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001 | 9.816817 |
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003 | CaOODSP |
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005 | 20221107142332 |
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007 | cr ||||||||||| |
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008 | 160504s2016 oncd ob f000 0 eng d |
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040 | |aCaOODSP|beng |
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041 | |aeng|bfre |
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043 | |an-cn--- |
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086 | 1 |aFs70-5/2016-027E-PDF |
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100 | 1 |aThornborough, Kate. |
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245 | 10|aDevelopment of risk-based indicators for the SGaan Kinghlas-Bowie Seamount Marine Protected Area |h[electronic resource] / |cKate Thornborough, Jason Dunham, and Miriam O. |
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246 | 33|aÉlaboration d'indicateurs fondés sur les risques pour la zone de protection marine du mont sous-marin Bowie (SGaan Kinghlas) |
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260 | |aOttawa : |bFisheries and Oceans Canada, |c2016. |
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300 | |avii, 121 p. : |bill. |
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490 | 1 |aCanadian Science Advisory Secretariat research document, |x1919-5044 ; |v2016/027, Pacific Region |
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500 | |a“April 2016.” |
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504 | |aIncludes bibliographical references. |
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520 | 3 |aFisheries and Oceans Canada (DFO) Science was asked to recommend scientifically defensible indicators to monitor the achievement of the SGaan Kinghlas-Bowie Seamount Marine Protected Area (SK-B MPA) conservation objective. In response, a framework was developed to select and prioritize ecological risk-based indicators based on the outputs of an ecological risk assessment conducted on the SK-B MPA. Risk-based indicators are a novel approach to selecting indicators to monitor the risk of harm to Significant Ecosystem Components (SECs) from anthropogenic activities and associated stressors. Measures of abundance were commonly proposed across all indicator suites, highlighting the need to establish baselines of information as a priority. Both current snapshot and potential stressor indicator suites should be considered when developing monitoring strategies and plans, using a combination of SEC, stressor, and SEC-stressor interaction indicators. Due to the remote access and associated cost of monitoring indicators at the SK-B MPA, many of the suggested indicators may be measured using visual surveys and, due to the overlapping distribution of several SECs, multiple indicators may be measured or sampled during the same operations period. As data are collected through the monitoring of indicators, this information may be fed back into the adaptive management framework for future iterations of risk assessments, evaluation of selected indicators, selection of new indicators, and the refinement of monitoring plans. |
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692 | 07|2gccst|aMarine conservation areas |
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692 | 07|2gccst|aRisk management |
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692 | 07|2gccst|aEnvironmental indicators |
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700 | 1 |aDunham, J. S. |
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700 | 1 |aO, Miriam,|d1974- |
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710 | 1 |aCanada. |bDepartment of Fisheries and Oceans. |
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710 | 2 |aCanadian Science Advisory Secretariat. |
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830 | #0|aResearch document (Canadian Science Advisory Secretariat)|x1919-5044 ; |v2016/027, Pacific Region|w(CaOODSP)9.507396 |
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856 | 40|qPDF|s1.13 MB|uhttps://publications.gc.ca/collections/collection_2016/mpo-dfo/Fs70-5-2016-027-eng.pdf |
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