UK salt marshes in retreat: anthropogenic versus natural origin: Group J Salt marshes: • Range in size from a few mm’s to an entire estuary • Found on the fringes of estuaries, lagoons and bays • Generally found where sediment deposits are sheltered from wave action • Also above the levels of the high neap tide • Formed on areas of mudflats where vegetation eventually takes hold Salt marshes have important functions both as natural habitats and coastal defence. • Form important roosting areas and nesting sites for birds, including species of international importance • Act as natural buffers in terms of sea defence, absorbing the impact of wave energy and reducing the probability of breach of defences The principle natural threat to saltmarshes is erosion, which is caused by a number of factors, • Migration of estuarine channels • Changes in coastal nearshore profile • Reduction in sediment supply • Increase in sea level • Increase in storm wave activity • Damage to the vegetation, caused by disease or environmental stress The erosion of saltmarshes takes numerous forms, including • Landward retreat of the marsh edge as a cliff, or a seaward dipping ramp • Internal dissecation of the marsh by widening, deepening and headward extension of the tidal creeks • Large scale death and removal of vegetation, lowering parts of the marsh surface Major salt marshes are found in southeast, northwest, eastern and southern England and in southeast and mid west Wales. Salt marsh erosion is not occurring in all of these areas. For example the Dyfi Estuary in mid west Wales, is undergoing substantial salt marsh accretion [1]. Most saltmarshes in northwest England have shown stability and lateral accretion in the past two decades. Net erosion over the same period has occurred on the southeast and southern English coasts, the Severn Estuary and along the shores of the Bristol Channel [2]. The retreat of saltmarshes has numerous causes, which can be divided into different categories. Biological causes • Coastal wetland such as saltmarshes and mangrove forests are likely to be heavily impacted by sea level rise if they are inundated with sea water and can’t migrate inland sufficiently to compensate • Temperature increases may disrupt peat accumulation: more peat will be broken down under higher temperatures as microbial activity increases (Stevenson et al. 1986). This may however be offset by increased production of root and other plant parts (and subsequently, peat) from increased CO2. The Humber Estuary: An example of destabilising biological action • The erosion threshold is reduced as algal benthic mats become sodden and release sediment that acts as a binding force. Macoma Balthica (clam) breaks up sediment leading to reduced accretion, leading to increased erosion. This was seen in July 1996-97 when reduced density of Macoma on the tidal limits led to increased accretion. Geological Causes The present rate of mean sea level rise is estimated at 3.8mm/year (conservative) to 20mm/year (high). This is due to • Isostatically related upward movement of relative sea level in UK due to positioning on the forebulge of the former Devonian ice mass to the north [2]. This is shown in the Wash area of the eastern English coast, which has a crustal subsidence rate of 0.91m/year [3]. • Warming of the atmosphere occurring naturally due to changes in solar radiation - being further increased by ‘Greenhouse Effect’. Increased global temperature leads to melting of polar ice caps, which leads to increased mean sea levels. It appears that the nature of the tides plays a very significant role in determining whether marshes in any given area are eroding or accreting. In many areas where the salt marshes are eroding (Essex and north Kent), there is an asymmetry in the shallow water tidal curves so that the flood is longer than the ebb. This leads to a higher current velocity on the ebb which means that there is a net seaward transfer of sediment. Natural Retreat The concept of natural retreat as a coastal management method has many advantages, and can work to minimise further detrimental anthropogenic effects. Case Studies Some example of the success of natural retreat are given. Bridge Creek, Dengie Peninsula, southeast Essex [4] The rate of sea level rise is approximately 3mm/year, but the salt marsh vegetation has shown no signs of stress due to increased submergence indicating continued accretion of the marsh surface. It has been shown from aerial photos that the marsh front has retreated over 40m since 1955 due to erosion. The area shows an uneven sedimentation rate, with erosion being dominant at the seaward margin of the marsh and the marsh surface being dominated by deposition, with deposition levels being higher at the seaward edge of the marsh. Despite the uneven distribution all areas of the marsh appear to be receiving sufficient sediment to maintain the elevation of the marsh despite