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Draft guidance framework for marine navigation dredging and disposal decision making. Presentation by Jan Brooke Environmental Consultant. Background.
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Draft guidance framework for marine navigation dredging and disposal decision making Presentation by Jan Brooke Environmental Consultant
Background • Navigation-related dredging and disposal has the potential to affect the ability of a water body to meet its WFD and Birds/Habitats Directive (BHD) objectives • Marine navigation dredging and disposal framework developed as joint initiative of Environment Agency and ports sector by a team led by HR Wallingford
Overview • Methodology can be applied to both maintenance and capital dredging projects • Joined-up approach aims to reduce burden on both regulators and operators • Robust but practical, pragmatic approach to WFD compliance assessment • Linked to equivalent steps in Habitats Regulations and Environmental Impact Assessments
Two most important FAQ questions • 4.3 Is there a relationship between HD Article 6(3)-6(4) and WFD Article 4(7)? • 3.2 What is the difference between the species/biological quality elements addressed in the WFD and BHD?
Capital dredging projects • Create new channel or deepen or widen existing channel or berth • Typically already subject to EIA and Habitats Regulations Assessment (under Habitats Directive Articles 6(3) and 6(4)) • WFD methodology links into these data collection and assessment processes • Follows similar screening, scoping and assessment steps
Maintenance dredging projects • Maintenance dredging: routine, often frequent, activity • Typically temporary, local effects • No new physical modifications; seabed communities typically opportunistic species • Assessment approach applied to capital projects is often disproportionate or impractical
Maintenance Dredging Protocol • Maintenance Dredging Protocol aim: demonstrate compliance with BHD in England and Wales • Baseline document and initial assessment • Assessment repeated only if there are changes in either: • dredging (method, quantity, etc.) or • environmental interest • Similar approach for maintenance dredging under WFD?
Dredging and Disposal Framework • Aim: informed, proportionate decisions • Step 1 screening: could dredging or disposal cause deterioration or otherwise affect ability of water body to meet its WFD objectives including protected areas? • Step 2 scoping: which WFD parameters could be affected; type/scale of effect; assessment scope; parallels with other processes? • Step 3 targeted assessment, agreed by regulator
Issues arising during development of framework • Assumed WFD deterioration can be caused by reduction in status class of any parameter even if does not affect overall status class • Need more clarity with regard to consideration of cumulative or in-combination effects in relation to WFD Article 4(7)?
Mersey case study • Maintenance Dredging Protocol ‘baseline document’ being prepared to support forthcoming maintenance dredging applications • Objective: use this process to establish which WFD parameters may be affected by dredging or disposal; also to identify significant data gaps
Synergies • Similar methodological processes, approaches to screening and scoping • Option to coordinate data collection and assessment processes where practicable • Can help to rationalise costs (data collection in marine environment can be very expensive) • May also be opportunities to rationalise post-project monitoring • However, also important differences!
Water quality: list of priority (hazardous) substances Ecological quality elements (e.g. aquatic flora, phytoplankton, fish, benthic invertebrates) Hydromorphological and physico-chemical supporting elements Consider wide range of protected areas Sediment quality: CEFAS list of parameters; not typically water quality Ecological interest features (i.e. particular designated species, habitats) Hydromorphological and physico-chemical supporting elements Not typically concerned with other protected areas WFD vs. BHD parameters
Main ‘problems’ encountered • Gaps in baseline data; in status class boundaries • Practical difficulties reconciling boundaries; scale • Extent to which detailed parameters coincide; care not to make unsubstantiated assumptions • Relationship between water quality and sediment quality not clear (e.g. whether substance adsorbed to sediment is bio-available if re-suspended): research is needed
Lessons from case study…… • Make best use of available data: pragmatism is essential • Recognise differences (e.g. specific parameters): manage expectations about extent of common ground • Differences can be important e.g. determining what is ‘significant’ in WFD and BHD terms • WFD: cause deterioration in water body status … failure to achieve good status • Habitats Directive: likely significant effect … individually or in combination with other plans or projects… adversely affect integrity
Application of WFD Article 4(7) • WFD applies to all water bodies; BHD to ‘special’ areas • Application of 4(7) needs to be proportionate • Also useful experience from EIA • Where protected area is present in a water body, option to refer to Articles 4(8) and BHD 6(3)/6(4) to modify the degree of ‘over-riding’ and/or the expected ‘balance’ between and costs-benefits • Communicate clearly what is expected