Seasonal Variation in the Occurrence of Planktic Bivalve Larvae in the Schleswig-Holstein Wadden Sea
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High Level Environmental Screening Study for Offshore Wind Farm Developments – Marine Habitats and Species Project
High Level Environmental Screening Study for Offshore Wind Farm Developments – Marine Habitats and Species Project AEA Technology, Environment Contract: W/35/00632/00/00 For: The Department of Trade and Industry New & Renewable Energy Programme Report issued 30 August 2002 (Version with minor corrections 16 September 2002) Keith Hiscock, Harvey Tyler-Walters and Hugh Jones Reference: Hiscock, K., Tyler-Walters, H. & Jones, H. 2002. High Level Environmental Screening Study for Offshore Wind Farm Developments – Marine Habitats and Species Project. Report from the Marine Biological Association to The Department of Trade and Industry New & Renewable Energy Programme. (AEA Technology, Environment Contract: W/35/00632/00/00.) Correspondence: Dr. K. Hiscock, The Laboratory, Citadel Hill, Plymouth, PL1 2PB. [email protected] High level environmental screening study for offshore wind farm developments – marine habitats and species ii High level environmental screening study for offshore wind farm developments – marine habitats and species Title: High Level Environmental Screening Study for Offshore Wind Farm Developments – Marine Habitats and Species Project. Contract Report: W/35/00632/00/00. Client: Department of Trade and Industry (New & Renewable Energy Programme) Contract management: AEA Technology, Environment. Date of contract issue: 22/07/2002 Level of report issue: Final Confidentiality: Distribution at discretion of DTI before Consultation report published then no restriction. Distribution: Two copies and electronic file to DTI (Mr S. Payne, Offshore Renewables Planning). One copy to MBA library. Prepared by: Dr. K. Hiscock, Dr. H. Tyler-Walters & Hugh Jones Authorization: Project Director: Dr. Keith Hiscock Date: Signature: MBA Director: Prof. S. Hawkins Date: Signature: This report can be referred to as follows: Hiscock, K., Tyler-Walters, H. -
Ring Test Bulletin – RTB#52
www.nmbaqcs.org Ring Test Bulletin – RTB#52 Tim Worsfold David Hall Søren Pears (Images) APEM Ltd. March 2017 E-mail: [email protected] RING TEST DETAILS Ring Test #52 Type/Contents – Targeted - Bivalvia Circulated – 12/11/16 Results deadline – 16/12/16 Number of Subscribing Laboratories – 24 Number of Participating Laboratories – 21 Number of Results Received – 21* *multiple data entries per laboratory permitted Summary of differences Total differences for 21 Specimen Genus Species Size returns Genus Species RT5201 Thyasira flexuosa 2-3mm 0 1 RT5202 Abra alba 10mm 0 1 RT5203 Cochlodesma praetenue 3-5mm 5 5 RT5204 Thyasira equalis 2-4mm 3 9 RT5205 Abra nitida 4-6mm 0 1 RT5206 Fabulina fabula 3-5mm 1 1 RT5207 Cerastoderma edule 1mm 6 13 RT5208 Tellimya ferruginosa 3-4mm 0 0 RT5209 Nucula nucleus 8-9mm 0 3 RT5210 Nucula nitidosa 2-3mm 1 3 RT5211 Asbjornsenia pygmaea 2-3mm 1 1 RT5212 Abra prismatica 3-5mm 1 1 RT5213 Chamelea striatula 3-4mm 7 9 RT5214 Montacuta substriata 1-2mm 5 5 RT5215 Spisula subtruncata 1mm 4 6 RT5216 Adontorhina similis 1-2mm 4 4 RT5217 Goodallia triangularis 1-2mm 0 0 RT5218 Scrobicularia plana 1mm 20 20 RT5219 Cerastoderma edule 2-3mm 9 13 RT5220 Arctica islandica 1mm 4 4 RT5221 Kurtiella bidentata 2-3mm 2 2 RT5222 Venerupis corrugata 2-3mm 9 9 RT5223 Barnea parva 10-20mm 0 0 RT5224 Abra alba 4-5mm 1 2 RT5225 Nucula nucleus 2mm 0 11 Total differences 83 124 Average 4.0 5.9 differences /lab. NMBAQC RT#52 bulletin Differences 10 15 20 25 0 5 Arranged in order of increasing number of differences (by specific followed by generic errors). -
Attachments Table of Contents
