Ecological Impact of Nutrients from Shrimp Farms Mark O’Donohue, Adrian Jones, Simon Costanzo, Michele Burford, Pat Glibert, Judy O’Neil, Cindy Heil & William Dennison Marine Botany THE UNIVERSITY OF QUEENSLAND Assessing Ecological Health Ecological health has been variously defined, including: • Ecological health is the maintenance of biodiversity and ecosystem integrity (Draft ANZECC Guidelines) • Ecological health is represented by a) a lack of ‘distress syndrome’ b) stability over time and c) resilience to change These definitions are appropriate for describing the ecological health concept, but do not define ecological health in terms of measurable quantities Measuring Ecological Health Ecological Health Indicators • Habitat: seagrass depth range, phytoplankton density (Chla) • Anthropogenic Impact: delta 15N, %N, amino acids, nutrient flux, water quality • Key Processes: denitrification, sediment N flux, phytoplankton bioassays N Limitation in coastal waters Phytoplankton bioassay responses N (not P) additions stimulate phytoplankton biomass Treatment Stimulation Factor Control DIN (NH4 + NO 3) PO4 1 6 1 SiO3 All 1 11 DIBM 1998 Macroalgal tissue nutrient content* %N correlates with dissolved inorganic [N] r2 = 0.68 %P does not correlate with dissolved inorganic [P] r2 = 0.08 *Horrocks et al. 94 N-Form influences biotic response 100 80 60 40 20 0 0 20 40 60 80 100 100 80 60 40 20 0 0 20 40 60 80 100 Macrophyteb • NH4+/Urea/NO3- ratio affects macrophyte amino acid content a Glibert, % Uptake of urea % Uptake of ammonium Planktona • N preference NH4+>Urea>>NO3• NH4+ Diatoms • Urea Dinoflagellates • NO3Denitrifying bacteria % Diatoms % Dinoflagellates O’Neil, Heil and O’Donohue b Jones, Horrocks, Udy and Dennison The Problem •Small fraction of nutrients added to aquaculture ponds is absorbed by target species Feed 2600 10400 Effluent 7000 NH4 15000 5400 Sediment (g/ha/d) Nitrogen budget (Burford et al. 99) •Large fraction of nutrients added to aquaculture ponds is exported •Nutrient enrichment of receiving waters could have potential deleterious impact on ecological health Key features of Shrimp Farm Effluent • • • • • Composition seawater clay particles marine phytoplankton particulate and dissolved nutrients [NH4+]>[NO3-]>[PO43-] By comparison, sewage effluent • freshwater • dissolved nutrients • [NO3-]>[NH4+][PO43-] Implications High [nutrient] particularly [NH4+] phytoplankton bloom potential Elevated turbidity potential for nutrient sorption Aims • Develop & test ecological health indicators for shrimp farm effluent • Using appropriate indicators, assess influence of shrimp farm effluent on ecological health of receiving waters • Formulate recommendations for aquaculture effluent management Vegetation Nutrient Content Delta 15N [Amino Acid] Study Site: Moreton Bay (estuary) Moreton Bay Delta 15N mangrove, seagrass and macroalgae (passive indicators) Amino acid concentration and composition - seagrass Amino Acid Concentration 15 000 10 000 Amino Acid Composition Other Glutamine 5 000 nmol g fresh -1 Proline Phytoplankton bioassays Nutrient response Study Site: Hinchinbrook Channel (tidal creek) Hinchinbrook Channel 0 5 10 15 20 25 30 Kilometers Phytoplankton bioassays - Dry Phytoplankton bioassay - Dry/Wet Delta 15N - Macroalgae (4 day incubation) Shrimp farm - Conceptual model Dissolved N Elevated delta15N Particulate N Elevated Elevated phytoplankton [amino acid] bloom potential Low particulate and dissolved N •Low delta15N •Low [amino acid] •Low phytoplankton bloom potential Summary • Coastal ecosystems N limited • Shrimp farms contribute large proportion of feed N to receiving waters • Nutrients from aquaculture discharge stimulate phytoplankton blooms (but effluent is not an ‘inoculum’ for receiving waters) • N form can influence physiology and community structure in receiving waters • Ecological health indicators provide direct measures of influence of aquaculture discharge Implications Recommend • On-farm N removal to reduce downstream impacts • Oxidation of N compounds to reduce potentially toxic dinoflagellates and enhance denitrification Ecological Health Indicators • Can be used to assess potential influence of discharge on intake waters • Provide a mechanism for assessing downstream impacts in a growing industry in relation to other N sources Acknowledgments • • • • Cooperative Research Centre for Aquaculture Marine Botany, University of Queensland CSIRO Marine Research Horn Pt Labs, University of Maryland