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Fal Estuary (Lower) and Percuil River (Cornwall)

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Fal Estuary (Lower) and Percuil River (Cornwall) EC Regulation 854/2004 CLASSIFICATION OF BIVALVE MOLLUSC PRODUCTION AREAS IN ENGLAND AND WALES SANITARY SURVEY REPORT Fal Estuary (lower) and Percuil River (Cornwall) 2010 (amended 2012) SANITARY SURVEY REPORT LOWER FAL ESTUARY Cover photo: East Bank. CONTACTS: For enquires relating to this report or For enquires relating to policy matters on the further information on the implementation of Sanitary Surveys in England implementation of Sanitary Surveys in and Wales: England and Wales: Simon Kershaw/Carlos Campos Linden Jack Food Safety Group Hygiene & Microbiology Division Cefas Weymouth Laboratory Food Standards Agency Barrack Road 3rd Floor Aviation House The Nothe 125 Kingsway Weymouth London Dorset WC2B 6NH DT43 8UB ( +44 (0) 1305 206600 ( +44 (0) 20 7276 8955 * [email protected] * [email protected] © Crown copyright 2010, amended 2012. Queen scallops (A. opercularis) at East Bank and overall review of production 2 areas in the lower Fal Estuary and Percuil River SANITARY SURVEY REPORT LOWER FAL ESTUARY STATEMENT OF USE: This report provides information from a study of the information available relevant to perform a sanitary survey of bivalve mollusc harvesting areas in the lower Fal Estuary, Cornwall. Its primary purpose is to demonstrate compliance with the requirements for classification of bivalve mollusc production areas in EC Regulation 854/2004 laying down specific rules for the organisation of official controls on products of animal origin intended for human consumption. The Centre for Environment, Fisheries & Aquaculture Science (Cefas) undertook this work on behalf of the Food Standards Agency (FSA). DISSEMINATION STATUS: Food Standards Agency, Falmouth & Truro Port Health Authority, Cornwall Sea Fisheries Committee, Environment Agency. RECOMMENDED BIBLIOGRAPHIC REFERENCE: Cefas, 2012. Sanitary Survey of the lower Fal Estuary and Percuil River (Cornwall). Cefas report on behalf of the Food Standards Agency, to demonstrate compliance with the requirements for classification of bivalve mollusc production areas in England and Wales under of Regulation (EC) No. 854/2004. Queen scallops (A. opercularis) at East Bank and overall review of production 3 areas in the lower Fal Estuary and Percuil River SANITARY SURVEY REPORT LOWER FAL ESTUARY CONTENTS 1. INTRODUCTION 2. SHELLFISHERIES 3. OVERALL ASSESSMENT 4. RECOMMENDATIONS 5. SAMPLING PLAN REFERENCES LIST OF ABBREVIATIONS GLOSSARY ACKNOWLEDGEMENTS APPENDICES I. Human population: density and activities II. Hydrometric data: rainfall III. Hydrometric data: freshwater inputs IV. Hydrodynamic data: bathymetry V. Hydrodynamic data: tides and currents VI. Meteorological data: wind VII. Sources and variation of microbiological pollution: sewage discharges VIII. Sources and variation of microbiological pollution: agriculture IX. Sources and variation of microbiological pollution: birds X. Sources and variation of microbiological pollution: boats XI. Microbiological data: water XII. Microbiological data: shellfish flesh XIII. Shoreline survey Queen scallops (A. opercularis) at East Bank and overall review of production 4 areas in the lower Fal Estuary and Percuil River SANITARY SURVEY REPORT LOWER FAL ESTUARY 1 INTRODUCTION 1.1 LEGISLATIVE REQUIREMENT Filter feeding, bivalve molluscan shellfish (e.g. scallops, mussels, native oysters) retain and accumulate a variety of microorganisms from their natural environments. Since filter feeding promotes retention and accumulation of these microorganisms, the microbiological safety of bivalves for human consumption depends heavily on the quality of the waters from which they are taken (Bell 2006). When consumed raw or lightly cooked, bivalves contaminated with pathogenic microorganisms may cause infectious diseases (e.g. Norovirus-associated gastroenteritis, Hepatitis A and Salmonellosis) in humans. Infectious disease outbreaks are more likely to occur in coastal areas, where bivalve mollusc production areas (BMPAs) are impacted by sources of microbiological contamination of human and or animal origin. In England and Wales, fish and shellfish constitute the fourth most reported food item causing infectious disease outbreaks in humans after poultry, red meat and desserts (Hughes et al. 2007). The risk of contamination of bivalve molluscs with pathogens is assessed through the microbiological monitoring of bivalves. This assessment results in the classification of BMPAs, which determines the level of treatment (e.g. purification, relaying, cooking) required before human consumption of bivalves (Lee and Younger 2002). Under EC Regulation 854/2004 laying down specific rules for the organisation of official controls on products of animal origin