The intention is to show the boundaries of all refuges in Manitoba, as designated by the Designation of Wildlife Lands Regulation (171/2001) under The Wildlife Act (C.C.S.M. c. W130). Refuge types include Wildlife Refuge, Game Bird Refuge, Goose Refuge, and Fur Bearing Animal Refuge. The Use of Wildlife Lands Regulation (77/99) determines what activities are prohibited within each refuge.Boundaries are drawn based on the physical description described in regulation, or imported using CAD files from the official Director of Surveys Plan stated in regulation.

Wildlife Refuges in Saskatchewan.The Saskatchewan Wildlife Refuges are described in Part V of the Wildlife Management Zones and Special Areas Boundaries Regulation (WMZSABR). They are constituted as areas for protecting, propagating, managing, controlling, regulating or enhancing wildlife or its habitat.

Punctual location of the refuges on the Route Blanche.The Route Blanche is a snowmobile trail located on the Lower North Shore, constituting the only winter land link between Kegaska and Blanc-Sablon, thus bridging the road link between municipalities. Note: The White Road shelters are already part of the “Establishment” dataset https://www.donneesquebec.ca/recherche/dataset/etablissement-du-mtq (see “Refuge” in the “typetablis” attribute column). The need is to be able to have a metadata sheet to describe its distinction from other establishments in the Ministry and to be able to download the dataset exclusively (without obtaining all the institutions).**This third party metadata element was translated using an automated translation tool (Amazon Translate).**

Biological refuges are small forest areas located on the domain of the State and permanently removed from forest management activities in order to maintain the biological diversity associated with old forests. Their management is under the responsibility of the Ministry of Natural Resources and Forests (MRNF). Forest management activities are prohibited on the territory of a biological refuge, with few exceptions. There are currently 3,704 biological refuges in Quebec, distributed relatively uniformly throughout managed forests in the domain of the State. Biological refuges can be designated under the Sustainable Forest Development Act (LADTF, chapter A-18.1) or in draft before legal designation. Legally designated organic refuges make up the vast majority. They are exempt from industrial activities, which allows them to be registered in the Quebec Register of Protected Areas (RAP) maintained by the Ministry of the Environment and the Fight against Climate Change, Wildlife and Parks (MELCCFP).This data comes from the MRNF STF system, which is the __official source__ of this geographic information.**This third party metadata element was translated using an automated translation tool (Amazon Translate).**

The Wildlife Refuge feature class provides the geographical boundaries (polygons) of New Brunswick's Wildlife Refuges and Wildlife Management Areas. Most of these entities were established in the mid 1900s for the management of wildlife species that were hunted, trapped or snared by providing areas where hunting, trapping or snaring could be prohibited or restricted. Some areas were included because they were recognized tourist destinations (Acadian Village and Kings Landing Wildlife Management Areas) or other areas designated for "protection". As of early 2008, hunting, trapping and snaring is not allowed in any Wildlife Refuge and some Wildlife Management Areas; while in some Wildlife Management Areas trapping and snaring are allowed but no hunting; and in other Wildlife Management Areas hunting, trapping and snaring are allowed; ie, no restrictions.Most of New Brunswick's Wildlife Refuges and Wildlife Management Areas were established in the mid-1900s for the management of wildlife species that were hunted, trapped or snared by providing areas where those activities could be prohibited or restricted. Some areas were included because they were recognized tourist destinations (Acadian Village and Kings Landing Wildlife Management Areas) or other areas designated for "protection". 1. 2.Do not confuse Wildlife Refuges and Wildlife Management Areas with Wildlife Management Zones (WMZ GIS layer).

Habitat Protection and management are the primary focus of the Fish and Wildlife Development fund. This data includes lands used for management of habitat within the Province.Saskatchewan Environment's Fish and Wildlife Development Fund Lands (FWDF) derived from ISC's (1:20,000) surface layer.As anglers, hunters and trappers in Saskatchewan, you recognize that healthy and diverse wildlife populations are an indication of a healthy ecosystem. Your responsible conservation ethic and love of nature are making positive and vital contributions to the management and preservation of wildlife and wildlife habitat. The revenue (30 per cent) from all fur, angling and hunting licences you purchase, is used to manage, preserve and enhance fish and wildlife habitat.The fund has identified three fish and wildlife management goals:-Maintain natural habitat through conservation, biodiversity, land management and awareness of rare species.-Maintain and grow sustainable fish populations and their habitat.-Maintain game populations and ensure accessible hunting.

