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Science forum Day 2 - Suan Pheng Kam - Integrated aquculture planning
 

Science forum Day 2 - Suan Pheng Kam - Integrated aquculture planning

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  • The youngest wetlands at the present Yellow River estuary is under strict conservation zone (about 37,000 ha) of the YRD Nature Reserve. Dongying is undergoing rapid economic development, fueled by rich petroleum resources – the Shengli oilfield in the YRD is the second largest in China Former and existing wetlands outside of the nature reserve are used for various economic activities.
  • Apart from the open waters of the river and the coastal waters, the most obvious natural wetlands in the Yellow River delta include the tidal mudflats, the saline reed marshes and isolated pockets of freshwater reed meadows. Figure 1 shows the spatial pattern of occurrence of these wetland types.
  • The ecosystem services identified with local experts as being important in the context of the YRD wetlands included provision of direct economic uses, water purification, greenhouse gases (GHG) mitigation and food web support. These were correspondingly used as the economic, water quality, climate change and biodiversity criteria in the analysis of land use impacts on the wetlands ecosystem services. For each of these criteria one or more indicators were identified, as listed in Table 2.
  • For the economic indicator, the production values of the major commodities were estimated based on secondary data available for the study area (Table 3).
  • For the biodiversity criterion, bird biodiversity was selected as the indicator. Birds are higher up the food chain and therefore their occurrence is a good indicator of ecosystem richness. Birds are also more easily spotted and counted. Table 4 compares the occurrence of four important crane species in different habitats in the YRD. It clearly shows that the reed swamp supports the highest diversity and numbers of cranes, followed by the tidal flats. With conversion of wetlands to agriculture and aquaculture, the biodiversity supporting function declines.
  • No local data were available to quantify greenhouse gas mitigation and nutrient retention by the YRD wetlands. Data from studies conducted on similar types of temperate wetlands in North America and Europe were presented as evidence to stakeholders, together with explanation provided in Table 7 on what factors enhance these ecosystem services. With this information, local stakeholders were asked to judge how changes made to the wetlands in the study area would compromise their water quality regulation and climate change mitigation services.
  • This is the standardized rating scores on wetland ecosystem services for different land use types. For criteria other than the economic indicator, benchmark conditions would be those of the undisturbed natural wetland habitats within the core nature reserve, which was assigned the maximum score of 10. The ratings results indicate recognition by stakeholders that while increasing the direct economic value, conversion of wetlands for agriculture, aquaculture and industrial development compromises other ecosystem services.
  • The location of the natural wetlands at the Yellow River estuary and along the coast, with conversional use of wetlands further inland, explains the sharp geographical contrast that is evident when the indicator scores are mapped (Figure 3) based on present land use. The contrast is stark and in opposing patterns for the climate change mitigation and economic indicators. The direct economic value of the nature reserve area is low compared with other areas where economic activities are carried out. On the other hand the natural wetlands rate highly for the other criteria representing ecosystem services associated with indirect use values. Notably, in terms of mitigation of GHG emission, the core area of the YRDNR with the largest extent of pristine salt marsh and reed swamp rates the highest.
  • In the multi-criteria evaluation exercise, the stakeholders were not comfortable about articulating specific preferences for unfamiliar concepts like ecosystem goods and services. Instead, in the group sessions different weighting scenarios were explored. In the “equal weighting” scenario, the four criteria categories (Table 2) were given equal weight of 0.25 when combining the standardized rating scores of their corresponding indicators for each land use type (shown in Figure 2). The mapped result is shown in Figure 4. It shows that with the non-economic aspects of wetlands ecosystem services being given equal consideration as the direct economic use, the natural wetlands have higher overall importance in delivering these services.
  • Even with proportionately greater emphasis (50% weight) given to the direct economic use criterion (with the other three criteria taking equal shares of the remaining 50%), the overall value of natural wetlands is not unsubstantial (Figure 5).
  • The importance the natural wetlands in providing services for climate change mitigation is illustrated in Figure 6, where emphasis is placed on this criterion in the multi-criteria evaluation. Given the prevailing concern over global warming issues, this important role of the estuarine wetlands of the YRD should not be overlooked.
  • Table 1 lists the current uses of the land and wetlands within the study area that were recognized by stakeholders, in relation with the main categories of use values generally recognized for natural resources.
