Aim. Survey Methodology

Similar documents
THE DYNAMICS OF ESTUARIES AND THEIR FISH POPULATIONS: implications for fish conservation in the Tidal Thames

Sampling Gears and other method. Teerapong Duangdee: Department of Marine Science, Faculty of Fisheries, Kasetsart University

Lecture 2: Sampling gear. Ichthyology 3

Downstream Migrant Trapping in Russian River Mainstem, Tributaries, and Estuary

Downstream Migrant Trapping in Russian River Mainstem, Tributaries, and Estuary

PROJECT Nº 96/005: SIZE SELECTIVITY AND RELATIVE FISHING POWER OF BALTIC COD GILL-NETS

Results of the 2015 nontidal Potomac River watershed Smallmouth Bass Young of Year Survey

Diadromous Fish Assemblage Assessment in the Saco River Estuary, ME

A guide to fisheries regulations ENVIRONMENT CORNWALL SEA FISHERIES COMMITTEE. WaW AGENCY

Sourced from:

Striped Bass and White Hybrid (x) Striped Bass Management and Fishing in Pennsylvania

Sustainable Recreational Fishing Student Activity Workbook 6.2. Sustainable Recreational Fishing

Welsh Waters Scallop Strategy 28 th May Summary of research

Juvenile Salmon Use of Knik Arm Estuaries. Hannah N. Ramage

Salmon in the classroom

Cambridge International Examinations Cambridge International Advanced Subsidiary and Advanced Level

THE BIOLOGY OF THE PRAWN, PALAEMON

FIGURE 1. TOTAL LENGTH OF FISH, IN THIS CASE A PILE PERCH, IS MEASURED FROM MOUTH TO TIP OF TAIL (ILLUSTRATION LARRY G. ALLEN).

Report on a Salmon Survey in the Waterford Estuary in 2010

ATLANTIC STATES MARINE FISHERIES COMMISSION. Winter Flounder Abundance and Biomass Indices from State Fishery-Independent Surveys

During the mid-to-late 1980s

Risk Assessments in the Pacific Fisheries for BC & Yukon

Fish Survey Report and Stocking Advice for Loch Milton. (Loch a Mhuilinn), May 2011

Introduction and Background

2014 Threatened and Endangered Fish Survey of. East Loon Lake and West Loon Lake. Lake County, Illinois

Countermeasures against Alien Fishes (Largemouth Bass and Bluegill) in Lake Biwa

Management advisory for the Bay of Bengal Indian mackerel fishery

SEAGRASS MAPPING FOR THE PENRHYN ESTUARY HABITAT ENHANCEMENT PLAN

Three different funding sources funded different facets of the research.

Fish Conservation and Management

2016 Diadromous Migration Season on the Presumpscot A R E P O RT F R OM THE GMR I FIS HE R IE S E C O L OGY LAB ON CB AS S

Size selectivity of tuna purse seine nets estimated from FAD sets data

New York District Briefing Template

Tracking Juvenile Summer Flounder

ICES WGCSE REPORT

European Smelt (Osmerus eperlanus L.) Baseline Surveys on the River Foyle, River Finn, River Deele & Burndennet River

IPHC Regulatory Area 2A Directed Commercial Pacific Halibut Fishery Sample Vessel Fishing Period Limit Options for Longer Fishing Periods

SOP Number: SOP026 Title: Fish Field Collection Methods Revision No: 04. Replaces: 03

A Combined Recruitment Index for Demersal Juvenile Cod in NAFO Divisions 3K and 3L

Fish Survey of Goose Lake (ID # ), Ramsey County, Minnesota in 2012

Balance in the Bay. An introduction to ecosystem-based management and the Monterey Bay market squid fishery.

Dauphin Lake Fishery. Status of Walleye Stocks and Conservation Measures

STOCK STATUS OF SOUTHERN BLUEFIN TUNA

2014 Winnebago System Walleye Report

We would also like to thank Dr. Martin O Grady (CFB) and No. 3 Operational Wing, Irish Air Corps (Aer Chór na héireann) for the aerial photographs.

Assessment of lumpfish Marine and Freshwater Research Institute, 13 June 2017

Cable Grid Testing 2018 Panama City Beach Trawl Diving and TED Testing

SEA GRANT PROGRESS REPORT

NEVADA DEPARTMENT OF WILDLIFE STATEWIDE FISHERIES MANAGEMENT

LAKE WASHINGTON SOCKEYE SALMON STUDIES. Richard E. Thorne and James J. Dawson

Falmouth and St.Austell pspa bird bycatch analysis report year

Salmon and Migratol~Y Trout of the N,anaimo 'River lind Adjacent Streams (Revised 1,973)

ASMFC Stock Assessment Overview: Red Drum

Preliminary analysis of yellowfin tuna catch, effort, size and tagging data using an integrated age-structured model

We would also like to thank Dr. Martin O Grady (CFB) and No. 3 Operational Wing, Irish Air Corps (Aer Chór na héireann) for the aerial photographs.

Stillwater Status Report: Lough Muck, County Donegal

Nearshore Ecology of Atlantic Salmon in the Gulf of Maine Region. Workshop 2: Bays and the Gulf of Maine

Trials of a Net Grid for the UK Nephrops trawl fisheries

Potomac River Muskellunge

Managing Chesapeake Bay s Land Use, Fish Habitat, and Fisheries: Studies. Jim Uphoff & Margaret McGinty, Fisheries Service

Distribution of fishing intensity of pulseand beam trawling in the North Sea. Marcel Machiels. IMARES rapport C146A/15

MOANA NEW ZEALAND & SANFORD MĀUI DOLPHIN PROTECTION PLAN

Know Your River River Afan Salmon and Sea Trout Catchment Summary

Stillwater Status Report: Lough Muck, County Tyrone

5. purse seines 3 000

Annual Pink Shrimp Review

Gear Changes for the Pacific Coast Groundfish Fishery s Trawl Catch Share Program Preliminary Draft EIS

Winter Culture of Caged Rainbow Trout in the South.

Status of Yellow Perch in Lake Michigan

FISHERIES & CONSERVATION SCIENCE GROUP

Cedar Lake Comprehensive Survey Report Steve Hogler and Steve Surendonk WDNR-Mishicot

c h a p t e r 6 n n n Related to the VAMP

Fishing for Red Drum

Ref. No. [UMCES CBL]

Marine Aquaculture Opportunities for NC. Chuck Weirich NC Sea Grant

Stuart J. Hetherington, Victoria A. Bendall & Paul Trebilcock. FDI symposium, Rome 3 rd 6 th March 2014

Baltic Marine Environment Protection Commission Group on Ecosystem-based Sustainable Fisheries Gothenburg, Sweden, May 2016

Fish Conservation and Management

Characterization of the Sole Fishery in The Gambia. Gambia-Senegal Sustainable Fisheries Program (Ba Nafaa)

The Life History and Management of Alewife (Alosa pseudoharengus)

Nechako white sturgeon are an Endangered Species

Observed pattern of diel vertical migration of Pacific mackerel larvae and its implication for spatial distribution off the Korean Peninsula

2015 Winnebago System Walleye Report

Atlantic States Marine Fisheries Commission

Preliminary Report. Note: calculations reported are preliminary and should not be cited without the author s permission. December 21, 2003.

Water Framework Directive Fish Stock Survey of Transitional Waters in the South Western River Basin District Lough Gill

2017 Lake Winnebago Bottom Trawling Assessment Report

Small pelagic fishery and research in Albania

Management advisory for the Bay of Bengal hilsa fishery June 2012

The development of novel sampling protocols for endangered fish species in Irish lakes: Trials and Triumphs Inland Fisheries Ireland

Essential Fish Habitat Description Atlantic herring (Clupea harengus)

Figure 1. Pair trawlers are in operation.

LONE TREE POCKET ESTUARY RESTORATION 2004 FISH SAMPLING AND PRE-RESTORATION PROJECT MONITORING REPORT

Managing Development and Chesapeake Bay s Estuarine Fish

CONSERVATION AND MANAGEMENT MEASURE TO MITIGATE THE IMPACT OF FISHING FOR HIGHLY MIGRATORY FISH STOCKS ON SEABIRDS

Taïp chí Khoa hoïc - Coâng ngheä Thuûy saûn Soá 1/2010 THOÂNG BAÙO KHOA HOÏC. Nguyen Phong Hai 1 and Other 2

SARASOTA BAY ESTUARY PROGRAM OYSTER HABITAT MONITORING RESULTS: YEAR 1. Jay R. Leverone

Hakes Assessment SARC 51. Whiting NEFMC PDT Meeting February 14, 2011 Milford, MA

Best Practice Guidance for Assessing the Financial Performance of Fishing Gear: Industry-led gear trials

Project Limulus on Napatree Point: Horseshoe Crab Surveys in 2017

Transcription:

