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Beach Topographic Variability in Relation to Significant Biological Change

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Webb, H., Pye, K., Huckle, J. and Blott, S.J. (2010) Beach Topographic Variability in Relation to Significant Biological Change. Report to Countryside Council for Wales by APEM Ltd. and Kenneth Pye Associates Ltd., CCW Contract Science Report No 906, Countryside Council for Wales, Bangor, xiii + 160 pp.

Executive Summary

The Welsh Assembly Government (WAG) is funding the development of an all Wales Monitoring Centre that will collate and manage regional shoreline data. This national scale background monitoring will complement strategic investigations at a regional level. It is vital that full use is made of the information that the Monitoring Centre generates to ensure the funding delivers best value.  This project is designed to assist Countryside Council for Wales (CCW) to specify its data requirements and thus maximise the use of the Monitoring Centre from the outset.

For CCW, a major driver for physical and biological monitoring arises from international and national obligations with respect to nature conservation. The data held by the Monitoring Centre will underpin the identification and monitoring of regional changes and will inform protected site management in terms of reporting and understanding changes occurring at each sites. CCW spends a great deal of effort characterising and mapping inter-tidal habitats in Wales and undertakes an extensive program of biological monitoring. However, monitoring of coastal physical processes and morphological change undertaken by CCW is very limited; therefore, there is a valuable opportunity to maximise the use of physical data gathered and reported on by the Monitoring Centre. Key to achieving this is the development of an integrated programme which combines physical and biological monitoring. CCW would also like to identify environmental thresholds relevant to each biotope and designated area of conservation interest. Such thresholds would inform site management and trigger appropriate conservation activities. An understanding of the extent and timescales of topographic variability of different types of coastal profile is also required for assisting in prescribing operational management plans to minimise the potential impacts of pollution events such as the 1996 Sea Empress disaster in Milford Haven.

A key aim of this project was to provide a review of the nature of coastal monitoring that is currently being undertaken elsewhere, so that appropriate recommendations as to CCW’s data requirements can be made to the new Monitoring Centre. These recommendations concern the measurement and reporting of environmental processes and features which are of biological significance.

Many environmental factors exert an influence on coastal biological communities, principally water quality, exposure to wave action, tidal range, and tidal currents. A review of the definitions and terminology used when describing these environmental factors is presented to set the context for the rest of the report and to assist in identifying environmental trigger thresholds for key ecological features.

A thorough review of relevant published and unpublished information relating to beach volatility and biological communities was undertaken. A number of key ecological features were selected as case studies, namely: Sabellaria reefs, Eelgrass (Zostera sp.) beds, beaches supporting the amphipod Pectenogammarus planicrurus, low shore and sub-littoral bivalve-rich communities, and muddy gravels. Key biological sensitivities in relation to changes in physical characteristics of beaches were identified and where possible, thresholds of topographic change defined. Such thresholds would indicate where biological changes are likely to occur and could be used as triggers for reporting/notification of change to CCW. This review considers both beach topography and associated changes in the hydrodynamic regime.

The physical requirements of the case study species and communities could be defined in a broad qualitative sense.  However, the ability to ascribe quantitative levels of change in physical environmental variables as causes of biological change requires more work before a robust assessment of significant impacts on species and habitats can be made. A key factor in gaining this understanding is developing an improved knowledge base regarding the levels of ‘natural’ change occurring in coastal environments.

The importance of monitoring changes in beach and nearshore morphology has been recognised for many years. An overview of the main methodologies available for the monitoring of beach/nearshore topographic change and the driving environmental processes has been provided, including those currently used in Strategic Regional Coastal Monitoring Programmes (SRCMPs) in England. For monitoring coastal change these include visual observation and photography, land-based surveying, hydrographic surveys, aerial photography and photogrammetry, CASI, satellite imagery and LiDAR. The methods and importance of monitoring the physical forcing factors such as tidal levels and currents, wind speed, wind direction and wave action, including examples of the types of data which can be gathered, is also given along with methods used to monitor sediment characteristics. 

The issues surrounding beach volatility and biological communities were considered within the context of a number of selected case study areas (Traeth Crugan, Morfa Dyffryn, the Dyfi Estuary, and Burry Inlet). These case studies were used to identify some of the key data requirements for each of the sites that the Monitoring Centre could deliver and thereby demonstrate the practical applications of the results of this study.

Existing SRCMPs throughout the UK have developed a relatively comprehensive set of procedures for data capture and reporting and a great deal of the information being gathered is relevant to biological conservation interests. To date, these results have been poorly integrated with ecological and wider environmental monitoring. An overview is provided of the methods for the monitoring of beach topographic variability carried out by these SRCMPs. The frequency and intensity of the monitoring employed is generally considered adequate for the purposes of monitoring medium to longer term changes (at annual to decadal timescales).  Such methods are therefore highly relevant to the assessment of medium term threats to habitats of national and international conservation importance.  The current monitoring programmes may be less adequate for the purposes of biological monitoring of species and communities where their survival may be as much dependent on the occurrence of extreme events as on long-term changes. Short-lived episodes of very low or very high beach levels may not, for example, be detected by annual or bi-annual monitoring; to obtain a true picture of beach topographic variability high frequency monitoring may be required, ideally after, or even during, individual tides.  An understanding of short-term changes in beach levels need to be accompanied by a knowledge of the associated variations in surface sediment mobility and particle size characteristics, which exert a significant influence on many species.

The data to be held by the Monitoring Centre offers great potential to assist in defining thresholds of topographic change above which biological changes are likely to occur and which could be used as triggers for reporting/notification of change to CCW.  For some habitats and species, for which there is a better understanding of the biological implications of physical changes in beach topography, such thresholds would be relatively easy to define.  For most ecological features however, more work is required before these quantitative thresholds could be set. Individual critical levels established by niche modelling or further field investigations would be required in order to specify reporting requirements. The strategic regional monitoring should be supplemented by more detailed local area studies to achieve a better understanding of critical thresholds of topographic change, sediment character and water quality which are relevant to particular species and communities of national and international conservation interest.

Key to being able to define quantitative thresholds is the requirement for an interim period of baseline data collection. The Monitoring Centre provides an excellent opportunity to provide data that can contribute to the establishment of this baseline information, and thus improve our understanding of the conditions in which the biological communities and habitats exist at the moment, and the degree of spatial and temporal variability that occurs naturally. Beaches are extremely dynamic environments and therefore an understanding of the degree of such natural variability in the physical environment is crucial in understanding how they influence the biodiversity of these important ecosystems.
 


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