Impacts of Land Use Management on Ecosystem Services and Their Regulations

Zheng Hua

Research Center for EcoEco--EnvironmentalEnvironmental Sciences, Chinese Academy of Sciences

May 15, 2011 Xi’an Outline

 Challenges of ecosystem service management  Introduction of InVEST models  Impacts of alternative land use management on multiple ES: Island case study Challenges of ecosystem service management

 The benefits people obtain from ecosystems (MA, 2003)

Ecosystem services

Provisioning services Regulating services Cultural services

 Food  Spiritual/religious  Climate regulation  Freshwater  Recreation and  Disease regulation  Fuelwood ecotourism  Water regulation  Fibre  Aesthetic  Water purification  Inspirational  Biochemicals  Pollination  Educational  Genetic resources  Storm mitigation  Sense of place  Hydropower ……  Cultural heritage …… ……

Supporting services

Soil formation, Nutrient cycling, Primary production…… Challenges of ecosystem service management

 Uneven delivery of different kinds of services Agricultural productionTimber production Hydropower production

Water pollution regulation Flood mitigation Avoided reservoir sedimentation Challenges of ecosystem service management

 MA (2005): Approximately 60% (15 out of 24) of the ecosystem services (70% of regulating and cultural services) are being degraded or used unsustainably. Challenges of ecosystem service management

How to quantify and manage tradeoffs of multiple ecosystem services? How to sustain natural resources while promoting economic growth and quality of life? Introduction of InVEST models

 Stanford University, WWF and TNC (www.naturalcapitalproject.org).  A software system - InVEST: Integrated Valuation of Ecosystem Services and Tradeoffs  This tool informs managers and policy makers about the impacts of alternative resource management choices on the economy, human well-being, and the environment, in an integrated way (Daily, et al., 2009) Introduction of InVEST models InVEST can map & value  Biodiversity  Water pollution regulation  Carbon sequestration & storage  Managed timber production  Crop pollination  Avoided reservoir sedimentation  Tourism & recreation  Land use  Agricultural production  Soil type  Flood mitigation  Topograph  Hydropower production  Road  Irrigation  Cities  Open access products  Infrastructure Outline

Challenges of ecosystem service management Introduction of InVEST models Impacts of alternative land use management on multiple ES: Hainan Island case study  Study area: Hainan Island  Ecological protection challenges  Model selection and validation  Impacts of LULC change between 1998-2008  Alternative land use management impacts Study area: Hainan Island

Map of China  South of China, tropical climate  3.4 ×××10 4 km 2, 8.6 million people (2009)  Center: mountains, forest land 70%.  ; Yinggeling Mountain

Map of Hainan Island Terrain Study area: Hainan Island

 Water resource conservation  , Changhua River and : 47% area

 Biodiversity conservation  23th priority ecoregion for global conservation: 11 nature reserves

Hainan Peacock Pheasant Hainan Hill Partridge

endemic and endangered species Tianchi in Jianfengling

Daguangba reservoir in Ledong county Homalium hainanense Tree-fern ES protection challenges

Challenges on ES protection

 Large economy difference among the regions  Low compensative standard for Ecological Forest  Increasing area in Rubber tree (Hevea brasiliensis) is threatening the water quality and biodiversity of Hainan Island ES protection challenges Poverty

Simple house Simple house

Simple kitchen papaya ES protection challenges Rubber plantation and increased impacts

Rubber tree ( Hevea brasiliensis )

Natural forest destruction

五指山市化肥施用量 琼中县农药施用量

2000 250 200 1500 150 1000 100 500 50 农药施用量(吨) 化肥施用量(吨) 0 0 2002 2003 2004 2005 2002 2003 2004 2005 Used amount of fertilizer in Used amount of pesticide in Qiongzhong County ES protection challenges  Sharp contradiction between population and usable land

Destruction of tropical rain forest Destruction of natural forest

Nibbling into natural forest Killing of wildlife ES protection challenges

Questions:

 What are the impacts of LULC on important ES?

 How to improve regional ES by sustainable land use management in the future?  How to coordinate regional development and ES conservation by scientific policy design? Model selection and validation

Watershed name Area (km 2) Nandujiang 6841 Changhuajiang 4635 Wanquanhe 3235 Model selection and validation

Model application  Rubber production  Natural habitat  Water yield model  Water purification models (TN & TP): E&R  Sedimentation retention model: E&R  Storm peak mitigation model: Time to outlet; E&R  Carbon sequestration Model selection and validation

Corn

wetland Corn

Wetland

Wetland Mitigation Model selection and validation

 Model application – Regulating Services  Water yield model  Water purification models (TN & TP)  Sedimentation retention model

