260303pd_teesport_eir_request_-_maintenance_dredging
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| 260303pd_teesport_eir_request_-_maintenance_dredging [2026/05/01 14:06] – nefcadmin | 260303pd_teesport_eir_request_-_maintenance_dredging [2026/05/14 21:11] (current) – [Analysis] nefcadmin | ||
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| I am writing on behalf of North East Marine Research Group (NEMRG) to seek the following information relating to the Tees Maintenance Dredge Protocol (MDP) Baseline Document (dated May 20, 2025) and to PD Ports Ltd’s maintenance dredging operations. | I am writing on behalf of North East Marine Research Group (NEMRG) to seek the following information relating to the Tees Maintenance Dredge Protocol (MDP) Baseline Document (dated May 20, 2025) and to PD Ports Ltd’s maintenance dredging operations. | ||
| - | 1. Trailing Suction Hopper Dredger (TSHD) Operational Data | + | ==== 1. Trailing Suction Hopper Dredger (TSHD) Operational Data ==== |
| The MDP acknowledges the use of the Emerald Duchess and Heortnesse but omits technical details on hopper overflow. Please provide the following: | The MDP acknowledges the use of the Emerald Duchess and Heortnesse but omits technical details on hopper overflow. Please provide the following: | ||
| Line 14: | Line 14: | ||
| * Request 1.3: All internal reports and studies used by PD Teesport to validate the claim of environmental sustainability of the dredging operations, specifically that green valves contribute to environmental sustainability by reducing the mass flux of contaminants, | * Request 1.3: All internal reports and studies used by PD Teesport to validate the claim of environmental sustainability of the dredging operations, specifically that green valves contribute to environmental sustainability by reducing the mass flux of contaminants, | ||
| - | 2. Estuarine Plume Modelling and Hydrodynamics | + | ==== 2. Estuarine Plume Modelling and Hydrodynamics |
| The MDP provides plume modelling for the offshore disposal site (Tees Bay A) but contains no equivalent modelling for the inner estuary reaches. | The MDP provides plume modelling for the offshore disposal site (Tees Bay A) but contains no equivalent modelling for the inner estuary reaches. | ||
| * Request 2.1: Disclose all 3D hydrodynamic or sediment transport modelling held by PD Teesport that specifically simulates the " | * Request 2.1: Disclose all 3D hydrodynamic or sediment transport modelling held by PD Teesport that specifically simulates the " | ||
| * Request 2.2: Provide all data regarding the " | * Request 2.2: Provide all data regarding the " | ||
| - | 3. Contaminant Partitioning and "Fine Fraction" | + | ==== 3. Contaminant Partitioning and "Fine Fraction" |
| The MDP relies on bulk sediment sampling and Cefas Action Levels designed for offshore disposal rather than known toxicity of contaminants. It fails to account for the fact that hydrophobic contaminants (PAHs, PCBs, PBDEs) adsorb preferentially to the fine particles (<63µm) that are systematically released via overflow. | The MDP relies on bulk sediment sampling and Cefas Action Levels designed for offshore disposal rather than known toxicity of contaminants. It fails to account for the fact that hydrophobic contaminants (PAHs, PCBs, PBDEs) adsorb preferentially to the fine particles (<63µm) that are systematically released via overflow. | ||
| * Request 3.1: Disclose all chemical analysis held by PD Teesport that was conducted specifically on the overflow water/fine sediment fraction, rather than bulk bed samples. | * Request 3.1: Disclose all chemical analysis held by PD Teesport that was conducted specifically on the overflow water/fine sediment fraction, rather than bulk bed samples. | ||
| * Request 3.2: Provide the raw data for the Year 9 (2024) mid-licence sampling, specifically the Total Organic Carbon (TOC) levels used to normalise PBDE concentrations, | * Request 3.2: Provide the raw data for the Year 9 (2024) mid-licence sampling, specifically the Total Organic Carbon (TOC) levels used to normalise PBDE concentrations, | ||
| - | 4. Water Framework Directive (WFD) and Protected Sites | + | ==== 4. Water Framework Directive (WFD) and Protected Sites ==== |
| The Tees Transitional water body is currently failing for PBDEs, mercury, and benzo(g, | The Tees Transitional water body is currently failing for PBDEs, mercury, and benzo(g, | ||
| * Request 4.1: Provide the "WFD Compliance Assessment" | * Request 4.1: Provide the "WFD Compliance Assessment" | ||
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| === Request 4.2: Disclose any evidence used to conclude that dredging-induced turbidity does not impact the foraging success of Common Terns over their entire estuarine range, particularly in the silty upper reaches. === | === Request 4.2: Disclose any evidence used to conclude that dredging-induced turbidity does not impact the foraging success of Common Terns over their entire estuarine range, particularly in the silty upper reaches. === | ||
| - | PD Teesport holds information responsive to this part of your Request. | + | PD Teesport holds information responsive to this part of your Request. |
| === Request 4.3: Records of any Turbidity/ | === Request 4.3: Records of any Turbidity/ | ||
| Line 188: | Line 188: | ||
| Richard Ellison | Richard Ellison | ||
| - | Data Protection Officer | ||
| - | PD Teesport Limited | ||
| - | |||
| - | Enclosures | ||
| - | Docusign Envelope ID: C489310D-465A-8FC6-801B-545ED10BA623 | + | ===== Analysis ===== |
| + | |||
| + | No information has been supplied which suggests that any environmental impact assessment is carried out on the maintenance dredging operation. | ||
| + | |||
| + | A trailing suction hopper dredger presents two sources of contamination: | ||
| + | - the dredge head resuspending material which is not captured in the suction (up to 20% of dredged amount) | ||
| + | - the overflow from the hopper (up to 25% of the dredged amount) | ||
| + | |||
| + | The response confirms that overflow happens every time the dredgers are deployed, but despite operating within the Tees SSSI, SPA and Ramsar, does not show any definition of the pathways when operating within the river. | ||
| + | |||
| + | There is no evidence of a least significant effect appraisal of the maintenance dredging operations. | ||
| + | ==== 1. Trailing Suction Hopper Dredger (TSHD) Operational Data ==== | ||
| + | - Dredge logs - 1 supplied for 20th December 2025 - no information on overflowing. | ||
| + | - Green valve - no information supplied as considered commercially sensitive. | ||
| + | - Proof of environmental sustainability of dredging operations - no information supplied as considered commercially sensitive. | ||
| + | |||
| + | ==== 2. Estuarine Plume Modelling and Hydrodynamics ==== | ||
| + | - Plume dynamics from overflow - no information held. | ||
| + | - Sediment trap effect - no information held. | ||
| + | ==== 3. Contaminant Partitioning and "Fine Fraction" | ||
| + | - Chemical analysis of overflow fraction - no information help. | ||
| + | - TOC for mid-licence sampling - MMO templates supplied. | ||
| + | ==== 4. Water Framework Directive (WFD) and Protected Sites ==== | ||
| + | - WFD compliance for extraction phase of dredging - pointed to previous WFD for disposal. | ||
| + | - Dredging induced turbidity impact on terns etc. - MDP and should look at the [[https:// | ||
| + | - Records of turbidity / dissolved oxygen - PD Teesport holds no records. | ||
| + | - Test of likely significance SPA - MDP and extension of SPA. Without plume modelling once again these documents refer to the disposal not the dredging operation. | ||
260303pd_teesport_eir_request_-_maintenance_dredging.1777644406.txt.gz · Last modified: by nefcadmin