The fish that smells of cucumber: conservation of smelt Osmerus eperlanus in the Thames Estuary Interim Report on results of 2015 survey work Joanna Barker Project Manager, Europe Conservation Programme December 2015 Aim Identify important habitats for smelt in the Thames Estuary, in particular the spawning ground, to inform a Smelt Management Plan for the region. This interim report provides initial results of the 2015 survey data, completed to inform the design of the 2016 survey season. Full analysis of data will be completed at the end of the 2016 survey season. Survey Methodology Seine netting was conducted at low tide once every other week from 1 March 2015 to 31 July 2015. The seine net has 1.5-mm knotless mesh and measures 23.1 m long by 2.8 m high with rope wings of 18.3 m on each end. Depending on catch rates, between three and five sites were sampled on the two-hour slack period before and after low tide. Ichthyoplankton netting was conducted every other week to alternate with seine netting between 1 March and 31 July (Fig.1). The ichthyoplankton sampler consists of a metal frame suspended between two 2.5 m long floating pipes spaced 90 cm apart. The frame supports a 30 cm square steel collar that is lowered 40 cm below the surface and forms the opening into the fry net. The 250 mm mesh net has a square pyramid shape narrowing into a collection bottle with a 1 m total length. The 1 L collection bottles are modified with 1 mm mesh panels to allow water to pass through while retaining fish larvae. A digital flow meter is attached to the steel collar and suspended in the water column. To minimize fry disturbance, the floats are grey in colour and the collection net is placed forward of the floats. Additionally, the sampler is situated to the side and front of the 3.5-m inflatable boat so as to avoid interference from shadows and the wake. Depending on catch rates, between two and five sites were sampled on the two-hour slack period before and after low tide.. Figure 1: Ichthyoplankton netting equipment used in the 2015 survey

Chiswick Hammersmith Fulham Battersea Putney Hurlingham Wandle Battersea Reach Figure 2: Location and survey effort at eight sampling sites where seine netting and ichthyoplankton netting was completed in the 2015 smelt survey period.

Survey Effort In total, 18 surveys were completed on a weekly basis between 1 March 2015 and 31 July 2015, except for 13 May and 1 July where surveys were cancelled due to poor weather conditions. An equal number of ichthyoplankton and seine netting surveys were completed: ichtyoplankton surveys were conducted on 17 March, 2 April, 9 April, 21 April, 7 May, 29 May, 18 June, 16 July and 30 July; seine netting surveys were conducted on 11 March, 25 March, 13 April, 27 April, 20 May, 10 June, 24 June, 8 July and 22 July. In addition, 2 public seine net demonstrations to increase awareness of biodiversity in the Thames were completed on 6 June and 11 September. Any smelt captured in these events were recorded. The majority of surveys were completed at three sites, Putney, Wandle and Battersea, but survey effort varied each week due to tide times and the amount of catch that had to be processed (Fig. 2). Additional sites were sampled at the beginning of the survey season, when different areas were tested for their suitability, and at the end of the survey season, when the experience gained allowed for greater efficiency at each site (Fig.2) Preliminary Results Comparison of Smelt Catch per Unit Effort (scpue) In total, 284 smelt fry were caught during the 2015 survey period. Smelt were caught at every site except for Hurlingham and Battersea Reach, however only one survey was completed at each of these sites. Smelt Catch Per Unit Effort (scpue) for ichthyoplankton netting was calculated by dividing the number of smelt caught by the volume of water trawled during each ichthyoplankton trawl, then multiplying by 1000. Seine netting scpue was simply calculated by dividing the number of smelt caught by the number of seine netting events completed. Due to the difference in methodology, the scpue for seine netting and ichthyoplankton netting cannot be directly compared. The greatest scpue for ichthyoplankton netting and seine netting was at the Wandle site (Ichthyoplankton = 0.38 scpue, Seine = 4.14) (Fig. 3). Interestingly, the seine netting scpue was high at the westernmost sampling locations, Chiswick and Hammersmith, and the easternmost sampling locations, Wandle and Battersea, but low at Putney and Hurlingham (Fig.3). In 2016, it would be beneficial to sample further East and further West to investigate whether there is a gradient in scpue in the Tidal Thames. The ichthyoplankton scpue was greatly influenced by a single, large catch of smelt on 2 April 2015 (see Analysis of 2 April Catch ). When smelt catch was analysed over different months, April was identified as the greatest scpue for Ichthyoplankton netting (scpue = 0.32) while June was identified as the greatest scpue for seine netting (scpue = 3.67) (Fig.4). The temporal difference in peak scpue for seine netting and ichthyoplankton netting can be explained by the selectivity of the different gear types (see Analysis of smelt fry size ).

