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COSEWIC Annual Report - 2006
- Item I - COSEWIC Activities
- Item II – Election of Chair of COSEWIC
- Item III - COSEWIC Membership
- Item IV - COSEWIC Operations and Procedures
- Item V – Species Status Assignments
- Item VI - Wildlife Species Assessed by COSEWIC Since its Inception
- Appendix I
- Appendix II - Species Selected for Status Report Preparation to be included in the Next Call for Bids Fall 2006
- Appendix III
- Appendix IV - Biosketches
- Appendix V - Approach to Streamlining Reassessments
- Appendix VI - Guidelines for recognizing Designatable Units Below the Species Level
- Appendix VII - Detailed COSEWIC Species Assessments, April 2006
- Appendix VIII - August 2006 Canadian Species at Risk Publication Cover
Appendix VI - Guidelines for recognizing Designatable Units Below the Species Level
Approved by CESCC in October 2005
Subsequent changes submitted for approval by CESCC
(see footnote under Precautions section)
It is widely recognised that species status assessment and conservation of biological diversity require that populations below the species level (using “species” in the accepted sense of the taxonomic hierarchy) be considered when appropriate. Most legislation allows for status designation of populations below the species level. For example, the federal Species at Risk Act (SARA) includes subspecies, varieties and “geographically or genetically distinct” populations in its definition of wildlife species thus allowing for listing of populations below the species level. COSEWIC's recognition of populations below the species level for assessment (i.e. designatable units) is guided by the same general objective of preventing wildlife species from becoming extinct or extirpated.
COSEWIC strives to recognize designatable units that are significant and irreplaceable units of biodiversity yet there are difficulties inherent in achieving a uniform interpretation of the word "significant". Furthermore, because patterns of population structure, life history, and genetic variability differ across taxonomic groups, use of uniform criteria in determining appropriate designatable units a priori can be difficult. Guidelines are needed in order to interpret, on a case-by-case basis, what constitutes a significant element of biological diversity to be recognized for the purpose of conservation status assessment by COSEWIC.
COSEWIC's usualapproach to assigning status is, first, to examine the species as a whole and then, if deemed appropriate, to examine the status of designatable units below the species level.
In cases where particular designatable units are strongly suspected of being at risk, or where they are so different in distribution or conservation status that an overall assessment would not capture the conservation concerns, COSEWIC will assess single designatable units below the species level.
Status may be assigned to subspecies, varieties, or geographically or genetically distinct populations which may be recognized in cases where a single status designation for a species is not sufficient to accurately portray probabilities of extinction within the species. Designatable units are to be recognized in accordance with the following guidelines.
Specifically, the units to which status may be assigned below the species level are recognized on the basis of any one of the four criteria (1 - 4) described below. Typically, COSEWIC will consider, in order of precedence, 1) established taxonomy, 2) genetic evidence, 3) range disjunction, and 4) biogeographic distinction.
1) named subspecies or varieties:
published subspecies of animals according to the Code of Zoological Nomenclature or published subspecies or varieties of plants according to the Code of Botanical Nomenclature.
- Water Snake: Nerodia sipedon sipedon (NAR), N. s. insularum (E)
- Loggerhead Shrike: Lanius ludovicianus migrans (E), L. l. excubitorides (T)
2) units identified as genetically distinctive:
evidence of genetic distinctiveness including, but not limited to, appropriate inherited traits (morphological, life history, behaviour) and/or genetic markers (e.g. allozymes, DNA microsatellites, DNA restriction fragment length polymorphisms (RFLPs), DNA sequences, etc.).
- Coho salmon: Interior Fraser River (E), as opposed to other populations
3) units separated by major range disjunction:
disjunction between substantial portions of the species' global geographic range such that dispersal of individuals between separated regions has been severely limited for an extended period of time and is not likely in the foreseeable future.
- Boreal Felt Lichen: Atlantic (E), Boreal (SC)
- Blanding's Turtle: Atlantic population (T), as opposed to other populations
4) units identifed as biogeographically distinct:
occupation of differing eco-geographic regions that are relevant to the species and reflect historical or genetic distinction, as may be depicted on an appropriate ecozone or biogeographic zone map (Figs. 1 - 3).
- Mormon Metalmark: Southern Mountain population (E), Prairie population (T).
- Woodland Caribou: an assortment of designations based on biogeographic zones.
Appropriate caution in interpreting data should be exercised when identifying designatable units. The biological significance of phenotypic, genetic or geographic variation, must be considered in light of potential limitations in the data available. Inadequate information on temporal variability, insufficient sample sizes, or evidence from inappropriate traits (those which are either inordinately variable or overly conservative) will compromise the significance of available information.
Separate status designations should not be recognized for management units that are not based on biological criteria consistent with these guidelines.
NOTE: Paragraph striken
Status designations should not be individually assigned to units below the species level if all such units within the species have the same status designation. In such cases, the status designation should be applied to the entire species.
When a COSEWIC assessment has been conducted using designatable units below the species level, and adjacent designatable units are classified as having the same status, on the basis of the same criteria, then COSEWIC may apply a single status assessment to those units if a single assessment better addresses the conservation status of the units that are combined.1
Figure. 1. Terrestrial ecozones of Canada
Figure. 2. Aquatic ecozones of Canada
Figure. 3. Faunal provinces of terrestrial amphibians, reptiles, and molluscs in Canada.
1 Shaded text indicates the changes to the guidelines approved by COSEWIC in April 2006.
- Date Modified: