 2. Digitized by B. Fournier, ENR, as instructed by COSEWIC (J. Ray) in 2015.Polygon not availableSouthampton IslandAs shown in COSEWIC (2016) Fig. 2. Digitized by B. Fournier, ENR, as instructed by Mitch Campbell (Govt of NU) in 2014, for the COSEWIC report. Used entire island as there were no quantitative seasonal range data available.Polygon not availableCoats IslandAs shown in COSEWIC (2016) Fig. 2. Digitized by B. Fournier, ENR, as instructed by Mitch Campbell (Govt of NU) in 2014, for the COSEWIC report. Used entire island as there were no quantitative seasonal range data available.Polygon not availableBaffin IslandAs shown in COSEWIC (2016) Fig. 2. Digitized by B. Fournier, ENR, from an image provided by Troy Pretzlaw (Govt of NU) in 2014, for the COSEWIC report. Polygon not availableAcronyms:BQCMB = Beverly and Qamanirjuaq Caribou Management BoardCARMA = CircumArctic Rangifer Monitoring and Assessment NetworkCOSEWIC = Committee on the Status of Endangered Wildlife in CanadaReferences cited in table:BQCMB. 2014. Beverly and Qamanirjuaq Caribou Management Plan 2013-2022. Beverly and Qamanirjuaq Caribou Management Board, Stonewall, MB. Available at http://arctic-caribou.com/pdf/bqcmb_managementplan_detailed2014.pdfCARMA. 2012. Caribou herd information. CircumArctic Rangifer Monitoring and Assessment Network. Web site: http://www.caff.is/carmaherds[accessed December 2012]COSEWIC. 2011. Designatable Units for Caribou (Rangifer tarandus) in Canada. Committee on the Status of Endangered Wildlife in Canada, Ottawa, ON. 88 pp. Available at http://www.cosewic.gc.ca/D37AB818-5F3B-44DC-9D56-EE22C63F4512/COSEWIC_Caribou_DU_Report_23Dec2011.pdfCOSEWIC. 2016. COSEWIC Status Report on Barren-ground caribou Rangifer tarandus in Canada. Draft - 2-month interim status report. Committee on the Status of Endangered Wildlife in Canada.Nagy, J.A., D. L. Johnson, N. C. Larter, M. W. Campbell, A. E. Derocher, A. Kelly, M. Dumond, D. Allaire, and B. Croft. 2011. Subpopulation structure of caribou (Rangifer tarandusL.) in arctic and subarctic Canada. Ecological Applications 21:2334–2348. http://dx.doi.org/10.1890/10-1410.1Poole, K. 2011. Methodology and sources for preparing seasonal shape files for caribou herds for CARMA. Unpublished document, Aurora Wildlife Research. 11 pp.",
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(2011) Fig. 3, based on mean 90% utilization distribution from accumulated collar data 2000-2006Calving ground I from Nagy et al. (2011) Fig. 1Boothia PeninsulaAs shown in COSEWIC (2016) Fig. 2. Digitized by B. Fournier, ENR, as instructed by COSEWIC (J. Ray) in 2015.Polygon not availableSouthampton IslandAs shown in COSEWIC (2016) Fig. 2. Digitized by B. Fournier, ENR, as instructed by Mitch Campbell (Govt of NU) in 2014, for the COSEWIC report. Used entire island as there were no quantitative seasonal range data available.Polygon not availableCoats IslandAs shown in COSEWIC (2016) Fig. 2. Digitized by B. Fournier, ENR, as instructed by Mitch Campbell (Govt of NU) in 2014, for the COSEWIC report. Used entire island as there were no quantitative seasonal range data available.Polygon not availableBaffin IslandAs shown in COSEWIC (2016) Fig. 2. Digitized by B. Fournier, ENR, from an image provided by Troy Pretzlaw (Govt of NU) in 2014, for the COSEWIC report. Polygon not availableAcronyms:BQCMB = Beverly and Qamanirjuaq Caribou Management BoardCARMA = CircumArctic Rangifer Monitoring and Assessment NetworkCOSEWIC = Committee on the Status of Endangered Wildlife in CanadaReferences cited in table:BQCMB. 2014. Beverly and Qamanirjuaq Caribou Management Plan 2013-2022. Beverly and Qamanirjuaq Caribou Management Board, Stonewall, MB. Available at http://arctic-caribou.com/pdf/bqcmb_managementplan_detailed2014.pdfCARMA. 2012. Caribou herd information. CircumArctic Rangifer Monitoring and Assessment Network. Web site: http://www.caff.is/carmaherds[accessed December 2012]COSEWIC. 2011. Designatable Units for Caribou (Rangifer tarandus) in Canada. Committee on the Status of Endangered Wildlife in Canada, Ottawa, ON. 88 pp. Available at http://www.cosewic.gc.ca/D37AB818-5F3B-44DC-9D56-EE22C63F4512/COSEWIC_Caribou_DU_Report_23Dec2011.pdfCOSEWIC. 2016. COSEWIC Status Report on Barren-ground caribou Rangifer tarandus in Canada. Draft - 2-month interim status report. Committee on the Status of Endangered Wildlife in Canada.Nagy, J.A., D. L. Johnson, N. C. Larter, M. W. Campbell, A. E. Derocher, A. Kelly, M. Dumond, D. Allaire, and B. Croft. 2011. Subpopulation structure of caribou (Rangifer tarandusL.) in arctic and subarctic Canada. Ecological Applications 21:2334–2348. http://dx.doi.org/10.1890/10-1410.1Poole, K. 2011. Methodology and sources for preparing seasonal shape files for caribou herds for CARMA. Unpublished document, Aurora Wildlife Research. 11 pp.",