ATTACHMENTS TABLE OF CONTENTS FORESHORE LICENCE APPLICATION Fenit Harbour, Tralee, Co. Kerry ATTACHMENT CONTENTS Attachment A Figure 1 proximity to sensitive shellfish areas Attachment B B.1 Sediment Chemistry Results Attachment B.1(I) Dumping at Sea Material Analysis Reporting Form Attachment B.1(II) Copies of the laboratory reports Attachment B.1(III) Comparison to Irish Action Level B.2 Characteristics /Composition of the Substance or Material for Disposal Attachment B.2 Sediment Characterisation Report (AQUAFACT, 2018) Attachment C Assessment of Alternatives Attachment D D.1 Purpose Of The Operation D.2 Loading Areas D.3 Details Of The Loading Operations Attachment E E.1 DUMPING SITE SELECTION E.2 GENERAL INFORMATION E.3 DETAILS OF THE DUMPING OPERATION Attachment E.1(I) Attachment E.2(I) Marine Benthic Study Fenit Harbour Dredging and Disposal Operations (Aquafact 2018) Attachment F F.1 Assessment of Impact on the Environment Appendix 1 Assessment of Risk to Marine Mammals from Proposed Dredging and Dumping at Sea Activity, Fenit Harbour, Co. Kerry. Appendix 2 Underwater Archaeological Impact Assessment Report Fenit Harbour and Tralee Bay, Co. Kerry. Appendix 3: Nature Impact Statement Attachment G G.1 Monitoring Programme Attachment-A FIGURE 1 SHELLFISH WATERS FORESHORE LICENCE APPLICATION Fenit Harbour, Tralee, Co. Kerry Legend Foreshore Licence Area Shellfish Area 5091m Proposed Dump Site 4 89m Fenit Harbour Map Reproduced From Ordnance Survey Ireland By Permission Of The Government. Licence Number EN 0015719. 0 1.5 3 km Ü Project Title: Fenit Harbour Client: Kerry County Council Drawing Title: Foreshore Licence and Shellfish Areas Drawn: JK Checked: CF Date: 15-10-2019 Scale (A4): 1:85,000 Attachment-B MATERIAL ANALYSIS DUMPING AT SEA PERMIT APPLICATION Fenit Harbour, Tralee, Co. -
Supplementary Tales
Metabarcoding reveals different zooplankton communities in northern and southern areas of the North Sea Jan Niklas Macher, Berry B. van der Hoorn, Katja T. C. A. Peijnenburg, Lodewijk van Walraven, Willem Renema Supplementary tables 1-5 Table S1: Sampling stations and recorded abiotic variables recorded during the NICO 10 expedition from the Dutch Coast to the Shetland Islands Sampling site name Coordinates (°N, °E) Mean remperature (°C) Mean salinity (PSU) Depth (m) S74 59.416510, 0.499900 8.2 35.1 134 S37 58.1855556, 0.5016667 8.7 35.1 89 S93 57.36046, 0.57784 7.8 34.8 84 S22 56.5866667, 0.6905556 8.3 34.9 220 S109 56.06489, 1.59652 8.7 35 79 S130 55.62157, 2.38651 7.8 34.8 73 S156 54.88581, 3.69192 8.3 34.6 41 S176 54.41489, 4.04154 9.6 34.6 43 S203 53.76851, 4.76715 11.8 34.5 34 Table S2: Species list and read number per sampling site Class Order Family Genus Species S22 S37 S74 S93 S109 S130 S156 S176 S203 Copepoda Calanoida Acartiidae Acartia Acartia clausi 0 0 0 72 0 170 15 630 3995 Copepoda Calanoida Acartiidae Acartia Acartia tonsa 0 0 0 0 0 0 0 0 23 Hydrozoa Trachymedusae Rhopalonematidae Aglantha Aglantha digitale 0 0 0 0 1870 117 420 629 0 Actinopterygii Trachiniformes Ammodytidae Ammodytes Ammodytes marinus 0 0 0 0 0 263 0 35 0 Copepoda Harpacticoida Miraciidae Amphiascopsis Amphiascopsis cinctus 344 0 0 992 2477 2500 9574 8947 0 Ophiuroidea Amphilepidida Amphiuridae Amphiura Amphiura filiformis 0 0 0 0 219 0 0 1470 63233 Copepoda Calanoida Pontellidae Anomalocera Anomalocera patersoni 0 0 586 0 0 0 0 0 0 Bivalvia Venerida -
Processing of 13C-Labelled Phytoplankton in a Fine-Grained Sandy-Shelf Sediment (North Sea): Relative Importance of Different Macrofauna Species