intended for human consumption, sanitary surveys of BMPAs and their associated hydrological catchments and coastal waters are required in order to establish the appropriate representative monitoring points (RMPs) for the monitoring programme. The Centre for Environment, Fisheries & Aquaculture Science (Cefas) is performing sanitary surveys for new BMPAs in England and Wales, on behalf of the Food Standards Agency (FSA). The purposes of the sanitary surveys are to demonstrate compliance with the requirements stated in Annex II (Chapter II paragraph 6) of EC Regulation 854/2004, whereby “if the competent authority decides in principle to classify a production or relay area it must: (a) make an inventory of the sources of pollution of human or animal origin likely to be a source of contamination for the production area; (b) examine the quantities of organic pollutants which are released during the different periods of the year, according to the seasonal variations of both human and animal populations in the catchment area, rainfall readings, waste-water treatment, etc.; Queen scallops (A. opercularis) at East Bank and overall review of production 5 areas in the lower Fal Estuary and Percuil River SANITARY SURVEY REPORT LOWER FAL ESTUARY (c) determine the characteristics of the circulation of pollutants by virtue of current patterns, bathymetry and the tidal cycle in the production area; and (d) establish a sampling programme of bivalve molluscs in the production area which is based on the examination of established data, and with a number of samples, a geographical distribution of the sampling points and a sampling frequency which must ensure that the results of the analysis are as representative as possible for the area considered.” EC Regulation 854/2004 also specifies the use of Escherichia coli as an indicator of microbiological contamination in bivalves. This bacterium is present in animal and human faeces in large numbers and is therefore indicative of contamination of faecal origin. In addition to better targeting the location of RMPs and frequency of sampling for microbiological monitoring, it is believed that the sanitary survey may serve to help to target future water quality improvements and better analyse their effects on BMPAs. Improved monitoring should lead to improved detection of pollution events and identification of the likely sources of pollution. Remedial action may then be possible either through funding of improvements in point sources of contamination or as a result of changes in land management practices. This report documents information relevant to undertake a sanitary survey for a new production area for queen scallops (A. opercularis), existing production areas for mussels (Mytilus spp.) and native oysters (O. edulis) in the lower Fal Estuary (Cornwall), and historic production areas in Percuil River. A draft report was issued for consultation in 2010. In light of new information subsequently received on fisheries and changes in harvesting, this final report is dated 2012. Queen scallops (A. opercularis) at East Bank and overall review of production 6 areas in the lower Fal Estuary and Percuil River SANITARY SURVEY REPORT LOWER FAL ESTUARY 1.2 SITE DESCRIPTION FAL ESTUARY (LOWER) The Fal Estuary, national grid reference (NGR) SW825342, is situated in south Cornwall, southwest coast of England. The estuary is sheltered, branched with many large and small tributaries and has a long shoreline (Table 1.1). It is a type 3b Ria without spits (Halcrow Group Ltd., 2002). Table 1.1 Main characteristics of the Fal Estuary. Geomorphological type 3b drowned river valley or ria Shoreline length (km) 127 Core area (ha) 2,482 Intertidal area (ha) 746 Data from the Estuary Guide (ABPmer and Wallingford 2009) The estuary narrows significantly towards its upper reaches. The bivalve mollusc production areas (BMPAs) assessed for the purposes of this sanitary survey are situated in Carrick Roads, a deep sub-tidal area which extends from Turnaware Point towards the mouth of the estuary at Falmouth (Figure 1.1). Figure 1.1 Aerial view of the Fal Estuary. Reproduced under licence Google EarthTM mapping service. Queen scallops (A. opercularis) at East Bank and overall review of production 7 areas in the lower Fal Estuary and Percuil River SANITARY SURVEY REPORT LOWER FAL ESTUARY Substrates in the lower Fal include rocky intertidal areas (Figure 1.2A), rockpools, gravel, intertidal sediments, subtidal rocks and sediments, fine and sandy muds (Figure 1.2B) and maerl debris (Potts and Swaby, 1993). Figure 1.2 Rocky shore at East Bank (A) and intertidal mudflat at St. Just Creek (B). Queen scallops (A. opercularis) at East Bank and overall review of production 8 areas in the lower Fal Estuary and Percuil River SANITARY SURVEY REPORT LOWER FAL ESTUARY Areas of saltmarsh occur
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