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"description": "Barren-ground caribou annual ranges and calving areas by herd (i.e. subpopulation). The supplementary table BIO_ENR_WFE_SARA_AttributeTable contains additional attribute information for this species and its status and range in the NWT. All barren-ground caribou subpopulations considered by COSEWIC (2016) as part of Designatable Unit 3 are included in this shapefile. See COSEWIC (2011) for details on the Designatable Unit. Subpopulation structure of caribou (Rangifer tarandusL.) is as described by Nagy et al. (2011) for the Qamanirjuaq, Ahiak (i.e. Queen Maud Gulf), Beverly, Bathurst, Bluenose-East, Bluenose-West, Cape Bathurst, Lorillard and Wager Bay subpopulations. Other types of caribou (e.g. Dolphin and Union, Peary, mountain woodland, boreal woodland) are not included. Their ranges are available as separate NWT species at risk range shapefiles. 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In 2017, the Ahiak annual range was extended by B.Fournier (ENR) to cover the Queen Maud Gulf calving area produced by J.Nagy, when it was discovered that 2 areas in the northwest and northeast of the calving area were not covered by the annual range polygon.Calving ground E from Nagy et al. (2011) Fig. 1QamanirjuaqGeneralized annual range polygon from Nagy et al. (2011) Fig. 3, based on mean 90% utilization distribution from accumulated collar data 1993-2008Based on BQCMB compilation of all data from government surveys (1963-2008) and telemetry (1993-2012). See Poole (2011) for details.Polygons are as displayed by BQCMB (2014) as well as Nagy et al. (2011, Fig. 1, calving ground G).LorillardGeneralized annual range polygon from Nagy et al. (2011) Fig. 3, based on mean 90% utilization distribution from accumulated collar data 1998-2007Calving ground H from Nagy et al. (2011) Fig. 1Wager BayGeneralized annual range polygon from Nagy et al. 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Polygon not availableAcronyms:BQCMB = Beverly and Qamanirjuaq Caribou Management BoardCARMA = CircumArctic Rangifer Monitoring and Assessment NetworkCOSEWIC = Committee on the Status of Endangered Wildlife in CanadaReferences cited in table:BQCMB. 2014. Beverly and Qamanirjuaq Caribou Management Plan 2013-2022. Beverly and Qamanirjuaq Caribou Management Board, Stonewall, MB. Available at http://arctic-caribou.com/pdf/bqcmb_managementplan_detailed2014.pdfCARMA. 2012. Caribou herd information. CircumArctic Rangifer Monitoring and Assessment Network. Web site: http://www.caff.is/carmaherds[accessed December 2012]COSEWIC. 2011. Designatable Units for Caribou (Rangifer tarandus) in Canada. Committee on the Status of Endangered Wildlife in Canada, Ottawa, ON. 88 pp. Available at http://www.cosewic.gc.ca/D37AB818-5F3B-44DC-9D56-EE22C63F4512/COSEWIC_Caribou_DU_Report_23Dec2011.pdfCOSEWIC. 2016. COSEWIC Status Report on Barren-ground caribou Rangifer tarandus in Canada. Draft - 2-month interim status report. Committee on the Status of Endangered Wildlife in Canada.Nagy, J.A., D. L. Johnson, N. C. Larter, M. W. Campbell, A. E. Derocher, A. Kelly, M. Dumond, D. Allaire, and B. Croft. 2011. Subpopulation structure of caribou (Rangifer tarandusL.) in arctic and subarctic Canada. Ecological Applications 21:2334–2348. http://dx.doi.org/10.1890/10-1410.1Poole, K. 2011. Methodology and sources for preparing seasonal shape files for caribou herds for CARMA. Unpublished document, Aurora Wildlife Research. 11 pp.",
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(2011) Fig. 3, based on mean 90% utilization distribution from accumulated collar data 1996-2008Calving ground D from Nagy et al. (2011) Fig. 1BeverlyGeneralized annual range polygon from Nagy et al. (2011) Fig. 3, based on mean 90% utilization distribution from accumulated collar data 1995-2008There are 2 polygons, a northern and a southern calving ground. Based on BQCMB compilation of all data from government surveys (1957-2011) and telemetry (1996-2012). See Poole (2011) for details.Polygons are as displayed by BQCMB (2014) as well as Nagy et al. (2011, Fig. 1, calving grounds E-1 and F).AhiakGeneralized annual range polygon for ‘Queen Maud Gulf’ from Nagy et al. (2011) Fig. 3, based on mean 90% utilization distribution from accumulated collar data 1996-2008. 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(2011) Fig. 3, based on mean 90% utilization distribution from accumulated collar data 2000-2006Calving ground I from Nagy et al. (2011) Fig. 1Boothia PeninsulaAs shown in COSEWIC (2016) Fig. 2. Digitized by B. Fournier, ENR, as instructed by COSEWIC (J. Ray) in 2015.Polygon not availableSouthampton IslandAs shown in COSEWIC (2016) Fig. 2. Digitized by B. Fournier, ENR, as instructed by Mitch Campbell (Govt of NU) in 2014, for the COSEWIC report. Used entire island as there were no quantitative seasonal range data available.Polygon not availableCoats IslandAs shown in COSEWIC (2016) Fig. 2. Digitized by B. Fournier, ENR, as instructed by Mitch Campbell (Govt of NU) in 2014, for the COSEWIC report. Used entire island as there were no quantitative seasonal range data available.Polygon not availableBaffin IslandAs shown in COSEWIC (2016) Fig. 2. Digitized by B. Fournier, ENR, from an image provided by Troy Pretzlaw (Govt of NU) in 2014, for the COSEWIC report. Polygon not availableAcronyms:BQCMB = Beverly and Qamanirjuaq Caribou Management BoardCARMA = CircumArctic Rangifer Monitoring and Assessment NetworkCOSEWIC = Committee on the Status of Endangered Wildlife in CanadaReferences cited in table:BQCMB. 