MARINE ECOLOGY PROGRESS SERIES Vol. 297: 61–70, 2005 Published August 1 Mar Ecol Prog Ser Processing of 13C-labelled phytoplankton in a fine-grained sandy-shelf sediment (North Sea): relative importance of different macrofauna species Anja Kamp1, 2,*, Ursula Witte1, 3 1Max Planck Institute for Marine Microbiology, Celsiusstr. 1, 28359 Bremen, Germany 2Present address: Institute for Microbiology, University of Hannover, Schneiderberg 50, 30167 Hannover, Germany 3Present address: Oceanlab, University of Aberdeen, Newburgh, Aberdeen AB41 6AA, UK ABSTRACT: On-board and in situ experiments with 13C-labelled diatoms were carried out to inves- tigate the processing of algal carbon by the macrofauna community of a fine sandy-shelf site in the southern German Bight (North Sea). The time series (12, 30, 32 and 132 h incubations) was supple- mented by additional laboratory experiments on the role of the dominant macrofauna organism, the bivalve Fabulina fabula (Bivalvia: Tellinidae), for particulate organic matter subduction to deeper sediment layers. The specific uptake of algal 13C by macrofauna organisms was visible after 12 h and constantly increased during the incubation periods. F. fabula, a facultative (surface) deposit- and suspension-feeder, Lanice conchilega (Polychaeta: Terebellidae), a suspension-feeder and the (sur- face) deposit-feeder Echinocardium cordatum (Echinodermata: Spatangidae) were responsible for the majority of macrofaunal carbon processing. Predatory macrofauna organisms like Nephtys spp. (Polychaeta: Nephtyidae) also quickly became labelled. The rapid subduction of fresh organic matter by F. fabula down to ca. 4 to 7 cm sediment depth could be demonstrated, and it is suggested that entrainment by macrofauna in this fine-grained sand is much more efficient than advective transport. -
A Biotope Sensitivity Database to Underpin Delivery of the Habitats Directive and Biodiversity Action Plan in the Seas Around England and Scotland
English Nature Research Reports Number 499 A biotope sensitivity database to underpin delivery of the Habitats Directive and Biodiversity Action Plan in the seas around England and Scotland Harvey Tyler-Walters Keith Hiscock This report has been prepared by the Marine Biological Association of the UK (MBA) as part of the work being undertaken in the Marine Life Information Network (MarLIN). The report is part of a contract placed by English Nature, additionally supported by Scottish Natural Heritage, to assist in the provision of sensitivity information to underpin the implementation of the Habitats Directive and the UK Biodiversity Action Plan. The views expressed in the report are not necessarily those of the funding bodies. Any errors or omissions contained in this report are the responsibility of the MBA. February 2003 You may reproduce as many copies of this report as you like, provided such copies stipulate that copyright remains, jointly, with English Nature, Scottish Natural Heritage and the Marine Biological Association of the UK. ISSN 0967-876X © Joint copyright 2003 English Nature, Scottish Natural Heritage and the Marine Biological Association of the UK. Biotope sensitivity database Final report This report should be cited as: TYLER-WALTERS, H. & HISCOCK, K., 2003. A biotope sensitivity database to underpin delivery of the Habitats Directive and Biodiversity Action Plan in the seas around England and Scotland. Report to English Nature and Scottish Natural Heritage from the Marine Life Information Network (MarLIN). Plymouth: Marine Biological Association of the UK. [Final Report] 2 Biotope sensitivity database Final report Contents Foreword and acknowledgements.............................................................................................. 5 Executive summary .................................................................................................................... 7 1 Introduction to the project .............................................................................................. -
Distribution, Abundance, and Diversity of Epifaunal Benthic Organisms in Alitak and Ugak Bays, Kodiak Island, Alaska
