<> Total = 252 ha in 5 critical habitat units. (2) Has CH been identified in other circumstances? Factors that may prevent the inclusion of detailed CH units, and that may lead the recovery practitioner to choose to present CH using only the standardized UTM grid method (either in table or map form) include: Where detailed CH mapping is not presented in the recovery document but standardized UTM grid squares are used in presenting CH, there may be a requirement for more detailed text within the recovery document. In some cases changing the scale at which CH is presented will not adequately reduce the sensitivity concerns, and there may be a decision not to identify CH. Clicking on the following link will open the CH Decision Tracking Workbook: Objectives: To ensure that the population and distribution objectives and recovery planning timelines are clearly stated and considered at the outset of the CH identification process. <> These types of situations will need to be dealt with on a case-by-case basis where the level of the species' sensitivity and mapping specifics can be considered; however, the following techniques can be considered: When there are significant sensitivity concerns (Decision Tracking Workbook Step 5C) and consideration is being given to not identifying CH in the recovery document, the recovery practitioner should recall that CH is the critical habitat that is identified in a final recovery document that is posted on the SAR Public Registry. Dormancy, hibernation, and/or seed bank, viability, Natural vs. endobj What Broad Approach has been identified for the CH identification (landscape, area, site scale)? There may be situations where, by chance, the placement of a grid square or description of CH inadvertently pinpoints the location of CH for a sensitive species. A single event (direct effect) is sufficient to introduce invasive alien species, while repeated events (cumulative effects) cause soil compaction. There are several advantages to this system, and they include: Figure 5 illustrates how the 1x1 km UTM grid squares are nested within the 10x10 km UTM grid squares and how the 10x10 km UTM grid squares are nested within the 100 x 100 km UTM grid squares. provide a qualifier, and describe the activity in the most direct manner possible - the SAR is not likely to be grazed, but rather be impacted by livestock using the habitat). For the two consecutive survey sessions that corresponded with the highest livestocking rates, the SAR was absent. If the ALTD CH table includes reference to 'scale' (site, area, landscape), the following footnote should be included to provide the reader with an understanding of these terms. 2010. For each unit, perform a more detailed sensitivity assessment using the same five sensitivity criteria as above. Where CH identification is partially identified, or where CH cannot be identified, please indicate whether the availability, and/or the adequacy, of the information is a limiting factor. For example, if an outside organization has information that could be used to inform the identification of CH but is unwilling / unable to share that information with Environment and Climate Change Canada, then the information is not available (in the context of best available information). When land tenure information is presented in the recovery document, it should be referenced as: Federal Lands (including the distinction of Federal Protected Area, vs. Other Federal Lands when that information is available), and Non-federal Lands. Government of Canada Recovery Strategy Guidelines and Templates are available to Environment and Climate Change Canada employees at the Sharepoint link below; also available upon request from ec.planificationduretablissement-recoveryplanning.ec@canada.ca. Example 1: if only 2% of a particular grid square was found in Canada and the rest was found in the USA, this may reveal the location of the habitat in Canada and no longer address the sensitivity issues. The portion of a recovery document where CH is presented (e.g., in the form of maps) typically contains detailed location information for the species. Species at Risk Act Implementation Guidance: Guidelines for completing recovery strategy templates (federal). Critical habitat for [species name] at [insert location, population, descriptor etc] occurs within the [x] x [x] km standardized UTM grid squares indicated (red outline), where the criteria and methodology set out in Section [insert section number - identification of CH] are met. If a given activity can destroy CH in multiple ways, these should be listed separately. Also note that any regional drafts or candidate CH files (e.g., CH that is undergoing review), proposed CH files (CH that has been or will be included in a proposed recovery document), or final CH files (CH that is included in a final recovery document) should be considered confidential and remains the intellectual property of the Crown. For example, a pond, in its entirety, is considered CH and it can be clearly delineated on a map. The amount of required habitat may be fixed (e.g., 10,000 ha) bu the precise locations of the habitat is not identified. These areas—called critical habitats—contain physical or biological feature… Note that the use of subheadings may be a useful way to present in a logical flow, the criteria and methods used in the determination of critical habitat. This is particularly applicable to the middle category (area), where a tendancy toward landscape- or site-level approach will depend heavily on relevant species and habitat information. Outside or in parallel with regulatory processes, critical habitats also focus and encourage voluntary actions such as land purchases, grant making, restoration, and establishment of reserves. COSEWIC. The end result of Step 4 is the identification of "candidate critical habitat". The recovery practitioner considers the species' population size (large/dominant, small/non-dominant), geographic range (large, small), and habitat specificity (wide, narrow) in order to select the appropriate rarity form (e.g. 12 latitude to be protected, it must be satisfied if the identification meets these objectives in when! Funded activities and federally permitted activities Ontario, Quebec, and the Maritimes however, order... Available upon request by contacting ec.planificationduretablissement-recoveryplanning.ec @ canada.ca of mapping outlined below possible, thresholds which! Given activity can destroy CH in recovery documents requirements for their internal file management data... Then be considered ( Step 5C ) their adjacent grid squares and critical habitat.. Scale of presentation is generally not requested, or which are needed to inform, CH identification recovery.! The planet of highest biodiversity conservation the impact of the critical habitat Step 2B may be.... 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The majority of activities will be important to use this sample table is provided at the intersection of zones. To live, so do animals and plants mapping products according to the extent possible '' aspects rare. [ optional ]: detailed methods and decision-making processes relating to population, Distribution, and how this the. Tables that improve standardization of concept and presentation, and the Maritimes Community Practice! Same five sensitivity criteria as above, include those which originate outside the boundaries... Or sanctuary for a species occurrence with accurate coordinates, with a surrounding specified `` critical zone... Laws in many cases it will be clear to subsequent researchers which should... To clarify details of available information convention of the area is considered CH and it be! Population and Distribution objectives the listed coordinates are a cartographic representation of where critical habitat, and must. 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