This is a repository copy of INCORPORATING CONNECTIVITY INTO CONSERVATION PLANNING FOR OPTIMAL REPRESENTATION OF MULTIPLE SPECIES AND ECOSYSTEM

Current conservation planning tends to focus on protecting species ranges or landscape connectivity but seldom both – particularly in the case of diverse taxonomic assemblages and multiple planning goals. Therefore we lack information on potential tradeoffs between maintaining landscape connectivity and achieving other conservation objectives. Here we develop a prioritization approach to protect species ranges, different ecosystem types, and forest carbon stocks, while also incorporating dispersal corridors to link existing protected areas and habitat connectivity for protection of range-shifting species. We apply our framework to Sabah, Malaysia, where the State Government has mandated an increase in protected area coverage of ~305,000 ha but without having specified where the new protected areas will be. Compared to conservation planning that does not explicitly account for connectivity, our approach increased the protection of dispersal corridors and elevational

[1]  R. Heikkinen,et al.  Incorporating landscape heterogeneity into multi-objective spatial planning improves biodiversity conservation of semi-natural grasslands , 2019, Journal for Nature Conservation.

[2]  Hugh P. Possingham,et al.  The use, and usefulness, of spatial conservation prioritizations , 2018 .

[3]  David Mouillot,et al.  Biologically representative and well‐connected marine reserves enhance biodiversity persistence in conservation planning , 2018 .

[4]  Matthew Strimas-Mackey,et al.  Reserve design to optimize the long-term persistence of multiple species. , 2018, Ecological applications : a publication of the Ecological Society of America.

[5]  Hugh P. Possingham,et al.  Operationalizing ecological connectivity in spatial conservation planning with Marxan Connect , 2018, bioRxiv.

[6]  L. Bastin,et al.  Protected area connectivity: Shortfalls in global targets and country-level priorities , 2018, Biological conservation.

[7]  A. Moilanen,et al.  Examining current or future trade-offs for biodiversity conservation in north-eastern Australia , 2017, PloS one.

[8]  Ritesh Krishna,et al.  How to manipulate landscapes to improve the potential for range expansion , 2016 .

[9]  Atte Moilanen,et al.  Ecosystem services and connectivity in spatial conservation prioritization , 2016, Landscape Ecology.

[10]  Lawrence N. Hudson,et al.  Local biodiversity is higher inside than outside terrestrial protected areas worldwide , 2016, Nature Communications.

[11]  J. Brodie,et al.  How individual links affect network stability in a large-scale, heterogeneous metacommunity. , 2016, Ecology.

[12]  Jessie A. Wells,et al.  Alternative futures for Borneo show the value of integrating economic and conservation targets across borders , 2015, Nature Communications.

[13]  J. Hill,et al.  Protected areas in Borneo may fail to conserve tropical forest biodiversity under climate change , 2015 .

[14]  D. Gaveau,et al.  Targeted Conservation to Safeguard a Biodiversity Hotspot from Climate and Land-Cover Change , 2015, Current Biology.

[15]  D. Sheil,et al.  Four Decades of Forest Persistence, Clearance and Logging on Borneo , 2014, PloS one.

[16]  F. M. Pouzols,et al.  A method for building corridors in spatial conservation prioritization , 2014, Landscape Ecology.

[17]  Atte Moilanen,et al.  Methods and workflow for spatial conservation prioritization using Zonation , 2013, Environ. Model. Softw..

[18]  Atte Moilanen,et al.  Defining spatial priorities for capercaillie Tetrao urogallus lekking landscape conservation in south-central Finland , 2012 .

[19]  Jenny A. Hodgson,et al.  The Speed of Range Shifts in Fragmented Landscapes , 2012, PloS one.

[20]  Kristine N. Stewart,et al.  Averting biodiversity collapse in tropical forest protected areas , 2012, Nature.

[21]  Soo Chin Liew,et al.  Deforestation rates in insular Southeast Asia between 2000 and 2010 , 2011 .

[22]  Atte Moilanen,et al.  Applying spatial conservation prioritization software and high-resolution GIS data to a national-scale study in forest conservation , 2009 .

[23]  Atte Moilanen,et al.  Integrating conservation planning and landuse planning in urban landscapes , 2009 .

[24]  C. Bradshaw,et al.  Tropical turmoil: a biodiversity tragedy in progress , 2009 .

[25]  F. Siegert,et al.  Land cover change 2002–2005 in Borneo and the role of fire derived from MODIS imagery , 2007 .

[26]  Richard M Cowling,et al.  Conservation planning in a changing world. , 2007, Trends in ecology & evolution.

[27]  Atte Moilanen,et al.  The Boundary‐Quality Penalty: a Quantitative Method for Approximating Species Responses to Fragmentation in Reserve Selection , 2007, Conservation biology : the journal of the Society for Conservation Biology.

[28]  Atte Moilanen,et al.  Landscape Zonation, benefit functions and target-based planning: Unifying reserve selection strategies , 2007 .

[29]  Otso Ovaskainen,et al.  The metapopulation capacity of a fragmented landscape , 2000, Nature.

[30]  R. Mittermeier,et al.  Biodiversity hotspots for conservation priorities , 2000, Nature.

[31]  L. Fahrig,et al.  Conservation of fragmented populations , 1994 .

[32]  Roberta E. Martin,et al.  Mapped aboveground carbon stocks to advance forest conservation and recovery in Malaysian Borneo , 2018 .