DISTRIBUTION, ABUNDANCE, AND DIVERSITY OF EPIFAUNAL BENTHIC ORGANISMS IN ALITAK AND UGAK BAYS, KODIAK ISLAND, ALASKA by Howard M. Feder and Stephen C. Jewett Institute of Marine Science University of Alaska Fairbanks, Alaska 99701 Final Report Outer Continental Shelf Environmental Assessment Program Research Unit 517 October 1977 279 We thank the following for assistance during this study: the crew of the MV Big Valley; Pete Jackson and James Blackburn of the Alaska Department of Fish and Game, Kodiak, for their assistance in a cooperative benthic trawl study; and University of Alaska Institute of Marine Science personnel Rosemary Hobson for assistance in data processing, Max Hoberg for shipboard assistance, and Nora Foster for taxonomic assistance. This study was funded by the Bureau of Land Management, Department of the Interior, through an interagency agreement with the National Oceanic and Atmospheric Administration, Department of Commerce, as part of the Alaska Outer Continental Shelf Environment Assessment Program (OCSEAP). SUMMARY OF OBJECTIVES, CONCLUSIONS, AND IMPLICATIONS WITH RESPECT TO OCS OIL AND GAS DEVELOPMENT Little is known about the biology of the invertebrate components of the shallow, nearshore benthos of the bays of Kodiak Island, and yet these components may be the ones most significantly affected by the impact of oil derived from offshore petroleum operations. Baseline information on species composition is essential before industrial activities take place in waters adjacent to Kodiak Island. It was the intent of this investigation to collect information on the composition, distribution, and biology of the epifaunal invertebrate components of two bays of Kodiak Island. The specific objectives of this study were: 1) A qualitative inventory of dominant benthic invertebrate epifaunal species within two study sites (Alitak and Ugak bays). -
Cellular Level Response of the Bivalve Limecola Balthica To
Science of the Total Environment 794 (2021) 148593 Contents lists available at ScienceDirect Science of the Total Environment journal homepage: www.elsevier.com/locate/scitotenv Cellular level response of the bivalve Limecola balthica to seawater acidification due to potential CO2 leakage from a sub-seabed storage site in the southern Baltic Sea: TiTank experiment at representative hydrostatic pressure Adam Sokołowski a,1, Justyna Świeżak a,⁎,1, Anna Hallmann b, Anders J. Olsen c, Marcelina Ziółkowska a, Ida Beathe Øverjordet d, Trond Nordtug d, Dag Altin e, Daniel Franklin Krause d, Iurgi Salaberria c, Katarzyna Smolarz a a University of Gdańsk, Faculty of Oceanography and Geography, Institute of Oceanography, Al. Piłsudskiego 46, 81-378 Gdynia, Poland b Medical University of Gdańsk, Department of Pharmaceutical Biochemistry, Dębinki 1, 80-211 Gdańsk, Poland c Norwegian University of Science and Technology, NO-7491 Trondheim, Norway d SINTEF Ocean AS, Brattorkaia 17C, NO-7465 Trondheim, Norway e Altins Biotrix, Finn Bergs veg 3, 7022 Trondheim, Norway HIGHLIGHTS GRAPHICAL ABSTRACT • Cellular level responses of L. balthica to acidification caused by CO2 was tested at 9 ATM pressure. • The bivalve is tolerant to medium-term severe environmental hypercapnia. • Seawater pH 7.0 induced effects on rad- ical defence mechanisms (GPx, GST, CAT). • pH 6.3 caused increased cellular oxida- tive stress (MDA) and detoxification (tGSH). article info abstract Article history: Understanding of biological responses of marine fauna to seawater acidification due to potential CO2 leakage Received 7 April 2021 from sub-seabed storage sites has improved recently, providing support to CCS environmental risk assessment. Received in revised form 15 June 2021 Physiological responses of benthic organisms to ambient hypercapnia have been previously investigated but Accepted 17 June 2021 rarely at the cellular level, particularly in areas of less common geochemical and ecological conditions such as Available online 24 June 2021 brackish water and/or reduced oxygen levels. -