Figure 3: Comparison of Smelt Catch Per Unit Effort (scpue) at each site using different sampling methodology Figure 4: Comparison of Smelt Catch Per Unit Effort (scpue) over each month using different sampling methodology Analysis of 2 April catch The largest catch was on 2 nd April 2015, when 230 smelt fry were caught during two trawls West of Wandsworth Bridge (Site name = Wandle ) (Fig. 5). These fry ranged between 4 mm and 7 mm long and due to their ontogenetic staging (straightened body, large but elongated yolk sac, poorly developed mouth and gill structure), were estimated to be between 2 and 5 days old (Adrian Pinder pers. comms.). Based on this information, the smelt hatching date was estimated at between 28 March and 31 March 2015. In 2016, it would be beneficial to start sampling at the beginning of March, to increase chances of catching recently hatched smelt fry and more accurately identify spawning location.

Start trawl 2 End trawl 2 End trawl 1 Start trawl 1 Figure 5: The start and end location of two ichthyoplankton trawls completed on 2 April 2015 where 230 smelt fry were caught (Trawl 1 caught 200 fry and trawl 2 caught 30 smelt fry). Analysis of smelt fry size The smallest smelt measured 4 mm in total length and was caught using the ichthyoplankton net on 2 April 2015 at Wandle. The largest smelt measured 73 mm in total length and was caught using the seine net on 22 July 2015 at Wandle. The total length for smelt increased from April to July, with an average growth rate of 0.48 mm per day (Fig. 6). Ichthyoplankton netting only caught smelt fry under 20 mm in length and seine netting only caught smelt fry above 20 mm in length, thus a combined approach using these two methodologies was appropriate and should be repeated in 2016. Interestingly, smelt fry caught using the ichthyoplankton net on 29 May 2015 and 16 July 2015 were much smaller than other smelt fry caught in the same time period by seine netting (circled red in Fig. 6). This may suggest that there are two spawning locations and/or two spawning times for smelt in the Tidal Thames, which needs to be closely investigated in 2016. Figure 6: Size of smelt fry caught during the 2015 survey period. The points circled in red could suggest there were two spawning locations and/or timings.

Sampling by citizen scientists Trained citizen science volunteers conducted kick netting and foreshore assessment of catch at 9 sites between Hammersmith and Greenwich, once per week at low water from 16 March 2015 to 28 July 2015. Throughout this survey period no smelt eggs or smelt fry were identified. Significant changes to the citizen science survey methodology will be made in 2016 to increase chances of identifying smelt eggs and fry based on this experience. Challenges during 2015 During the 2015 survey season, fish fry identification was a major challenge for the team, especially distinguishing between the different species of coarse fish. The help of Steve Colclough at the Institute of Fisheries Management, Tom Cousins and Pete Grey at the Environment Agency and Adrian Pinder at Bournemouth University was much appreciated when trying to identify fry and a fry ID guide will be developed for the 2016 survey using the photographs taken in the 2015 survey (Fig. 8). The second major challenge was that ZSL s survey boat was not robust enough for the survey work, especially the ichthyoplankton netting. Sampling sites were restricted to areas close to access points, so that the ichthyoplankton net could be disassembled between sites. This reduced the scope of the survey and the number of sites able to be sampled each week. We are currently fundraising to buy a new aluminium boat for the 2016 survey season, so that we can increase survey effort and the number of sites sampled each week. Collaboration with HR Wallingford Ltd. ZSL and HR Wallingford have started a collaborative project to investigate how juvenile smelt fry use the Thames Estuary and identify important habitats for their conservation. ZSL will provide data collected during the 2015 survey season for HR Wallingford to use in their TELEMAC flow model of the Thames Estuary in combination with their Individual Behaviour Model (IBM). The collaborative project will focus on the following objectives: Investigate whether the 230 fry surveyed on 2 April 2015 originated from a single spawning ground. Identify the probable location of the spawning ground. Investigate the likelihood that the larger fry found in subsequent surveys came from this cohort. Investigate how juvenile smelt fry use the estuary and identify important habitats for their conservation. Probability kernels will be produced for the probable spawning location and distribution of smelt fry by December 2015 and these will be used to help inform the 2016 survey location and methodology. 7 May

2 April 10 June Figure 8: Photographs of smelt fry showing development during the 2015 survey period Acknowledgements We would like to thank Steve Colclough at the Institute of Fisheries Management; Tom Cousins and Pete Grey at the Environment Agency; Adrian Pinder at Bournemouth University; Tanya Ferry at Port of London Authority; Jenn McCard and Jacob Ainscough for all their support in the 2015 Smelt Survey. We would also like to thank the 67 citizen scientists who volunteered to be part of the project and the Heritage Lottery Fund for funding the project.