2014. Beverly and Qamanirjuaq Caribou Management Plan 2013-2022. Beverly and Qamanirjuaq Caribou Management Board, Stonewall, MB. Available at http://arctic-caribou.com/pdf/bqcmb_managementplan_detailed2014.pdfCARMA. 2012. Caribou herd information. CircumArctic Rangifer Monitoring and Assessment Network. Web site: http://www.caff.is/carmaherds[accessed December 2012]COSEWIC. 2011. Designatable Units for Caribou (Rangifer tarandus) in Canada. Committee on the Status of Endangered Wildlife in Canada, Ottawa, ON. 88 pp. Available at http://www.cosewic.gc.ca/D37AB818-5F3B-44DC-9D56-EE22C63F4512/COSEWIC_Caribou_DU_Report_23Dec2011.pdfCOSEWIC. 2016. COSEWIC Status Report on Barren-ground caribou Rangifer tarandus in Canada. Draft - 2-month interim status report. Committee on the Status of Endangered Wildlife in Canada.Nagy, J.A., D. L. Johnson, N. C. Larter, M. W. Campbell, A. E. Derocher, A. Kelly, M. Dumond, D. Allaire, and B. Croft. 2011. Subpopulation structure of caribou (Rangifer tarandusL.) in arctic and subarctic Canada. Ecological Applications 21:2334–2348. http://dx.doi.org/10.1890/10-1410.1Poole, K. 2011. Methodology and sources for preparing seasonal shape files for caribou herds for CARMA. Unpublished document, Aurora Wildlife Research. 11 pp.",
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"description": "Barren-ground caribou annual ranges and calving areas by herd (i.e. subpopulation). The supplementary table BIO_ENR_WFE_SARA_AttributeTable contains additional attribute information for this species and its status and range in the NWT. All barren-ground caribou subpopulations considered by COSEWIC (2016) as part of Designatable Unit 3 are included in this shapefile. See COSEWIC (2011) for details on the Designatable Unit. Subpopulation structure of caribou (Rangifer tarandusL.) is as described by Nagy et al. (2011) for the Qamanirjuaq, Ahiak (i.e. Queen Maud Gulf), Beverly, Bathurst, Bluenose-East, Bluenose-West, Cape Bathurst, Lorillard and Wager Bay subpopulations. Other types of caribou (e.g. Dolphin and Union, Peary, mountain woodland, boreal woodland) are not included. Their ranges are available as separate NWT species at risk range shapefiles. 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(2011) Fig. 3, based on mean 90% utilization distribution from accumulated collar data 1996-2008Calving ground D from Nagy et al. (2011) Fig. 1BeverlyGeneralized annual range polygon from Nagy et al. (2011) Fig. 3, based on mean 90% utilization distribution from accumulated collar data 1995-2008There are 2 polygons, a northern and a southern calving ground. Based on BQCMB compilation of all data from government surveys (1957-2011) and telemetry (1996-2012). See Poole (2011) for details.Polygons are as displayed by BQCMB (2014) as well as Nagy et al. (2011, Fig. 1, calving grounds E-1 and F).AhiakGeneralized annual range polygon for ‘Queen Maud Gulf’ from Nagy et al. (2011) Fig. 3, based on mean 90% utilization distribution from accumulated collar data 1996-2008. In 2017, the Ahiak annual range was extended by B.Fournier (ENR) to cover the Queen Maud Gulf calving area produced by J.Nagy, when it was discovered that 2 areas in the northwest and northeast of the calving area were not covered by the annual range polygon.Calving ground E from Nagy et al. (2011) Fig. 1QamanirjuaqGeneralized annual range polygon from Nagy et al. (2011) Fig. 3, based on mean 90% utilization distribution from accumulated collar data 1993-2008Based on BQCMB compilation of all data from government surveys (1963-2008) and telemetry (1993-2012). See Poole (2011) for details.Polygons are as displayed by BQCMB (2014) as well as Nagy et al. (2011, Fig. 1, calving ground G).LorillardGeneralized annual range polygon from Nagy et al. (2011) Fig. 3, based on mean 90% utilization distribution from accumulated collar data 1998-2007Calving ground H from Nagy et al. (2011) Fig. 1Wager BayGeneralized annual range polygon from Nagy et al. (2011) Fig. 3, based on mean 90% utilization distribution from accumulated collar data 2000-2006Calving ground I from Nagy et al. (2011) Fig. 1Boothia PeninsulaAs shown in COSEWIC (2016) Fig. 2. Digitized by B. Fournier, ENR, as instructed by COSEWIC (J. Ray) in 2015.Polygon not availableSouthampton IslandAs shown in COSEWIC (2016) Fig. 2. Digitized by B. Fournier, ENR, as instructed by Mitch Campbell (Govt of NU) in 2014, for the COSEWIC report. Used entire island as there were no quantitative seasonal range data available.Polygon not availableCoats IslandAs shown in COSEWIC (2016) Fig. 2. Digitized by B. Fournier, ENR, as instructed by Mitch Campbell (Govt of NU) in 2014, for the COSEWIC report. Used entire island as there were no quantitative seasonal range data available.Polygon not availableBaffin IslandAs shown in COSEWIC (2016) Fig. 2. Digitized by B. Fournier, ENR, from an image provided by Troy Pretzlaw (Govt of NU) in 2014, for the COSEWIC report. Polygon not availableAcronyms:BQCMB = Beverly and Qamanirjuaq Caribou Management BoardCARMA = CircumArctic Rangifer Monitoring and Assessment NetworkCOSEWIC = Committee on the Status of Endangered Wildlife in CanadaReferences cited in table:BQCMB. 