Changes in Macrobenthos: Past Versus Present
Human Footprint on the Seafloor Brussel - RBINS 2/9/2011 Changes in macrobenthos: past versus present Jean-Sébastien Houziaux BMM - UGMM Human Footprint on the Seafloor Brussel - RBINS 2/9/2011 New European legislation: what is a “Good Ecosystem State”? GES • Since the 1990s, various european Directives aimed at nature protection have been issued. The most recent is the « Marine Strategy » Framework Directive – « MSFD » • The MSFD targets reaching a GES in European seas. Targets are defined for 11 different descriptors of the marine ecosystem, including « seafloor integrity ». – “Sea-floor integrity is at a level that ensures that the structure and functions of the ecosystems are safeguarded and benthic ecosystems, in particular, are not adversely affected.” • This directive and others involves the definition of objective criteria towards measurement of the GES • The measurement of the amplitude of change induced by human pressures is necessary to set meaningful targets => Baseline assessment => Benthos composition = sensitive indicator for change in the seafloor condition => Monitoring Human Footprint on the Seafloor Brussel - RBINS 2/9/2011 Belgium: a unique historical macrobenthic data set: The surveys and material of G. Gilson, 1899-1908 Gilson’s « ground-collector » Gilson’s dredge (Tow : one nautical mile) Human Footprint on the Seafloor Brussel - RBINS 2/9/2011 Seafloor and benthos, 1900: highlights Western coast: Epibenthic community moderate diversity of open-sea gravels: and density (in- and large taxonomic epifauna) diversity and densities Highest densities (infauna), low species diversity Human Footprint on the Seafloor Brussel - RBINS 2/9/2011 Coastal waters: case of dominant bivalves • Long-term analysis challenges for coastal macrobenthos: Gilson’s dredge data Ù Recent Van Veen data, 1994-2008 (joint DB of U. -
Marine Ecology Progress Series 373:25–35 (2008)
The following appendices accompany the article Distributional overlap rather than habitat differentiation characterizes co-occurrence of bivalves in intertidal soft sediment systems Tanya J. Compton1, 2, 3,*, Tineke A. Troost1, Jaap van der Meer1, Casper Kraan1, 2, Pieter J. C. Honkoop1, Danny I. Rogers4, Grant B. Pearson3, Petra de Goeij1, Pierrick Bocher5, Marc S. S. Lavaleye1, Jutta Leyrer1, 2, Mick G. Yates6, Anne Dekinga1, Theunis Piersma1, 2 1Department of Marine Ecology, Royal Netherlands Institute for Sea Research (NIOZ), PO Box 59, 1790 AB Den Burg, Texel, The Netherlands 2Centre for Ecological and Evolutionary Studies, University of Groningen, PO Box 14, 9750 AA Haren, The Netherlands 3Western Australian Department of Environment and Conservation (DEC), WA Wildlife Research Centre, PO Box 51, Wanneroo, Western Australia 6065, Australia 4Institute of Land, Water and Society, Charles Sturt University, PO Box 789, Albury, New South Wales 2640, Australia 5Centre de Recherche sur les Ecosystèmes Littoraux Anthropisés (CRELA), UMR 6217, Pôle science, CNRS-IFREMER-Université de la Rochelle, La Rochelle 17042, France 6Centre for Ecology and Hydrology — Monks Wood, Abbots Ripton, Huntingdon, Cambridgeshire PE28 2LS, UK *Email: [email protected] Marine Ecology Progress Series 373:25–35 (2008) Appendix 1. Maps showing the gridding programme in each system. Benthic sampling points are shown as small dots; sediment sample points are indicated as larger dots. Median grain size values are shown in categories (Wentworth scale). Darker colours are muddy sample points, whereas lighter colours are sandier. The map of the German Wadden Sea has been divided to show the grid sampling at each location (A: 54° 32’ N, 8° 34’ E; B: 53° 59’ N, 8° 51’ E) 2 Appendix 1 (continued) Appendix 1 (continued) 3 4 Appendix 1 (continued) 5 Appendix 2. -