Speckled Dace (Rhinichthys osculus) are listed under the Species at Risk Act (SARA) as endangered. These fresh water fish, of the family Cyprinidae, are found in Canada only in the Kettle Valley of British Columbia. Proposed critical habitat was based on minimum viable population analysis and assumed densities of fish. From October 19th to the 22nd of 2015, night time pole seining surveys were conducted to enumerate Speckled Dace in proposed critical habitat on the West Kettle River; one of three rivers containing Speckled Dace. The estimated population abundance of Speckled Dace within the survey area was 8,978 (6,143-11,814), however only 1,014 of these are estimated to be adults.

A relative exposure index (REI), unweighted fetch, effective fetch, and other fetch-based indices (i.e., sum, minimum) were calculated for the Newfoundland and Labrador (NL) Shelves bioregion. Due to the extensive coastline of the study region, this analysis was conducted for a 5km buffered region along the coast at a spatial resolution of 250m. Detailed methods on the selection of input points for the NL bioregion are included below.MethodsPreprocessing and input point selection:Land boundary files were obtained for Eastern Canada and the Canadian Arctic (NrCan 2017) at a scale of 1:50,000 as well as for Saint Pierre and Miquelon (Hijmans 2015), and the New England states (GADM 2012) however the scale at which these layers were produced is unknown. Land boundary files were merged into a single land polygon layer and watercourses reaching for in-land and/or above sea level were clipped from this polygon layer (Greyson 2021). A 5km buffer was generated around the NL provincial boundary. This buffer was then clipped by all land polygons to remove areas overlapping land polygons within the study area. All buffer segments intersecting the NAFO divisions within the NL bioregion were selected and the Union tool in ArcGIS Pro (v. 2.7.2) was used to fill-in gaps within the buffered area, creating a more continuous polygon. The buffered layer was then dissolved, and the NL provincial boundary polygon was erased from the buffered layer to create the study area polygon. A 250m fishnet was created and clipped to the study area (5km buffer layer) and the feature to point tool was used (with the “inside parameter checked”) to convert this grid into a point layer (approx. 1,000,000 points). The spatial resolution for all subsequent analyses was matched to the fishnet grid at 250m.ReferencesGADM database of Global Administrative Areas (2012). Global Administrative Areas, version 2.0. (accessed 2 December 2020). www.gadm.orgGreyson, P (2021) Land boundary file for Eastern Canada, the Canadian Arctic, the New England States and Saint Pierre and Miquelon. [shapefile]. Unpublished data.Hijmans, R. and University of California, Berkeley, Museum of Vertebrate Zoology. (2015). First-level Administrative Divisions, Saint Pierre and Miquelon, 2015. UC Berkeley, Museum of Vertebrate Zoology. Available at: http://purl.stanford.edu/bz573nv9230Natural Resources Canada (2017) Administrative Boundaries in Canada - CanVec Series - Administrative Features - Open Government Portal. (accessed 2 December 2020). https://open.canada.ca/data/en/dataset/306e5004-534b-4110-9feb-58e3a5c3fd97.

A Priority Place is an area of high biodiversity value that is seen as a distinct place with a common ecological theme by the people who live and work there. As part of the Pan-Canadian approach to transforming Species at Risk conservation in Canada, a total of 11 Priority Places were affirmed by federal, provincial, and territorial governments. One additional priority place was affirmed in 2024. The places selected have significant biodiversity, concentrations of species at risk, and opportunities to advance conservation efforts. In each Priority Place, the federal and provincial or territorial governments are working with Indigenous Peoples, partners, and stakeholders to develop conservation implementation plans. This dataset displays the geographic area covered by each of the 12 Priority Places using the best available information from the Canadian Wildlife Service (CWS). Boundary information for each Priority Place was provided by its respective CWS regional office.The federal government, in collaboration with the provinces and territories, has agreed to the implementation of the Pan-Canadian Approach to Transforming Species at Risk Conservation in Canada. This new approach shifts from a single-species approach to conservation to one that focuses on multiple species and ecosystems. This enables conservation partners to work together to achieve better outcomes for species at risk. These 12 Priority Places are complemented by a suite of Community-Nominated Priority Places (CNPP), identified through an open call for applications.

Modeled data showing the likely distribution of Northern fur seals. CRIMS is a legacy dataset of BC coastal resource data that was acquired in a systematic and synoptic manner from 1979 and was intermittently updated throughout the years. Resource information was collected in nine study areas using a peer-reviewed provincial Resource Information Standards Committee consisting of DFO Fishery Officers, First Nations, and other subject matter experts. There are currently no plans to update this legacy data.