Simon Bray

Comparative biodiversity of rivers, streams, ditches and ponds in an agricultural landscape in Southern England

Information about the relative biodiversity value of different waterbody types is a vital pre-requisite for many strategic conservation goals. In practice, however, exceptionally few inter-waterbody comparisons have been made. The current study compared river, stream, ditch and pond biodiversity within an 80 km2 area of lowland British countryside. The results showed that although all waterbody types contributed to the diversity of macrophytes and macroinvertebrates in the region, they differed in relative value. Individual river sites were rich but relatively uniform in their species composition. Individual ponds varied considerably in species richness, with the richest sites supporting similar numbers of taxa to the best river sections, but the poorest sites amongst the most impoverished for all waterbody types. At a regional level, however, ponds contributed most to biodiversity, supporting considerably more species, more unique species and more scarce species than other waterbody types. Streams typically supported fewer species and fewer unique species at local and regional level than either ponds or rivers. Ditches (most of which were seasonal) were the least species-rich habitat, but supported uncommon species, including temporary water invertebrates not recorded in other waterbody types. Multivariate analysis indicated that permanence, depth, flow and altitude were the main environmental variables explaining invertebrate and plant assemblage composition. The findings, as a whole, suggest that ponds and other small waterbodies can contribute significantly to regional biodiversity. This contrasts markedly with their relative status in national monitoring and protection strategies, where small waterbodies are largely ignored.

Recovery of polluted ecosystems: the case for long-term studies

Recovery of marine ecosystems from pollution has tended to receive less attention than the study of new or continuing impacts, but such studies are important in charting recovery from acute incidents and following legislation to deal with chronic contamination. Recovery is inevitably a long-term process, and where such studies have been made they are often too short-lived. Interest quickly wanes following an acute incident and governmental bodies rapidly switch to new legislative priorities for chronic inputs. We review three case studies: recovery of dogwhelk populations after local extinction by tributyl tin leachates from anti-fouling paints; recovery of rocky shore communities from oil spills; and recovery of estuarine ecosystems from industrial and urban development. We then make some generalisations about recovery processes before making a plea for long-term studies of polluted areas.

Impacts of anthropogenic stress on rocky intertidal communities

Rocky shores provide a harsh environment for marine organisms andwe briefly discuss natural sources of variation in community structure beforeconsidering anthropogenic impacts in detail. We review impacts caused by (a) acutedisturbances: oil spills, toxic algal blooms and (b) chronic disturbances: nutrient pollution,oil, heavy metals, pesticides, antifouling paints, collecting, trampling/habitatdegradation, siltation and introduced species. Community level effects are emphasisedthroughout and illustrative examples are drawn from field-based case studies. Particularattention is given to the lessons learned from oil spills and the effect of chronicpollution by tributyltin on dogwhelks, the impacts of which ranged from the biochemical tocommunity levels of organisation. Impacts are placed in a global and historicalperspective and the potential for the recovery of shores under appropriate management isdiscussed. Finally we consider the relative merits of the multivariate and univariateapproaches to studying impacted communities and suggest priorities for future research.

Intertidal mudflat and saltmarsh conservation and sustainable use in the UK: A review

The adoption of the Convention on Wetlands of International Importance in Ramsar, Iran in 1971 committed the UK to conserve and sustainably use intertidal mudflats and saltmarshes for the benefit of present and future generations. Through consideration of their importance and value, current status, the characteristics, causes and consequences of their loss, and the associated responses to loss, this paper reviews the UK progress towards the conservation and sustainable use of intertidal mudflats and saltmarshes. Uncertainties in their current status and trends make it difficult to assess the overall net change in extent across the UK. However, it is apparent that losses due to erosion continue to exceed gains from intertidal mudflat and saltmarsh reparation (IMSR) schemes in south-east and southern England. IMSR schemes in the UK have been generally limited to relatively small-scale trials in comparison to elsewhere in Europe and in the USA. No research to date has unequivocally identified the causes of erosion. Regardless of the cause, the loss of intertidal mudflats and saltmarshes has adverse impacts on the provision of ecosystem services upon which humans and other species depend. The evidence presented in this paper suggests that alongside further science-based research, there is a need to develop a decision-making process capable of accommodating complexity, uncertainty and multiple diverse perspectives, through which more informed, timely decisions and more effective, concerted actions to conserve and sustainably use intertidal mudflats and saltmarshes can be taken.

Restoration of temperate marine and coastal ecosystems: nudging nature

1. The main impacts on marine ecosystems are summarised and the potential for their restoration is discussed in relation to their key features. Rocky shores, seagrass beds and disused docks are focused on. 2. The term restoration is used to describe intervention in the recovery process of a marine ecosystem, with a view to enhancing the process, but not necessarily forcing the system to recover to its original condition. 3. Rocky shore systems are subject to shellfish and seaweed exploitation, point source pollution, diffuse impacts such as tributyl tin and acute impacts such as oil spills. The consideration of whether to employ restoration or allow natural recovery is discussed in relation to these systems. 4. Seagrass systems have suffered serious declines in many parts of the world due to the direct and indirect effects of human impacts. In the North Atlantic a wasting disease first noted in the 1930s caused a serious decline in the subtidal seagrass Zostera marina. The link between this disease and the marine slime mould Labrynthula zosterae is now well established. Human impacts on seagrass systems allow the disease to gain a foothold. Attempts at restoring seagrass beds have met with some success, but it is suggested that the action of conservation of remaining beds and better management of human activities may be the best approach. 5. Disused docks occur in many parts of Britain and Europe. Active management of the physical environment by mixing and biomanipulation by filter feeding organisms have led to improvements in water quality and ecosystem function. Thus healthy marine ecosystems have been restored to inner city areas, although these artificial marine lakes have few natural equivalents and are different from the original ecosystem at the site. 6. When compared to freshwater ecosystems, the scope for coastal and marine restoration is limited although the capacity for recovery is greater.

The regional recovery of Nucella lapillus populations from marine pollution, facilitated by man-made structures

The dogwhelk Nucella lapillus experienced localized extinction in the 1980s and 1990s due to the use of tributyltin (TBT) antifoulants, causing imposex in females. The aim of this study was to establish the extent of the return of the species across the mainland coast of central southern England as TBT use has been progressively restricted, and to quantify the extent of imposex impact on the populations present. We surveyed from Poole to Selsey where isolated populations had become extinct, and the Isle of Wight where some populations had persisted. We found evidence that since TBT restrictions, recolonization and colonization by N. lapillus has been rapid. By 2007–2008, of the eleven surveyed mainland sites, seven were colonized, although indications of reduced imposex impacts were mixed. Distribution had also extended on the Isle of Wight and populations were larger with less imposex impact in sites with long term populations. The lack of continuous suitable habitat blocks and the hydrodynamic complexity of the region, leads us to hypothesize that recovery has been facilitated by man-made structures which may be acting as ‘stepping stones’. Populations that have become established on engineered structures such as sea walls, breakwaters and rock groynes demonstrate accelerated recovery in the region as TBT in the environment has generally declined. Sites with suitable substrates and food sources near to ports were either not recolonized or had small populations with imposex evident. For species with a short pelagic larval stage or with direct development, population connectivity between patches of harder substrata along hydrodynamically complex coastlines may be greater than previously thought.