What Will Remain? Predicting the Representation in Protected Areas of Suitable Habitat for Endangered Tropical Avifauna in Borneo under a Combined Climate- and Land-Use Change Scenario
Abstract
:1. Introduction
2. Materials and Methods
2.1. Study Site
2.2. Focal Species Selection
2.3. Environmental Data
2.3.1. Present Climate Data
2.3.2. Future Climate Data
2.3.3. Topographic Data
2.3.4. Land-Use Data
2.3.5. Layer Preparation
2.3.6. Protected Area Data
2.3.7. Habitat Suitability Modelling
2.3.8. Habitat Suitability and Protected Area Coverage Calculation and Analysis
3. Results
3.1. Current (2010) Habitat Suitability Modelling and Estimated Portion Protected
3.2. Future Habitat Suitability Modelling and Estimated Portion Protected
4. Discussion
4.1. Changes in the Area of Suitable Habitat
4.2. Representation of Threatened Avifauna in the BORNEAN PA Network
4.3. Conservation Implications and Recommendations
5. Conclusions
Supplementary Materials
Author Contributions
Funding
Institutional Review Board Statement
Informed Consent Statement
Data Availability Statement
Acknowledgments
Conflicts of Interest
References
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Species (Latin) | Species (Common) | IUCN Category | Habitat Preference |
---|---|---|---|
Aceros corrugatus | WrinkledHornbill | EN | Lowland evergreen forest extends into the selectively logged forest (Kemp, A.C, Boesman, P and Sharpe, 2019) |
Anthracoceros malayanus | Black hornbill | VU | Lowland primary forest, mostly <200 m, very occasionally up to 600 m (Kemp, Boesman and Sharpe, 2019) |
Berenicornis comatus | White-crowned hornbill | EN | Primary lowland and sometimes montane forest up to 1675 m (A. C. Kemp and Boesman, 2019b) |
Buceros rhinoceros | Rhinoceros hornbill | VU | Primary lowland forest, extending into the secondary forest up to 1400 m (A. C. Kemp and Boesman, 2019a) |
Caprimulgus concretus | Bonaparte’s Nightjar | VU | Lowland dipterocarp forest and secondary growth, sea level to <500 m (Cleere and Sharpe, 2019) |
Centropus rectunguis | Centropus rectunguis | VU | The undergrowth of lowland forest (Payne and de Juana, 2019) |
Chloropsis sonnerati | Greater green leafbird | VU | Lowland evergreen forest, extending up to 1100 m (Wells and Sharpe, 2019) |
Ciconia stormi | Storm’s stork | EN | Undisturbed lowland forest |
Cyornis caerulatus | Sunda Blue Flycatcher | VU | Lowland dipterocarp forest, sea-level to <500 m (Clement, 2019) |
Hydrornis baudii | blue-headed pitta | VU | Lowland primary forest extends up to 600 m (Erritzoe, 2019) |
Leptoptilos javanicus | Lesser adjutant | VU | Mangroves, coastland wetlands adjacent to lowland forest |
Mulleripicus pulverulentus | Great slaty woodpecker | VU | Semi-open tropical lowland forests, extending up to 2000 m (Winkler, Christie and Kirwan, 2019) |
Nisaetus nanus | Wallace’s hawk-eagle | VU | Lowland forest, rarely up to 1000 m (Clark and Kirwan, 2019) |
Psittacula longicauda | Long-tailed parakeet | VU | Extreme lowland, <300 m (Collar and Sharpe, 2019) |
Ptilocichla leucogrammica | Bornean wren-babbler | VU | Lowland dipterocarp forest extends into the montane forest (Collar and Robson, 2019) |
Rhinoplax vigil | Helmeted hornbill | CR | Extends up to 1500 m (Kemp, Sharpe and Boesman, 2019) |
Rhyticeros undulatus | Wreathed hornbill | VU | Occasionally lowland forest extends up to 2560 m (A. Kemp and Boesman, 2019) |
Setornis criniger | hook-billed bulbul | VU | Lowland forest, extending up to 1000 m (Myers, 2016b) |
Spilornis kinabaluensis | Mountain serpent eagle | VU | Montane and sub-montane forests, preferably ridgetops, 750–2900 m (Clark, Kirwan and Christie, 2019) |
Treron capellei | large green pigeon | VU | Lowland forest, preferably primary forest (Baptista et al., 2019) |
Available Range Size | IUCN Status | Species | Habitat Type | Suitable Available Habitat (km2) | Habitat within a PA (%) |
---|---|---|---|---|---|
Large | VU | Buceros rhinoceros | Lowland/Montane | 36,400 | 11.1 |
VU | Ptilocichla leucogrammica | Lowland/Montane | 44,616 | 6.16 | |
CR | Rhinoplax vigil | Lowland | 50,166 | 5.9 | |
VU | Rhyticeros undulatus | Lowland/Montane | 41,200 | 18.2 | |
Medium | VU | Anthracoceros malayanus | Lowland | 25,554 | 9.6 |
EN | Berenicornis comatus | Lowland/Montane | 12,721 | 13.4 | |
