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Trends in Extinction Risk for Imperiled Species in Canada

  • Brett Favaro ,

    brett.favaro@mi.mun.ca

    Affiliations Department of Biology, University of Victoria, Victoria, Canada, Centre for Sustainable Aquatic Resources, Fisheries and Marine Institute of Memorial University of Newfoundland, St John's, Canada, Department of Ocean Sciences, Memorial University of Newfoundland, St. John's, Canada

  • Danielle C. Claar,

    Affiliation Department of Biology, University of Victoria, Victoria, Canada

  • Caroline H. Fox,

    Affiliations Department of Geography, University of Victoria, Victoria, Canada, Raincoast Conservation Foundation, Sidney, Canada

  • Cameron Freshwater,

    Affiliation Department of Biology, University of Victoria, Victoria, Canada

  • Jessica J. Holden,

    Affiliation Department of Biology, University of Victoria, Victoria, Canada

  • Allan Roberts,

    Affiliation Bamfield Marine Sciences Centre, Bamfield East, Canada

  • UVic Research Derby

    Membership of the UVic Research Derby is provided in the Acknowledgments.

    Affiliations Department of Biology, University of Victoria, Victoria, Canada, Department of Geography, University of Victoria, Victoria, Canada, School of Environmental Studies, University of Victoria, Victoria, Canada

Trends in Extinction Risk for Imperiled Species in Canada

  • Brett Favaro, 
  • Danielle C. Claar, 
  • Caroline H. Fox, 
  • Cameron Freshwater, 
  • Jessica J. Holden, 
  • Allan Roberts, 
  • UVic Research Derby
PLOS
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Abstract

Protecting and promoting recovery of species at risk of extinction is a critical component of biodiversity conservation. In Canada, the Committee on the Status of Endangered Wildlife in Canada (COSEWIC) determines whether species are at risk of extinction or extirpation, and has conducted these assessments since 1977. We examined trends in COSEWIC assessments to identify whether at-risk species that have been assessed more than once tended to improve, remain constant, or deteriorate in status, as a way of assessing the effectiveness of biodiversity conservation in Canada. Of 369 species that met our criteria for examination, 115 deteriorated, 202 remained unchanged, and 52 improved in status. Only 20 species (5.4%) improved to the point where they were ‘not at risk’, and five of those were due to increased sampling efforts rather than an increase in population size. Species outcomes were also dependent on the severity of their initial assessment; for example, 47% of species that were initially listed as special concern deteriorated between assessments. After receiving an at-risk assessment by COSEWIC, a species is considered for listing under the federal Species at Risk Act (SARA), which is the primary national tool that mandates protection for at-risk species. We examined whether SARA-listing was associated with improved COSEWIC assessment outcomes relative to unlisted species. Of 305 species that had multiple assessments and were SARA-listed, 221 were listed at a level that required identification and protection of critical habitat; however, critical habitat was fully identified for only 56 of these species. We suggest that the Canadian government should formally identify and protect critical habitat, as is required by existing legislation. In addition, our finding that at-risk species in Canada rarely recover leads us to recommend that every effort be made to actively prevent species from becoming at-risk in the first place.

Introduction

Unsustainable exploitation, climate change, ocean acidification and other anthropogenic impacts have resulted in a global extinction rate that is as much as 1000 times the historic background rate [1][3]. Given the irreversibility of extinctions, preventing or reversing the continuing decline of at-risk species is a major focus of conservation [4]. Preserving global biodiversity is also considered essential for human well-being and the maintenance of ecosystem processes [3], [5][7].

Many countries have legislation that explicitly protects species at risk of extinction. In general, such legislation is designed to identify vulnerable taxa, establish recovery plans, prevent further declines, and promote recovery [8]. Recognizing that habitat loss is the leading cause of extinction [9][12], the identification and preservation of habitat is often required, contributing to the stabilization and recovery of threatened species [13]. Despite the implementation of laws and conservation programs, global biodiversity continues to decline [3], [5], [14].

In Canada, species at risk are identified and protected in a multi-step process. The process begins with the Committee on the Status of Endangered Wildlife in Canada (COSEWIC), an independent scientific body formed in 1977. COSEWIC assesses the status of candidate species that are potentially at risk of extinction or extirpation [15]. This body only considers scientific evidence relevant to a species' recovery potential, and ignores socioeconomic costs or benefits of protection [15]. Their assessments are based on the Canadian extent of the species' range, even if the species occurs in the United States or elsewhere [15]. Species assessed as at-risk by COSEWIC do not automatically secure legal protection from the committee's decision. Rather, protection is issued under the Species at Risk Act (SARA), which was passed in 2003, and which formalized the use of COSEWIC assessments as the scientific basis for listing decisions [16]. Upon receipt of a COSEWIC assessment, the Minister of the Environment must issue a response statement indicating whether the species will be listed at the status recommended by the assessment, or whether more information is required [17]. The ultimate decision whether to list may also incorporate the socio-economic impacts of listing. If listed, it becomes illegal to kill or harm individuals of that species and the species' critical habitat must be identified and protected to the extent possible [18]. Protections derived from SARA automatically apply to federal lands (including oceans), but for these measures to apply outside of these areas (e.g. in provincial or private land) complementary protections must be implemented that applies to the species and its habitat [19]. If the Minister of the Environment decides that provincial or territorial law is insufficient to effectively protect a listed species, the federal government has the power to apply SARA's protections to provincial or territorial lands [20]. Recovery strategies and action plans (required by SARA) are mandated to be released within a specified timeframe, the length of which depends on the species' designation and when it was listed [21], [22]. Furthermore, SARA requires that management plans be produced for species that are not at immediate risk of extinction or extirpation, but are nevertheless of ‘special concern’ since they may become at-risk in the future [23]. Species of special concern do not receive the full protections offered to species listed under SARA as threatened, endangered, or extirpated.

Previous studies have identified biases, limitations, and a general lack of implementation associated with at-risk species legislation in Canada (Table 1). For instance, harvested species and those found in northern territories are less likely to be listed under SARA [24], [26], as are species threatened by biological resource use, including those that are unintentionally harvested [27]. In addition, recovery strategies and action plans are often not completed within deadlines established by SARA [22], leading to concerns that species are not receiving timely protections, despite being listed. This finding was confirmed in a recent federal court decision [28]. Moreover, COSEWIC itself has been criticized for its assessment criteria and apparent biases [31][32]. For example, species with low information availability tend to receive less severe assessments than would be suggested under the precautionary principle [30].

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Table 1. Summary of review papers related to endangered species assessment and legislation in Canada.

https://doi.org/10.1371/journal.pone.0113118.t001

In this study, we examine trends in the status of species repeatedly assessed by COSEWIC, used here as a proxy for Canada's effectiveness in species conservation. Using records obtained from COSEWIC [33] and the SARA Public Registry [34], we analyze trends in the designations of species with two or more assessments to determine whether species are, on average, improving, deteriorating, or remaining stable in status. In addition, we examine outcome differences across taxonomic groups, and whether the basic obligation to identify critical habitat for listed species has been met. Finally, we assess whether species listed for longer have better outcomes. While this study builds on previous work reviewing the process of listing species under SARA (Table 1), it is the first to assess the overall trends in status of at-risk species that have been assessed more than once by COSEWIC.

Methods

COSEWIC Wildlife Species Database

Species, subspecies, and populations (hereafter ‘species’) that are assessed by COSEWIC are placed into one of five categories on a scale of increasing risk of extinction or extirpation [32]: not at risk, special concern, threatened, endangered, or extinct or extirpated (hereafter extirpated). A sixth category, data deficient, is used when there are insufficient data to classify a species. The criteria for categorization depends on a variety of factors including changes in total numbers of mature individuals, whether a species has a small and declining population size, and the changes in size of its range [35]. COSEWIC's assessment criteria were updated in 2001 [35]. Although the same assessment categories were employed after the revision in 2001, species required a more severe decline in total population to qualify as either endangered or threatened. For example, prior to 2001 the criteria for an Endangered assessment (Criteria A1: [35]) required a reduction of ≥50% in the total number of mature individuals over the last 10 years or 3 generations. As of 2001, this same category required a ≥70% decline [36].

The definition of full recovery that we employ here is a change in COSEWIC assessment status to ‘not at risk.’ Although this may not equate to a full ecological recovery (e.g. [37], [38]) it allows us to broadly assess trends with a consistent metric.

Data collection

We identified all species that COSEWIC has assessed more than once using the Wildlife Species Search Engine on the COSEWIC website [33]. Assessments occurred between 1977 (COSEWIC's establishment) and December 2013 (when we conducted our search). We recognize that our analysis may be limited by biases associated with which species have been assessed multiple times and that COSEWIC listing criteria have changed since 2001. However, because the 2001 revision tightened criteria for more-severe listings, the expected bias introduced by the criteria change would be a greater proportion of less severe species listings. We used the ‘change in status’ tab on the website to include any species ‘in a higher risk category’ (N = 81); ‘in a lower risk category’ (N = 36); ‘no longer at risk’ (N = 21); ‘changed’ (N = 20); ‘reassigned’ (N = 69); and ‘no change’ (N = 272); populating our database with a total of 499 species. In our analysis, we excluded any species that had ever been assessed as ‘data deficient’ by COSEWIC (N = 30 species), or that had experienced some form of reassignment (e.g. a species split into multiple designatable units, N = 106 species), because changes in status for these species cannot be interpreted as a true change in extinction risk. We excluded six species that were both data deficient and reclassified, leaving a total of 369 species in our analysis.

We collected the history of COSEWIC assessments for each species on its respective species summary page. We recorded the date and status designation of each COSEWIC assessment for each species, and the taxonomic group to which that species belongs (due to small sample sizes, we combined molluscs and arthropods into a single ‘invertebrates’ category, and combined lichens and mosses). We then used the SARA public registry [34] to record whether species were SARA listed, and to access COSEWIC status reports for each species. To account for differences between species' life histories, COSEWIC and the IUCN place rates of decline into a biological context by scaling assessments by the generation time (GT) of each species [35], [39]. Therefore we also recorded each species' generation time, if available. If the species was SARA-listed as extirpated, endangered, or threatened, we recorded whether a recovery strategy had been completed. If the recovery strategy was completed, we recorded whether the strategy indicated that critical habitat had been fully, partially, or not identified. If a recovery strategy was not complete for the species, we recorded that critical habitat had not been identified. For SARA-listed species, Environment Canada provided us with the dates when species were listed.

For some species, the COSEWIC summary explained that an apparent improvement in status was due to the discovery of new populations through increased sampling, and not because of an actual recovery in population. We made note of these cases (N = 20) so as to distinguish them from improvements due to conservation action.

Data analysis

We assigned each COSEWIC status a numerical value in descending order of severity (5 = not at risk, 4 = special concern, 3 = threatened, 2 = endangered, 1 = extirpated). We then calculated the overall change for each species, between the first and most recent COSEWIC assessment. For example, a species that was initially classified as special concern, and then deteriorated to endangered in its most recent assessment would receive a score of −2. For species requiring critical habitat designation (extirpated, endangered and threatened), we performed a Pearson's chi-squared test to determine whether critical habitat identifications (full, partial, or not identified) across the ten taxonomic groups differed from the proportions across all species. We used the statistical software R for computations and data plots [40].

We identified species whose most recent COSEWIC assessment occurred after the species had been listed under SARA for at least three of that species' GT, to identify species for which some recovery may be biologically possible. We then employed a cumulative link mixed model using the “ordinal” package in R [41] to test whether the number of GTs since SARA-listing was associated with a change in final COSEWIC status across species. Cumulative link mixed models test the influence of one or more independent variables (herein: number of generation times since listing) on an ordinal dependent variable (change in COSEWIC status), and are analogous to generalized linear mixed effects models in that they allow for the incorporation of a random effect, or ‘grouping’ factor (taxonomic order) [41][43].

Results

There were a total of 369 species across ten taxonomic groups that met our criteria for inclusion (Table S1, Fig. 1). For all taxonomic groups (except marine fish), the majority of species declined or remained the same in status (Table S1, Fig. 2). However, species trajectories varied substantially based on their initial assessment (Fig. 3). For species initially classified as not at risk, endangered, or extirpated, the most common outcome was to remain at their initially assessed status. However, for species initially classified as special concern or threatened, deterioration in status was the most common outcome. For example, 47% of species listed as special concern deteriorated in status (Fig. 3). Only 20 species (5.4%) received a ‘not at risk’ assessment after previously being listed in an at-risk category (three terrestrial mammals, nine birds, four freshwater fish, one marine fish, two vascular plants, and one lichen). Five of these cases were not due to conservation action, but were instead due to increased sampling effort. A total of 221 species are listed under SARA as threatened, endangered, or extirpated (Fig. 4), and therefore their critical habitat should be identified. Overall, and for all taxonomic groups, critical habitat has not been fully identified for more than half of SARA-listed species (Fig. 4). Further, critical habitat identifications (full, partial, or not identified) significantly varied across the ten taxonomic groups (÷2 = 51.90, df = 18, p<0.001).

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Figure 1. Overview of COSEWIC assessment statuses for all species that have been assessed more than once, and that have never been data deficient or taxonomically reassigned.

Each species is represented by points (assessment date and outcome) connected by lines. Species that deteriorated in status from their first to final COSEWIC assessments are red, species that have improved are blue, and species that have remained constant are black. The vertical dotted line indicates 2003, or the passing of SARA. Species whose apparent recovery was due to increased sampling effort, and not biological recovery (N = 20) are not shown.

https://doi.org/10.1371/journal.pone.0113118.g001

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Figure 2. Frequencies of occurrence of change in COSEWIC assessed status for each taxonomic group.

Positive numbers indicate improvement (e.g. a transition from endangered to threatened would be +1, while endangered to special concern would be +2), negative numbers indicate deterioration, and zero indicates no change across assessments. Red bars indicate apparent recoveries due to increased sampling efforts. Note that the y-axis for vascular plants is scaled differently from other taxonomic groups.

https://doi.org/10.1371/journal.pone.0113118.g002

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Figure 3. Trends in COSEWIC statuses for each species, grouped by initial assessments.

Proportions are grouped by initial assessment status (column). Change from first to final assessment is indicated on the Y axis, and colours indicate the final assessment status. For example, of species that were initially assessed as threatened (third column), 19 of them (or a proportion of 0.2) improved by one status level (+1 on Y-axis), ultimately placing them into the special concern category (yellow).

https://doi.org/10.1371/journal.pone.0113118.g003

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Figure 4. Proportion of SARA-listed species (listed as extirpated, endangered, or threatened) that have critical habitat (CH) fully identified (light green), partially identified (dark green), or not at all identified (dark red), overall and by taxonomic group.

Values under bars indicate the number of species in each taxonomic category.

https://doi.org/10.1371/journal.pone.0113118.g004

There were 163 species that met our criteria for inclusion in the Generation Time analysis (listed as extirpated, endangered, or threatened; GT reported; schedule 1), and 69 that have been listed for three or more GT. The number of GT since listing ranged from 0.11 to 35.8 (mean ±1 S.D., 3.7±4.3, Figure 5). If a species has been adequately protected, the probability of a species improving in status should increase with the number of generations since listing. However, there was an estimated decline in the probability of a species improving as the number of generations since listing increased ( = −0.05, {} = {−2.40, −0.18, 2.44, 4.31}, 95% C.I. = −0.124 to 0.008), but it was not significant (Wald p = 0.084). This model had a small absolute gradient (7.4*10−6) and a condition number of the Hessian of 720, indicating that the model was able to converge and was well-defined, respectively [42]. The cumulative odds ratio was between 0.88 and 1.01 (95% C.I.), meaning that for each unit increase in GT since listing, the odds of a species improving in status ranged from increasing by 1% to decreasing by 12%.

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Figure 5. Change in COSEWIC assessment statuses versus the number of GT that have passed since initial SARA listing for all schedule 1 species listed as threatened, endangered, or extirpated.

Dot colour indicates whether CH has been fully identified (green), partially identified (dark green), or not identified (red). The black vertical line indicates three GT.

https://doi.org/10.1371/journal.pone.0113118.g005

Discussion

For species that have been assessed more than once by COSEWIC, improvement was rare, and recovery to a ‘not at risk’ status occurred in only 5.7% of cases. Moreover, one quarter of those were apparent recoveries due to increased sampling, rather than increases in population size driven by conservation action. Contrary to the intent of endangered species legislation in Canada, the probability of a species improving in status did not increase with the number of generations since initial listing under SARA. Moreover, species had a greater probability of deteriorating in status with the number of generations since listing, although this relationship was marginally statistically non-significant (Wald p = 0.084). In contrast, species recovery in the United States was strongly correlated with the number of years of protection under the Endangered Species Act [44], indicating that endangered species legislation can be effective. These results suggest a potential failure of Canadian legislation, its subsequent implementation, or both. While COSEWIC's assessment criteria were modified in 2001 [35], the revisions made it harder to qualify for more-severe categories. Therefore we have no evidence to suggest that observed declines in status were an artifact of changes in criteria.

The lack of observed recovery for SARA-listed species may be due to the lack of implementation of the law. For example, for those species without identified critical habitat, the habitat protection provisions of SARA cannot be fully implemented. Overall, the proportion of species with critical habitat identified was higher than what has been reported in a previous study [25], although our study focused on a subset of species that have been assessed multiple times, and that have never been data deficient. These are the species for which it should have been most feasible to identify critical habitat, as they have been scrutinized for a relatively long time and have sufficient data to complete an accurate assessment. The fact remains that despite the importance of critical habitat identification, the proportion of species whose critical habitat was fully identified remained low, and varied significantly across the ten taxonomic groups. This pattern suggests that there are considerable differences between the protections that species should receive under SARA, and what is actually achieved.

Since our data demonstrate that it is rare for at-risk species to recover in Canada, it is essential that substantial efforts be made to prevent species from becoming at-risk in the first place. Given that imperiled species are usually threatened by loss of habitat [45], recent weakening of federal laws that protect habitat in Canada [25], [46], [47], [48] will be unhelpful in the long term, as it may result in additional species declining to the point where they receive an at-risk designation. Habitat protection should not be limited to critical habitat – it should be managed appropriately for all habitat such that protection does not become critical. The experience in the United States demonstrates that protection of critical habitat is associated with improved conservation outcomes relative to species without such protection [44], [47]. In addition, since we found that the most common outcome for a species assessed as special concern was to deteriorate, an assessment of special concern does not currently result in sufficient protection to promote recovery.

The single most common outcome across taxonomic groups was for species to remain at the same status across assessments, and the number of species that declined outnumbered those that recovered by a ratio of approximately 2∶1. These findings are alarming for three reasons. First, by definition, a species that has been assessed as anything other than ‘not at risk’ is at elevated risk of extinction or extirpation given current conditions, and therefore maintaining a species at a threatened status should not be interpreted as a conservation victory. Second, it takes a substantial decline in population size or range size to trigger a change in assessment status, so real declines (or increases) could still occur within species held at the same COSEWIC threat level across assessments. Third, a ‘not at risk’ designation only means that the species is not at elevated risk of extinction or extirpation – it does not imply that the population has recovered to historical levels. Even species that are classified ‘not at risk’ can be heavily depleted and unable to serve their historic roles in ecosystem structure or function. This has implications for managers in the United States as well as Canada, because many at-risk species have ranges that extend into both countries. At the very least, a successful species at risk program should demonstrate species recovering to a point where they are not at risk of extinction or extirpation given current conditions. Currently, this goal is not being achieved in Canada for the overwhelming majority of species.

Recommendations

Our results lead us to make three core recommendations for at-risk species in Canada. First, given that it was much more common for species of special concern to deteriorate than to improve, we should recognize that a special concern listing warns of a coming deterioration, and we therefore suggest that the protections associated with this listing should be strengthened. Second, given the poor outcomes of at-risk species in Canada, it should be a policy priority to prevent species from becoming at-risk in the first place. The importance of critical habitat indicates that future legislation should be underpinned by a strong mandate to conserve habitat and we recommend that any legislative changes that may reduce habitat protection (e.g. the Fisheries Act [48]) should be reconsidered. Third, to experience conservation benefits from SARA, this law must be fully implemented. Implementation requires that critical habitat be fully identified and subsequently protected for SARA-listed species. The federal government should also be prepared to enact its ‘safety net’ provision, in the event that species in these regions are not receiving adequate protection to enable recovery (as it did with greater sage-grouse, Centrocercus urophasianus [49]).

Finally, even if these recommendations were accepted and put into effect, recovery takes time. Effective management requires that conservation measures be sustained over the long term, even if positive outcomes are not immediately observed.

Supporting Information

Table S1.

Summary counts of species across taxonomic groups, for all species assessed more than once by COSEWIC. Values for species listed for >3 generation times (GT) refer to the subset of species for which GTs were reported.

https://doi.org/10.1371/journal.pone.0113118.s001

(DOCX)

Data S1.

Raw data for the present study in both wide and long formats.

https://doi.org/10.1371/journal.pone.0113118.s002

(ZIP)

Acknowledgments

We thank Environment Canada for providing us with dates that species were listed under SARA. The idea for this paper originated within a Research Derby conducted at the University of Victoria [50]. The 2013 UVic Research Derby author group consisted of the authors of this paper, as well as A.F. Martin, K. Pawluk, D. Roberts, and J. Robinson, and can be contacted through B. Favaro (brett.favaro@mi.mun.ca). We thank S. Pinkus and three anonymous reviewers for providing useful comments.

Author Contributions

Conceived and designed the experiments: BF DCC CHF CF JJH. Performed the experiments: BF DCC CHF CF JJH. Analyzed the data: BF DCC CHF CF JJH AR. Wrote the paper: BF DCC CHF CF JJH AR.

References

  1. 1. Pimm SL, Russell GJ, Gittleman JL, Brooks TM (1995) The future of biodiversity. Science 269: 347–350.
  2. 2. Chapin FS III, Zavaleta ES, Eviner VT, Naylor RL, Vitousek PM, et al. (2000) Consequences of changing biodiversity. Nature 6783: 234–242.
  3. 3. Rands MRW, Adams WM, Bennun L, Butchart SHM, Clements A, et al. (2010) Biodiversity conservation: Challenges beyond 2010. Science 329: 1298–1303.
  4. 4. Arponen A (2012) Prioritizing species for conservation planning. Biodivers Conserv 21: 875–893.
  5. 5. Hassan RM, Scholes R, Ash N, editors. (2005) Ecosystems and human well-being: Current state and trends. Findings of the condition and trends working group millennium ecosystem assessment series. Washington DC: Island Press.
  6. 6. Hooper DU, Chapin FS III, Ewel JJ, Hector A, Inchausti P, et al. (2005) Effects of biodiversity on ecosystem functioning: A consensus of current knowledge. Ecol Monogr 75: 3–35.
  7. 7. Barton J, Pretty J (2010) What is the best dose of nature and green exercise for improving mental health? A multi-study analysis. Environ Sci Tech 44: 3947–3955.
  8. 8. Waples RS, Nammack M, Cochrane JF, Hutchings JA (2013) A tale of two acts: Endangered species listing practices in Canada and the United States. Bioscience 63: 723–734.
  9. 9. Brooks TM, Mittermeier RA, Mittermeier CG, Da Fonseca GAB, Rylands AB, et al. (2002) Habitat loss and extinction in the hotspots of biodiversity. Conserv Biol 16: 909–923.
  10. 10. Kareiva P, Wennergren U (1995) Connecting landscape patterns to ecosystem and population processes. Nature 373: 299–302.
  11. 11. Wilcove DS, Rothstein D, Dubow Jason, Phillips A, Losos E (1998) Quantifying threats to imperiled species in the United States. Bioscience 48: 607–615.
  12. 12. Homan RN, Windmiller BS, Reed JM (2004) Critical thresholds associated with habitat loss for two vernal pool-breeding amphibians. Ecol App 14: 1547–1553.
  13. 13. Taylor MFJ, Sattler PS, Evans M, Fuller RA, Watson JEM, et al. (2011) What works for threatened species recovery? An empirical evaluation for Australia. Biodivers Conserv 20: 767–777.
  14. 14. “Secretariat of the Convention on Biological Diversity.” (2010) Global biodiversity outlook 3. Montreal. 94 p.
  15. 15. COSEWIC (2013) Terms of reference: Committee on the status of endangered wildlife in Canada (COSEWIC), revised and approved by COSEWIC November 2011.
  16. 16. SARA (Species at Risk Act) (2002) An act respecting the protection of wildlife species at risk in Canada. SC 2002, c 29, s 15. Available: http://Laws-lois.justice.gc.ca/PDF/S-15.3.pdf. Accessed 2014 August 11.
  17. 17. SARA (Species at Risk Act) (2002) An act respecting the protection of wildlife species at risk in Canada. SC 2002, c 29, s 27. Available: http://Laws-lois.justice.gc.ca/PDF/S-15.3.pdf. Accessed 2014 August 11.
  18. 18. SARA (Species at Risk Act) (2002) An act respecting the protection of wildlife species at risk in Canada. SC 2002, c 29, ss 32–36. Available: http://Laws-lois.justice.gc.ca/PDF/S-15.3.pdf. Accessed 2014 August 11.
  19. 19. SARA (Species at Risk Act) (2002) An act respecting the protection of wildlife species at risk in Canada. SC 2002, c 29, ss 34(1)-35(1,2). Available: http://Laws-lois.justice.gc.ca/PDF/S-15.3.pdf. Accessed 2014 August 11.
  20. 20. SARA (Species at Risk Act) (2002) An act respecting the protection of wildlife species at risk in Canada. SC 2002, c 29, ss 3435. Available: http://Laws-lois.justice.gc.ca/PDF/S-15.3.pdf. Accessed 2014 August 11.
  21. 21. SARA (Species at Risk Act) (2002) An act respecting the protection of wildlife species at risk in Canada. SC 2002, c 29, ss 41–45. Available: http://Laws-lois.justice.gc.ca/PDF/S-15.3.pdf. Accessed 2014 August 11.
  22. 22. Auditor General of Canada (2013) Chapter 6: Recovery planning for species at risk. In: Anonymous Report of the commissioner of the environment and sustainable development. Office of the Auditor General of Canada. pp. 1–22. Available: http://www.oag-bvg.gc.ca/internet/English/parl_cesd_201311_06_e_38676.html. Accessed 2014 August 11.
  23. 23. SARA (Species at Risk Act) (2002) An act respecting the protection of wildlife species at risk in Canada. SC 2002, c 29, ss 65–72. Available: http://Laws-lois.justice.gc.ca/PDF/S-15.3.pdf. Accessed 2014 August 11.
  24. 24. Findlay C, Elgie S, Giles B, Burr L (2009) Species listing under Canada's Species at Risk Act. Conserv Biol 23: 1609–1617.
  25. 25. Mooers AO, Doak DF, Findlay CS, Green DM, Grouios C (2010) Science, policy, and species at risk in Canada. Bioscience 60: 843–849.
  26. 26. Schultz JA, Darling ES, Côté IM (2013) What is an endangered species worth? Threshold costs for protecting imperilled fishes in Canada. Mar Policy 42: 125–132 http://dx.doi.org/10.1016/j.marpol.2013.01.021.
  27. 27. McCune JL, Harrower WL, Avery-Gomm S, Brogan JM, Csergő A, et al. (2013) Threats to Canadian species at risk: An analysis of finalized recovery strategies. Biol Conserv 166: 254–265 http://dx.doi.org/10.1016/j.biocon.2013.07.006.
  28. 28. Western Canada Wilderness Committee, David Suzuki Foundation, Greenpeace Canada, Sierra Club of British Columbia Foundation, and Wildsite v. Minister of Fisheries and Oceans and Minister of the Environment (2014) Canada Federal Court, 2014 FC 148, T-1777-12. Available: http://cas-ncr-nter03.cas-satj.gc.ca/rss/T-1777-12%20SARA%20decision%2014-02-2014%20ENG.pdf. Accessed 2014 August 11.
  29. 29. Lukey JR, Crawford SS (2009) Consistency of COSEWIC species at risk designations: Freshwater fishes as a case study. Can J Fish Aquat Sci 66: 959–971.
  30. 30. Lukey JR, Crawford SS, Gillis D (2010) Effect of information availability on assessment and designation of species at risk. Conserv Biol 24: 1398–1406.
  31. 31. Powles H (2011) Assessing risk of extinction of marine fishes in Canada - the COSEWIC experience. Fisheries 36: 231–246.
  32. 32. Kowalchuk KA, Kuhn RG (2012) Mammal distribution in Nunavut: Inuit harvest data and COSEWIC's species at risk assessment process. Ecol Soc 17: 4.
  33. 33. COSEWIC (2013) Database of wildlife species assessed by COSEWIC. Available: http://www.cosewic.gc.ca/eng/sct1/searchform_e.cfm. Accessed 2014 August 11.
