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Remote sensing to reduce uncertainty in environmental policy in SE Asia Daniel Friess, Edward L. Webb [email protected]

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Page 1: Remote sensing to reduce uncertainty in environmental ...lcluc.umd.edu/sites/default/files/lcluc_documents/friess_0.pdf · 50% of all mangroves lost since 19007 Dramatic mangrove

Remote sensing to reduce uncertainty in environmental 

policy in SE Asia

Daniel Friess, Edward L. Webb        

[email protected]

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50% of all mangroves lost since 19007Dramatic mangrove loss

50 000 ha lost in Indonesia in 5 years41.9 million ha lost in SE 

Asia from 1980 to 20054

1225.5 km2 in Sabah wood chip export to Japan5

Thailand 312700 ha  168683 ha between 1975 and 19932

75% of Asian mangroves lost in 20th century8

Mangrove loss > x2 rainforest loss7

24% of mangroves globally are degraded6

2.1% global decline per year3

38% global mangrove loss by shrimp culture6

Malaysia loss 17% 1965‐851

Philippines 70% loss 1920 to 19901 India loss 50% 1963‐19771

110 000 ha lost in Malaysia in 25 years4

Vietnam loss from 4000 km2 (1945) to 2130 km2 (1998)9

12% of Singapore’s mangrove lost 1980‐904

Mangrove cover in Singapore from 13% to 0.5% of land area by 2002

SE Asia shows the highest mangrove loss globally6

50% of mangrove loss due to shrimp aquaculture8

50% of global wetlands have been lost

1‐3% loss in SE Asia per year10

All mangroves lost by 21003

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Conservation needs solid baselines

‐ Payment for Ecosystem Services (e.g. REDD+). How to prove quantitatively that deforestation has been reduced?

Uncertainty shown for tropical forest, global forest, peat swamp, with poor national inventories in developing nations (Grainger, FAO 2007 and others) 

Current mangrove loss statistics do not meet these requirements 

UNFCCC resolution FCCC/CP/2009/11/Add.1 (Copenhagen):

a monitoring system must be established and historical data utilised by signatory countries in order to “provide estimates that are transparent, consistent, as far as possible accurate, and that reduce uncertainties”

5 UNFCCC principles – transparency, consistency, comparability, completeness,  accuracy

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Do we have solid baselines?‐ In‐depth literature review: >600 data points – 461 points used‐ 6 Trends: FAO (2007a,b, 2010), inter‐/non‐governmental, academic, govt.‐ Linear regression models, ANCOVA, prediction intervals to highlight uncertainty

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Indonesia

23 661 km2

20.9% of global mangrove cover (1st) (Spalding et al. 2010)

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Australia

FAO (2007) trend 7763FAO (2007) pred. 7424

All 2227

FAO (2010) pred. 2147

academic

worst case 2020

Govt. 2101

6.5% of global mangrove cover (3rd) (Spalding et al. 2010)

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Vietnam0.7% of global mangrove cover (Spalding et al. 2010)

0

500

1000

1500

2000

2500

3000

3500

4000

4500

5000

1940 1950 1960 1970 1980 1990 2000 2010

Man

grove area

 (sq km

)

Year

FAO (2007a) trend

FAO (2007a) prediction

FAO (2010) prediction

IGO

Academic

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Peninsular Malaysia

Friess & Webb 2011, Environmental Conservation 38: 1‐5

0.8% of global mangrove cover (Spalding et al. 2010)

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Why so much uncertainty?

1. lack of robust methodology (grey/govt. literature)‐ how derived? Remote sensing? Best guess?

Friess & Webb 2011, Environmental Conservation 38: 1‐5

Poor transparency in historical estimates

2. traceability of secondary info‐ poor referencing, poor citation‐ grey literature (Corlett, 2011)

3. propagation of erroneous info

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The way forward

We increase robustness by increasing transparency

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Remote sensing

State inventories for P. Malaysia

Unsupervised env. modelling method for classifying land use change in the Ayerwaddy delta, Myanmar 

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Remote sensing

+ work by Giri and others(global, SE Asia, Philippines, Pacific)

Govt. studies e.g. CONABIO

+ for other forest types:‐NASA LCLUC programmes‐ Global Forest Info System ‐ EU TREES project‐FAO GFRA 2010 (Potapov et al. 2011)

i.e. transparentmapping, accepted interpretation (GOFC‐GOLD REDD sourcebook)

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CONABIO (Mexico)

How do we ensure that all countries present data like this?

How do we connect academics, IGOs, Govts to provide accurate information for REDD+?

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Conclusions

• Mangroves have not been quantified to the extent of other ecosystems: uncertainty will hamper future conservation policies

• Increasing transparency and rigour will improve historical estimates, while explicit methodologies will improve future prediction

• How to ensure accurate national monitoring systems – ASEAN level? Are current institutions adequate? Who should lead?

• These actions will provide environmental policy with more solid scientific foundations

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Acknowledgements

‐ Jacob Phelps, Alan Ziegler, Nick Jachowski (NUS)

‐ C Giri, K Krauss (US Geological Survey)

‐ N Saleh (Universiti Putra Malaysia)

‐ C Sudtongkong (Rajamangala University, Thailand)

‐MM Than (Mangrove and Environmental Rehabilitation 

Network, Myanmar)

‐ Landsat data shown acquired from GLCF

http://staff.science.nus.edu.sg/~apelab/friess.htm

[email protected]

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Such a monitoring system does not exist

‐ Variation in 6 trend lines:

‐ Grey denotes annual mangrove loss

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3. Error propagation – a UK example

Saltmarsh loss = 100 ha a‐1(UK Biodiversity Group 1999)

IPCC (2001) WG2, 3rd Assessment

2001

2002

2004Pontee et al. 2004Pilcher et al. 2004

2005

2006Badley & Alcorn 2006Hannaford et al. 2006

2007

Airoldi & Beck 2007

2010

+ 10s of local govt. reports and policies

2000 ‐ 2010

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The way forward

Also: World Mangrove Atlas, Giri et al. (2011)

Madagascar ‐ Giri et al. (2008)Kenya ‐ Neukermans et al. (2008)