VU | Caprimulgus concretus | Lowland | 10,431 | 20.5 | |
VU | Centropus rectunguis | Lowland | 15,404 | 14.2 | |
VU | Cyornis caerulatus | Lowland | 21,760 | 15.5 | |
VU | Hydrornis baudii | Lowland | 25,542 | 14.9 | |
VU | Mulleripicus pulverulentus | Lowland/Montane | 22,292 | 8.6 | |
VU | Psittacula longicauda | Lowland | 21,394 | 6.7 | |
VU | Treron capellei | Lowland | 15,702 | 3.4 | |
Small | VU | Aceros corrugatus | Lowland | 8844 | 8.2 |
EN | Ciconia stormi | Lowland | 3950 | 11.5 | |
VU | Leptoptilos javanicus | Lowland | 5957 | 6.5 | |
VU | Nisaetus nanus | Lowland | 9639 | 16.4 | |
VU | Spilornis kinabaluensis | Lowland/Montane | 7881 | 30.2 |
Available Range Size | IUCN Status | Species | Predicted Change in Range Size over the 2010–2050 Window (%) | Predicted Change in the Portion of the Range Found within a PA over the 2010–2050 Window (%) | ||
---|---|---|---|---|---|---|
Scenario A1-B | Scenario B1 | Scenario A1-B | Scenario B1 | |||
Large | VU | Buceros rhinoceros | −10.41 | −7.10 | 0.67 | −2.53 |
VU | Ptilocichla leucogrammica | −71.22 | −66.20 | 6.16 | 4.14 | |
CR | Rhinoplax vigil | −32.15 | −37.45 | 2.01 | 0.79 | |
VU | Rhyticeros undulatus | −12.12 | −3.91 | 1.10 | −2.82 | |
Medium | VU | Anthracoceros malayanus | 19.21 | 37.74 | −3.59 | −4.11 |
EN | Berenicornis comatus | 22.26 | 51.09 | −3.80 | −6.50 | |
VU | Caprimulgus concretus | 292.22 | 207.51 | −11.90 | −13.86 | |
VU | Centropus rectunguis | 13.49 | 26.09 | −7.44 | −8.44 | |
VU | Cyornis caerulatus | −5.58 | −25.75 | −0.27 | 0.88 | |
VU | Hydrornis baudii | −31.47 | −30.46 | 2.39 | 1.09 | |
VU | Mulleripicus pulverulentus | −6.57 | 2.08 | −2.96 | −4.41 | |
VU | Psittacula longicauda | 9.32 | 27.34 | −2.97 | −3.88 | |
VU | Treron capellei | −16.57 | −2.01 | 1.90 | 0.93 | |
Small | VU | Aceros corrugatus | 67.31 | 39.15 | −2.52 | −3.99 |
EN | Ciconia stormi | 16.63 | 19.18 | −4.64 | −5.14 | |
VU | Leptoptilos javanicus | 19.25 | 21.67 | −2.38 | −3.63 | |
VU | Nisaetus nanus | 79.49 | 84.81 | −10.12 | −10.65 | |
VU | Spilornis kinabaluensis | −20.94 | −24.49 | −6.73 | −5.01 |
Scenario B1 Predictions (Low Emissions) | Scenario A1B Predictions (Medium–High Emissions) | |||||||
---|---|---|---|---|---|---|---|---|
Predicted Change in Suitable Habitat between 2010 and 2050 | ||||||||
F | d.f. | p | effect | F | d.f. | p | Effect | |
IUCN Category | 0.09 | 1,13 | 0.77 | none detected | 0.00 | 1,13 | 0.97 | none detected |
Habitat | 0.28 | 1,14 | 0.60 | none detected | 1.10 | 1,14 | 0.31 | none detected |
Current (2010) area available | 9.35 | 1,15 | 0.008 | Greater loss for large ranged-species | 11.24 | 1,15 | 0.004 | Greater loss for large ranged- species |
Predicted change in the proportion of the suitable habitat within a currently protected area between 2010 and 2050 | ||||||||
F | d.f. | p | effect | F | d.f. | p | Effect | |
IUCN Category | 0.08 | 1,13 | 0.78 | None detected | 0.08 | 1,13 | 0.77 | None detected |
Habitat | 0.11 | 1,14 | 0.77 | None detected | 1.04 | 1,14 | 0.33 | None detected |
Current (2010) coverage in PAs | 2.45 | 1,15 | 0.14 | None detected | 4.39 | 1,15 | 0.05 | None detected |
Current (2010) area available | 8.93 | 1,16 | 0.008 | Most loss at higher initial coverage | 13.24 | 1,16 | 0.002 | Most loss at higher initial coverage |
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Singh, M.; Badcock-Scruton, J.; Collins, C.M. What Will Remain? Predicting the Representation in Protected Areas of Suitable Habitat for Endangered Tropical Avifauna in Borneo under a Combined Climate- and Land-Use Change Scenario. Sustainability 2021, 13, 2792. https://0-doi-org.brum.beds.ac.uk/10.3390/su13052792
Singh M, Badcock-Scruton J, Collins CM. What Will Remain? Predicting the Representation in Protected Areas of Suitable Habitat for Endangered Tropical Avifauna in Borneo under a Combined Climate- and Land-Use Change Scenario. Sustainability. 2021; 13(5):2792. https://0-doi-org.brum.beds.ac.uk/10.3390/su13052792
Chicago/Turabian StyleSingh, Minerva, Jessamine Badcock-Scruton, and C. Matilda Collins. 2021. "What Will Remain? Predicting the Representation in Protected Areas of Suitable Habitat for Endangered Tropical Avifauna in Borneo under a Combined Climate- and Land-Use Change Scenario" Sustainability 13, no. 5: 2792. https://0-doi-org.brum.beds.ac.uk/10.3390/su13052792