{include:Teesworks - keywords - menu} [[this>Infrastructure/projects/north-east/the-net-zero-teesside-project/EN010103-002552-NZT DCO 5.13 - HRA Report (Clean) - Nov 2022 (D12) (1).pdf|EN010103-002552-NZT DCO 5.13 - HRA Report (Clean) - Nov 2022 (D12) (1).pdf]]:24: crustaceans and polychaete worms. [[this>Infrastructure/projects/north-east/the-net-zero-teesside-project/EN010103-002552-NZT DCO 5.13 - HRA Report (Clean) - Nov 2022 (D12) (1).pdf|EN010103-002552-NZT DCO 5.13 - HRA Report (Clean) - Nov 2022 (D12) (1).pdf]]:25: sand banks, which support a community of polychaetes, bivalves and crustaceans. [[this>Infrastructure/projects/north-east/the-net-zero-teesside-project/EN010103-002552-NZT DCO 5.13 - HRA Report (Clean) - Nov 2022 (D12) (1).pdf|EN010103-002552-NZT DCO 5.13 - HRA Report (Clean) - Nov 2022 (D12) (1).pdf]]:32: consisting mainly of crustaceans and few polychaetes. More sheltered areas of the [[this>Infrastructure/projects/north-east/the-net-zero-teesside-project/EN010103-002552-NZT DCO 5.13 - HRA Report (Clean) - Nov 2022 (D12) (1).pdf|EN010103-002552-NZT DCO 5.13 - HRA Report (Clean) - Nov 2022 (D12) (1).pdf]]:40: crustaceans and polychaetes (Stark, 1998). [[this>Infrastructure/projects/north-east/the-net-zero-teesside-project/EN010103-002552-NZT DCO 5.13 - HRA Report (Clean) - Nov 2022 (D12) (1).pdf|EN010103-002552-NZT DCO 5.13 - HRA Report (Clean) - Nov 2022 (D12) (1).pdf]]:41: crustaceans. By affecting the prevailing water quality, the Proposed Development [[this>Infrastructure/projects/north-east/the-net-zero-teesside-project/EN010103-002258-NZT DCO - 5.13 - HRA (Tracked) - Sept 2022(D8).pdf|EN010103-002258-NZT DCO - 5.13 - HRA (Tracked) - Sept 2022(D8).pdf]]:24: crustaceans and polychaete worms. [[this>Infrastructure/projects/north-east/the-net-zero-teesside-project/EN010103-002258-NZT DCO - 5.13 - HRA (Tracked) - Sept 2022(D8).pdf|EN010103-002258-NZT DCO - 5.13 - HRA (Tracked) - Sept 2022(D8).pdf]]:26: crustaceans. Some unusual communities also occur, including brittlestar beds and [[this>Infrastructure/projects/north-east/the-net-zero-teesside-project/EN010103-002258-NZT DCO - 5.13 - HRA (Tracked) - Sept 2022(D8).pdf|EN010103-002258-NZT DCO - 5.13 - HRA (Tracked) - Sept 2022(D8).pdf]]:32: community consisting mainly of crustaceans and few polychaetes. More sheltered [[this>Infrastructure/projects/north-east/the-net-zero-teesside-project/EN010103-002258-NZT DCO - 5.13 - HRA (Tracked) - Sept 2022(D8).pdf|EN010103-002258-NZT DCO - 5.13 - HRA (Tracked) - Sept 2022(D8).pdf]]:41: crustaceans and polychaetes (Stark, 1998). [[this>Infrastructure/projects/north-east/the-net-zero-teesside-project/EN010103-002258-NZT DCO - 5.13 - HRA (Tracked) - Sept 2022(D8).pdf|EN010103-002258-NZT DCO - 5.13 - HRA (Tracked) - Sept 2022(D8).pdf]]:42: molluscs and crustaceans. By affecting the prevailing water quality, the Proposed [[this>Infrastructure/projects/north-east/the-net-zero-teesside-project/EN010103-001667-Natural England - Written Representations (WRs), including summaries of all WRs exceeding 1500 words.pdf|EN010103-001667-Natural England - Written Representations (WRs), including summaries of all WRs exceeding 1500 words.pdf]]:46:invertebrates, including worms, molluscs and crustaceans, which provide an important food [[this>Infrastructure/projects/north-east/the-net-zero-teesside-project/EN010103-002424-NZT DCO - 6.4.11 ES Vol III Appendix 9C WFD Assessment - Oct 2022 (D11) (Tracked).pdf|EN010103-002424-NZT DCO - 6.4.11 ES Vol III Appendix 9C WFD Assessment - Oct 2022 (D11) (Tracked).pdf]]:57: event of crustaceans in the bay and [[this>Infrastructure/projects/north-east/the-net-zero-teesside-project/EN010103-002074-NZT DCO 9.28 - Applicants' Responses to Deadline 5 Submissions August 2022 (D6).pdf|EN010103-002074-NZT DCO 9.28 - Applicants' Responses to Deadline 5 Submissions August 2022 (D6).pdf]]:91: crustaceans, please provide than calculating values within the paper. The range of up to 8,000 µT is based on a paper (Cada et al., 2011) which [[this>Infrastructure/projects/north-east/the-net-zero-teesside-project/EN010103-001196-NZT DCO 5.13 - HRA Report - Oct 2021 Rev.2.0.pdf|EN010103-001196-NZT DCO 5.13 - HRA Report - Oct 2021 Rev.2.0.pdf]]:23: crustaceans and polychaete worms. [[this>Infrastructure/projects/north-east/the-net-zero-teesside-project/EN010103-001196-NZT DCO 5.13 - HRA Report - Oct 2021 Rev.2.0.pdf|EN010103-001196-NZT DCO 5.13 - HRA Report - Oct 2021 Rev.2.0.pdf]]:24: sand banks, which support a community of polychaetes, bivalves and crustaceans. [[this>Infrastructure/projects/north-east/the-net-zero-teesside-project/EN010103-001196-NZT DCO 5.13 - HRA Report - Oct 2021 Rev.2.0.pdf|EN010103-001196-NZT DCO 5.13 - HRA Report - Oct 2021 Rev.2.0.pdf]]:31: consisting mainly of crustaceans and few polychaetes. More sheltered areas of the [[this>Infrastructure/projects/north-east/the-net-zero-teesside-project/EN010103-001196-NZT DCO 5.13 - HRA Report - Oct 2021 Rev.2.0.pdf|EN010103-001196-NZT DCO 5.13 - HRA Report - Oct 2021 Rev.2.0.pdf]]:39: crustaceans and polychaetes (Stark, 1998). [[this>Infrastructure/projects/north-east/the-net-zero-teesside-project/EN010103-001196-NZT DCO 5.13 - HRA Report - Oct 2021 Rev.2.0.pdf|EN010103-001196-NZT DCO 5.13 - HRA Report - Oct 2021 Rev.2.0.pdf]]:40: crustaceans. By affecting the prevailing water quality, the Proposed Development [[this>Infrastructure/projects/north-east/the-net-zero-teesside-project/EN010103-001142-NZT DCO 6.4.31 ES Vol III Appendix 14C Marine Mammal Baseline.pdf|EN010103-001142-NZT DCO 6.4.31 ES Vol III Appendix 14C Marine Mammal Baseline.pdf]]:20: demersal fish species, cephalopods and crustaceans (Santos et al., 2001). [[this>Infrastructure/projects/north-east/the-net-zero-teesside-project/EN010103-001142-NZT DCO 6.4.31 ES Vol III Appendix 14C Marine Mammal Baseline.pdf|EN010103-001142-NZT DCO 6.4.31 ES Vol III Appendix 14C Marine Mammal Baseline.pdf]]:31: cephalopods, and crustaceans obtained from surface, mid-water, and [[this>Infrastructure/projects/north-east/the-net-zero-teesside-project/EN010103-000889-NZT DCO 6.4.28 ES Vol III Appendix 13A Aquatic Ecology Supplementary Desk Study and Field Survey Report.pdf|EN010103-000889-NZT DCO 6.4.28 ES Vol III Appendix 13A Aquatic Ecology Supplementary Desk Study and Field Survey Report.pdf]]:20: crustaceans (Crangonyx sp.), true bugs (Gerris sp., Nepa cinerea), mayflies [[this>Infrastructure/projects/north-east/the-net-zero-teesside-project/EN010103-000889-NZT DCO 6.4.28 ES Vol III Appendix 13A Aquatic Ecology Supplementary Desk Study and Field Survey Report.pdf|EN010103-000889-NZT DCO 6.4.28 ES Vol III Appendix 13A Aquatic Ecology Supplementary Desk Study and Field Survey Report.pdf]]:21: crustaceans (Gammarus pulex, Asellus aquaticus), true bugs (Plea [[this>Infrastructure/projects/north-east/the-net-zero-teesside-project/EN010103-000889-NZT DCO 6.4.28 ES Vol III Appendix 13A Aquatic Ecology Supplementary Desk Study and Field Survey Report.pdf|EN010103-000889-NZT DCO 6.4.28 ES Vol III Appendix 13A Aquatic Ecology Supplementary Desk Study and Field Survey Report.pdf]]:21: (Pisidium sp.), crustaceans (Gammarus zaddachi, Asellus aquaticus), true [[this>Infrastructure/projects/north-east/the-net-zero-teesside-project/EN010103-000889-NZT DCO 6.4.28 ES Vol III Appendix 13A Aquatic Ecology Supplementary Desk Study and Field Survey Report.pdf|EN010103-000889-NZT DCO 6.4.28 ES Vol III Appendix 13A Aquatic Ecology Supplementary Desk Study and Field Survey Report.pdf]]:22: Potamopyrgus antipodarum), crustaceans (Asellus aquaticus), true bugs [[this>Infrastructure/projects/north-east/the-net-zero-teesside-project/EN010103-000889-NZT DCO 6.4.28 ES Vol III Appendix 13A Aquatic Ecology Supplementary Desk Study and Field Survey Report.pdf|EN010103-000889-NZT DCO 6.4.28 ES Vol III Appendix 13A Aquatic Ecology Supplementary Desk Study and Field Survey Report.pdf]]:28: Potamopyrgus antipodarum, the crustacean Crangonyx [[this>Infrastructure/projects/north-east/the-net-zero-teesside-project/EN010103-002062-NZT DCO 7.12 - Habitats Regulations Assessment Report (Change Request) (Clean) August 2022 (D6).pdf|EN010103-002062-NZT DCO 7.12 - Habitats Regulations Assessment Report (Change Request) (Clean) August 2022 (D6).pdf]]:24: crustaceans and polychaete worms. [[this>Infrastructure/projects/north-east/the-net-zero-teesside-project/EN010103-002062-NZT DCO 7.12 - Habitats Regulations Assessment Report (Change Request) (Clean) August 2022 (D6).pdf|EN010103-002062-NZT DCO 7.12 - Habitats Regulations Assessment Report (Change Request) (Clean) August 2022 (D6).pdf]]:25: sand banks, which support a community of polychaetes, bivalves and crustaceans. [[this>Infrastructure/projects/north-east/the-net-zero-teesside-project/EN010103-002062-NZT DCO 7.12 - Habitats Regulations Assessment Report (Change Request) (Clean) August 2022 (D6).pdf|EN010103-002062-NZT DCO 7.12 - Habitats Regulations Assessment Report (Change Request) (Clean) August 2022 (D6).pdf]]:32: consisting mainly of crustaceans and few polychaetes. More sheltered areas of the [[this>Infrastructure/projects/north-east/the-net-zero-teesside-project/EN010103-002062-NZT DCO 7.12 - Habitats Regulations Assessment Report (Change Request) (Clean) August 2022 (D6).pdf|EN010103-002062-NZT DCO 7.12 - Habitats Regulations Assessment Report (Change Request) (Clean) August 2022 (D6).pdf]]:40: crustaceans and polychaetes (Stark, 1998). [[this>Infrastructure/projects/north-east/the-net-zero-teesside-project/EN010103-002062-NZT DCO 7.12 - Habitats Regulations Assessment Report (Change Request) (Clean) August 2022 (D6).pdf|EN010103-002062-NZT DCO 7.12 - Habitats Regulations Assessment Report (Change Request) (Clean) August 2022 (D6).pdf]]:41: crustaceans. By affecting the prevailing water quality, the Proposed Development [[this>Infrastructure/projects/north-east/the-net-zero-teesside-project/EN010103-002553-NZT