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Shrimp Farming and the Environment - Library

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arrangement in Thail<strong>and</strong>, for example <strong>the</strong> Kung Krabaen Bay Royal Development Project inChantaburi.The third approach is to reduce <strong>the</strong> total area of shrimp farming, <strong>and</strong>/or ensure that any future increasesin production come from <strong>the</strong> same or a lesser area of l<strong>and</strong>, so that no fur<strong>the</strong>r destruction of mangrove isallowed. This implies intensification of production. It is essential that appropriate skills, improvedwater management <strong>and</strong> technology, strategies for disease management, <strong>and</strong> appropriate infrastructureare developed in parallel with intensification, if this approach is implemented.Whatever approach is taken, <strong>the</strong> value of natural habitat <strong>and</strong> productive l<strong>and</strong> must be assessed withinan appropriate natural resource planning framework, <strong>and</strong> some form of rational l<strong>and</strong> use allocation<strong>and</strong>/or zoning must be introduced. If effectively implemented, such policies should minimize habitatdestruction by coastal aquaculture <strong>and</strong> o<strong>the</strong>r activities, <strong>and</strong> protect <strong>the</strong> most valuable remaining naturalhabitat. Approaches to resource assessment <strong>and</strong> l<strong>and</strong> use planning in relation to aquaculture have beenrecently reviewed by GESAMP (1999). Where shrimp farms are developed on acid soils, pond wateracidity may be countered through regular flushing <strong>and</strong> treatment with lime, or in some cases withoxidation <strong>and</strong> flushing. Alternatively, ponds may be lined with concrete, laterite, or PVC, although<strong>the</strong>re may be some disadvantages in using PVC pond liners in terms of water quality (Wanuchsoontorn1997). However, all <strong>the</strong>se practices will increase <strong>the</strong> cost of operation <strong>and</strong> <strong>the</strong> risk of failure, comparedto farms constructed in nonacidic or low-acid soils.Contamination <strong>and</strong> salinization of groundwaterContamination of groundwaterWater use in shrimp farming is extremely variable, ranging from little more than make-up water tocompensate for evaporation <strong>and</strong> seepage to very high rates of exchange. For example, for each metricton of shrimp produced, intensive farms require 50 to 60 million liters of water, according to Gujja <strong>and</strong>Finger-Stich (1995). Recent trends in Thail<strong>and</strong>, however, have intensive farms using minimal waterexchange, relying on intensive aeration <strong>and</strong> skilled management to maintain water quality.While extensive farms often rely on exchanging water by using tidal ebb <strong>and</strong> flow, some semiintensive<strong>and</strong> intensive farms use large amounts of freshwater to mix with seawater, or to make up forevaporation in ponds, in order to maintain what is thought to be an optimum salinity of 15–20 ppt.Pumping freshwater from groundwater is reported to have significant environmental effects,contributing to problems such as:• Saltwater intrusion into groundwater reservoirs;• L<strong>and</strong> subsidence; <strong>and</strong>• Loss of water supplies for agricultural <strong>and</strong> domestic purposes.These effects are reported in a number of countries <strong>and</strong> regions, including Taiwan, Republic of China;Thail<strong>and</strong>; Indonesia; <strong>the</strong> Philippines; <strong>and</strong> Ecuador (Primavera 1994; Clay 1996; Dierberg &Kiattisimkul 1996). In Taiwan, Republic of China, such problems contributed to <strong>the</strong> shrimp crisis in <strong>the</strong>late 1980s.Some experts claim that <strong>the</strong> practice of mixing water to obtain a salinity of approximately 15 ppt is notnecessary, <strong>and</strong> that this practice is rare even in Asia (Boyd 1997). New management practices that uselow water exchange rates have probably reduced this problem substantially worldwide.<strong>Shrimp</strong> farming in freshwaterPenaeus monodon is highly tolerant of low salinity <strong>and</strong>, if given time to acclimatize, can be grown inwater of close to zero salinity (Ullah 1995). This adaptability has allowed <strong>the</strong> spread of shrimp farminginto inl<strong>and</strong> waters (Ponza 1999). Concentrated seawater is trucked inl<strong>and</strong> <strong>and</strong> added to small ponds ornursery enclosures to provide an initial salinity of 7–10 ppt. Passive water exchange with a partiallyfilled grow-out pond results in a steady reduction in salinity. Finally <strong>the</strong> ponds are filled, <strong>and</strong> salinity isreduced to close to zero for <strong>the</strong> bulk of <strong>the</strong> grow-out cycle. Water management is usually based on <strong>the</strong>semiclosed system, in which water is added to <strong>the</strong> system, but effluent is not discharged until <strong>the</strong> end of23

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