the continuing sea level rise. Fig1. Examples of net erosion/deposition measured at points along Bridge Creek [4] The findings at Bridge Creek can be used as template for the maintenance of salt marshes in areas subjected to relative sea level rise. Lymington and Keyhaven Saltmarshes, Hampshire In common with the rest of the Solent maritime region, this site’s geomorphological evolution since the late Pleistoene, from a coastal fluvial valley to a coastal embayment, is continuing. Most of the saltmarsh lies within the Hurst spit and Lymington estuary. This shelter and reduced wave energy environment together with the shelter from the Isle of Wight is primarily responsible for its formation and existence. Acceleration of intertidal zone narrowing rates (as the edges of the marsh retreat), coupled with salt marsh losses over large areas as a result of spartina anglica decline is of significant local concern. Reasons for the saltmarshes retreating are as follows, • The tidal regime comprises and asymmetrical tidal curve with flood tide duration being longer than the ebb tide duration. This results in greater ebb current speeds, (approximately 1.1 to 1.5 times greater than the flood tide) • Wind/wave climate is controlled predominately by SW winds and waves of local origin. Extreme wave conditions are possible as a result of both easterly winds and a combination of strong winter winds with strong ebb tides • Sediment characteristics suggest relatively low suspended sediment concentrations, but high concentrations in the water along the front edge of the marsh • Relative sea level rise is accelerating and is reflected in increasingly frequent storm surge events • Saltmarsh vegetation dominates the intertidal area at a height of 2.5 to 2.9m (above chart datum). Mean water depth over the salt marsh is 0.2 - 0.5m during spring tides, therefore the vegetation serves to decrease current velocity and wave energy. Fig2. Location of Lymington and Keyhaven saltmarshes Severn Estuary, Bristol Channel [2] The regression or retreat of a marine coastal environment depends on the balance between the supply of sediment and the rate of change of relative sea level. It has been established that the Severn Estuary system has recently reached maximum capacity and has been retreating inland. Therefore its pattern of retreat can be explained by the continuing upward trend of relative sea level, and is only a part of the continuing cycle of deposition and erosion is it in. Fig3. Model for the evolution and retreat of the Severn Estuary over postglacial time under the influence of a rising relative sea level [2] Benacre Broad, Suffolk [5] • Saline lagoon with associated reedbeds occupying a shallow glacial outwash valley • Broad is separated from the sea by a low shingle bar, reduced in width and height as the coastline has rapidly receded in recent years, leading to more frequent breaching • Broad now reduced in area and becoming fully saline rather than brackish, causing extensive die-back of reedbeds, and adverse effects on lagoonal invertebrates Since repair of the bar was deemed too expensive, a low cost retreat scheme was created to allow continuation of the naturally occurring retreat, with some preventative measure to ensure the continuing presence of the lagoon invertebrates for which the site was noted. Two low earth bunds were constructed to limit the frequency of breaches of the shingle bar and so preserve conditions of comparatively low salinity, with the seaward bun being lower and providing conditions intermediate between the open lagoon and the reedbeds between the two structures. Fig4. Example of managed retreat for flood defence [5] Managed retreat is described as being ‘a policy of stepping back from the presents show defence location and allowing the shore to develop the wider profiles which it would adopt under a natural regime’, [5]. Managed retreat schemes are not a ‘ do nothing’ option. The proposed retreat must be carefully planned, modelled and predicted using knowledge of estuarine history, hydrology and sediment behaviour and feedback from successful natural retreat examples, whilst taking into consideration the specifications of the planned site such as sedimentation rates, species present and local tidal processes. The effects of the retreat on the soil chemistry, tidal regime and wave climate need to be considered before the retreat can be implemented. Natural and Managed retreat schemes both have examples of successes and failures, they both have merits and flaws and all aspects of their implementation should be investigated before they are employed. References [1] Shi Z (1993) Recent saltmarsh accretion and sea level fluctuations in the Dyfi Estuary, central Cardigan Bay, Wales, UK. Geo-Marine Letters, 13: 182-188 [2] Allen JRL (1990) The Severn Estuary in southwest Britain: its retreat under marine transgression, and fine-sediment regime. Sedimentary Geology, 66: 13-28 [3] Tooley MJ, Jelgersma S (1992) Impacts of Sea Level rise on European Coastlines. pp 83, 76 [4] Reed DJ (1988) Sediment dynamics and deposition in a Retreating Coastal Salt Marsh. Estuarine, Coastal and Shelf Science, 26: 67-79 [5] Pethwick J, Burd F (1999) Coastal defence and the environment: a guide to good practice. London: MAFF [6] French PW (1999) Managed retreat: a natural analogue from the Medway estuary, UK. Ocean and Coastal Management, 42: 49-62 [7] Nicholls RJ, Klein RJT (1999) Adaptation Frameworks for sea-level rise impacts www References 1 http://www.ipieca.org/publications/oilspillsummaries/saltmarshes.html. 