DCO 5.13 - HRA Report (Tracked) - Nov 2022 (D12).pdf|EN010103-002553-NZT DCO 5.13 - HRA Report (Tracked) - Nov 2022 (D12).pdf]]:24: crustaceans and polychaete worms. [[this>Infrastructure/projects/north-east/the-net-zero-teesside-project/EN010103-002553-NZT DCO 5.13 - HRA Report (Tracked) - Nov 2022 (D12).pdf|EN010103-002553-NZT DCO 5.13 - HRA Report (Tracked) - Nov 2022 (D12).pdf]]:25: sand banks, which support a community of polychaetes, bivalves and crustaceans. [[this>Infrastructure/projects/north-east/the-net-zero-teesside-project/EN010103-002553-NZT DCO 5.13 - HRA Report (Tracked) - Nov 2022 (D12).pdf|EN010103-002553-NZT DCO 5.13 - HRA Report (Tracked) - Nov 2022 (D12).pdf]]:32: consisting mainly of crustaceans and few polychaetes. More sheltered areas of the [[this>Infrastructure/projects/north-east/the-net-zero-teesside-project/EN010103-002553-NZT DCO 5.13 - HRA Report (Tracked) - Nov 2022 (D12).pdf|EN010103-002553-NZT DCO 5.13 - HRA Report (Tracked) - Nov 2022 (D12).pdf]]:40: crustaceans and polychaetes (Stark, 1998). [[this>Infrastructure/projects/north-east/the-net-zero-teesside-project/EN010103-002553-NZT DCO 5.13 - HRA Report (Tracked) - Nov 2022 (D12).pdf|EN010103-002553-NZT DCO 5.13 - HRA Report (Tracked) - Nov 2022 (D12).pdf]]:41: crustaceans. By affecting the prevailing water quality, the Proposed Development [[this>Infrastructure/projects/north-east/the-net-zero-teesside-project/EN010103-002331-NZT DCO 5.13 - Habitats Regulations Assessment Report (Tracked) Oct 2022 (D9).pdf|EN010103-002331-NZT DCO 5.13 - Habitats Regulations Assessment Report (Tracked) Oct 2022 (D9).pdf]]:24: crustaceans and polychaete worms. [[this>Infrastructure/projects/north-east/the-net-zero-teesside-project/EN010103-002331-NZT DCO 5.13 - Habitats Regulations Assessment Report (Tracked) Oct 2022 (D9).pdf|EN010103-002331-NZT DCO 5.13 - Habitats Regulations Assessment Report (Tracked) Oct 2022 (D9).pdf]]:25: sand banks, which support a community of polychaetes, bivalves and crustaceans. [[this>Infrastructure/projects/north-east/the-net-zero-teesside-project/EN010103-002331-NZT DCO 5.13 - Habitats Regulations Assessment Report (Tracked) Oct 2022 (D9).pdf|EN010103-002331-NZT DCO 5.13 - Habitats Regulations Assessment Report (Tracked) Oct 2022 (D9).pdf]]:32: consisting mainly of crustaceans and few polychaetes. More sheltered areas of the [[this>Infrastructure/projects/north-east/the-net-zero-teesside-project/EN010103-002331-NZT DCO 5.13 - Habitats Regulations Assessment Report (Tracked) Oct 2022 (D9).pdf|EN010103-002331-NZT DCO 5.13 - Habitats Regulations Assessment Report (Tracked) Oct 2022 (D9).pdf]]:40: crustaceans and polychaetes (Stark, 1998). [[this>Infrastructure/projects/north-east/the-net-zero-teesside-project/EN010103-002331-NZT DCO 5.13 - Habitats Regulations Assessment Report (Tracked) Oct 2022 (D9).pdf|EN010103-002331-NZT DCO 5.13 - Habitats Regulations Assessment Report (Tracked) Oct 2022 (D9).pdf]]:41: crustaceans. By affecting the prevailing water quality, the Proposed Development [[this>Infrastructure/projects/north-east/the-net-zero-teesside-project/EN010103-002063-NZT DCO 7.12 - Habitats Regulations Assessment Report (Change Request) (Tracked) August 2022 (D6).pdf|EN010103-002063-NZT DCO 7.12 - Habitats Regulations Assessment Report (Change Request) (Tracked) August 2022 (D6).pdf]]:24: crustaceans and polychaete worms. [[this>Infrastructure/projects/north-east/the-net-zero-teesside-project/EN010103-002063-NZT DCO 7.12 - Habitats Regulations Assessment Report (Change Request) (Tracked) August 2022 (D6).pdf|EN010103-002063-NZT DCO 7.12 - Habitats Regulations Assessment Report (Change Request) (Tracked) August 2022 (D6).pdf]]:25: sand banks, which support a community of polychaetes, bivalves and crustaceans. [[this>Infrastructure/projects/north-east/the-net-zero-teesside-project/EN010103-002063-NZT DCO 7.12 - Habitats Regulations Assessment Report (Change Request) (Tracked) August 2022 (D6).pdf|EN010103-002063-NZT DCO 7.12 - Habitats Regulations Assessment Report (Change Request) (Tracked) August 2022 (D6).pdf]]:32: consisting mainly of crustaceans and few polychaetes. More sheltered areas of the [[this>Infrastructure/projects/north-east/the-net-zero-teesside-project/EN010103-002063-NZT DCO 7.12 - Habitats Regulations Assessment Report (Change Request) (Tracked) August 2022 (D6).pdf|EN010103-002063-NZT DCO 7.12 - Habitats Regulations Assessment Report (Change Request) (Tracked) August 2022 (D6).pdf]]:41: crustaceans and polychaetes (Stark, 1998). [[this>Infrastructure/projects/north-east/the-net-zero-teesside-project/EN010103-002063-NZT DCO 7.12 - Habitats Regulations Assessment Report (Change Request) (Tracked) August 2022 (D6).pdf|EN010103-002063-NZT DCO 7.12 - Habitats Regulations Assessment Report (Change Request) (Tracked) August 2022 (D6).pdf]]:41: crustaceans. By affecting the prevailing water quality, the Proposed Development [[this>Infrastructure/projects/north-east/the-net-zero-teesside-project/EN010103-001478-NZT DCO 5.13 Habitat Regulations Assessment Report Rev 3 Tracked.pdf|EN010103-001478-NZT DCO 5.13 Habitat Regulations Assessment Report Rev 3 Tracked.pdf]]:23: crustaceans and polychaete worms. [[this>Infrastructure/projects/north-east/the-net-zero-teesside-project/EN010103-001478-NZT DCO 5.13 Habitat Regulations Assessment Report Rev 3 Tracked.pdf|EN010103-001478-NZT DCO 5.13 Habitat Regulations Assessment Report Rev 3 Tracked.pdf]]:24: sand banks, which support a community of polychaetes, bivalves and crustaceans. [[this>Infrastructure/projects/north-east/the-net-zero-teesside-project/EN010103-001478-NZT DCO 5.13 Habitat Regulations Assessment Report Rev 3 Tracked.pdf|EN010103-001478-NZT DCO 5.13 Habitat Regulations Assessment Report Rev 3 Tracked.pdf]]:31: consisting mainly of crustaceans and few polychaetes. More sheltered areas of the [[this>Infrastructure/projects/north-east/the-net-zero-teesside-project/EN010103-001478-NZT DCO 5.13 Habitat Regulations Assessment Report Rev 3 Tracked.pdf|EN010103-001478-NZT DCO 5.13 Habitat Regulations Assessment Report Rev 3 Tracked.pdf]]:39: crustaceans and polychaetes (Stark, 1998). [[this>Infrastructure/projects/north-east/the-net-zero-teesside-project/EN010103-001478-NZT DCO 5.13 Habitat Regulations Assessment Report Rev 3 Tracked.pdf|EN010103-001478-NZT DCO 5.13 Habitat Regulations Assessment Report Rev 3 Tracked.pdf]]:40: crustaceans. By affecting the prevailing water quality, the Proposed Development [[this>Infrastructure/projects/north-east/the-net-zero-teesside-project/EN010103-002509-NZT DCO 7.16 - HRA for Change Request (Tracked) - Nov 2022 (D12).pdf|EN010103-002509-NZT DCO 7.16 - HRA for Change Request (Tracked) - Nov 2022 (D12).pdf]]:24: crustaceans and polychaete worms. [[this>Infrastructure/projects/north-east/the-net-zero-teesside-project/EN010103-002509-NZT DCO 7.16 - HRA for Change Request (Tracked) - Nov 2022 (D12).pdf|EN010103-002509-NZT DCO 7.16 - HRA for Change Request (Tracked) - Nov 2022 (D12).pdf]]:25: sand banks, which support a community of polychaetes, bivalves and crustaceans. [[this>Infrastructure/projects/north-east/the-net-zero-teesside-project/EN010103-002509-NZT DCO 7.16 - HRA for Change Request (Tracked) - Nov 2022 (D12).pdf|EN010103-002509-NZT DCO 7.16 - HRA for Change Request (Tracked) - Nov 2022 (D12).pdf]]:32: consisting mainly of crustaceans and few polychaetes. More sheltered areas of the [[this>Infrastructure/projects/north-east/the-net-zero-teesside-project/EN010103-002509-NZT DCO 7.16 - HRA for Change Request (Tracked) - Nov 2022 (D12).pdf|EN010103-002509-NZT DCO 7.16 - HRA for Change Request (Tracked) - Nov 2022 (D12).pdf]]:40: crustaceans and polychaetes (Stark, 1998). [[this>Infrastructure/projects/north-east/the-net-zero-teesside-project/EN010103-002509-NZT DCO 7.16 - HRA for Change Request (Tracked) - Nov 2022 (D12).pdf|EN010103-002509-NZT DCO 7.16 - HRA for Change Request (Tracked) - Nov 2022 (D12).pdf]]:41: crustaceans. By affecting the prevailing water quality, the Proposed Development [[this>Infrastructure/projects/north-east/the-net-zero-teesside-project/EN010103-000885-NZT DCO 5.13 - Habitat Regulations Assessment Report.pdf|EN010103-000885-NZT DCO 5.13 - Habitat Regulations Assessment Report.pdf]]:23: crustaceans and polychaete worms. [[this>Infrastructure/projects/north-east/the-net-zero-teesside-project/EN010103-000885-NZT DCO 5.13 - Habitat Regulations Assessment Report.pdf|EN010103-000885-NZT DCO 5.13 - Habitat Regulations Assessment Report.pdf]]:24: sand banks, which support a community of polychaetes, bivalves and crustaceans. [[this>Infrastructure/projects/north-east/the-net-zero-teesside-project/EN010103-000885-NZT DCO 5.13 - Habitat Regulations Assessment Report.pdf|EN010103-000885-NZT DCO 5.13 - Habitat Regulations Assessment Report.pdf]]:31: consisting mainly of crustaceans and few polychaetes. More sheltered areas of the [[this>Infrastructure/projects/north-east/the-net-zero-teesside-project/EN010103-000885-NZT DCO 5.13 - Habitat Regulations Assessment Report.pdf|EN010103-000885-NZT DCO 5.13 - Habitat Regulations Assessment Report.pdf]]:39: crustaceans and polychaetes (Stark, 1998). [[this>Infrastructure/projects/north-east/the-net-zero-teesside-project/EN010103-000885-NZT DCO 5.13 - Habitat Regulations Assessment Report.pdf|EN010103-000885-NZT DCO 5.13 - Habitat Regulations Assessment Report.pdf]]:40: crustaceans. By affecting the prevailing water quality, the Proposed Development [[this>Infrastructure/projects/north-east/the-net-zero-teesside-project/EN010103-002056-NZT DCO 5.13 - Habitats Regulations Assessment Report (Clean) August 2022 (D6).pdf|EN010103-002056-NZT DCO 5.13 - Habitats Regulations Assessment Report (Clean) August 2022 (D6).pdf]]:24: crustaceans and polychaete worms. [[this>Infrastructure/projects/north-east/the-net-zero-teesside-project/EN010103-002056-NZT DCO 5.13 - Habitats Regulations Assessment Report (Clean) August 2022 (D6).pdf|EN010103-002056-NZT DCO 5.13 - Habitats Regulations Assessment Report (Clean) August 2022 (D6).pdf]]:25: sand banks, which support a community of polychaetes, bivalves and crustaceans. [[this>Infrastructure/projects/north-east/the-net-zero-teesside-project/EN010103-002056-NZT DCO 5.13 - Habitats Regulations Assessment Report (Clean) August 2022 (D6).pdf|EN010103-002056-NZT DCO 5.13 - Habitats Regulations Assessment Report (Clean) August 2022 (D6).pdf]]:32: consisting mainly of crustaceans and few polychaetes. More sheltered areas of the [[this>Infrastructure/projects/north-east/the-net-zero-teesside-project/EN010103-002056-NZT DCO 5.13 - Habitats Regulations Assessment Report (Clean) August 2022 (D6).pdf|EN010103-002056-NZT DCO 5.13 - Habitats Regulations Assessment Report (Clean) August 2022 (D6).pdf]]:40: crustaceans and polychaetes (Stark, 1998). [[this>Infrastructure/projects/north-east/the-net-zero-teesside-project/EN010103-002056-NZT DCO 5.13 - Habitats Regulations Assessment Report (Clean) August 2022 (D6).pdf|EN010103-002056-NZT DCO 5.13 - Habitats Regulations Assessment Report (Clean) August 2022 (D6).pdf]]:41: crustaceans. By affecting the prevailing water quality, the Proposed Development [[this>Infrastructure/projects/north-east/the-net-zero-teesside-project/EN010103-001479-NZT DCO 5.13 Habitat Regulations Assessment Report Rev 3 Final 2022-04-26.pdf|EN010103-001479-NZT DCO 5.13 Habitat Regulations Assessment Report Rev 3 Final 2022-04-26.pdf]]:23: crustaceans and polychaete worms. [[this>Infrastructure/projects/north-east/the-net-zero-teesside-project/EN010103-001479-NZT DCO 5.13 Habitat Regulations Assessment Report Rev 3 Final 2022-04-26.pdf|EN010103-001479-NZT DCO 5.13 Habitat Regulations Assessment Report Rev 3 Final 2022-04-26.pdf]]:24: sand banks, which support a community of polychaetes, bivalves and crustaceans. [[this>Infrastructure/projects/north-east/the-net-zero-teesside-project/EN010103-001479-NZT DCO 5.13 Habitat Regulations Assessment Report Rev 3 Final 2022-04-26.pdf|EN010103-001479-NZT DCO 5.13 Habitat Regulations Assessment Report Rev 3 Final 2022-04-26.pdf]]:31: consisting mainly of crustaceans and few polychaetes. More sheltered areas of the [[this>Infrastructure/projects/north-east/the-net-zero-teesside-project/EN010103-001479-NZT DCO 5.13 Habitat Regulations Assessment Report Rev 3 Final 2022-04-26.pdf|EN010103-001479-NZT DCO 5.13 Habitat Regulations Assessment Report Rev 3 Final 2022-04-26.pdf]]:39: crustaceans and polychaetes (Stark, 1998). [[this>Infrastructure/projects/north-east/the-net-zero-teesside-project/EN010103-001479-NZT DCO 5.13 Habitat Regulations Assessment Report Rev 3 Final 2022-04-26.pdf|EN010103-001479-NZT DCO 5.13 Habitat Regulations Assessment Report Rev 3 Final 2022-04-26.pdf]]:40: crustaceans. By affecting the prevailing water quality, the Proposed Development [[this>Infrastructure/projects/north-east/the-net-zero-teesside-project/EN010103-001849-5.13 - HRA Report (Clean) - June 2022(D3).pdf|EN010103-001849-5.13 - HRA Report (Clean) - June 2022(D3).pdf]]:23: crustaceans and polychaete worms. [[this>Infrastructure/projects/north-east/the-net-zero-teesside-project/EN010103-001849-5.13 - HRA Report (Clean) - June 2022(D3).pdf|EN010103-001849-5.13 - HRA Report (Clean) - June 2022(D3).pdf]]:24: sand banks, which support a community of polychaetes, bivalves and crustaceans. [[this>Infrastructure/projects/north-east/the-net-zero-teesside-project/EN010103-001849-5.13 - HRA Report (Clean) - June 2022(D3).pdf|EN010103-001849-5.13 - HRA Report (Clean) - June 2022(D3).pdf]]:31: consisting mainly of crustaceans and few polychaetes. More sheltered areas of the [[this>Infrastructure/projects/north-east/the-net-zero-teesside-project/EN010103-001849-5.13 - HRA Report (Clean) - June 2022(D3).pdf|EN010103-001849-5.13 - HRA Report (Clean) - June 2022(D3).pdf]]:40: crustaceans and polychaetes (Stark, 1998). [[this>Infrastructure/projects/north-east/the-net-zero-teesside-project/EN010103-001849-5.13 - HRA Report (Clean) - June 2022(D3).pdf|EN010103-001849-5.13 - HRA Report (Clean) - June 2022(D3).pdf]]:41: crustaceans. By affecting the prevailing water quality, the Proposed Development [[this>Infrastructure/projects/north-east/the-net-zero-teesside-project/EN010103-002330-NZT DCO 5.13 - Habitats Regulations Assessment Report (Clean) Oct 2022 (D9).pdf|EN010103-002330-NZT DCO 5.13 - Habitats Regulations Assessment Report (Clean) Oct 2022 (D9).pdf]]:24: crustaceans and polychaete worms. [[this>Infrastructure/projects/north-east/the-net-zero-teesside-project/EN010103-002330-NZT DCO 5.13 - Habitats Regulations Assessment Report (Clean) Oct 2022 (D9).pdf|EN010103-002330-NZT DCO 5.13 - Habitats Regulations Assessment Report (Clean) Oct 2022 (D9).pdf]]:25: sand banks, which support a community of polychaetes, bivalves and crustaceans. [[this>Infrastructure/projects/north-east/the-net-zero-teesside-project/EN010103-002330-NZT DCO 5.13 - Habitats Regulations Assessment Report (Clean) Oct 2022 (D9).pdf|EN010103-002330-NZT DCO 5.13 - Habitats Regulations Assessment Report (Clean) Oct 2022 (D9).pdf]]:32: consisting mainly of crustaceans and few polychaetes. More sheltered areas of the [[this>Infrastructure/projects/north-east/the-net-zero-teesside-project/EN010103-002330-NZT DCO 5.13 - Habitats Regulations Assessment Report (Clean) Oct 2022 (D9).pdf|EN010103-002330-NZT DCO 5.13 - Habitats Regulations Assessment Report (Clean) Oct 2022 (D9).pdf]]:40: crustaceans and polychaetes (Stark, 1998). [[this>Infrastructure/projects/north-east/the-net-zero-teesside-project/EN010103-002330-NZT DCO 5.13 - Habitats Regulations Assessment Report (Clean) Oct 2022 (D9).pdf|EN010103-002330-NZT DCO 5.13 - Habitats Regulations Assessment Report (Clean) Oct 2022 (D9).pdf]]:41: crustaceans. By affecting the prevailing water quality, the Proposed Development [[this>Infrastructure/projects/north-east/the-net-zero-teesside-project/EN010103-001139-NZT DCO 6.4.30 ES Vol III Appendix 14B Fisheries and Fish Ecology Baseline Part 1.pdf|EN010103-001139-NZT DCO 6.4.30 ES Vol III Appendix 14B Fisheries and Fish Ecology Baseline Part 1.pdf]]:12: presbyter), as well as molluscs, crustaceans and worms (Green, 2017). [[this>Infrastructure/projects/north-east/the-net-zero-teesside-project/EN010103-001143-NZT DCO 6.4.32 ES Vol III Appendix 14D Subtidal Benthic Ecology.pdf|EN010103-001143-NZT DCO 6.4.32 ES Vol III Appendix 14D Subtidal Benthic Ecology.pdf]]:12:14.2.14 Major group biomass (Annelida, Crustacea, Mollusca, Echinodermata and [[this>Infrastructure/projects/north-east/the-net-zero-teesside-project/EN010103-001143-NZT DCO 6.4.32 ES Vol III Appendix 14D Subtidal Benthic Ecology.pdf|EN010103-001143-NZT DCO 6.4.32 ES Vol III Appendix 14D Subtidal Benthic Ecology.pdf]]:12: • Crustacea = 22.5 %; [[this>Infrastructure/projects/north-east/the-net-zero-teesside-project/EN010103-001143-NZT DCO 6.4.32 ES Vol III Appendix 14D Subtidal Benthic Ecology.pdf|EN010103-001143-NZT DCO 6.4.32 ES Vol III Appendix 14D Subtidal Benthic Ecology.pdf]]:19: total average abundance across all the samples (Figure 14D-3). Crustacea [[this>Infrastructure/projects/north-east/the-net-zero-teesside-project/EN010103-001143-NZT DCO 6.4.32 ES Vol III Appendix 14D Subtidal Benthic Ecology.pdf|EN010103-001143-NZT DCO 6.4.32 ES Vol III Appendix 14D Subtidal Benthic Ecology.pdf]]:19: the greatest proportion to average biomass (34.2%) followed by Crustacea [[this>Infrastructure/projects/north-east/the-net-zero-teesside-project/EN010103-001143-NZT DCO 6.4.32 ES Vol III Appendix 14D Subtidal Benthic Ecology.pdf|EN010103-001143-NZT DCO 6.4.32 ES Vol III Appendix 14D Subtidal Benthic Ecology.pdf]]:20: Annelida Crustacea Mollusca Echinodermata Other [[this>Infrastructure/projects/north-east/the-net-zero-teesside-project/EN010103-001143-NZT DCO 6.4.32 ES Vol III Appendix 14D Subtidal Benthic Ecology.pdf|EN010103-001143-NZT DCO 6.4.32 ES Vol III Appendix 14D Subtidal Benthic Ecology.pdf]]:20: Annelida Crustacea Mollusca Echinodermata Other [[this>Infrastructure/projects/north-east/the-net-zero-teesside-project/EN010103-001143-NZT DCO 6.4.32 ES Vol III Appendix 14D Subtidal Benthic Ecology.pdf|EN010103-001143-NZT DCO 6.4.32 ES Vol III Appendix 14D Subtidal Benthic Ecology.pdf]]:20:14.3.20 Two amphipod crustacean species were recorded in the top ten most [[this>Infrastructure/projects/north-east/the-net-zero-teesside-project/EN010103-001143-NZT DCO 6.4.32 ES Vol III Appendix 14D Subtidal Benthic Ecology.pdf|EN010103-001143-NZT DCO 6.4.32 ES Vol III Appendix 14D Subtidal Benthic Ecology.pdf]]:21: and biomass per major group (Annelida, Crustacea, Mollusca, [[this>Infrastructure/projects/north-east/the-net-zero-teesside-project/EN010103-001850-5.13 - HRA Report (Tracked) - June 2022(D3).pdf|EN010103-001850-5.13 - HRA Report (Tracked) - June 2022(D3).pdf]]:23: crustaceans and polychaete worms. [[this>Infrastructure/projects/north-east/the-net-zero-teesside-project/EN010103-001850-5.13 - HRA Report (Tracked) - June 2022(D3).pdf|EN010103-001850-5.13 - HRA Report (Tracked) - June 2022(D3).pdf]]:24: sand banks, which support a community of polychaetes, bivalves and crustaceans. [[this>Infrastructure/projects/north-east/the-net-zero-teesside-project/EN010103-001850-5.13 - HRA Report (Tracked) - June 2022(D3).pdf|EN010103-001850-5.13 - HRA Report (Tracked) - June 2022(D3).pdf]]:31: consisting mainly of crustaceans and few polychaetes. More sheltered areas of the [[this>Infrastructure/projects/north-east/the-net-zero-teesside-project/EN010103-001850-5.13 - HRA Report (Tracked) - June 2022(D3).pdf|EN010103-001850-5.13 - HRA Report (Tracked) - June 2022(D3).pdf]]:40: crustaceans and polychaetes (Stark, 1998). [[this>Infrastructure/projects/north-east/the-net-zero-teesside-project/EN010103-001850-5.13 - HRA Report (Tracked) - June 