2014. Beverly and Qamanirjuaq Caribou Management Plan 2013-2022. Beverly and Qamanirjuaq Caribou Management Board, Stonewall, MB. Available at http://arctic-caribou.com/pdf/bqcmb_managementplan_detailed2014.pdfCARMA. 2012. Caribou herd information. CircumArctic Rangifer Monitoring and Assessment Network. Web site: http://www.caff.is/carmaherds[accessed December 2012]COSEWIC. 2011. Designatable Units for Caribou (Rangifer tarandus) in Canada. Committee on the Status of Endangered Wildlife in Canada, Ottawa, ON. 88 pp. Available at http://www.cosewic.gc.ca/D37AB818-5F3B-44DC-9D56-EE22C63F4512/COSEWIC_Caribou_DU_Report_23Dec2011.pdfCOSEWIC. 2016. COSEWIC Status Report on Barren-ground caribou Rangifer tarandus in Canada. Draft - 2-month interim status report. Committee on the Status of Endangered Wildlife in Canada.Nagy, J.A., D. L. Johnson, N. C. Larter, M. W. Campbell, A. E. Derocher, A. Kelly, M. Dumond, D. Allaire, and B. Croft. 2011. Subpopulation structure of caribou (Rangifer tarandusL.) in arctic and subarctic Canada. Ecological Applications 21:2334–2348. http://dx.doi.org/10.1890/10-1410.1Poole, K. 2011. Methodology and sources for preparing seasonal shape files for caribou herds for CARMA. Unpublished document, Aurora Wildlife Research. 11 pp.",
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"description": "Tlicho Land Use Plan approved April 25, 2013 and comes into effect June 1, 2013.Norm Mair (GIS Specialist/NWTCG) - September 11, 2013 - Received this data from Sjoerd van der Wielen/GIS Technician/Tlicho Government. http://www.tlicho.ca/news/press-release-t%C5%82%C4%AFch%C7%AB-land-use-plan-effect-june-1-2013On Thursday, April 25, 2013, the Tłı̨chǫGovernment approved the Tłı̨chǫLands Protection Amendment Law 2013 and the Tłı̨chǫLand Use Plan Law, which brings into effect the Tłı̨chǫWene’ke or Tłı̨chǫLand Use Plan. “The Tłı̨chǫLand Use Plan is a significant accomplishment for the Tłı̨chǫGovernment as it has been a work in progress for seven years” said Grand Chief Eddie Erasmus. “This Tłı̨chǫLand Use Plan represents the Tłı̨chǫvision for use of our lands that protects the land while recognizing that opportunities may be out there for land use proposals.”Plan development was guided by the Tłı̨chǫelders who considered their knowledge of the land of the past and present to determine how Tłı̨chǫlands would look in the future. The Tłı̨chǫLand Use Plan will come into effect on June 1, 2013. At that time the moratorium on Tłı̨chǫLands will be lifted and Tłı̨chǫwill start considering proposals and applications for uses on Tłı̨chǫLands.October 2018 names field was edited, in conjunction with Michael Birlea of the Tlicho Gov't, to correspond correctly with the Land Use Plan.",
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"description": "Heritage ValueNagwichoonjik (Mackenzie River) was designated a national historic site of Canada because:- it is prominent as a cultural landscape within the Gwichya Gwich’in traditional territory;- it is culturally, socially and spiritually significant to the people; - the history of life on the land and along the river is remembered through names that are given to a great number of places on the land and along the river.The heritage value of Nagwichoonjik (Mackenzie River) is reflected in the cultural landscape along the river that reflects the river’s role as a principal repository of the stories (oral histories) that suffuse with meaning the history of the landscape as the Gwichya Gwich’in know it. The traditional lifestyle of the Gwichya Gwich’in has been shaped by their close connection with the land and the river, and many points along the river play an essential role in the transmission and survival of Gwich’in culture. Nagwichoonjik represents the complex sets of relationships between the Gwich’in people, their traditional lands and their past, before and after the arrival of the European explorers.Sources: Historic Sites and Monuments Board of Canada Minutes, June 1997; Commemorative Integrity Statement.Character-Defining ElementsKey elements that contribute to the heritage character of the site include:- the Mackenzie River and the land along its banks between Thunder River and Point Separation in its location and as a dramatic river valley consisting of a wide waterway, beaches, high cliffs in some places and gentle slopes in others, cut with many creeks, and displaying human impacts from pre-contact to modern times;- archaeological evidence of Gwich’in use, including camps, settlements, fisheries, quarries, connecting trails and trail heads, burial places, ritual and sacred places;- the health and wholeness of the riparian ecosystem (its water quality, quantity, rates of flow, sandbars and siltation, fish quality, the health of species such as inconnu and moose;- the undisturbed land and unimpeded views of the river and along the valley from the river; - sacred sites along the river (currently being identified by the Gwich’in Cultural Institute);- ritual sites along the river (currently being identified by the Gwich’in Cultural Institute);- Gwich’in knowledge of traditional