  • For the water quality criterion, the indicator identified was nutrient (nitrogen, phosphorus) retention. In the absence of local data for these indicators, evidences were collected from studies conducted elsewhere. Table 5 lists the estimates of removal rates of nitrogen and phosphorus obtained from a study of Dutch wetlands (Goosen, 2006), indicating the high efficiency of the reed marsh in providing the water purification function in comparison with other land cover types.
  • Table 6 compares the carbon standing stock and carbon storage rates of different forest types. The estimates for temperate tidal salt marshes indicate a very high carbon sequestration capacity. YRD is found the same type of wetland.

Science forum Day 2 - Suan Pheng Kam - Integrated aquculture planning Science forum Day 2 - Suan Pheng Kam - Integrated aquculture planning Presentation Transcript

  • Valuing wetlands: what if TEV doesn’t work? - case of the Yellow River Delta * , China Presenter: Kam Suan Pheng WorldFish Science Week 18-22 July 2011 * Part of a two-year research project ‘Valuing living aquatic resources of wetlands in China’, funded by the Challenge Program for Water and Food, CPWF Phase 1
  • The Yellow River and its Delta
    • The Yellow River supplies water to12% of China's 1.3 billion people and 15% of its farmland; its annual runoff is only 2% of the national total
    • Prior to 1999, the lower reaches of the Yellow River ran dry in 21 out of 27 years, for a total of 1,090 days
    • The Yellow River Delta (YRD) covers 6000 km 2 and is still accreting, forming the youngest temperate wetland ecosystem in the world
    • 153,000 ha of the YR estuary has been gazetted as nature reserve, with 58,000 ha of core zone
    The Yellow River
  • Challenges faced
    • To justify maintaining environmental flow to the YRD estuary
    • Direct economic value of the delta resources is extremely high; the Shengli oilfield fuels Dongying’s economic growth - 2008 GDP: RMB2 trillion (~USD300 billion), growth rate: 13.7%
    • Local awareness of ecosystem services of wetlands is low; TEV for YRD is RMB3.2 billion
    • Rather than conducting economic valuation, we opted for semi-quantitative approach, focusing on raising stakeholder awareness
  • Study Site: Eastern Dongying municipality in the Yellow River Delta Oilfield Pond aquacultre and salt evaporatiuon pans Mudflats used for mollusk collection Agriculture, with pockets of drained wetlands Dongying City 20 June 2009 Landsat 5 satellite image courtesy of the U.S. Geological Survey, http://www.usgs.gov Protective coastal dyke & road The YRD Nature Reserve core conservation area – 37,000 ha Yellow River Airport
  • Methodology
    • Stakeholder consultations to identify the main wetlands ecological functions and ecosystem services that they recognize as important
    • GIS mapping of landuse using satellite imagery
    • Literature review to collect evidence and quantification of ecosystems services of wetlands
    • Engaged the local experts in rating the relative contributions of the main ecosystem services of the natural, disturbed and man-made wetlands (including aquaculture areas)
  • Map of land use in the study area
  • Criteria and indicators of the key ecosystem services of the wetlands in the Yellow River delta Criteria category Wetland service Indicator Economic Direct human use Production value: Harvesting mollusks Harvesting reeds Aquaculture Salt production Agriculture Eco-tourism Cultural value Water quality Purification Nutrient (N, P) retention Climate change GHG mitigation C storage & GHG emission Biodiversity Food web support Bird diversity
  • Estimates of production value for economic indicators related to direct use of wetland resources Per unit area production value RMB/ha Harvesting mollusks 4,300 Harvesting reeds 2,300 Freshwater – crab 21,600 Freshwater – fish 40,500 Freshwater - shrimp 120,000 Brackishwater - shrimp 67,500 Brackishwater - sea cucumber 120,000 Salt production 47,000-310,000 Agriculture 12,000-28,000
  • Aquatic bird occurrence in different habitats in the Yellow River Delta Nature Reserve
  • Factors that favor carbon and nutrient retention in wetlands Factors that favor GHG mitigation Nutrient sinks High rate of sediment accumulation Increases C burial Increases nutrient (N, P) burial High biomass (roots, microflora, phytoplankton) Captures atmospheric CO 2 Some vegetation types increase N burial Low O 2 condition Discourages CO 2 and NO 2 release Encourages N 2 release Saline condition, high SO 4 2- Lowers CH 4 generation
  • Standardized rating scores on wetland ecosystem services for different land use types.