2022(D3).pdf|EN010103-001850-5.13 - HRA Report (Tracked) - June 2022(D3).pdf]]:41: crustaceans. By affecting the prevailing water quality, the Proposed Development [[this>Infrastructure/projects/north-east/the-net-zero-teesside-project/EN010103-002423-NZT DCO - 6.4.11 ES Vol III Appendix 9C WFD Assessment - Oct 2022 (D11) (Clean).pdf|EN010103-002423-NZT DCO - 6.4.11 ES Vol III Appendix 9C WFD Assessment - Oct 2022 (D11) (Clean).pdf]]:55: event of crustaceans in the bay and [[this>Infrastructure/projects/north-east/the-net-zero-teesside-project/EN010103-001113-NZT DCO 6.4.29 ES Vol III Appendix 14A Intertidal Benthic Ecology Survey Report.pdf|EN010103-001113-NZT DCO 6.4.29 ES Vol III Appendix 14A Intertidal Benthic Ecology Survey Report.pdf]]:10:14.2.12 Major group biomass (Annelida, Crustacea, Mollusca, Echinodermata and [[this>Infrastructure/projects/north-east/the-net-zero-teesside-project/EN010103-001113-NZT DCO 6.4.29 ES Vol III Appendix 14A Intertidal Benthic Ecology Survey Report.pdf|EN010103-001113-NZT DCO 6.4.29 ES Vol III Appendix 14A Intertidal Benthic Ecology Survey Report.pdf]]:10: • Crustacea = 22.5 %; [[this>Infrastructure/projects/north-east/the-net-zero-teesside-project/EN010103-001113-NZT DCO 6.4.29 ES Vol III Appendix 14A Intertidal Benthic Ecology Survey Report.pdf|EN010103-001113-NZT DCO 6.4.29 ES Vol III Appendix 14A Intertidal Benthic Ecology Survey Report.pdf]]:23: species), megalopa (the final larval stage of a decapod crustacean), juvenile, [[this>Infrastructure/projects/north-east/the-net-zero-teesside-project/EN010103-001113-NZT DCO 6.4.29 ES Vol III Appendix 14A Intertidal Benthic Ecology Survey Report.pdf|EN010103-001113-NZT DCO 6.4.29 ES Vol III Appendix 14A Intertidal Benthic Ecology Survey Report.pdf]]:23: parasitic, and zoea (early larval stage of a decapod crustacean) taxa. [[this>Infrastructure/projects/north-east/the-net-zero-teesside-project/EN010103-001113-NZT DCO 6.4.29 ES Vol III Appendix 14A Intertidal Benthic Ecology Survey Report.pdf|EN010103-001113-NZT DCO 6.4.29 ES Vol III Appendix 14A Intertidal Benthic Ecology Survey Report.pdf]]:23: group (Annelida, Crustacea, Mollusca, Echinodermata and Others), in all [[this>Infrastructure/projects/north-east/the-net-zero-teesside-project/EN010103-001113-NZT DCO 6.4.29 ES Vol III Appendix 14A Intertidal Benthic Ecology Survey Report.pdf|EN010103-001113-NZT DCO 6.4.29 ES Vol III Appendix 14A Intertidal Benthic Ecology Survey Report.pdf]]:23: (27.9%) followed by crustaceans, particularly amphipods, and molluscs [[this>Infrastructure/projects/north-east/the-net-zero-teesside-project/EN010103-001113-NZT DCO 6.4.29 ES Vol III Appendix 14A Intertidal Benthic Ecology Survey Report.pdf|EN010103-001113-NZT DCO 6.4.29 ES Vol III Appendix 14A Intertidal Benthic Ecology Survey Report.pdf]]:23: taxa identified across all stations. Crustaceans were the second most [[this>Infrastructure/projects/north-east/the-net-zero-teesside-project/EN010103-001113-NZT DCO 6.4.29 ES Vol III Appendix 14A Intertidal Benthic Ecology Survey Report.pdf|EN010103-001113-NZT DCO 6.4.29 ES Vol III Appendix 14A Intertidal Benthic Ecology Survey Report.pdf]]:23: respectively. Crustaceans contributed 0.4% to total biomass across all [[this>Infrastructure/projects/north-east/the-net-zero-teesside-project/EN010103-001113-NZT DCO 6.4.29 ES Vol III Appendix 14A Intertidal Benthic Ecology Survey Report.pdf|EN010103-001113-NZT DCO 6.4.29 ES Vol III Appendix 14A Intertidal Benthic Ecology Survey Report.pdf]]:24: 50 Crustacea [[this>Infrastructure/projects/north-east/the-net-zero-teesside-project/EN010103-001113-NZT DCO 6.4.29 ES Vol III Appendix 14A Intertidal Benthic Ecology Survey Report.pdf|EN010103-001113-NZT DCO 6.4.29 ES Vol III Appendix 14A Intertidal Benthic Ecology Survey Report.pdf]]:28: group (Annelida, Crustacea, Mollusca, Echinodermata and Others), in all [[this>Infrastructure/projects/north-east/the-net-zero-teesside-project/EN010103-001113-NZT DCO 6.4.29 ES Vol III Appendix 14A Intertidal Benthic Ecology Survey Report.pdf|EN010103-001113-NZT DCO 6.4.29 ES Vol III Appendix 14A Intertidal Benthic Ecology Survey Report.pdf]]:67:Crustacea [[this>Infrastructure/projects/north-east/the-net-zero-teesside-project/EN010103-001113-NZT DCO 6.4.29 ES Vol III Appendix 14A Intertidal Benthic Ecology Survey Report.pdf|EN010103-001113-NZT DCO 6.4.29 ES Vol III Appendix 14A Intertidal Benthic Ecology Survey Report.pdf]]:69:Station/Replicate Annelida Crustacea Mollusca Echinodermata Other [[this>Infrastructure/projects/north-east/the-net-zero-teesside-project/EN010103-001113-NZT DCO 6.4.29 ES Vol III Appendix 14A Intertidal Benthic Ecology Survey Report.pdf|EN010103-001113-NZT DCO 6.4.29 ES Vol III Appendix 14A Intertidal Benthic Ecology Survey Report.pdf]]:70:Crustacea [[this>Infrastructure/projects/north-east/the-net-zero-teesside-project/EN010103-001113-NZT DCO 6.4.29 ES Vol III Appendix 14A Intertidal Benthic Ecology Survey Report.pdf|EN010103-001113-NZT DCO 6.4.29 ES Vol III Appendix 14A Intertidal Benthic Ecology Survey Report.pdf]]:70:Station/Replicate Annelida Crustacea Mollusca Echinodermata Other [[this>Infrastructure/projects/north-east/the-net-zero-teesside-project/EN010103-002257-NZT DCO - 5.13 - HRA (Clean) - Sept 2022(D8).pdf|EN010103-002257-NZT DCO - 5.13 - HRA (Clean) - Sept 2022(D8).pdf]]:24: crustaceans and polychaete worms. [[this>Infrastructure/projects/north-east/the-net-zero-teesside-project/EN010103-002257-NZT DCO - 5.13 - HRA (Clean) - Sept 2022(D8).pdf|EN010103-002257-NZT DCO - 5.13 - HRA (Clean) - Sept 2022(D8).pdf]]:25: sand banks, which support a community of polychaetes, bivalves and crustaceans. [[this>Infrastructure/projects/north-east/the-net-zero-teesside-project/EN010103-002257-NZT DCO - 5.13 - HRA (Clean) - Sept 2022(D8).pdf|EN010103-002257-NZT DCO - 5.13 - HRA (Clean) - Sept 2022(D8).pdf]]:32: consisting mainly of crustaceans and few polychaetes. More sheltered areas of the [[this>Infrastructure/projects/north-east/the-net-zero-teesside-project/EN010103-002257-NZT DCO - 5.13 - HRA (Clean) - Sept 2022(D8).pdf|EN010103-002257-NZT DCO - 5.13 - HRA (Clean) - Sept 2022(D8).pdf]]:41: crustaceans and polychaetes (Stark, 1998). [[this>Infrastructure/projects/north-east/the-net-zero-teesside-project/EN010103-002257-NZT DCO - 5.13 - HRA (Clean) - Sept 2022(D8).pdf|EN010103-002257-NZT DCO - 5.13 - HRA (Clean) - Sept 2022(D8).pdf]]:42: crustaceans. By affecting the prevailing water quality, the Proposed Development [[this>Infrastructure/projects/north-east/the-net-zero-teesside-project/EN010103-001150-NZT DCO 6.4.48 ES Vol III Appendix 24C Statement of Combined Effects.pdf|EN010103-001150-NZT DCO 6.4.48 ES Vol III Appendix 24C Statement of Combined Effects.pdf]]:13: Sandbanks provide a home to many species including burrowing fauna such as polychaete worms, crustaceans, bivalve molluscs and echinoderms. [[this>Infrastructure/projects/north-east/the-net-zero-teesside-project/EN010103-001150-NZT DCO 6.4.48 ES Vol III Appendix 24C Statement of Combined Effects.pdf|EN010103-001150-NZT DCO 6.4.48 ES Vol III Appendix 24C Statement of Combined Effects.pdf]]:13: Callianassa subterranean and the cumacean crustacean Eudorella truncactula. Coarser sediments in less than 30m are typified by two communities, [[this>Infrastructure/projects/north-east/the-net-zero-teesside-project/EN010103-001150-NZT DCO 6.4.48 ES Vol III Appendix 24C Statement of Combined Effects.pdf|EN010103-001150-NZT DCO 6.4.48 ES Vol III Appendix 24C Statement of Combined Effects.pdf]]:13: the first with the polychaete Nephtys cirrosa, the sea urchin Echinocardium cordatum and the amphipod crustacean Urothoe poseidonis. The second [[this>Infrastructure/projects/north-east/the-net-zero-teesside-project/EN010103-001150-NZT DCO 6.4.48 ES Vol III Appendix 24C Statement of Combined Effects.pdf|EN010103-001150-NZT DCO 6.4.48 ES Vol III Appendix 24C Statement of Combined Effects.pdf]]:13: by the polychaetes Anoides paucibranchiata and Pisione remota, and the amphipod crustacean Phoxocephalus holbolli. [[this>Infrastructure/projects/north-east/the-net-zero-teesside-project/EN010103-002057-NZT DCO 5.13 - Habitats Regulations Assessment Report (Tracked) August 2022 (D6).pdf|EN010103-002057-NZT DCO 5.13 - Habitats Regulations Assessment Report (Tracked) August 2022 (D6).pdf]]:24: crustaceans and polychaete worms. [[this>Infrastructure/projects/north-east/the-net-zero-teesside-project/EN010103-002057-NZT DCO 5.13 - Habitats Regulations Assessment Report (Tracked) August 2022 (D6).pdf|EN010103-002057-NZT DCO 5.13 - Habitats Regulations Assessment Report (Tracked) August 2022 (D6).pdf]]:25: sand banks, which support a community of polychaetes, bivalves and crustaceans. [[this>Infrastructure/projects/north-east/the-net-zero-teesside-project/EN010103-002057-NZT DCO 5.13 - Habitats Regulations Assessment Report (Tracked) August 2022 (D6).pdf|EN010103-002057-NZT DCO 5.13 - Habitats Regulations Assessment Report (Tracked) August 2022 (D6).pdf]]:32: consisting mainly of crustaceans and few polychaetes. More sheltered areas of the [[this>Infrastructure/projects/north-east/the-net-zero-teesside-project/EN010103-002057-NZT DCO 5.13 - Habitats Regulations Assessment Report (Tracked) August 2022 (D6).pdf|EN010103-002057-NZT DCO 5.13 - Habitats Regulations Assessment Report (Tracked) August 2022 (D6).pdf]]:41: crustaceans and polychaetes (Stark, 1998). [[this>Infrastructure/projects/north-east/the-net-zero-teesside-project/EN010103-002057-NZT DCO 5.13 - Habitats Regulations Assessment Report (Tracked) August 2022 (D6).pdf|EN010103-002057-NZT DCO 5.13 - Habitats Regulations Assessment Report (Tracked) August 2022 (D6).pdf]]:41: crustaceans. By affecting the prevailing water quality, the Proposed Development [[this>Infrastructure/projects/north-east/the-net-zero-teesside-project/EN010103-001141-NZT DCO 6.4.30 ES Vol III Appendix 14B Fisheries and Fish Ecology Baseline Part 3.pdf|EN010103-001141-NZT DCO 6.4.30 ES Vol III Appendix 14B Fisheries and Fish Ecology Baseline Part 3.pdf]]:36: crustaceans, and the pelagic larvae and juvenile stages of numerous [[this>Infrastructure/projects/north-east/the-net-zero-teesside-project/EN010103-001141-NZT DCO 6.4.30 ES Vol III Appendix 14B Fisheries and Fish Ecology Baseline Part 3.pdf|EN010103-001141-NZT DCO 6.4.30 ES Vol III Appendix 14B Fisheries and Fish Ecology Baseline Part 3.pdf]]:39: feed on crustaceans, including euphausids, mysids and crangonid shrimps. [[this>Infrastructure/projects/north-east/the-net-zero-teesside-project/EN010103-001141-NZT DCO 6.4.30 ES Vol III Appendix 14B Fisheries and Fish Ecology Baseline Part 3.pdf|EN010103-001141-NZT DCO 6.4.30 ES Vol III Appendix 14B Fisheries and Fish Ecology Baseline Part 3.pdf]]:41: polychaete worms and bivalve molluscs, but also feed on small crustaceans, [[this>Infrastructure/projects/north-east/the-net-zero-teesside-project/EN010103-001141-NZT DCO 6.4.30 ES Vol III Appendix 14B Fisheries and Fish Ecology Baseline Part 3.pdf|EN010103-001141-NZT DCO 6.4.30 ES Vol III Appendix 14B Fisheries and Fish Ecology Baseline Part 3.pdf]]:50: East Coast. Crustaceana. 