place names along the river.Historic Sites and Monuments Act, 1997/06/05from: http://www.historicplaces.ca/en/rep-reg/place-lieu.aspx?id=9161Nagwichoonjik is managed by the Gwich’in Tribal Council, a First Nations governing body established pursuant to the Gwich’in Comprehensive Land Claim Agreement (1992), working in co-operation with Gwich’in organizations like the Gwichya Gwich’in Council of Tsiigehtchic and Gwich’in Social and Cultural Institute along with various government agencies including Parks Canada. Parks Canada has worked closely with these Gwich’in organizations in developing a Commemorative Integrity Statement for the Nagwichoonjik National Historic Site of Canada. This important document identifies what is meant by commemorative integrity at this site and forms the basis for future planning, management and operation of the Nagwichoonjik National Historic Site of Canada. (http://www.pc.gc.ca/APPS/CP-NR/release_e.asp?bgid=618&andor1=bg)The Nagwichoonjik National Historic Site was designated in 1997 as an Aboriginal Cultural Landscape. It includes a 175 km stretch of the Mackenzie River from Vihtr'ii Tshik (Thunder River) to Srehtadhadlâîî (Point Separation), making it the largest National Historic Sitein Canada. The boundaries of the site reach 5 km inland from the river to ensure that all the major archaeological and cultural sites affiliated with it are included (The Canadian Encyclopedia, http://www.thecanadianencyclopedia.com/index.cfm?PgNm=TCE&Params=A1ARTA0010484)",
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"description": "The Contaminants and Remediation Directorate (CARD) is currently responsible for nearly 100 contaminated sites in the NWT, at various stages of remediation (clean up). This directorate brings together all of the work done by Indigenous and Northern Affairs Canada (INAC) associated with federal contaminated sites in the NWT. Many of these legacy sites became the Government of Canada's responsibility after private owners relinquished their properties according to the legislation of the day, or when companies went bankrupt. In past years, the properties then reverted to the Crown, and as representative of the Crown, INAC became custodian of these properties and related remediation activities. With new regulations in place that require new development to support the future costs of reclamation, similar reversions are prevented.10-Step Federal Approach to Contaminated SitesINAC follows a defined 10-step process for addressing federal contaminated sites to ensure that there is a common approach to the management of contaminated sites. For the purposes of mapping which stage the NWT sites are in, the 10-step process has been broken into 5 categories: Assessment, Pre-Remediation (Priority Site), Remediation, Monitoring, and Remediated/Closed. Assessment Step 1: INAC identifies sites that might be contaminated, based on activities (past or current) on or near the site.*Step 2: INAC assembles and reviews all historical information pertaining to the site.Step 3: INAC begins initial testing, which helps us to start to characterize the type of contamination at the site, and determine what condition the site is in.Step 4: INAC classifies the contaminated site using the Canadian Council of Ministers of the Environment (CCME) National Classification System. It is then assigned a priority for future investigations and remediation or risk management actions.Pre-remediationStep 5: INAC tests specific areas of concern identified in Step 3, and does in-depth investigations and analysis.Step 6: If necessary and depending on the result of the investigation, INAC reclassifies the site’s priority ranking. Step 7: INAC engages partners, Aboriginal communities, and stakeholders to develop a site-specific remediation or risk management plan to address contamination issues.Remediation Step 8: INAC implements the site specific remediation or risk management plan that addresses contamination issues.Step 9: INAC conducts confirmatory sampling and analysis to make sure the remediation was successful.Monitoring Step 10: INAC conducts long-term monitoring to make sure that remediation and long-term risk management goals are achieved, as required. Once the site is completely remediated, it may be closed (Remediated/Closed, 14 sites in the NWT are currently in this phase).Remediated SitesFor sites where the monitoring phase is complete or for sites where all contaminants have been removed from site and therefore there is no residual risk to manage, they have been listed under \"Remediated Sites\". Those that existed prior to Devolution were transferred to the GNWT. New sites that become \"Remediated Sites\" could be considered for future land transfer.