Macoma Balthica Class: Bivalvia; Heterodonta Order: Veneroida Family: Tellinidae
Phylum: Mollusca Macoma balthica Class: Bivalvia; Heterodonta Order: Veneroida Family: Tellinidae Taxonomy: Originally described as a height, and 11 mm in diameter (Oldroyd member of the genus Tellina, Macoma 1924). The illustrated specimen (from Coos balthica was the name of the Atlantic species. Bay) is 17.5 mm long. Our west coast clam was originally called M. Color: Distinct color is reddish, pale rose or inconspicua (Broderip and Sowerby 1829), white and is sometimes bluish or yellow but they are now generally considered to be (Oldroyd 1924; see Plate 17, Kozloff 1993). the same species (e.g., Vassallo, 1969, 1971; Coos Bay specimens are usually pink inside Haderlie and Abbott 1980). An extensive and out, but individuals from British Columbia, taxonomic history has yielded many Canada can have pink or yellow interiors synonyms for M. balthica. Some ambiguity (Quayle 1970). exists whether individuals from the General Morphology: Bivalve mollusks are southernmost reaches of the distribution on bilaterally symmetrical with two lateral valves east and west sides of the Atlantic should be or shells that are hinged dorsally and considered the same species (Beukema and surround a mantle, head, foot and viscera Meehan 1985) and some researchers (e.g., (see Plate 393B, Coan and Valentich-Scott Meehan 1985; Kamermans et al. 1990; 2007). Among the bivalves, the Heterodonta Luttikhuizen et al. 2012; Sanier et al. 2015) are characterized by ctenidia (or gills) that consider these allopatric populations to be are eulamellibranchiate, fused mantle subspecies (eastern Atlantic Macoma balthica margins and the presence of long siphons. balthica and western Atlantic Macoma Veneroid bivalves have well-developed hinge balthica rubra) that have been reproductively teeth and members of the family Tellinidae isolated for 2–3.5 million years (Luttikhuizen have short lateral hinge teeth (when present – et al. -
Bacterial Communities
A DNA (meta)barcoding approach to assess changes in seabed ecosystems related to human- induced pressures Devriese LisaA, De Backer AnneliesA, Maes SaraA, Van Hoey GertA, Haegeman AnneliesB, Ruttink TomB, Wittoeck JanA, Hillewaert HansA, De Tender CarolineA, Hostens KrisA A Institute for Agricultural and Fisheries Research (ILVO), Animal Sciences Unit, Aquatic environment and quality, Ankerstraat 1, 8400 Oostende, Belgium B Institute for Agricultural and Fisheries Research (ILVO), Plant Sciences Unit, Growth and Development, Caritasstraat 39, 9090 Melle, Belgium Contact: [email protected] I. Aim II. Methodology Macrobenthos communities Development of a DNA metabarcoding • Amplicon sequencing of the V4 fragment of the 18S rDNA using Illumina technology pipeline to assess marine benthic DNA extracts of individual species and artificial mixtures of various species biodiversity in the North Sea. • Sanger sequencing of 4 DNA barcode amplicons: COI (313-319 bp), COI (655-661 bp), V4 18S rDNA (370-582 bp), V7-V8 18S rDNA (281-592 bp) Evaluation of DNA metabarcoding to assess effects of sand extraction on Bacterial communities bacterial species composition in the • Amplicon sequencing of the V3-V4 fragment of the 16S rDNA using Illumina technology Belgian part of the North Sea. (De Tender et al., 2015) DNA extracts of sediment samples (Buiten Ratel sand bank) IV. Macrobenthos III. Macrobenthos Evaluation of the Sanger sequencing Amplicon sequencing, e.g. V4 18S rDNA effectiveness of the barcoding primers (V4 18S) on Taxonomic resolution Species identification OK individual species Failed sequencing of the barcoding Sequence not in public database Identification Genus level and artificial mix primers: Identified as other species * Failed PCR samples.