  • Climate change (GHG mitigation) 气候变化 ( 减少温室气体的危害 ) Economic (income/returns) 经济 ( 收入 / 收益 ) Biodiversity (food web support) 生物多样性 ( 维持食物链 ) Water quality (purification) 水质 ( 净化 ) Mapped results of standardized rating scores on wetland ecosystem services for different land use types.
  • Multi-criteria combination map 平等权重 Equal weight Figure 4. Overall rating of wetland ecosystem services for different land use types, with equal weighting for the four criteria – direct economic value, water quality regulation, climate change mitigation and biodiversity support.
  • Multi-criteria combination map 注重经济发展 Economics emphasis Figure 5. Overall rating of wetland ecosystem services for different land use types, with 50% weighting for direct economic value and the remaining 50% equally weighted among the other criteria - water quality regulation, climate change mitigation and biodiversity support.
  • Multi-criteria combination map 注重减缓气候变化 Climate change emphasis Figure 6. Overall rating of wetland ecosystem services for different land use types, with 50% weighting for climate change mitigation and the remaining 50% equally weighted among the other criteria - water quality regulation, biodiversity support and direct economic value.
  • Recommendations
    • Enhance the value and benefits of the Nature Reserve - use it as outdoor laboratory and benchmark for quantifying ecosystem services of temperate estuarine wetlands
    • Provide incentives for low-impact and biodiversity-enhancing agriculture surrounding the Nature Reserve
    • Promote low-carbon aquaculture of organisms that sequester carbon, are lower down the food chain and requiring good-quality water, e.g. molluscs, sea cucumber, algae
    • Promote cleaner industries that create less water pollution
  • Conclusions
    • Without being thoroughly quantitative, but by presenting map outputs, we were able to flag key issues relating to the management of the wetlands and other land uses
    • Opportunities to improve the management of the wetlands of the YRD hinge on recognizing the broader ecosystem services of wetlands, both natural and manmade, and how their value can be enhanced.
    • Protecting the wetlands does not have to mean depriving people of opportunities for economic benefits. Carefully chosen economic activities can coexist with natural wetland conservation and, further, complement the ecosystem services that the wetlands provide. This can help realize the “highly efficient eco-economy” that Dongying municipality envisions, and for it to be a model for emulation elsewhere in China and around the world.
  • Thank you for your attention
  • Table 1. Current uses of the wetlands in eastern Dongying municipality USE VALUES CURRENT USE DIRECT USE Conversion: physical land area Urban/industrial Agriculture Salt production Aquaculture - freshwater Aquaculture - brackish water Consumptive: product extraction Mollusk, crustacea, fish Reeds, medicinal plants Non-consumptive Recreation, tourism In-situ research, education INDIRECT USE Regulatory (due to ecological processes) Storm protection Water purification Climate change mitigation Biological (including living aquatic resources) Recruitment/feeding Biodiversity
  • Table 5 . Nutrient removal rates of wetland types (example from the Netherlands) Source: Goosen , 2006 Nutrient removal (kg/ha/yr) Land cover N P Agricultural use 0 0 Reed marsh 279 13 Open water 45 0 Woodland 95 9 Reservoir 0 0
  • Table 6 . Carbon sequestration capacities of different forest types Source: Kennedy and Bjork (2009) Ecosystem Standing carbon stock (gC m -2 ) Long-term rate of carbon accumulation in sediment (gC m -2 y -1 ) Plants Soil Tropical forests 12,045 12,273 2.3-2.5 Temperate forests 5,673 9,615 1.4-12.0 Boreal forests 6,423 34,380 0.8-2.2 Tropical savannas and grasslands 2,933 11,733 Temperate grass- and shrub-lands 720 23,600 2.2 Deserts and semi-deserts 176 4,198 0.8 Tundra 632 12,737 0.2-5.7 Croplands 188 8,000 Wetlands 4,286 72,857 20 Tidal Salt Marshes 210 Mangroves 7,990 139 Seagrass meadows 184 7,000 83 Kelp Forests 120-720 NA NA
  • Study objectives
    • To assess how the ecosystem services of the coastal wetlands have been affected due to modification and conversion of wetlands for various economic activities;
    • To raise awareness and understanding among development agencies of the value of wetlands beyond their immediate and direct economic contributions; and
    • To identify strategies for reducing development impacts and enhancing future use value of the wetlands.