* Note that traditional knowledge is used throughout the project lifecycle, from assessment through to monitoring and closure.For more information on the identified contaminated sites, visit:www.aadnc-INAC.gc.ca/eng/1100100026218/1100100026222Remediation of contaminated sites in the NWT is made possible with support from the Federal Contaminated Sites Action Plan (FCSAP), a program aimed at reducing the environmental and human health risk, and associated federal financial liabilities, from known federal contaminated sites. More information about FCSAP is available at:www.federalcontaminatedsites.gc.ca.IF YOU HAVE ANY QUESTIONS ABOUT SITES LISTED IN THIS DATASET, CONTACT US:Contaminants and Remediation DivisionIndigenous and Northern Affairs Canada, NWT RegionP.O. Box 1500Yellowknife, NT X1A 2R3Phone: 867 669 2416Fax: 867 669 2721ntcard@aandc-aadnc.gc.caLa Direction des polluants et de l’assainissement (DPA) compte actuellement sous sa responsabilité plus de 100sites contaminés dans les Territoires du Nord-Ouest (T.N.-O.) qui en sont à diverses étapes d’assainissement (dépollution). La Direction travaille à réunir toutes les activités d’Affaires autochtones et Développement du Nord Canada (AADNC) liées aux sites contaminés fédéraux dans les T.N.-O. Bon nombre de ces sites contaminés sont passés sous la responsabilité du gouvernement du Canada lorsque des exploitants privés se sont départis de leurs propriétés, conformément à la législation de l’époque, ou lorsque des entreprises ont déclaré faillite. Au fil des ans, les propriétés ont été retournées à la Couronne, et AADNC, en qualité de représentant de la Couronne, en a assumé la garde ainsi que la responsabilité des activités d’assainissement s’y rattachant. Pour éviter d’autres réversions similaires, de nouvelles dispositions réglementaires prévoient désormais la prise en charge des coûts de la remise en état par les exploitants.Les 10 étapes de l’Approche fédérale en matière de lieux contaminésPour garantir une gestion uniforme des sites contaminés fédéraux, AADNC applique un processus en 10 étapes. Afin d’aider à connaître la progression à l’égard des sites dans les T.N.-O., les étapes sont regroupées sous l’une des cinq étapes suivantes : évaluation, activités préalables à l’assainissement (site prioritaire), assainissement, surveillance et assainissement terminé/fermeture. Évaluation (19 sites dans les T.N.-O.)Étape 1 : AADNC cerne les sites qui pourraient être contaminés d’après les activités (passées ou présentes) menées sur ce site ou à proximité.Étape 2 : AADNC recueille et examine toutes les données historiques se rapportant au site.Étape 3 : AADNC amorce les essais, ce qui permet de commencer à définir le type de contamination au site et de déterminer la condition de ce dernier.Étape 4 : AADNC classifie le site contaminé au moyen du Système national de classification (SNC) des sites contaminés du Conseil canadien des ministres de l’Environnement (CCME). Il est ensuite possible d’attribuer un ordre de priorité au site en vue des activités futures d’analyse, d’assainissement ou de gestion du risque.Activités préalables à l’assainissement (site prioritaire) (63 sites dans les T.N.-O.)Étape 5 : AADNC mène des essais dans les zones préoccupantes relevées à l’étape 3 et procède à une étude et à une analyse plus approfondies.Étape 6 : AADNC révise la classification de la priorité du site, au besoin et en fonction des résultats de l’analyse. Étape 7 : AADNC fait appel à des partenaires, aux collectivités autochtones et aux parties prenantes afin d’élaborer un plan d’assainissement ou de gestion du risque propre au site en vue du traitement des problèmes de contamination.Assainissement (4 sites dans les T.N.-O.)Étape 8 : AADNC met en œuvre le plan d’assainissement ou de gestion du risque propre au site en vue du traitement des problèmes de contamination.Étape 9 : AADNC procède à l’échantillonnage de confirmation et à l’analyse pour confirmer la réussite des activités d’assainissement.Surveillance (9 sites dans les T.N.-O.)Étape 10 : AADNC mène une surveillance à long terme afin de veiller à l’atteinte des objectifs d’assainissement et de gestion durable du risque, suivant les besoins.Une fois les activités d’assainissement terminées à un site, il est possible de fermer ce dernier (assainissement terminé/fermeture, 14 sites dans les T.N.-O.).Pour obtenir de plus amples renseignements sur les sites contaminés connus, visitez le site suivant : http://www.aadnc-aandc.gc.ca/fra/1100100026218/1100100026222.L’assainissement des sites contaminés dans les T.N.-O. a été mis en œuvre grâce à l’appui du Plan d’action pour les sites contaminés fédéraux (PASCF), programme visant à réduire le risque pour la santé humaine et l’environnement ainsi que le fardeau financier fédéral associé aux sites contaminés fédéraux. Pour obtenir plus d’information sur le PASCF, rendez-vous à l’adresse : www.sitescontaminesfederaux.gc.ca.Si vous avez des questions relatives aux sites de votre région, veuillez communiquer avec nous.Direction des polluants et de l’assainissementAffaires autochtones et Développement du Nord Canada, bureau régional des T.N.-O.C.P. 1500Yellowknife (T.N.-O.) X1A 2R3Téléphone : 867-669-2416Télécopieur : 867-669-2721Courriel : ntcard@aandc-aadnc.gc.ca",