Hydrological Main LULC in 2008 Area (km 2) stations Longtang AL: 24%; RP: 40%; NF: 13% 6841 Santan - 1215 Jiaji AL: 4%; RP: 52%; NF: 25% 3235 Jiabao - 1157 Baoqiao AL: 6%; RP: 20%; NF: 52% 4635 Model selection and validation

Water yield model Water purification model – TP 100 600 y = 1.01x R² = 0.97 y = 0.81x 80 p < 0.01 500 R² = 0.94

) p< 0.01 3 m

8 400 60

300

40 200 Simulated value value (10 Simulated

20 phosphorus (t) total Simulated 100 Five watersheds 0 0 0 20 40 60 80 100 0 100 200 300 400 500 600 700 Observed value (10 8 m3) Observed total phosphorus (t)

Water purification model – TN Sedimentation retention model 7000 450

y = 1.11x 400 y = 1.23x 6000 R² = 0.92 R² = 0.74 p< 0.01 350 p < 0.01 t)

5000 3 300

4000 250

3000 200 150 2000 Simulated soil loss (10 loss soil Simulated 100 Simulated total nitrogen nitrogen total(t) Simulated

1000 50

0 0 0 50 100 150 200 250 0 1000 2000 3000 4000 5000 6000 Observed soil loss (10 3 t) Observed total nitrogen (t) Impacts of LULC change on ecosystem services

LULC change in Hainan Island

40 50 1998 1998 35 40 2008 30 30 20

10 25 2008in (%) 0 PL DL NF RP OF Shr G-L GL WBCLO

20 plantation plantation percentpercentrubberrubberAreaArea of of Land use and land cover type in 1998

15 Percent ofofPercentPercentareaarea (%) (%)

10

5 2008

0 PL DL NF RP OF Shr G-L GL WB CLO Land use and land cover type  Rubber plantation: 17.3% - 36.1%  Natural forest: 37.4% - 28.0% 1998 2008 Rubber Impacts of production 2.0 Carbon 1.5 Natural sequestration habitate 1.0 LULC 0.5 0.0 Storm peak Soil mitigation conservation

Total change on Total nitrogen phosphorus retention retention ecosystem (A) Nandujiang watershed

Rubber production 2.5 services 2.0 Carbon Natural sequestration 1.5 habitate 1.0 0.5 0.0 Storm peak Soil mitigation conservation

Total Total nitrogen phosphorus retention retention

(B) Changhuajiang watershed

Rubber production 2.0 Carbon 1.5 Natural sequestration habitate 1.0 0.5 0.0 Storm peak Soil mitigation conservation

Total Total nitrogen phosphorus retention retention

(C) Wanquanhe watershed Impacts of LULC change on ecosystem services

Impacts of LULC change on ecosystem services

Scenarios – NRPE: No Rubber Plantation Expansion – CEM: Complex Ecosystem Management – REP: Restoration of Natural Forest

Complex ecosystem management Monoculture (Adaptive management) Impacts of LULC change on ecosystem services Impacts of LULC change on ecosystem services

Tradeoffs between ecosystem provisioning and regulating services

2008 NRPE Rubber 2008 NRPE CEM RNF production Rubber 4.0 CEM RNF Carbon 3.0 Natural sequestration habitate production 2.0 2.0 1.0 0.0 1.5 Storm peak Soil Carbon Natural mitigation conservation sequestration habitate 1.0 Total Total nitrogen phosphorus retention 0.5 retention (A) Nandujiang watershed 0.0 Storm peak Soil Rubber production mitigation conservation 3.0 Carbon 2.0 Natural sequestration habitate 1.0

Total Total 0.0 Storm peak Soil phosphorus nitrogen mitigation conservation retention retention Total Total phosphorus nitrogen (B) Changhuajiang Watershed retention retention (C) Wanquanhe watershed Conclusions and recommendations

 One service may be gained at the expense of another. Rubber provisioning service production undermined the ecosystem regulating services: sediment, TN, TP retention, natural habitat, storm peak mitigation and the sustainability of productivity.  Actively adaptive management will improve sediment/TN/TP retention, storm peak mitigation and conserve regulating services.  The analysis of spatial patterns of ecosystem services with the InVEST models helped us understand how ecosystem services change and are distributed across the landscape.  The case provides a general methodology for managing tradeoffs between the ecosystem provisioning and regulating service, showing investment returns through time. Conclusions and recommendations

 Suggestions :  Accounting regulating ecosystem services for regional sustainable land use planning and restoration planning;  Excluding rubber plantation from the classification of ecological forest due to its great impacts;  Reforming water resource fee price system and implementing ecological compensation to coordinate ES conservation and development;  Implementing adaptive management for rubber plantation to improve the ecosystem regulating services. Many thanks to Professor Gretchen Daily and NatCap team!