67, 156 – 172. [[this>Infrastructure/projects/north-east/the-net-zero-teesside-project/EN010103-000900-NZT DCO 6.2.14 ES Vol I Chapter 14 Marine Ecology and Nature Conservation.pdf|EN010103-000900-NZT DCO 6.2.14 ES Vol I Chapter 14 Marine Ecology and Nature Conservation.pdf]]:61: sound for commercially valuable crustaceans. Marine invertebrates are [[this>Infrastructure/projects/north-east/the-net-zero-teesside-project/EN010103-000900-NZT DCO 6.2.14 ES Vol I Chapter 14 Marine Ecology and Nature Conservation.pdf|EN010103-000900-NZT DCO 6.2.14 ES Vol I Chapter 14 Marine Ecology and Nature Conservation.pdf]]:61: example, it is believed that the detection of particle motion in crustaceans and [[this>Infrastructure/projects/north-east/the-net-zero-teesside-project/EN010103-000900-NZT DCO 6.2.14 ES Vol I Chapter 14 Marine Ecology and Nature Conservation.pdf|EN010103-000900-NZT DCO 6.2.14 ES Vol I Chapter 14 Marine Ecology and Nature Conservation.pdf]]:62: Furthermore, whilst there is evidence that some adult crustaceans are affected [[this>Infrastructure/projects/north-east/the-net-zero-teesside-project/EN010103-000900-NZT DCO 6.2.14 ES Vol I Chapter 14 Marine Ecology and Nature Conservation.pdf|EN010103-000900-NZT DCO 6.2.14 ES Vol I Chapter 14 Marine Ecology and Nature Conservation.pdf]]:122: communication by decapod crustaceans. Journal of Comparative [[this>Infrastructure/projects/north-east/the-net-zero-teesside-project/EN010103-002508-NZT DCO 7.16 - HRA for Change Request (Clean) - Nov 2022 (D12).pdf|EN010103-002508-NZT DCO 7.16 - HRA for Change Request (Clean) - Nov 2022 (D12).pdf]]:24: crustaceans and polychaete worms. [[this>Infrastructure/projects/north-east/the-net-zero-teesside-project/EN010103-002508-NZT DCO 7.16 - HRA for Change Request (Clean) - Nov 2022 (D12).pdf|EN010103-002508-NZT DCO 7.16 - HRA for Change Request (Clean) - Nov 2022 (D12).pdf]]:25: sand banks, which support a community of polychaetes, bivalves and crustaceans. [[this>Infrastructure/projects/north-east/the-net-zero-teesside-project/EN010103-002508-NZT DCO 7.16 - HRA for Change Request (Clean) - Nov 2022 (D12).pdf|EN010103-002508-NZT DCO 7.16 - HRA for Change Request (Clean) - Nov 2022 (D12).pdf]]:32: consisting mainly of crustaceans and few polychaetes. More sheltered areas of the [[this>Infrastructure/projects/north-east/the-net-zero-teesside-project/EN010103-002508-NZT DCO 7.16 - HRA for Change Request (Clean) - Nov 2022 (D12).pdf|EN010103-002508-NZT DCO 7.16 - HRA for Change Request (Clean) - Nov 2022 (D12).pdf]]:40: crustaceans and polychaetes (Stark, 1998). [[this>Infrastructure/projects/north-east/the-net-zero-teesside-project/EN010103-002508-NZT DCO 7.16 - HRA for Change Request (Clean) - Nov 2022 (D12).pdf|EN010103-002508-NZT DCO 7.16 - HRA for Change Request (Clean) - Nov 2022 (D12).pdf]]:41: crustaceans. By affecting the prevailing water quality, the Proposed Development [[this>Infrastructure/projects/north-east/york-potash-harbour-facilities-order/TR030002-000443-ES Section 8 Marine ecology.pdf|TR030002-000443-ES Section 8 Marine ecology.pdf]]:26: the polychaetes Chaetozone christiei and Spio decorata, crustaceans (e.g. Diastylis bradyi) and [[this>Infrastructure/projects/north-east/york-potash-harbour-facilities-order/TR030002-000443-ES Section 8 Marine ecology.pdf|TR030002-000443-ES Section 8 Marine ecology.pdf]]:28: followed by Annelida (21%), Crustacea (19%), Mollusca (19%) and Echinodermata (8%). In terms of [[this>Infrastructure/projects/north-east/york-potash-harbour-facilities-order/TR030002-000443-ES Section 8 Marine ecology.pdf|TR030002-000443-ES Section 8 Marine ecology.pdf]]:28: the number of individuals, Crustacea dominated accounting for 89% of the total abundance. Fish [[this>Infrastructure/projects/north-east/york-potash-harbour-facilities-order/TR030002-000576-Doc 7.3 Appendix 7 - Appendices to Alternative Sites Assessment - Part 1.pdf|TR030002-000576-Doc 7.3 Appendix 7 - Appendices to Alternative Sites Assessment - Part 1.pdf]]:174: including glacio-eustatic oscillations and variations in the rate of crustal subsidence, [[this>RiverTees/Planning/EIA_2017_00041/Additional Documents/NGCT_Final_ES at KK with figs.pdf|NGCT_Final_ES at KK with figs.pdf]]:25:Amphipod A type of crustacean. The head carries two pairs of [[this>RiverTees/Planning/EIA_2017_00041/Additional Documents/NGCT_Final_ES at KK with figs.pdf|NGCT_Final_ES at KK with figs.pdf]]:308: the laver spire shell H. ulvae and the amphipod crustacean Corophium volutator [[this>RiverTees/Planning/EIA_2017_00041/Additional Documents/NGCT_Final_ES at KK with figs.pdf|NGCT_Final_ES at KK with figs.pdf]]:310: level (e.g. Polychaeta, Mollusca, Crustacea, etc). [[this>RiverTees/Planning/EIA_2017_00041/Additional Documents/NGCT_Final_ES at KK with figs.pdf|NGCT_Final_ES at KK with figs.pdf]]:318: Chaetozone christiei and Spio decorata species. Crustaceans (Diastylis bradyi [[this>RiverTees/Planning/MLA_2020_00079/Additional Documents/IBPB8270R001F01_EIA REPORT(2).pdf|IBPB8270R001F01_EIA REPORT(2).pdf]]:114: location of Hartlepool between areas of crustal uplift to the north and subsidence to south makes these [[this>RiverTees/Planning/MLA_2020_00079/Additional Documents/IBPB8270R001F01_EIA REPORT(2).pdf|IBPB8270R001F01_EIA REPORT(2).pdf]]:115:Crustaceans, echinoderms and other taxa all generally contributed little to abundance, diversity and [[this>RiverTees/Planning/MLA_2020_00079/Additional Documents/IBPB8270R001F01_EIA REPORT(2).pdf|IBPB8270R001F01_EIA REPORT(2).pdf]]:183: 10 to 100 individuals reported Most abundant in inner shelf May be found on sandy and soft substrates at time in the coastal nurseries, planktonic crustaceans. The main [[this>RiverTees/Planning/MLA_2020_00079/Additional Documents/IBPB8270R001F01_EIA REPORT(2).pdf|IBPB8270R001F01_EIA REPORT(2).pdf]]:183: the Tees. Numbers increase rates following the 50m and 100m terms of fish biomass in the North Sea after sprat June in the North Sea. temperature drops in autumn. polychaetes, small crustaceans, [[this>RiverTees/Planning/MLA_2020_00079/Additional Documents/IBPB8270R001F01_EIA REPORT(2).pdf|IBPB8270R001F01_EIA REPORT(2).pdf]]:183: crustaceans and fish, although [[this>RiverTees/Planning/MLA_2020_00079/Additional Documents/IBPB8270R001F01_EIA REPORT(2).pdf|IBPB8270R001F01_EIA REPORT(2).pdf]]:183: east of Dogger Bank. event. crustaceans (amphipods, mysids [[this>RiverTees/Planning/MLA_2020_00079/Additional Documents/IBPB8270R001F01_EIA REPORT(2).pdf|IBPB8270R001F01_EIA REPORT(2).pdf]]:183: in the coastal waters of Tees of the North Sea. rates in the North Sea are largest gravel or shell beds. crustaceans and brittle-stars) is also [[this>RiverTees/Planning/MLA_2020_00079/Additional Documents/IBPB8270R001F01_EIA REPORT(2).pdf|IBPB8270R001F01_EIA REPORT(2).pdf]]:183: species and crustaceans including [[this>RiverTees/Planning/MLA_2020_00079/Additional Documents/IBPB8270R001F01_EIA REPORT(2).pdf|IBPB8270R001F01_EIA REPORT(2).pdf]]:183: concentrated in the west, with rivers and coastal waters. They seldom use waters Spawning takes place in autumn or crustaceans, polychaetes and fish, [[this>RiverTees/Planning/MLA_2020_00079/Additional Documents/IBPB8270R001F01_EIA REPORT(2).pdf|IBPB8270R001F01_EIA REPORT(2).pdf]]:184: the North Sea are somewhat of the catches in the Fish Atlas and disappear completely the crustaceans (including crabs and [[this>RiverTees/Planning/MLA_2020_00079/Additional Documents/IBPB8270R001F01_EIA REPORT(2).pdf|IBPB8270R001F01_EIA REPORT(2).pdf]]:184: becoming negligible beyond 70m bivalves and crustaceans, but the [[this>RiverTees/Planning/MLA_2020_00079/Additional Documents/IBPB8270R001F01_EIA REPORT(2).pdf|IBPB8270R001F01_EIA REPORT(2).pdf]]:185: development. between northern and southern mackerel but crustaceans, squid [[this>RiverTees/Planning/MLA_2020_00079/Additional Documents/IBPB8270R001F01_EIA REPORT(2).pdf|IBPB8270R001F01_EIA REPORT(2).pdf]]:185:Anglerfish per hour in the coastal waters the northern and central North encountered at depths greater fish inhabit broader areas, including deeper waters. protracted based on the findings of 25km of the release location. fish, cephalopods and crustaceans. [[this>RiverTees/Planning/MLA_2020_00079/Additional Documents/IBPB8270R001F01_EIA REPORT(2).pdf|IBPB8270R001F01_EIA REPORT(2).pdf]]:295:also states that common terns feed on small fish, both marine and freshwater, as well as crustaceans, [[this>RiverTees/Planning/MLA_2020_00079/Additional Documents/IBPB8270R001F01_EIA REPORT(2).pdf|IBPB8270R001F01_EIA REPORT(2).pdf]]:307:Crangon Crangon: Journal of Crustacean Biology Vol. 7, No. 3 pp. 401-413 Published by: The Crustacean [[this>RiverTees/Planning/MLA_2020_00079/Additional Documents/IBPB8270R001F01_EIA REPORT(2).pdf|IBPB8270R001F01_EIA REPORT(2).pdf]]:392:and Spio decorata, crustaceans (e.g. Diastylis bradyi) and molluscs (e.g. Abra alba) were also present. [[this>RiverTees/Planning/MLA_2020_00079/Additional Documents/IBPB8270R001F01_EIA REPORT(2).pdf|IBPB8270R001F01_EIA REPORT(2).pdf]]:471:Following identification, all taxa from each sample were pooled into five major groups (Annelida, Crustacea, [[this>RiverTees/Planning/MLA_2020_00079/Additional Documents/IBPB8270R001F01_EIA REPORT(2).pdf|IBPB8270R001F01_EIA REPORT(2).pdf]]:472:- Crustacea = 22.5 % [[this>RiverTees/Planning/MLA_2020_00079/Additional Documents/IBPB8270R001F01_EIA REPORT(2).pdf|IBPB8270R001F01_EIA REPORT(2).pdf]]:481:each taxon and biomass per major group (Annelida, Crustacea, Mollusca, Echinodermata and Others) in all [[this>RiverTees/Planning/MLA_2020_00079/Additional Documents/IBPB8270R001F01_EIA REPORT(2).pdf|IBPB8270R001F01_EIA REPORT(2).pdf]]:481:Mollusc taxa generally contributed most to biomass (overall = 49.2 %), except in the QEII area. Crustaceans, [[this>RiverTees/Planning/MLA_2020_00079/Additional Documents/IBPB8270R001F01_EIA REPORT(2).pdf|IBPB8270R001F01_EIA REPORT(2).pdf]]:500:Chaetozone christiei and Spio decorata species. Crustaceans (Diastylis bradyi for example) and [[this>RiverTees/Planning/MLA_2020_00079/Additional Documents/IBPB8270R001F01_EIA REPORT.pdf|IBPB8270R001F01_EIA REPORT.pdf]]:114: location of Hartlepool between areas of crustal uplift to the north and subsidence to south makes these [[this>RiverTees/Planning/MLA_2020_00079/Additional Documents/IBPB8270R001F01_EIA REPORT.pdf|IBPB8270R001F01_EIA REPORT.pdf]]:115:Crustaceans, echinoderms and other taxa all generally contributed little to abundance, diversity and [[this>RiverTees/Planning/MLA_2020_00079/Additional Documents/IBPB8270R001F01_EIA REPORT.pdf|IBPB8270R001F01_EIA REPORT.pdf]]:183: 10 to 100 individuals reported Most abundant in inner shelf May be found on sandy and soft substrates at time in the coastal nurseries, planktonic crustaceans. The main [[this>RiverTees/Planning/MLA_2020_00079/Additional Documents/IBPB8270R001F01_EIA REPORT.pdf|IBPB8270R001F01_EIA REPORT.pdf]]:183: the Tees. Numbers increase rates following the 50m and 100m terms of fish biomass in the North Sea after sprat June in the North Sea. temperature drops in autumn. polychaetes, small crustaceans, [[this>RiverTees/Planning/MLA_2020_00079/Additional Documents/IBPB8270R001F01_EIA REPORT.pdf|IBPB8270R001F01_EIA REPORT.pdf]]:183: crustaceans and fish, although [[this>RiverTees/Planning/MLA_2020_00079/Additional Documents/IBPB8270R001F01_EIA REPORT.pdf|IBPB8270R001F01_EIA REPORT.pdf]]:183: east of Dogger Bank. event. crustaceans (amphipods, mysids [[this>RiverTees/Planning/MLA_2020_00079/Additional Documents/IBPB8270R001F01_EIA REPORT.pdf|IBPB8270R001F01_EIA REPORT.pdf]]:183: in the coastal waters of Tees of the North Sea. rates in the North Sea are largest gravel or shell beds. crustaceans and brittle-stars) is also [[this>RiverTees/Planning/MLA_2020_00079/Additional Documents/IBPB8270R001F01_EIA REPORT.pdf|IBPB8270R001F01_EIA REPORT.pdf]]:183: species and crustaceans including [[this>RiverTees/Planning/MLA_2020_00079/Additional Documents/IBPB8270R001F01_EIA REPORT.pdf|IBPB8270R001F01_EIA REPORT.pdf]]:183: concentrated in the west, with rivers and coastal waters. They seldom use waters Spawning takes place in autumn or crustaceans, polychaetes and fish, [[this>RiverTees/Planning/MLA_2020_00079/Additional Documents/IBPB8270R001F01_EIA REPORT.pdf|IBPB8270R001F01_EIA REPORT.pdf]]:184: the North Sea are somewhat of the catches in the Fish Atlas and disappear completely the crustaceans (including crabs and [[this>RiverTees/Planning/MLA_2020_00079/Additional Documents/IBPB8270R001F01_EIA REPORT.pdf|IBPB8270R001F01_EIA REPORT.pdf]]:184: becoming negligible beyond 70m bivalves and crustaceans, but the [[this>RiverTees/Planning/MLA_2020_00079/Additional Documents/IBPB8270R001F01_EIA REPORT.pdf|IBPB8270R001F01_EIA REPORT.pdf]]:185: development. between northern and southern mackerel but crustaceans, squid [[this>RiverTees/Planning/MLA_2020_00079/Additional Documents/IBPB8270R001F01_EIA REPORT.pdf|IBPB8270R001F01_EIA REPORT.pdf]]:185:Anglerfish per hour in the coastal waters the northern and central North encountered at depths greater fish inhabit broader areas, including deeper waters. protracted based on the findings of 25km of the release location. fish, cephalopods and crustaceans. [[this>RiverTees/Planning/MLA_2020_00079/Additional Documents/IBPB8270R001F01_EIA REPORT.pdf|IBPB8270R001F01_EIA REPORT.pdf]]:295:also states that common terns feed on small fish, both marine and freshwater, as well as crustaceans, [[this>RiverTees/Planning/MLA_2020_00079/Additional Documents/IBPB8270R001F01_EIA REPORT.pdf|IBPB8270R001F01_EIA REPORT.pdf]]:307:Crangon Crangon: Journal of Crustacean Biology Vol. 7, No. 3 pp. 401-413 Published by: The Crustacean [[this>RiverTees/Planning/MLA_2020_00079/Additional Documents/IBPB8270R001F01_EIA REPORT.pdf|IBPB8270R001F01_EIA REPORT.pdf]]:392:and Spio decorata, crustaceans (e.g. Diastylis bradyi) and molluscs (e.g. Abra alba) were also present. [[this>RiverTees/Planning/MLA_2020_00079/Additional Documents/IBPB8270R001F01_EIA REPORT.pdf|IBPB8270R001F01_EIA REPORT.pdf]]:471:Following identification, all taxa from each sample were pooled into five major groups (Annelida, Crustacea, [[this>RiverTees/Planning/MLA_2020_00079/Additional Documents/IBPB8270R001F01_EIA REPORT.pdf|IBPB8270R001F01_EIA REPORT.pdf]]:472:- Crustacea = 22.5 % [[this>RiverTees/Planning/MLA_2020_00079/Additional Documents/IBPB8270R001F01_EIA REPORT.pdf|IBPB8270R001F01_EIA REPORT.pdf]]:481:each taxon and biomass per major group (Annelida, Crustacea, Mollusca, Echinodermata and Others) in all [[this>RiverTees/Planning/MLA_2020_00079/Additional Documents/IBPB8270R001F01_EIA REPORT.pdf|IBPB8270R001F01_EIA REPORT.pdf]]:481:Mollusc taxa generally contributed most to biomass (overall = 49.2 %), except in the QEII area. Crustaceans, [[this>RiverTees/Planning/MLA_2020_00079/Additional Documents/IBPB8270R001F01_EIA REPORT.pdf|IBPB8270R001F01_EIA REPORT.pdf]]:500:Chaetozone christiei and Spio decorata species. Crustaceans (Diastylis bradyi for example) and [[this>RiverTees/Planning/MLA_2015_00334/Additional Documents/Appendix 16.1b - DNV Addendum Report 2005.pdf|Appendix 16.1b - DNV Addendum Report 2005.pdf]]:17:bass, dover sole or cod. Or crustacean species found on outer estuary rocky habitat primarily [[this>Teesworks/Planning/MLA_2020_00506/MLA_2020_00506-PC1084_RHD-ZZ-XX-RP-Z-1100_EIA Report_main body-10.pdf|MLA_2020_00506-PC1084_RHD-ZZ-XX-RP-Z-1100_EIA Report_main body-10.pdf]]:197: British periods. The location of Hartlepool between areas of crustal uplift to the north [[this>Teesworks/Planning/MLA_2020_00506/MLA_2020_00506-PC1084_RHD-ZZ-XX-RP-Z-1100_EIA Report_main body-10.pdf|MLA_2020_00506-PC1084_RHD-ZZ-XX-RP-Z-1100_EIA Report_main body-10.pdf]]:199:stations. Mollusc taxa generally contributed most to biomass. Crustaceans, echinoderms and other taxa [[this>Teesworks/Planning/MLA_2020_00506/MLA_2020_00506-PC1084_RHD-ZZ-XX-RP-Z-1100_EIA Report_main body-10.pdf|MLA_2020_00506-PC1084_RHD-ZZ-XX-RP-Z-1100_EIA Report_main body-10.pdf]]:223:as cephalopods, other molluscs, crustaceans and polychaetes have also been recorded. The diet varies [[this>Teesworks/Planning/MLA_2020_00506/MLA_2020_00506-PC1084_RHD-ZZ-XX-RP-Z-1100_EIA Report_main body-10.pdf|MLA_2020_00506-PC1084_RHD-ZZ-XX-RP-Z-1100_EIA Report_main body-10.pdf]]:317: • Byelaw XXVIII – Crustacea Conservation Byelaw – only vessels 10m or under in length can [[this>Teesworks/Planning/MLA_2020_00506/MLA_2020_00506-PC1084_RHD-ZZ-XX-RP-Z-1100_EIA Report_main body-10.pdf|MLA_2020_00506-PC1084_RHD-ZZ-XX-RP-Z-1100_EIA Report_main body-10.pdf]]:321:crustaceans), with the presence of the dredge head likely resulting in them temporarily relocating away from [[this>Teesworks/Planning/MLA_2020_00506/MLA_2020_00506-PC1084_RHD-ZZ-XX-RP-Z-1100_EIA Report_main body-10.pdf|MLA_2020_00506-PC1084_RHD-ZZ-XX-RP-Z-1100_EIA Report_main body-10.pdf]]:536:across all stations. Mollusc taxa generally contributed most to biomass. Crustaceans, echinoderms and [[this>Teesworks/Planning/MLA_2020_00506/MLA_2020_00506-PC1084-RHD-ZZ-XX-RP-Z-1115_South Bank Quay supplementary report-16.pdf|MLA_2020_00506-PC1084-RHD-ZZ-XX-RP-Z-1115_South Bank Quay supplementary report-16.pdf]]:20:such as crustaceans and echinoderms were present in lower numbers. There was no obvious dominance [[this>Teesworks/Planning/MLA_2020_00506/MLA_2020_00506-PC1084-RHD-ZZ-XX-RP-Z-1115_South Bank Quay supplementary report-16.pdf|MLA_2020_00506-PC1084-RHD-ZZ-XX-RP-Z-1115_South Bank Quay supplementary report-16.pdf]]:204:Cirriformia tentaculata, species of the genus Capitella and Eteone longa; oligochaetes, the crustaceans [[this>Teesworks/Planning/MLA_2020_00506/MLA_2020_00506-PC1084-RHD-ZZ-XX-RP-Z-1115_South Bank Quay supplementary report-16.pdf|MLA_2020_00506-PC1084-RHD-ZZ-XX-RP-Z-1115_South Bank Quay supplementary report-16.pdf]]:205:contributors to the biomass included the crustaceans B. crenatus and Crangon crangon; the bivalve [[this>Teesworks/Planning/MLA_2020_00506/MLA_2020_00506-PC1084-RHD-ZZ-XX-RP-Z-1115_South Bank Quay supplementary report-16.pdf|MLA_2020_00506-PC1084-RHD-ZZ-XX-RP-Z-1115_South Bank Quay supplementary report-16.pdf]]:206:Motile invertebrates comprised crustaceans and echinoderms, whereas epifauna comprised solitary [[this>Teesworks/Planning/MLA_2020_00506/MLA_2020_00506-PC1084-RHD-ZZ-XX-RP-Z-1115_South Bank Quay supplementary report-16.pdf|MLA_2020_00506-PC1084-RHD-ZZ-XX-RP-Z-1115_South Bank Quay supplementary report-16.pdf]]:218: high densities of benthic invertebrates (e.g. worms, molluscs, and crustaceans), which provide [[this>Teesworks/Planning/MLA_2020_00506/MLA_2020_00506-PC1084-RHD-ZZ-XX-RP-Z-1115_South Bank Quay supplementary report-16.pdf|MLA_2020_00506-PC1084-RHD-ZZ-XX-RP-Z-1115_South Bank Quay supplementary report-16.pdf]]:314: pseudogaster, Tubificoides benedii, Enchytraeidae), crustaceans (A. modestus, S. balanoides, [[this>Teesworks/Planning/MLA_2020_00506/MLA_2020_00506-PC1084-RHD-ZZ-XX-RP-Z-1115_South Bank Quay supplementary report-16.pdf|MLA_2020_00506-PC1084-RHD-ZZ-XX-RP-Z-1115_South Bank Quay supplementary report-16.pdf]]:314: food source for crustaceans such as C. crangon and C. maenas and fish such as P. flesus [[this>Teesworks/Planning/MLA_2020_00506/MLA_2020_00506-PC1084-RHD-ZZ-XX-RP-Z-1115_South Bank Quay supplementary report-16.pdf|MLA_2020_00506-PC1084-RHD-ZZ-XX-RP-Z-1115_South Bank Quay supplementary report-16.pdf]]:314: (P. ulvae, L. saxatilis) crustaceans (C. volutator), polychaetes (H. diversicolor, P. elegans, [[this>Teesworks/Planning/MLA_2020_00506/MLA_2020_00506-PC1084-RHD-ZZ-XX-RP-Z-1115_South Bank Quay supplementary report-16.pdf|MLA_2020_00506-PC1084-RHD-ZZ-XX-RP-Z-1115_South Bank Quay supplementary report-16.pdf]]:315: biomass included the crustaceans B. crenatus and C. crangon, the bivalve Y. limatula, and [[this>Teesworks/Planning/MLA_2020_00506/MLA_2020_00506-PC1084-RHD-ZZ-XX-RP-Z-1115_South Bank Quay supplementary report-16.pdf|MLA_2020_00506-PC1084-RHD-ZZ-XX-RP-Z-1115_South Bank Quay supplementary report-16.pdf]]:317: Additional macrofauna recorded from the trawl samples included crustaceans, (C. crangon, [[this>Teesworks/Planning/MLA_2020_00506/MLA_2020_00506-PC1084-RHD-ZZ-XX-RP-Z-1115_South Bank Quay supplementary report-16.pdf|MLA_2020_00506-PC1084-RHD-ZZ-XX-RP-Z-1115_South Bank Quay supplementary report-16.pdf]]:322: The faunal communities recorded in the beam trawls comprised fish, crustaceans, [[this>Teesworks/Planning/MLA_2020_00506/MLA_2020_00506-PC1084_RHD-ZZ-XX-RP-Z-1100_EIA Report_main body-8.pdf|MLA_2020_00506-PC1084_RHD-ZZ-XX-RP-Z-1100_EIA Report_main body-8.pdf]]:197: British periods. The location of Hartlepool between areas of crustal uplift to the north [[this>Teesworks/Planning/MLA_2020_00506/MLA_2020_00506-PC1084_RHD-ZZ-XX-RP-Z-1100_EIA Report_main body-8.pdf|MLA_2020_00506-PC1084_RHD-ZZ-XX-RP-Z-1100_EIA Report_main body-8.pdf]]:199:stations. Mollusc taxa generally contributed most to biomass. Crustaceans, echinoderms and other taxa [[this>Teesworks/Planning/MLA_2020_00506/MLA_2020_00506-PC1084_RHD-ZZ-XX-RP-Z-1100_EIA Report_main body-8.pdf|MLA_2020_00506-PC1084_RHD-ZZ-XX-RP-Z-1100_EIA Report_main body-8.pdf]]:223:as cephalopods, other molluscs, crustaceans and polychaetes have also been recorded. The diet varies [[this>Teesworks/Planning/MLA_2020_00506/MLA_2020_00506-PC1084_RHD-ZZ-XX-RP-Z-1100_EIA Report_main body-8.pdf|MLA_2020_00506-PC1084_RHD-ZZ-XX-RP-Z-1100_EIA Report_main body-8.pdf]]:317: • Byelaw XXVIII – Crustacea Conservation Byelaw – only vessels 10m or under in length can [[this>Teesworks/Planning/MLA_2020_00506/MLA_2020_00506-PC1084_RHD-ZZ-XX-RP-Z-1100_EIA Report_main body-8.pdf|MLA_2020_00506-PC1084_RHD-ZZ-XX-RP-Z-1100_EIA Report_main body-8.pdf]]:321:crustaceans), with the presence of the dredge head likely resulting in them temporarily relocating away from [[this>Teesworks/Planning/MLA_2020_00506/MLA_2020_00506-PC1084_RHD-ZZ-XX-RP-Z-1100_EIA Report_main body-8.pdf|MLA_2020_00506-PC1084_RHD-ZZ-XX-RP-Z-1100_EIA Report_main body-8.pdf]]:536:across all stations. Mollusc taxa generally contributed most to biomass. Crustaceans, echinoderms and [[this>Teesworks/Planning/MLA_2020_00506/MLA_2020_00506-PC1084-RHD-SB-EN-NT-EV-1142-MLA.2020.00506.2 South Bank Quay MLV2 Appraisal of Environmental Effects.pdf|MLA_2020_00506-PC1084-RHD-SB-EN-NT-EV-1142-MLA.2020.00506.2 South Bank Quay MLV2 Appraisal of Environmental Effects.pdf]]:12:stations). Whilst mollusc taxa generally contributed most to biomass, crustaceans, echinoderms and [[this>Teesworks/Planning/MLA_2020_00506/MLA_2020_00506-PC1084-RHD-ZZ-XX-RP-Z-1115_South Bank Quay supplementary report-31.pdf|MLA_2020_00506-PC1084-RHD-ZZ-XX-RP-Z-1115_South Bank Quay supplementary report-31.pdf]]:20:such as crustaceans and echinoderms were present in lower numbers. There was no obvious dominance [[this>Teesworks/Planning/MLA_2020_00506/MLA_2020_00506-PC1084-RHD-ZZ-XX-RP-Z-1115_South Bank Quay supplementary report-31.pdf|MLA_2020_00506-PC1084-RHD-ZZ-XX-RP-Z-1115_South Bank Quay supplementary report-31.pdf]]:204:Cirriformia tentaculata, species of the genus Capitella and Eteone longa; oligochaetes, the crustaceans [[this>Teesworks/Planning/MLA_2020_00506/MLA_2020_00506-PC1084-RHD-ZZ-XX-RP-Z-1115_South Bank Quay supplementary report-31.pdf|MLA_2020_00506-PC1084-RHD-ZZ-XX-RP-Z-1115_South Bank Quay supplementary report-31.pdf]]:205:contributors to the biomass included the crustaceans B. crenatus and Crangon crangon; the bivalve [[this>Teesworks/Planning/MLA_2020_00506/MLA_2020_00506-PC1084-RHD-ZZ-XX-RP-Z-1115_South Bank Quay supplementary report-31.pdf|MLA_2020_00506-PC1084-RHD-ZZ-XX-RP-Z-1115_South Bank Quay supplementary report-31.pdf]]:206:Motile invertebrates comprised crustaceans and echinoderms, whereas epifauna comprised solitary [[this>Teesworks/Planning/MLA_2020_00506/MLA_2020_00506-PC1084-RHD-ZZ-XX-RP-Z-1115_South Bank Quay supplementary report-31.pdf|MLA_2020_00506-PC1084-RHD-ZZ-XX-RP-Z-1115_South Bank Quay supplementary report-31.pdf]]:218: high densities of benthic invertebrates (e.g. worms, molluscs, and crustaceans), which provide [[this>Teesworks/Planning/MLA_2020_00506/MLA_2020_00506-PC1084-RHD-ZZ-XX-RP-Z-1115_South Bank Quay supplementary report-31.pdf|MLA_2020_00506-PC1084-RHD-ZZ-XX-RP-Z-1115_South Bank Quay supplementary report-31.pdf]]:314: pseudogaster, Tubificoides benedii, Enchytraeidae), crustaceans (A. modestus, S. balanoides, [[this>Teesworks/Planning/MLA_2020_00506/MLA_2020_00506-PC1084-RHD-ZZ-XX-RP-Z-1115_South Bank Quay supplementary report-31.pdf|MLA_2020_00506-PC1084-RHD-ZZ-XX-RP-Z-1115_South Bank Quay supplementary report-31.pdf]]:314: food source for crustaceans such as C. crangon and C. maenas and fish such as P. flesus [[this>Teesworks/Planning/MLA_2020_00506/MLA_2020_00506-PC1084-RHD-ZZ-XX-RP-Z-1115_South Bank Quay supplementary report-31.pdf|MLA_2020_00506-PC1084-RHD-ZZ-XX-RP-Z-1115_South Bank Quay supplementary report-31.pdf]]:314: (P. ulvae, L. saxatilis) crustaceans (C. volutator), polychaetes (H. diversicolor, P. elegans, [[this>Teesworks/Planning/MLA_2020_00506/MLA_2020_00506-PC1084-RHD-ZZ-XX-RP-Z-1115_South Bank Quay supplementary report-31.pdf|MLA_2020_00506-PC1084-RHD-ZZ-XX-RP-Z-1115_South Bank Quay supplementary report-31.pdf]]:315: biomass included the crustaceans B. crenatus and C. crangon, the bivalve Y. limatula, and [[this>Teesworks/Planning/MLA_2020_00506/MLA_2020_00506-PC1084-RHD-ZZ-XX-RP-Z-1115_South Bank Quay supplementary report-31.pdf|MLA_2020_00506-PC1084-RHD-ZZ-XX-RP-Z-1115_South Bank Quay supplementary report-31.pdf]]:317: Additional macrofauna recorded from the trawl samples included crustaceans, (C. crangon, [[this>Teesworks/Planning/MLA_2020_00506/MLA_2020_00506-PC1084-RHD-ZZ-XX-RP-Z-1115_South Bank Quay supplementary report-31.pdf|MLA_2020_00506-PC1084-RHD-ZZ-XX-RP-Z-1115_South Bank Quay supplementary report-31.pdf]]:322: The faunal communities recorded in the beam trawls comprised fish, crustaceans, [[this>Teesworks/Planning/R-2022-0816-FFM/R-2022-0816-FFM-INCA2022-42 EcIA Steel House Park and Ride.pdf|R-2022-0816-FFM-INCA2022-42 EcIA Steel House Park and Ride.pdf]]:8:7,000 to 3,000 years BP. The location of Hartlepool on the fulcrum between areas of crustal uplift to [[this>Teesworks/Planning/MLA_2022_00248/Additional Documents/CHK-JBAU-00-00-RP-EN-0001-S3-P02-South_Bank_WFD_Report.pdf|CHK-JBAU-00-00-RP-EN-0001-S3-P02-South_Bank_WFD_Report.pdf]]:67: including crustaceans, Diptera, Coleoptera, Trichoptera, annelids and molluscs. [[this>Teesworks/Planning/R-2020-0685-ESM/R-2020-0685-ESM-PC1084_RHD-ZZ-XX-RP-Z-1100_28. Water Framework Directive compliance assessment.pdf|R-2020-0685-ESM-PC1084_RHD-ZZ-XX-RP-Z-1100_28. Water Framework Directive compliance assessment.pdf]]:15:across all stations. Mollusc taxa generally contributed most to biomass. Crustaceans, echinoderms and [[this>Teesworks/Planning/R-2020-0685-ESM/R-2020-0685-ESM-PC1084_RHD-ZZ-XX-RP-Z-1100_9. Marine ecology.pdf|R-2020-0685-ESM-PC1084_RHD-ZZ-XX-RP-Z-1100_9. Marine ecology.pdf]]:7: British periods. The location of Hartlepool between areas of crustal uplift to the north [[this>Teesworks/Planning/R-2020-0685-ESM/R-2020-0685-ESM-PC1084_RHD-ZZ-XX-RP-Z-1100_9. Marine ecology.pdf|R-2020-0685-ESM-PC1084_RHD-ZZ-XX-RP-Z-1100_9. Marine ecology.pdf]]:9:stations. Mollusc taxa generally contributed most to biomass. Crustaceans, echinoderms and other taxa [[this>Teesworks/Planning/R-2020-0685-ESM/R-2020-0685-ESM-PC1084_RHD-ZZ-XX-RP-Z-1100_10. Marine mammals.pdf|R-2020-0685-ESM-PC1084_RHD-ZZ-XX-RP-Z-1100_10. Marine mammals.pdf]]:7:as cephalopods, other molluscs, crustaceans and polychaetes have also been recorded. The diet varies [[this>Teesworks/Planning/R-2020-0685-ESM/R-2020-0685-ESM-PC1084_RHD-ZZ-XX-RP-Z-1100_13. Fish and fisheries.pdf|R-2020-0685-ESM-PC1084_RHD-ZZ-XX-RP-Z-1100_13. Fish and fisheries.pdf]]:11: • Byelaw XXVIII – Crustacea Conservation Byelaw – only vessels 10m or under in length can [[this>Teesworks/Planning/R-2020-0685-ESM/R-2020-0685-ESM-PC1084_RHD-ZZ-XX-RP-Z-1100_13. Fish and fisheries.pdf|R-2020-0685-ESM-PC1084_RHD-ZZ-XX-RP-Z-1100_13. Fish and fisheries.pdf]]:15:crustaceans), with the presence of the dredge head likely resulting in them temporarily relocating away from [[this>Teesworks/Planning/R-2019-0427-FFM/R-2019-0427-FFM-201920 Ecology report final.pdf|R-2019-0427-FFM-201920 Ecology report final.pdf]]:25:7,000 to 3,000 years BP. The location of Hartlepool on the fulcrum between areas of crustal uplift to [[this>Teesworks/Planning/R-2021-0166-FFM/R-2021-0166-FFM-Ecological Assessment.pdf|R-2021-0166-FFM-Ecological Assessment.pdf]]:7:7,000 to 3,000 years BP. The location of Hartlepool on the fulcrum between areas of crustal uplift to [[this>Teesworks/Planning/R-2022-0494-FFM/R-2022-0494-FFM-Ecological Impact Assessment.pdf|R-2022-0494-FFM-Ecological Impact Assessment.pdf]]:8:location of Hartlepool on the fulcrum between areas of crustal uplift to the north and [[this>Teesworks/Planning/R-2021-1048-FFM/R-2021-1048-FFM-2021-83 EcIA NZT Remediation Rev A.PDF|R-2021-1048-FFM-2021-83 EcIA NZT Remediation Rev A.PDF]]:7:7,000 to 3,000 years BP. The location of Hartlepool on the fulcrum between areas of crustal uplift to [[this>Teesworks/Planning/R-2020-0357-OOM/R-2020-0357-OOM-Habitats Regulation Assessment.pdf|R-2020-0357-OOM-Habitats Regulation Assessment.pdf]]:30:including crustaceans, molluscs and worms mainly in the intertidal mudflats and [[this>Teesworks/Planning/R-2020-0820-ESM/R-2020-0820-ESM-Lackenby EcIA Rev A.pdf|R-2020-0820-ESM-Lackenby EcIA Rev A.pdf]]:8:7,000 to 3,000 years BP. The location of Hartlepool on the fulcrum between areas of crustal uplift to [[this>Teesworks/Planning/R-2021-0924-CD/R-2021-0924-CD-CHK-JBAU-00-00-RP-EN-0001-S3-P02-South_Bank_WFD_Report.pdf|R-2021-0924-CD-CHK-JBAU-00-00-RP-EN-0001-S3-P02-South_Bank_WFD_Report.pdf]]:67: including crustaceans, Diptera, Coleoptera, Trichoptera, annelids and molluscs. [[this>Teesworks/Planning/R-2021-0608-PND/R-2021-0608-PND-210801_Ecolgy screening (EIA criteria) for Teesworks demolitions_INCA_RevA.pdf|R-2021-0608-PND-210801_Ecolgy screening (EIA criteria) for Teesworks demolitions_INCA_RevA.pdf]]:14:location of Hartlepool on the fulcrum between areas of crustal uplift to the north and [[this>Teesworks/Planning/MLA_2020_00507/MLA_2020_00507-PC1084_RHD-ZZ-XX-RP-Z-1100_EIA Report_main body-9.pdf|MLA_2020_00507-PC1084_RHD-ZZ-XX-RP-Z-1100_EIA Report_main body-9.pdf]]:197: British periods. The location of Hartlepool between areas of crustal uplift to the north [[this>Teesworks/Planning/MLA_2020_00507/MLA_2020_00507-PC1084_RHD-ZZ-XX-RP-Z-1100_EIA Report_main body-9.pdf|MLA_2020_00507-PC1084_RHD-ZZ-XX-RP-Z-1100_EIA Report_main body-9.pdf]]:199:stations. Mollusc taxa generally contributed most to biomass. Crustaceans, echinoderms and other taxa [[this>Teesworks/Planning/MLA_2020_00507/MLA_2020_00507-PC1084_RHD-ZZ-XX-RP-Z-1100_EIA Report_main body-9.pdf|MLA_2020_00507-PC1084_RHD-ZZ-XX-RP-Z-1100_EIA Report_main body-9.pdf]]:223:as cephalopods, other molluscs, crustaceans and polychaetes have also been recorded. The diet varies [[this>Teesworks/Planning/MLA_2020_00507/MLA_2020_00507-PC1084_RHD-ZZ-XX-RP-Z-1100_EIA Report_main body-9.pdf|MLA_2020_00507-PC1084_RHD-ZZ-XX-RP-Z-1100_EIA Report_main body-9.pdf]]:317: • Byelaw XXVIII – Crustacea Conservation Byelaw – only vessels 10m or under in length can [[this>Teesworks/Planning/MLA_2020_00507/MLA_2020_00507-PC1084_RHD-ZZ-XX-RP-Z-1100_EIA Report_main body-9.pdf|MLA_2020_00507-PC1084_RHD-ZZ-XX-RP-Z-1100_EIA Report_main body-9.pdf]]:321:crustaceans), with the presence of the dredge head likely resulting in them temporarily relocating away from [[this>Teesworks/Planning/MLA_2020_00507/MLA_2020_00507-PC1084_RHD-ZZ-XX-RP-Z-1100_EIA Report_main body-9.pdf|MLA_2020_00507-PC1084_RHD-ZZ-XX-RP-Z-1100_EIA Report_main body-9.pdf]]:536:across all stations. Mollusc taxa generally contributed most to biomass. Crustaceans, echinoderms and [[this>Teesworks/Planning/MLA_2020_00507/MLA_2020_00507-PC1084_RHD-ZZ-XX-RP-Z-1100_EIA Report_main body-8.pdf|MLA_2020_00507-PC1084_RHD-ZZ-XX-RP-Z-1100_EIA Report_main body-8.pdf]]:197: British periods. The location of Hartlepool between areas of crustal uplift to the north [[this>Teesworks/Planning/MLA_2020_00507/MLA_2020_00507-PC1084_RHD-ZZ-XX-RP-Z-1100_EIA Report_main body-8.pdf|MLA_2020_00507-PC1084_RHD-ZZ-XX-RP-Z-1100_EIA Report_main body-8.pdf]]:199:stations. Mollusc taxa generally contributed most to biomass. Crustaceans, echinoderms and other taxa [[this>Teesworks/Planning/MLA_2020_00507/MLA_2020_00507-PC1084_RHD-ZZ-XX-RP-Z-1100_EIA Report_main body-8.pdf|MLA_2020_00507-PC1084_RHD-ZZ-XX-RP-Z-1100_EIA Report_main body-8.pdf]]:223:as cephalopods, other molluscs, crustaceans and polychaetes have also been recorded. The diet varies [[this>Teesworks/Planning/MLA_2020_00507/MLA_2020_00507-PC1084_RHD-ZZ-XX-RP-Z-1100_EIA Report_main body-8.pdf|MLA_2020_00507-PC1084_RHD-ZZ-XX-RP-Z-1100_EIA Report_main body-8.pdf]]:317: • Byelaw XXVIII – Crustacea Conservation Byelaw – only vessels 10m or under in length can [[this>Teesworks/Planning/MLA_2020_00507/MLA_2020_00507-PC1084_RHD-ZZ-XX-RP-Z-1100_EIA Report_main body-8.pdf|MLA_2020_00507-PC1084_RHD-ZZ-XX-RP-Z-1100_EIA Report_main body-8.pdf]]:321:crustaceans), with the presence of the dredge head likely resulting in them temporarily relocating away from [[this>Teesworks/Planning/MLA_2020_00507/MLA_2020_00507-PC1084_RHD-ZZ-XX-RP-Z-1100_EIA Report_main body-8.pdf|MLA_2020_00507-PC1084_RHD-ZZ-XX-RP-Z-1100_EIA Report_main body-8.pdf]]:536:across all stations. Mollusc taxa generally contributed most to biomass. Crustaceans, echinoderms and [[this>Teesworks/Planning/R-2020-0371-SCP/R-2020-0371-SCP-PC1084_R-2020-0371-SCP-RHD-ZZ-XX-RP-Z-1100_EIA_Report_main_body-from-gov-uk.pdf|R-2020-0371-SCP-PC1084_R-2020-0371-SCP-RHD-ZZ-XX-RP-Z-1100_EIA_Report_main_body-from-gov-uk.pdf]]:197: British periods. The location of Hartlepool between areas of crustal uplift to the north [[this>Teesworks/Planning/R-2020-0371-SCP/R-2020-0371-SCP-PC1084_R-2020-0371-SCP-RHD-ZZ-XX-RP-Z-1100_EIA_Report_main_body-from-gov-uk.pdf|R-2020-0371-SCP-PC1084_R-2020-0371-SCP-RHD-ZZ-XX-RP-Z-1100_EIA_Report_main_body-from-gov-uk.pdf]]:199:stations. Mollusc taxa generally contributed most to biomass. Crustaceans, echinoderms and other taxa [[this>Teesworks/Planning/R-2020-0371-SCP/R-2020-0371-SCP-PC1084_R-2020-0371-SCP-RHD-ZZ-XX-RP-Z-1100_EIA_Report_main_body-from-gov-uk.pdf|R-2020-0371-SCP-PC1084_R-2020-0371-SCP-RHD-ZZ-XX-RP-Z-1100_EIA_Report_main_body-from-gov-uk.pdf]]:223:as cephalopods, other molluscs, crustaceans and polychaetes have also been recorded. The diet varies [[this>Teesworks/Planning/R-2020-0371-SCP/R-2020-0371-SCP-PC1084_R-2020-0371-SCP-RHD-ZZ-XX-RP-Z-1100_EIA_Report_main_body-from-gov-uk.pdf|R-2020-0371-SCP-PC1084_R-2020-0371-SCP-RHD-ZZ-XX-RP-Z-1100_EIA_Report_main_body-from-gov-uk.pdf]]:317: • Byelaw XXVIII – Crustacea Conservation Byelaw – only vessels 10m or under in length can [[this>Teesworks/Planning/R-2020-0371-SCP/R-2020-0371-SCP-PC1084_R-2020-0371-SCP-RHD-ZZ-XX-RP-Z-1100_EIA_Report_main_body-from-gov-uk.pdf|R-2020-0371-SCP-PC1084_R-2020-0371-SCP-RHD-ZZ-XX-RP-Z-1100_EIA_Report_main_body-from-gov-uk.pdf]]:321:crustaceans), with the presence of the dredge head likely resulting in them temporarily relocating away from [[this>Teesworks/Planning/R-2020-0371-SCP/R-2020-0371-SCP-PC1084_R-2020-0371-SCP-RHD-ZZ-XX-RP-Z-1100_EIA_Report_main_body-from-gov-uk.pdf|R-2020-0371-SCP-PC1084_R-2020-0371-SCP-RHD-ZZ-XX-RP-Z-1100_EIA_Report_main_body-from-gov-uk.pdf]]:536:across all stations. Mollusc taxa generally contributed most to biomass. Crustaceans, echinoderms and [[this>Teesworks/Planning/R-2020-0684-ESM/R-2020-0684-ESM-PC1084_RHD-ZZ-XX-RP-Z-1100_13. Fish and fisheries.pdf|R-2020-0684-ESM-PC1084_RHD-ZZ-XX-RP-Z-1100_13. Fish and fisheries.pdf]]:11: • Byelaw XXVIII – Crustacea Conservation Byelaw – only vessels 10m or under in length can [[this>Teesworks/Planning/R-2020-0684-ESM/R-2020-0684-ESM-PC1084_RHD-ZZ-XX-RP-Z-1100_13. Fish and fisheries.pdf|R-2020-0684-ESM-PC1084_RHD-ZZ-XX-RP-Z-1100_13. Fish and fisheries.pdf]]:15:crustaceans), with the presence of the dredge head likely resulting in them temporarily relocating away from [[this>Teesworks/Planning/R-2020-0684-ESM/R-2020-0684-ESM-PC1084_RHD-ZZ-XX-RP-Z-1100_9. Marine ecology.pdf|R-2020-0684-ESM-PC1084_RHD-ZZ-XX-RP-Z-1100_9. Marine ecology.pdf]]:7: British periods. The location of Hartlepool between areas of crustal uplift to the north [[this>Teesworks/Planning/R-2020-0684-ESM/R-2020-0684-ESM-PC1084_RHD-ZZ-XX-RP-Z-1100_9. Marine ecology.pdf|R-2020-0684-ESM-PC1084_RHD-ZZ-XX-RP-Z-1100_9. Marine ecology.pdf]]:9:stations. Mollusc taxa generally contributed most to biomass. Crustaceans, echinoderms and other taxa [[this>Teesworks/Planning/R-2020-0684-ESM/R-2020-0684-ESM-PC1084_RHD-ZZ-XX-RP-Z-1100_28. Water Framework Directive compliance assessment.pdf|R-2020-0684-ESM-PC1084_RHD-ZZ-XX-RP-Z-1100_28. Water Framework Directive compliance assessment.pdf]]:15:across all stations. Mollusc taxa generally contributed most to biomass. Crustaceans, echinoderms and [[this>Teesworks/Planning/R-2020-0684-ESM/R-2020-0684-ESM-PC1084_RHD-ZZ-XX-RP-Z-1100_10. Marine mammals.pdf|R-2020-0684-ESM-PC1084_RHD-ZZ-XX-RP-Z-1100_10. Marine mammals.pdf]]:7:as cephalopods, other molluscs, crustaceans and polychaetes have also been recorded. The diet varies [[this>Teesworks/Planning/R-2021-0405-FFM/R-2021-0405-FFM-210512, EcIA for South Bank Site Remediation_INCA_RevA Final.PDF|R-2021-0405-FFM-210512, EcIA for South Bank Site Remediation_INCA_RevA Final.PDF]]:9:7,000 to 3,000 years BP. The location of Hartlepool on the fulcrum between areas of crustal uplift to [[this>Teesworks/Planning/R-2020-0819-ESM/R-2020-0819-ESM-Dorman Point ES - Vol 2 - Chapter D - Biodiversity and Ecology - Dec 2020.PDF|R-2020-0819-ESM-Dorman Point ES - Vol 2 - Chapter D - Biodiversity and Ecology - Dec 2020.PDF]]:16: fulcrum between areas of crustal uplift to the north and subsidence to the south makes these [[this>Teesworks/Planning/R-2020-0822-ESM/R-2020-0822-ESM-Long Acres ES - Vol 2 - Chapter D - Biodiversity and Ecology - Dec 2020(1).PDF|R-2020-0822-ESM-Long Acres ES - Vol 2 - Chapter D - Biodiversity and Ecology - Dec 2020(1).PDF]]:15: fulcrum between areas of crustal uplift to the north and subsidence to the south makes these