Thank you for the opportunity to present at this committee meeting.
I'm a lecturer in environmental governance from the University of Hull in the United Kingdom. I studied the planning of marine conservation zones, MCZs, in England for my Ph.D. research between 2010 and 2013. I'm currently investigating the governance incentives underpinning the management effectiveness of MCZs, on which this statement is based.
My Ph.D. research on the English MCZ process involved key-informant interviews with scientific experts and decision-makers, and participant observations of the stakeholder-informed planning process. The objectives of English MCZs were to protect representative broad-scale seabed habitats and species of conservation interest from human pressures.
The process was target-driven, with sites designated irrespective of whether the conservation features were deemed vulnerable to human disturbance. Most conservation objectives for MCZs were set to maintain the feature in its present condition, rather than recover the feature to an unknown baseline.
Monitoring of the designated features at a site level is necessary to judge whether objectives are being met. As of 2024, only 10% of U.K. MPAs have monitoring in place. For many MPAs, there's a lack of resources for conducting surveys at the require frequency and spatial scale to measure whether conservation objectives are being met.
Generally, the initial planning process of one and a half years was viewed as too rushed for the spatial scale at which many of the MCZs were being designated. It certainly did not allow enough time for adequate ecological evidence to be gathered from many of the sites, and the accuracy of broad-scale habitat maps was also questioned. Certain fishing representatives were also cynical of the target-driven process and the lack of clarity over what the MCZs were being designated to protect.
There have been 91 MCZs designated in three tranches between 2013 and 2019. Socio-economic impact assessments have been undertaken for all sites, and currently, management measures have been implemented in inshore MCZs designated within six nautical miles.
In 2025, the U.K. government ran a consultation on the management measures for 42 offshore MCZs. However, this consultation was criticized by industry for providing a binary choice of doing nothing or banning bottom trawling. The U.K. fishing industry had to oppose the ban, despite advocating for a pragmatic zonal approach to protect site features. Some of the offshore MCZs designated are more than 4,000 square kilometres, and that could have significant impacts on fisheries and offshore wind development if they restricted all human activities. Currently, three MCZs are highly protected across the whole site.
The U.K. government is currently facing ongoing campaigns from environmental organizations for more highly protected MPAs, with the main justification being that many recently designated MCZs have insufficient protections at site level.
The U.K. is also rapidly developing offshore wind sites to meet its net-zero emissions targets, with further new MPAs being discussed with regard to offsetting the potential biodiversity impacts of large offshore developments. The U.K. fishing industry is concerned that they will be essentially paying for the impacts of offshore wind development through the loss of more fishing grounds designated as MPAs.
It is therefore imperative that MPAs are designated within a wider framework of marine spatial planning, which is something that the MCZ process failed to do. This failure is still causing the U.K. fishing industry challenges with respect to ongoing uncertainty over site management measures and the perceived legitimacy of policy decisions being made.
However, I'd like to stress that there are examples of effective MPA governance in the U.K. for specific sites where the fishing industry and the conservation community have worked together to meet conservation objectives. A good example of a community-focused conservation initiative is out of the Lyme Bay MPA in the south of England.
Despite a ban on trawling, a study has shown that trawl landings have largely remained the same, with an increase in the value of static gear catches. An additional turnover of 2.2 million pounds was also realized for recreational dive operators and charter vessels during the three years after the closure. Annual monitoring is carried out by the University of Plymouth, and the conservation benefits have been significant.
From personal experience and as documented in the wider academic literature, building trust between industry and conservation stakeholders is key with respect to both the provision of data and the legitimacy of decision-making. The fishing industry has detailed knowledge and fine-scale plotter data from areas being fished, which can allow for more targeted conservation measures. If industry is also involved in objective setting and site design, this can lead to win-win situations for both fisheries and conservation, such as what has been achieved in Lyme Bay.
Within the context of the growing pressures on fishers' access to marine space, the impacts of environmental change and the need to balance marine conservation with food and energy security, any restriction of fishing needs to be justified by robust ecological evidence.
It is also imperative that consultation with stakeholders takes place at the point where their knowledge and data can influence the final management decision, not after a decision has been made or the scope of policy options reduced.
Thank you.