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"description": "January 23, 2023The following are what it contains (252 entities in total) when classified using codes in the AGREEETYP:EL = Exploration Licence - count = 0PL = Production Licence - count = 20PPL = Oil and gas lease under former regulations, a Pioneer Production Lease - count = 1SDL = Significant Discovery Licence - count = 90CDD = Commercial Discovery Declaration - count = 16SDD = Significant Discovery Declaration - count = 125Two SDLs were surrrendered, and three PLs were surrenedered since the March 2021 version.March 11, 2021The following are what it contains (257 entities in total) when classified using codes in the AGREEETYP:EL = Exploration Licence - count = 0PL = Production Licence - count = 23PPL = Oil and gas lease under former regulations, a Pioneer Lease - count = 1SDL = Significant Discovery Licence - count = 92CDD = Commercial Discovery Declaration - count = 16SDD = Significant Discovery Declaration - count = 125The following updates were applied to licences and leases:SDL 150 corrected a lowercase LAND_CODE reference in the original Land Administration System (LAS4Land) database.SDL152, 154: Corrected some anomalous land description missing element in the orginal LAS4Land database.SDL 153: Issuance of Husky Oil Ltd. significant discovery licence (SDL153) in August of 2020, signed by the Minister in January of 2021. Issuance of this SDL has converted the last remaining, as of March 11, 2021, Exploration Licence in the NWT into a Significant Discovery Licence.Correction of various (Perimieter, Hectare, Area_km2 and ACRE), calculations that hadn't been updated in one or two iterations of the data set.Prarie Provident Resources Ltd. the new owners of all the Pioneer Production Leases in the Liard area have surrendered all their titles except for one section of PPL 838-70, which still has one suspended well on the lease.Representatitves i.e. \"COMPANY_NM\" field names have been updated to reflect the current representatives for each title.June 11, 2019The following updates were applied to SDLs 152 and 156:Current Hectares were re-calculated due to some anomolies in the original source database:SDL152:CURRENT_HECTARES: 50,262It was formerly:CURRENT_HECTARES: 49,991SDL156:CURRENT_HECTARES: 25,276It was formerly:CURRENT_HECTARES: 13,411July 31, 2017 - Updates to the NWT Oil and Gas Rights Feature Class:The following are what it contains (272 entities in total) when classified using codes in the AGREEETYP:EL = Exploration Licence - count = 8PL = Production Licence - count = 8PPL = Oil and gas lease under former regulations, a Pioneer Lease - count = 8SDL = Significant Discovery Licence - count = 92CDD = Commercial Discovery Declaration - count = 16SDD = Significant Discovery Declaration - count = 125A point of clarification for SDL079-NWT. This SDL has multiple owners at different stratigraphic horizons and different percentages at those horizons although the COMPANY_NM field only shows one owner, which is in fact the representative of all companies which are co-licencees of the SDL. Also of note, when displaying SDL079-NWT with Indigenous and Northern Affairs Canada's (INAC) oil and gas rights, there is an area of overlap between SDL079-NWT and SDL079-CAN (the NWT portion and government of Canada's portion). This is because at the time of devolution when the oil and gas rights were being split along jurisdictional boundaries, there was no surveyed delimitation accurate enough for the purposes of splitting these rights in this location. In the Definitions section of the Final Devolution Agreement document, states the following:(ttt) \"Onshore\" means,(i) lands, including lands under water, that lie landward of the low waterline (high-water line in respect of Settlement Lands ownedby the IRC) of the sea coast of the mainland or any naturallyoccurring permanent island in that part of Canada lying north ofthe sixtieth parallel of north latitude and not within Yukon,Nunavut or any province;(ii) lands under water within Small Enclosed Bays along the seacoast of the mainland or any naturally occurring permanentisland in that part of Canada referred to in paragraph (i); and(iii) lands, including lands under water, that lie landward of the Lineof Delimitation and seaward of the low-water line of the seacoast of the mainland in that part of Canada referred in toparagraph (i),but does not include any lands seaward of the Line of Delimitationother than the lands on the islands referred to in paragraph (i) or landsunder water within Small Enclosed Bays along the sea coast of suchislands referred to in paragraph (ii).This means that within the Inuvialuit Settlement Region that all lands landward of the high water mark the Government of the Northwest Territories (GNWT) has jurisdiction. Seaward of the high water mark, the Government of Canada has jurisdiction. The complication comes due to the lack of any official land / marine survey which clearly and legally defines the high water mark in the area of SDL079-NWT / SDL079-CAN, therefore until a legal survey is complete delineating this break and applying it to the SDL there must remain an overlap between the NWT and Government of Canada boundary definitions.The boundary of SDL012 at the Yukon / Northwest Territories border was edited to topologically refect the boundary of the Northwest Territories border at 1:1,000,000 scale. The boundary used to match the SDL against was teh Atlast of Canada 1:1,000,000 boundary, which can be