Regulatory Responsibilities & Enforcement Mechanisms Relevant to Marine Nature Conservation in the United Kingdom
(2003)
Report to JNCC
Boyes, W., Warren, L. & Elliott, H.
© Defra 2003
Introduction
The strengths and potentail weaknesses of
the sectoral approach to regulation of activities below mean
low water mark in the UK were discussed in a review undertaken by
the Department of Environment and the Welsh Office in 1993 (DoE /
Welsh Office, 1993a). Management arrangements in the UK are
divided for coastal areas above and below mean low water mark
(MLWM). Above MLWM, local authorities have powers to control
development and use of land under the Town and Country Planning
Act, 1990. The planning system is designed to control
development through an applications system, and decisions must be
made in accordance with the planning authorities' development
plans. There is also government planning guidance which
recognises the special nature of the coastal zone in PPG20, Coastal
Planning and PPG14, Development of Unstable Land (Humphrey &
Burbridge, 1999).
Below MHWM, statutory controls mostly operate on a
sectoral basis. Regulated
activities include aggregate extraction, shipping, oil and gas
development, cables and pipelines, coastal defence, historic sites,
nature conservation, fisheries, recreation and increasing moves to
establish offshore renewable energy sites. Consents and
licences are awarded for development below low water after an
informed judgement is made based on the best available evidence
through the Environmental Impact Assessment (EIA) procedure and the
imminent Strategic Environmental Assessment Directive (SEA).
The Government View procedure requires that a favourable Government
View is required to support applications to the Crown Estate.
Coastal areas have suffered from a lack of dedicated policy
and regulatory coordination (Huggett,
1998; Local Government Association (LGA), 2000; Allmendinger et al., 2002). However, there
is a growing realisation that "the coast is not only a complex
natural environment; it is also a complex policy area where a range
of agencies with differing, but often overlapping, objectives,
responsibilities and powers operate" (Scottish Office, 1997).
There is a mass of roles and responsibilities undertaken by
different government bodies that has led to the decline in water
quality in coastal regions, the degradation and destruction of
critical habitats, the loss of key fisheries and threats to
biodiversity (Olsen et al, 1997).
In the late 1990s, there has been an unparalleled increase in
the growth of responsibilities on marine authorities, to take
account environmental issues (Laffoley
& Bines, 2000) such as full compliance with the obligations of
the Habitats Directive. During the same period there has been less
evidence of the joined up thinking
required to match responsibilities to the required competencies,
resources and organisation of the authorities.
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Please cite as: Boyes, W., Warren, L. & Elliott, H., (2003), Regulatory Responsibilities & Enforcement Mechanisms Relevant to Marine Nature Conservation in the United Kingdom, Institute of Estuarine and Coastal Studies, University of Hull