Lake sturgeon's presence zones, breeding, feeding and concentration areas according to a literature review of documents produced between 1976 and 2002.Data extracted from the Fish Habitat Management Information System (FHAMIS).

Atlantic sturgeon. Important sites: reproduction, feeding juvenile and adult concentration area. Data extracted from the Fish Habitat Management Information System (FHAMIS) according to a literature review of documents produced between 1978 and 2002.

Off Road Vehicle (ORV) Trail Plan show the trails (whether individually or by zone) within the off-road vehicle management area or the part of the off-road vehicle management area for which a trail plan is developed, on which an off-road vehicle may be used. A red, yellow, green scheme is used to symbolize the level of restriction on the trail plan. Red: off road vehicles are prohibited; Yellow: off road vehicles are prohibited except where designated by an approved Off Road Management Area Trail Plan; Green: off road vehicles are not prohibitedDistributed from [GeoYukon](https://yukon.ca/geoyukon) by the [Government of Yukon](https://yukon.ca/maps) . Discover more digital map data and interactive maps from Yukon's digital map data collection.For more information: [geomatics.help@gov.yk. ca](mailto:geomatics.help@yukon.ca)

PURPOSE:Assess the distribution of freshwater mussels, including the Brook Floater (Alasmidonta varicosa), the Eastern Pearlshell (Margaritifera margaritifera), and the Yellow Lampmussel (Lampsilis cariosa) in New Brunswick.DESCRIPTION:This dataset contains the results of work undertaken from 2017 to 2024 to assess the distribution of freshwater mussels using environmental DNA (eDNA) surveys and species-specific qPCR assays. USE LIMITATION:To ensure scientific integrity and appropriate use of the data, we would encourage you to contact the data custodian.

Layers that present various important parameters such as inventories, presence, sightings, distribution, relative occurrence or catch rates, critical habitat, breeding and feeding areas, potential spawning and haul-out sites for the different species with status under the Species at Risk Act (SARA).The act classifies those species as being either extirpated, endangered, threatened, or of special concern. Under SARA, Fisheries and Oceans Canada must produce recovery strategies and action plans for aquatic species listed as endangered or threatened. The act is part of Canada’s strategy to protect hundreds of wild plants and animal species from becoming extinct, and to help in their recovery.The different species represented by the layers are the following:1. American shad (Alosa sapidissima)2. Atlantic sturgeon (Acipenser oxyrinchus)3. Atlantic wolffish (Anarhichas lupus)4. Beluga whale (Delphinapterus leucas)5. Blue whale (Balaenoptera musculus)6. Copper redhorse (Moxostoma hubbsi)7. Eelgrass (Zostera marina)8. Grey seal (Halichoerus grypus)9. Harbor seal (Phoca vitulina)10. Humpback whale (Megaptera novaeangliae)11. Lake sturgeon (Acipenser fulvescens)12. Lumpfish (Cyclopterus lumpus)13. Northern wolffish (Anarhichas denticulatus)14. Rainbow smelt (Osmerus mordax)15. Sea pens (Pennatulacea)16. Seaweed17. Smooth skate (Malacoraja senta)18. Sponges19. Spotted wolffish (Anarhichas minor)20. Striped bass (Morone saxatilis)21. Thorny skate (Amblyraja radiata)22. Winter skate (Leucoraja ocellata)

