4.6 Article

Integrating distribution models and habitat classification maps into marine protected area planning

Journal

ESTUARINE COASTAL AND SHELF SCIENCE
Volume 212, Issue -, Pages 40-50

Publisher

ACADEMIC PRESS LTD- ELSEVIER SCIENCE LTD
DOI: 10.1016/j.ecss.2018.06.015

Keywords

Ecological and functional surrogates; Endemic and threatened species; Fish; Habitat classification scheme; Habitat maps; Stakeholders; Local knowledge and expertise; Marine protected areas; Marxan; Conservation prioritization; Spatial management; Conservation planning; Data-deficient ecosystems

Funding

  1. University of Sydney
  2. NSW Department of Primary Industries
  3. Australia's Integrated Marine Observing System (IMOS) - Department of Innovation, Industry, Science and Research through the National Collaborative Research Infrastructure Scheme
  4. Australia's Integrated Marine Observing System (IMOS) - Department of Innovation, Industry, Science and Research through the Education Investment Fund
  5. Marine Biodiversity Hub through the Australian Government's National Environmental Research Program (NERP)

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Effective conservation planning requires biotic data across an entire region. In data-poor ecosystems conservation planning is informed by using environmental surrogates (e.g. temperature) predominantly in two ways: to develop habitat classification schemes (1) or develop species distribution models (2). We test the utility of both approaches for conservation planning of marine ecosystems, and rank environmental surrogates, such as depth and distance from shore, according to their power to predict the distribution and abundance of biotic species. Specifically, we compared a habitat classification scheme; based on coarse levels of habitat types derived from depth and distance from shore; against species distribution models, which predict fish abundance and prevalence as a function of environmental surrogates (depth, distance from shore, latitude, reef area, zoning, and several metrics of habitat structural complexity). We consistently set conservation target levels to 21% of each conservation feature, following global standards and a sensitivity analyses. Thus when running scenarios to protect fish species we aimed to protect at least 21% of each species, and when running scenarios of habitat classes, we aimed to protect at least 21% of each habitat class. We found that when aiming to protect 21% of the chosen conservation targets, distribution models protected 21% of the predicted abundance/occurrence of all modelled species and functional groups, but did not protect most habitats. Contrastingly, using a habitat classification scheme protected 21% of all habitat types and 34% of all species and functional groups, but required protecting three times more area. Thus, using only distribution models as targets in data-poor ecosystems could be a risky conservation planning strategy. Ultimately the best conservation outcomes were achieved by incorporating local knowledge to synthesize the conservation outcomes of both scenarios.

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