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Volume III: Wastewater and excreta use in aquaculture Peter Edwards Guidelines overview 1. 2. 3. 4. 5. 6. 7. 8. 9. Introduction The Stockholm Framework Assessment of health risk Health-based targets Health protection measures Monitoring and system assessment Sociocultural, environmental and economic aspects Policy aspects Planning and implementation Definitions Wastewater and excreta (waste) domestic sewage without significant industrial effluents excreta faeces and urine faecal sludge, septage and nightsoil Direct and indirect use of waste Aquaculture fish, non-molluscan shellfish (crustaceans) and aquatic plants filter-feeding molluscan shellfish not considered Historical overview Waste-fed aquaculture centuries old in several countries in East, South and Southeast Asia, especially China Developed mainly by farmers and local communities to use nutrients to produce aquatic food Engineered wastewater treatment systems with aquaculture Germany from end 19th century India from 1930s China from 1950s Vietnam from 1960s Very few engineered systems developed recently Wastewater-fed fish ponds in Munich, Germany Wastewater-fed fish ponds with primary sewage distribution canal in foreground in Kolkata, India Wastewater-fed fish ponds in Wuhan, China Wastewater-fed fish ponds in Hanoi, Vietnam Overhung fish pond latrine in south Vietnam Waste-fed aquaculture strategies Harvesting fingerlings raised on wastewater in Hanoi, Vietnam Harvesting fish from a wastewater-fed fish pond in Kolkata, India Discharge of wastewater and water spinach cultivation in Phnom Penh, Cambodia Harvesting duckweed from a pond fertilized with polluted surface water, Taiwan Major hazards of waste-fed of waste-fed aquaculture Hazard Excreta-related pathogens - Bacteria e.g. Relative importance - Low to medium - Always high concentrations in gut - Cross-contamination in kitchen greatest risk - Hygienic processing and cooking reduce risk - Low to high - Risks lower for fish than plant producers and consumers - Nil to high Restricted geographical ranges - Risk where endemic and fish or plants eaten raw Salmonella - Soil transmitted helminthes e.g. Ascaris - Foodborne trematodes e.g. liver flukes - Schistosome trematodes e.g. Schistosoma Comments - Nil to high - Restricted geographical ranges - Transmitted through water contact Major hazards of waste-fed aquaculture (continued) Hazard Relative importance Comments - Low to medium - Same as bacteria - Viruses e.g. hepatitis - Low to medium - Same as bacteria Skin irritants - Medium to high - Contact dermatitis - Cause likely due to microbes and chemicals Vector-borne - Nil to medium - No specific risk associated with aquaculture Excreta-related pathogens - Protozoa e.g. Giardia pathogens e.g. malaria Major hazards associated with waste-fed aquaculture (continued) Hazard Relative importance Comments Chemicals - Antibiotics - Nil to low - Heavy metals - Low - Halogenated hydrocarbons - Low - Not usually used in waste-fed aquaculture - May accumulate in fish or aquatic plants but rarely to un safe levels - Wastewater and excreta generally low concentrations Microbial quality targets for waste-fed aquaculture Health protection measures Group Measure Produce Worker & consumer family Wastewater and excreta treatment Produce restriction Waste application witholding periods Control of trematode intermediate hosts Depuration Hygienic food handling, preparation Post-harvest processing Health and hygiene promotion Produce washing, disinfection, cooking + + + + + + + + + Local community + + + Health protection measures (continued) Group Measure Chemotherapy and immunization Use of personal protective equipment Safe drinking water at pond site Sanitation facilities at pond site Disease vector and intermediate host control Reduced vector contact Restricted access to pond site Produce Worker & consumer family + Local community + + + + + + + + + + + + Health and control measures in waste-fed aquaculture Produce restriction Fingerlings High-protein animal feed waste use in aquacultural nurseries to produce seed seed grow-out to full-size table fish in separate systems without use of wastes waste use to raise duckweed or tilapia feed to fish or livestock in separate systems without use of wastes Benefits reduced public health risk ‘lengthening of food chain’ may increase social acceptability of waste use Tilapia raised on septage as high-protein animal feed Duckweed raised on wastewater to feed fish in Khulna, Bangladesh Trematodes - schistosomes Schistosomes (blood flukes) infection by larvae penetrating skin of people entering water for domestic, occupational or recreational purposes Complex life cycles involving intermediate hosts, mainly snails Restricted geographical range so present a risk where endemic Trematodes – schistosomes (continued) Global health burden of 200 million people, mostly in SubSaharan Africa Limited direct waste-fed aquaculture in Africa but indirect use occurs Pockets of disease in Asia Health protection measures for trematode schistosomes Difficult to control domestic and wild animals may act as reservoirs molluscides adversely affect fish Protection achieved by combination of different health protection measures removal of vegetation effectively controls intermediate host snail populations chemotherapy effective against trematode infections Sociocultural aspects Positive correlation between occurrence of traditional waste use in societies and their population densities in recent past nutritional imperative in poor societies e.g. East Asia (China), South Asia (West Bengal, India) and Southeast Asia (Java, Indonesia) better chance to introduce waste-fed aquaculture in poor communities to contribute towards increased incomes and food security? Poor wastewater-fed fish farmers, Kolkata, India Transport of small fish harvested from wastewater-fed fish ponds by poor traders for consumption by poor people, West Bengal, India Marketing low-cost fish from wastewater-fed ponds in Kolkata, India Socio cultural aspects (continued) Reluctance or opposition to waste-fed aquaculture in societies with improved social and economic status Best example is China where waste-fed aquaculture is traditional and previously widespread practice nightsoil transported from cities to ponds in rural and periurban areas wastewater-fed ponds in periurban areas Recent and dramatic decline in waste-fed aquaculture, especially in China Reduced availability of nightsoil through improved sanitation Domestic wastewater contaminated with industrial sewage Rapid urban expansion so land prices risen Intensification of aquaculture reduced demand for fertilizer Consumers demand high-value fish rather than low-value fish from waste-fed ponds (often tainted with phenols) Pumping nightsoil into a barge for transport to farms in rural areas in the mid 80s, Shanghai, China Modern intensive aquaculture in Hangzhou, China Domestic wastewater used to farm fish contaminated with industrial sewage in Hanoi, Vietnam Urban encroachment on waste-fed aquaculture in Hanoi, Vietnam Environmental benefits Reduction of surface water pollution Conservation or more rational use of water, especially in arid and semi-arid areas e.g. Australia and the Middle East Reduction of risk of flooding in urban areas as extensive pond areas act as buffers during heavy rain Economic and financial feasibility Especially important for appraisal of viability of new schemes for waste use in aquaculture Some economic considerations waste-fed aquaculture may be considered as low-cost waste treatment system costs of waste treatment offset by sale of fish or aquatic plants Examples model developed to calculate revenues for wastewater-fed aquaculture in tropical and subtropical areas based on R & D in Lima, Peru integrated agriculture/forestry – fish culture in Kolkata, India R & D on wastewater-fed aquaculture in Lima. Peru Vegetables and trees fertilized with wastewater-fed fish pond water in Kolkata, India Recommended wastewater-fed fish pond design (Annex 1) Concept of minimal wastewater treatment in stabilization ponds for maximal production of microbially safe fish Design takes into consideration extremely rapid die-off of enteric bacteria and viruses in ‘green water’ ponds No maturation ponds, only anaerobic, facultative and fish ponds Total pond area of 6.25 ha is 7X larger than a conventional WSP to treat wastewater only