AIS NL Biofouling Species Fisheries and Oceans Canada's (DFO) National Marine Biofouling Monitoring Program conducts annual field surveys to monitor the introduction, establishment, spread, species richness, and relative abundance of native and some non-native species in Newfoundland and Labrador (NL) Region since 2006. Standardized monitoring protocols employed by DFO's NL, Maritimes, Gulf, and Quebec regions include biofouling collector plates deployed from May to October at georeferenced intertidal and shallow subtidal sites, including public docks, and public and private marinas and nautical clubs. Initially, (2006-2017), the collectors consisted of three 10 cm by 10 cm PVC plates deployed in a vertical array and spaced approximately 40 cm apart, with the shallowest plate suspended at least 1 m below the surface to sample subtidal and shallow intertidal species (McKenzie et al 2016a). Three replicate arrays were deployed at least 5 m apart per site. Since 2018, collector networks have been modified to improve statistical replication, including up to 10 individual collectors deployed per site at 1 m depth and at least 5 m apart (as above) from May to October. Since 2006, seven invasive biofouling organisms have been detected in Newfoundland and Labrador harbours, marinas and coastal areas.Should be cited as follows: DFO Newfoundland and Labrador Region Aquatic Invasive Species Marine Biofouling Monitoring Program. Published March 2024. Coastal and Freshwater Ecology, Northwest Atlantic Fisheries Centre, Fisheries and Oceans Canada, St. John’s, Newfoundland and Labrador.Reference:TunicatesVase tunicate (Ciona intestinalis) 2012 The Vase tunicate, is a high impact solitary invader and was first detected by DFO in 2012 on the Burin Peninsula at Ship Cove and Little Bay, Placentia Bay. Various mitigation measures (McKenzie et al. 2016b) contained this invasive tunicate to a small area for six years within Placentia Bay. First detected in Fortune Bay as an established population in 2019, increasing reports of the Vase tunicate have been made along the south coast of Newfoundland. The data provided here indicates the detections of this AIS in coastal NL.From 2018-2022, the Coastal Environmental Baseline Program provided additional support to enhance sampling efforts in Placentia Bay.

