Common standards monitoring • Managed realignment
Managed realignment
Saltmarsh squeeze (loss of habitat resulting from enclosure and erosion caused by sea level rise and/or other factors) has occurred in many coastal and estuarine areas, especially in south east England. Reversing this process through the Managed Realignment of flood defences is an increasingly common option for recreating saltmarsh and forms one of the generic options of any flood management strategy. Monitoring the effectiveness of such realignment is important in helping to determine the success of such schemes and can contribute to wider knowledge to help shape the policy on how far, and over what scale (temporal and spatial), this approach to management should be applied.
A summary of a detailed monitoring approach applied at a single site, by way of an example, is provided below:
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Vegetation survey (based on the NVC classification and survey methodology) over the whole site following inundation, repeated over increasingly long time periods.
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Establish permanent quadrats for more detailed species (plants and animals) monitoring and consider how surrounding local change might be determined (for background levels of change).
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Establish frequency of site topographic survey and (within the area and, if appropriate at a control location) permanent locations for measuring sediment accretion and erosion.
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Establish ‘nested’ quadrats for more detailed assessment of vegetation change (after Hodgson et al., 1994).
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As necessary, investigate the factors affecting saltmarsh stability (e.g. pollution, tidal scour, grazing by herbivores).
In some situations a detailed NVC survey monitoring approach may not be required. Important trends can still be deduced from a more targeted, specific approach. For example, monitoring carried out on Trimley Marshes Managed Realignment site (Posford Haskoning, 2004) employs the following approach:
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Vegetation survey carried out biannually for five years.
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General walkover survey to record all species.
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Permanent quadrats (number depends on size of site) for more detailed species monitoring using Domin scores.
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Estimate of the areal extent of saltmarsh (spot measurements using either tape measure or GPS; where GIS is used to estimate coverage increase/decrease).
It should be noted that whatever monitoring regime is adopted for a scheme, it should be proportional to the size of the scheme and/or the impacts of it. This can be determined at a number of stages in the process but would certainly form part of an Environmental Impact Assessment for planning approval or could form part of a Strategic Environmental Assessment of a plan (for example a flood management strategy or Shoreline Management Plan). Each site (and project) is likely to have a different range of sensitivities that will determine the parameters to be monitored and the level of detail required.
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