  34. 34. Government of Canada (2014) Species at risk act public registry. Available: http://www.sararegistry.gc.ca/default_e.cfm. Accessed 2014 August 11.
  35. 35. COSEWIC (2011) COSEWIC's Assessment Process and Criteria. Available: http://www.cosewic.gc.ca/pdf/Assessment_process_and_criteria_e.pdf. Accessed 2014 August 11.
  36. 36. COSEWIC (2005) Original criteria and definitions used in the status assessment of species from October 1999 to May 2001. Available: http://www.cosewic.gc.ca/eng/sct0/original_criteria_e.cfm. Accessed 2014 August 11.
  37. 37. Redford KH, Amato G, Baillie J, Beldomenico P, Bennet EL, et al. (2011) What does It mean to successfully conserve a (vertebrate) species? BioScience 61: 39–48.
  38. 38. Westwood A, Reuchlin-Hugenholtz E, Keith DM (2014) Re-defining recovery: A generalized framework for assessing species recovery. Biological Conservation 172: 155–162.
  39. 39. IUCN Standards and Petitions Subcommittee (2014) Guidelines for using the IUCN Red List categories and criteria. Version 11. Available: http://www.iucnredlist.org/documents/RedListGuidelines.pdf. Accessed 2014 August 11.
  40. 40. R Core Team (2013) R: A language and environment for statistical computing. R Foundation for Statistical Computing, Vienne, Austria. http://www.R-project.org.
  41. 41. Christensen RHB (2013) Ordinal – Regression models for Ordinal Data. R package version 2013.9-30. Available: http://www.cran.r-project.org/package=ordinal/.
  42. 42. Tutz G, Hennevogl W (1996) Random effects in ordinal regression models. Comput Stat Data An 22: 537–557.
  43. 43. Christensen RHB (2013) A tutorial on fitting Cumulative Link Models with the ordinal package. Available: ftp://ftp.stat.math.ethz.ch/R-CRAN/web/packages/ordinal/vignettes/clm_tutorial.pdf.
  44. 44. Taylor MFJ, Suckling KF, Rachlinski JJ (2005) The effectiveness of the endangered species act: A quantitative analysis. Bioscience 55: 360–367.
  45. 45. Venter O, Brodeur NN, Nemiroff L, Belland B, Dolinsek IJ, et al. (2006) Threats to endangered species in Canada. Bioscience 56: 903–910.
  46. 46. Favaro B, Reynolds JD, Côté IM (2012) Canada's weakening aquatic protection. Science 337: 154.
  47. 47. Kirchhoff D, Tsuji LJS (2014) Reading between the lines of the ‘Responsible resource development’ rhetoric: The use of omnibus bills to ‘streamline’ Canadian environmental legislation. Impact Assessment and Project Appraisal 1–13 DOI:10.1080/14615517.2014.894673.
  48. 48. Hutchings JA, Post JR (2013) Gutting Canada's fisheries act: No fishery, no fish habitat protection. Fisheries 38: 497–501.
  49. 49. Canada Gazette (2013) Emergency Order for the Protection of the Greater Sage-Grouse. Species At Risk Act. Government of Canada. P.C. 2013–1245. Available: http://canadagazette.gc.ca/rp-pr/p2/2013/2013-12-04/html/sup-eng.php Accessed 2014 July 22.
  50. 50. Favaro B, Braun DC (2013) Earth2Ocean Research Derby (2013) The ‘research derby’: a pressure cooker for creative and collaborative science. Ideas Ecol Evol 6: 40–66.
  51. 51. Vanderzwaag DL, Hutchings JA (2005) Canada's marine species at risk: Science and law at the helm, but a sea of uncertainties. Ocean Dev Int Law 36: 219–259.
  52. 52. Mooers AO, Prugh LR, Festa-Bianchet M, Hutchings JA (2007) Biases in legal listing under Canadian endangered species legislation. Conserv Biol 21: 572–575.
  53. 53. Taylor EB, Pinkus S (2013) The effects of lead agency, nongovernmental organizations, and recovery team membership on the identification of critical habitat for species at risk: Insights from the Canadian experience. Environ Rev 21: 93–102.