Layer that includes the known information on lake sturgeon breeding, feeding and concentration areas in the St. Lawrence River and Estuary according to a literature review of documents produced between 1976 and 2002.Additional InformationLake sturgeon's breeding, feeding and concentration areas were produced according to a literature review of the following documents:Blais, J.-P. et V. Legendre. 1976. La ouananiche, Salmo salar, du lac Tremblant, Québec. Québec, Ministère du Loisir, de la Chasse et de la Pêche, Direction régionale de Montréal, Rapp. tech. 06-11, 116 p.Bouthillier, L., P. Dumont et G. Roy. 1993. Répertoire des habitats du poisson de la région de Montréal, Québec. Ministère du Loisir, de la Chasse et de la Pêche du Québec, Direction régionale de Montréal. ii + 6 p. + fiches d'habitats + 18 cartes d'habitats à l'échelle 1:50 000 + bibliographie 15 p.Desjardins, S. et P. Dumont. 1990. Avis du ministère du Loisir, de la Chasse et de la Pêche au sujet de l'acceptabilité environnementale du projet Soligaz. Québec, Ministère du Loisir, de la Chasse et de la Pêche, Direction régionale de Montréal.Dimension Environnement SNC. 1990. Évaluation de l'abondance de l'Esturgeon jaune (Acipenser fulvescens) dans la baie du Cap St-Michel. Rapport complémentaire présenté au ministère de l'Environnement du Québec dans le cadre de l'étude d'impact sur l'environnement du projet Soligaz, Montréal, 24 p.Dumont, P. et R. Fortin. 1977. Relations entre les niveaux d'eau printaniers et la reproduction du Grand Brochet du Haut-Richelieu et de la baie Missisquoi. Université du Québec à Montréal, Département des sciences biologiques, pour le Bureau international Champlain Richelieu, Comité d'impact sur l'environnement, x + 108 p.Dumont, P., J. Leclerc et L. Bouthillier. 1989b. Données d'inventaire, marais Fraser, lac Saint-François, Cazaville. Été 1989. Québec, Ministère du Loisir, de la Chasse et de la Pêche, Service de l'aménage¬ment et de l'exploitation de la faune, Montréal. [Données non publiées].Dumont, P., J. Leclerc et Y. Chagnon. 1990. Pêche électrique sur la rivière Yamaska le 18 avril 1990. Québec, Ministère du Loisir de la Chasse et de la Pêche, Service de l'aménagement et de l'exploitation de la faune, Montréal. [Données non publiées].Enquête auprès des pêcheurs et agents du MEF et du MPO. 1995.Fournier, P. et L.-M. Soyez. 1988. Étude de l'utilisation faunique printanière du marais de Rosemère. Québec, Ministre du Loisir, de la Chasse et de la Pêche, Service de l'aménagement et de l'exploitation de la faune, Montréal, 13 p.Gendron, M. 1986. Rivière-des-Prairies. Aménagement d'un haut-fond, printemps 1986. Groupe de recherche SEEEQ ltée pour la Direction Environnement d'Hydro-Québec, 103 p.Gendron, M. 1987. Rivière-des-Prairies. Suivi de l'aménagement d'un haut-fond, printemps 1987. Le Groupe de recherche SEEEQ ltée pour la Direction Environnement d'Hydro-Québec, 60 p.Gendron, M. 1988. Rivière-des-Prairies. Suivi de l'aménagement du haut-fond, synthèse 1982-1988. Le Groupe de recherche SEEEQ ltée pour le Service de recherche en environnement et santé publique, Vice-Présidence Environnement, Hydro-Québec, 95 p.LaHaye, M. et R. Fortin. 1990. Caractérisation de l'habitat de fraie et de l'habitat des juvéniles de l'Esturgeon jaune (Acipenser fulvescens) dans la région de Montréal. Rapport de recherche préparé pour le Département des sciences biologiques de l'Université du Québec à Montréal, 81 p. + annexes.Letendre, M., B. Dumas et M. Beaudoin. 1990. Inventaire de la rivière des Prairies, au niveau de l'île de Pierre. Québec, Ministère du Loisir de la Chasse et de la Pêche, Service de l'aménagement et de l'exploitation de la faune, Montréal. [Travaux en cours].Société de la Faune et des Parcs du Québec. 2000. Atlas des habitats critiques connus ou d'intérêt particulier pour les poissons du fleuve Saint-Laurent entre le port de Montréal et l'Île aux Coudres. Direction du développement de la faune.Therrien, J., Marquis, H., Shooner, G. et Bérubé, P. 1991. Caractérisation des habitats recherchés pour la fraie des principales espèces de poisson du fleuve Saint-Laurent (Cornwall à Montmagny). Études réalisées par le Groupe Environnement Shooner inc. Pour le compte des ministères des Pêches et des Océans et de l'Environnement du Canada. 16 pages. Un atlas accompagne ce document.Tremblay, S. 1996. Caractérisation de la pêcherie commerciale à l'esturgeon noir (Acipenser oxyrinchus) dans le secteur de Montmagny en 1994. Ministère de l'Environnement et de la Faune, Direction de la faune et des habitats. Rapport technique. 27 p.Trencia, G. 2002. Communication personnelle avec Guy Trencia, Faune et Parcs Québec.

