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231224s2014 xx |||||o 00| ||eng c |
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|a 10.1111/cobi.12364
|2 doi
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|a pubmed24n0804.xml
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|a (DE-627)NLM24128113X
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|a (NLM)25155174
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|a DE-627
|b ger
|c DE-627
|e rakwb
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|a eng
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| 100 |
1 |
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|a Connors, B M
|e verfasserin
|4 aut
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| 245 |
1 |
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|a Determining decision thresholds and evaluating indicators when conservation status is measured as a continuum
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|c 2014
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|a Text
|b txt
|2 rdacontent
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|a ƒaComputermedien
|b c
|2 rdamedia
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|a ƒa Online-Ressource
|b cr
|2 rdacarrier
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|a Date Completed 06.07.2015
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|a Date Revised 12.11.2014
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|a published: Print-Electronic
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|a Citation Status MEDLINE
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|a © 2014 Society for Conservation Biology.
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|a Categorization of the status of populations, species, and ecosystems underpins most conservation activities. Status is often based on how a system's current indicator value (e.g., change in abundance) relates to some threshold of conservation concern. Receiver operating characteristic (ROC) curves can be used to quantify the statistical reliability of indicators of conservation status and evaluate trade-offs between correct (true positive) and incorrect (false positive) classifications across a range of decision thresholds. However, ROC curves assume a discrete, binary relationship between an indicator and the conservation status it is meant to track, which is a simplification of the more realistic continuum of conservation status, and may limit the applicability of ROC curves in conservation science. We describe a modified ROC curve that treats conservation status as a continuum rather than a discrete state. We explored the influence of this continuum and typical sources of variation in abundance that can lead to classification errors (i.e., random variation and measurement error) on the true and false positive rates corresponding to varying decision thresholds and the reliability of change in abundance as an indicator of conservation status, respectively. We applied our modified ROC approach to an indicator of endangerment in Pacific salmon (Oncorhynchus nerka) (i.e., percent decline in geometric mean abundance) and an indicator of marine ecosystem structure and function (i.e., detritivore biomass). Failure to treat conservation status as a continuum when choosing thresholds for indicators resulted in the misidentification of trade-offs between true and false positive rates and the overestimation of an indicator's reliability. We argue for treating conservation status as a continuum when ROC curves are used to evaluate decision thresholds in indicators for the assessment of conservation status
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|a Journal Article
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| 650 |
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|a característica operante del receptor (ROC)
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| 650 |
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4 |
|a clasificación de amenazas
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| 650 |
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|a classification error
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| 650 |
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|a conservation status
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| 650 |
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|a error de clasificación
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|a estado de conservación
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| 650 |
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|a false negative
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| 650 |
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|a false positive
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| 650 |
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|a falso negativo
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|a falso positivo
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| 650 |
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|a incertidumbre
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| 650 |
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|a indicador
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| 650 |
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4 |
|a indicator
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| 650 |
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4 |
|a receiver operating characteristic (ROC)
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| 650 |
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4 |
|a signal detection theory
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| 650 |
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|a teoría de detección de señales
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| 650 |
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4 |
|a threat classification
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| 650 |
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4 |
|a uncertainty
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| 700 |
1 |
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|a Cooper, A B
|e verfasserin
|4 aut
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| 773 |
0 |
8 |
|i Enthalten in
|t Conservation biology : the journal of the Society for Conservation Biology
|d 1999
|g 28(2014), 6 vom: 26. Dez., Seite 1626-35
|w (DE-627)NLM098176803
|x 1523-1739
|7 nnns
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| 773 |
1 |
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|g volume:28
|g year:2014
|g number:6
|g day:26
|g month:12
|g pages:1626-35
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| 856 |
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|u http://dx.doi.org/10.1111/cobi.12364
|3 Volltext
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|d 28
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|h 1626-35
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