found here: http://ftp.geogratis.gc.ca/pub/nrcan_rncan/vector/framework_cadre/Atlas_of_Canada_1M/. The Yukon government uses a different base to \"trim\" the edge of their portion of the licences that fall within thir jurisdiction. Based on the nomenclature of their filename, presumably at 1:50,000 scale, but there is no publicly available base at 1:50,000 that depicts the boundary between the Yukon and the Northwest Territories, as a GIS data set that the editior of this GIS data set has found that will allow trimming SDL012 to, therefore at the present time SDL012 has been made topologically consistant to the boundary of the Atlas of Canada 1:1,000,000 Northwest Territories boundary.February 2, 2017 - Updates to the NWT Oil and Gas Rights Feature Class:The following are what it contains (271 entities in total) when classified using codes in the AGREEETYP:EL = Exploration Licence - count = 15PL = Production Licence - count = 23PPL = Oil and gase lease under former regulations, a Pioneer Lease - count = 8SDL = Significant Discovery Licence - count = 84CDD = Commercial Discovery Declaration - count = 16SDD = Significant Discovery Declaration - count = 125April 25, 2016 - Updates to the NWT Oil and Gas Rights Feature Class:In order to accomodate the additional information indicating the responsible authority editing and or creating new land tenture parcels, or updating the attributes of land tenure parcels, additional fields were created within the feature class. These new fields are:EDIT_DTE: The date the record / parcel attribute was updated.EDIT_ORG_E: The organization that edited the parcel (English).EDIT_ORG_F: The organization that edited the parcel (French).ORIG_ORG_E: The original organization that created the parcel (English).ORIG_ORG_F: The original organization that created the parcel (French).The following are what it contains (270 entities in total) when classified using codes in the AGREEETYP:EL = Exploration Licence - count = 15PL = Production Licence - count = 23PPL = Oil and gase lease under former regulations, a Pioneer Lease - count = 8SDL = Significant Discovery Licence - count = 84CDD = Commercial Discovery Declaration - count = 16SDD = Significant Discovery Declaration - count = 124April 1, 2014 - As part of Devolution, Neil Rask (Geomatics Officer, AANDC) and Lloyd Thiessen (Database and Systems Technician) using the Licencing and Administration System (LAS) in Inuvik, exported all licences to a shapefile which was imported to this feature class. LAS is part of the Petroleum Resources Division with ITI in Inuvik. The following are what it contains (267 entities in total) when classified using codes in the AGREEETYP:EL = Exploration Licence - count = 16PL = Production Licence - count = 23PPL = Oil and gase lease under former regulations - count = 8SDL = Significant Discovery Licence - count = 81CDD = Commercial Discovery Declaration - count = 16SDD = Significant Discovery Declaration - count = 123The digital boundaries provided have been generalized and may contain errors. Users should be alert to limitations with respect to resolution. The digital files are provided in shapefile format Attribute data contains: Title Id, Representative Name, Region, Date of Issuance, Expiry Date, and Area (hectares). These files are updated on a regular basis but may not be current on a particular day. 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"description": "Digital boundaries for existing exploration licences, significant discovery licences, production licences, former permits, former leases and the Norman Wells Proven Area are available for download. The digital boundaries provided have been generalized and may contain errors. Users should be alert to limitations with respect to resolution. The digital files are provided in shapefile format Attribute data contains: Title Id, Representative Name, Region, Date of Issuance, Expiry Date, and Area (hectares). These files are updated on a regular basis but may not be current on a particular day. Clients are cautioned to contact the Rights Administrator to confirm the accuracy or currency of information contained herein.Users should note that the legal descriptions of these rights using grid and section number as prescribed by the Canada Oil and Gas Lands Regulations are to be found in the title documents, copies of which may be obtained on application to the Registar. Users should also note that the digital file is incomplete for Hudson Bay: outlines of old oil and gas permits in this area will be added in due course. Exploration is not active in this area. Queries regarding specific licences should be addressed to the Rights Administrator, Northern Oil and Gas Directorate, telephone 819-639-7318. Data is updated on an irregular basis and will be checked for updates on the last Wednesday of March, June, September and December. If updates are required within these time frame the data can be updated.Data was downloaded by Norm Mair early October 2013 as RTS.shp.Data was updated by Shawn Larocque June 2017 with rts.shp transformed from NAD 27 to NAD 83. Data current as of February 3, 2017.",
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