Historical finds of Fenusa pumila

## Information document concerning the results of the threat analysisThis document provides additional information to better understand and use the threat data produced as part of the integrated recovery approach. This data highlights the sectors where the impacts of threats on occurrences listed by the [Quebec Natural Heritage Data Center (CDPNQ)] (https://www.quebec.ca/gouvernement/gouvernement-ouvert/transparence-performance/indicateurs-statistiques/donnees-especes-situation-precaire) are the most important.# #Quelles data included in the analyses?The analyses focus on the following 67 elements (wildlife species):* Amphibians: swamp frog, boreal chorus frog, western chorus frog, western chorus frog, purple salamander, Adirondack and Appalachian pop., mountain dusky salamander, mountain dusky salamander, mountain dusky salamander, mountain dusky salamander, mountain dusky salamander, mountain dusky salamander, mountain dusky salamander, mountain dusky salamander, mountain dusky salamander, mountain dusky salamander, mountain dusky salamander, mountain dusky salamander, mountain dusky salamander, mountain dusky salamander, mountain dusky salamander, mountain* Insects: satyr tawny from the Maritimes* Mammals: pygmy weasel, rock vole, forest vole, forest vole, forest vole, Cooper lemming vole, northern bat, eastern pygmy bat, Gaspé shrew, longicaude shrew, longicaude shrew, little flying squirrel, little flying squirrel, pop. of the plains of the Great Lakes, small brown bat, eastern pipistrelle* Birds: golden eagle, diving harlequin, eastern pop., eastern pop., bunting grasshopper pratensis, Pratensis, grasshopper, rufa, peregrine falcon, Anatum/tundrius, Iceland tourniquet, eastern pop., eastern pop., eastern pop., Bicknell's thrush, Bicknell's thrush, horned grebe, black tern, short-eared owl, shore swallow, chimney swift, eastern pop., eastern pop., Bicknell's thrush, thrush of Bicknell, thrush, horned grebe, black tern, short-eared owl, shore swallow, chimney swift, eastern pop. White-tailed Plover, Cerulean Warbler, Golden-winged Warbler, Golden-winged Warbler, Lesser Bittern, Melodus Piping Plover, Bald Eagle, Yellow Rail, Yellow Rail, Roseate Tern* Fish: savory shad, mesh pike, vermiculated pike, vermiculated pike, crazy cat-rapids, copper redhorse, river redhorse, northern crappy, sand stinger, lake sturgeon, black sturgeon, black sturgeon, black sturgeon, black sturgeon, Atlantic sturgeon, Atlantic sturgeon, black sturgeon, Atlantic sturgeon, black sturgeon, Atlantic sturgeon, black sturgeon, Atlantic sturgeon, Atlantic sturgeon, black sturgeon, gray rock digger, rock darter, northern lamprey, northern lamprey, grass minnow, brass minnow, oquassa arctic char, rainbow smelt, southern pop. of St. Lawrence Estuary* Reptiles: brown snake, northern water snake, northern ribbonsnake, northern ribbonsnake, spotted snake, green snake, northern collared snake, wood turtle, geographic turtle, geographic turtle, speckled turtle, speckled turtle, musky turtle, spiny softshell turtleOther species, including floristic species, could be added to the analyses.Threats: Threats are activities that, by their location, intensity, or time in which they occur, generate stress (see next section) that affects elements of biodiversity. In total, the available data concerns 16 threats:* Future conversion risk: Development of residential, industrial and commercial areas;* Ski resorts;* Future conversion risk: Annual agriculture (field crops);* Sustainable agriculture;* Quarries and sandpits;* Roads;* Total removal of forest cover;* Partial removal of forest cover;* Educational treatments;* Motorized vehicles;* Boating;* Drainage in agricultural areas;* Phragmites australis;* Rhamnus cathartica;* Increase in predation by mesopredators;* Nutrient load.# #Méthode for calculating the impact rating* The method used to calculate the impact score is presented in the document Integrated Recovery Approach for Threatened or Vulnerable Species — Development of a New Tool for Conservation Planning.* The results are presented using a map grid in which each 10 km x 10 km plot shows the cumulative impact of a threat on the occurrences present in this portion of territory. The cumulative impact is obtained by adding up the impact ratings of all the occurrences present within the plot. This accumulation makes it possible to identify, using a color code, the “hot spots” of a threat on occurrences. The absence of color indicates the absence of calculated or listed impacts on occurrences. The color gradient illustrates the variation in the cumulative impact of this threat on all occurrences in the plot, from the lowest score (yellow) to the highest (red).* Each threat is presented on a separate layer, while an additional layer called “Threat Compilation” shows the sum of the threats over all the occurrences present in a plot. # #Quelle is standardized classification used for analysis?The threats analyzed were defined according to the document Standardized Classification of Threats Affecting Biodiversity — Definitions for the Quebec Conservation Data Center (CDC) v1.0, published in 2021.**This third party metadata element was translated using an automated translation tool (Amazon Translate).**

Historical finds of Profenusa thomsoni