'Saltmarshes' - a summary of the IPIECA report 2 http://www.solentforum.hants.org.uk/othercoast/western_solent_smp.htm #saltmarsh. Western Solent Shoreline Management Plan 3 http://www.whoi.edu/seagrant/education/focalpoints/shoreline.html. WHOI Sea grant education and outreach. 4 http://chomsky.arts.adelaide.edu.au/Geogenvst/adams/abcostal.htm Coastal Environments Adelaide university The Debate Introduction Hannah Uttley Hello, my name is Hannah Uttley and we are group J. Our title for discussion is UK Saltmarshes in retreat and we are arguing the side of the natural origin. Coastal salt marshes are environments high in the intertidal zone, which are covered by halophytic vegetation. The lower limit of pioneer marsh vegetation corresponds approximately with the level of mean high water of neap tides, while the potential upper limit is slightly above the level of mean high water spring tides. In many areas algal-covered mud or sand flats occur to seaward of the salt marsh zone, while the landward margin is formed by a transition zone to brackish and freshwater communities, or by an artificial embankment. According to A. Pye and his work in 1992, active salt marshes play an important role both as natural habitats and as coastal defences. In ecological terms, marshes are particularly important as roosting areas and nesting sites for birds, including a number of species of international importance. In sea defence terms, Brampton 1992, states that salt marshes which are located in front of earth embankments act as a natural buffer which absorbs the impact of wave energy, thereby reducing the probability of overtopping and breaching. During storms, erosion of the saltmarsh edge serves to resupply the fronting mudflat with sediment, thereby reducing the rate of lowering of the intertidal profile and encouraging the establishment of a new equilibrium with the indicant waves (Pethick, 1992a, 1992b). The principal natural threat to saltmarshes is erosion, which may be induced by a number of factors including the migration of estuarine channels, changes in coastal near shore profile, a reduction in sediment supply, an increase in sea level, or an increase in storm wave activity. Coastal wetland such as saltmarshes and mangrove forests are likely to be heavily impacted by sea level rise if they are inundated with sea water and cannot migrate sufficiently inland to compensate. The will be possible destabilisation of biological action. For example in the Humber estuary the erosion threshold is reduced as algal benthic mats become sodden and release sediment that acts as a binding force. Balthica breaks up sediment leading to reduced accretion leading to increased erosion. This was seen in July of 1996-97 when reduced density of Macoma on the tidal limits lead to increased accretion. The erosion status of saltmarshes around the coast of England has indicated that the majority of erosion in salt marshes has generally been confined to areas where there have been recent shifts in channel position). A high proportion of marshes in Suffolk, Essex and north Kent, and on the south coast in West Sussex, Hampshire and east Dorset, have suffered net erosion in the last 20 years (e.g. Gray & Pearson, 1984). Lateral accretion (e.g. at Sheliness, Isle of Sheppey), has been the exception, rather than the rule in these areas. In the southwest most of the small estuarine Marshes in Cornwall and Devon have remained stable, but active marshes along the shores of the Bristol Channel and Severn estuary have suffered widespread erosion of the marsh edge. It appears that the nature of tides plays a very significant role in determining whether marshes in any given area are eroding. In many areas where the salt marshes are eroding such as Essex, of N, Kent for example, there is an asymmetry in the shallow water tidal curves so that the flood is longer than the neap. This leads to a higher velocity on the ebbs, which therefore leads to a net resource in the transfer of sediment. Neil Trickett Conclusion Alan Watson As we have already heard in the introduction, the principal natural threat to saltmarshes is erosion. However, as stated on the Woods Hole Sea Grant project website, without erosion, many of the Commonwealth's biologically productive bays such as estuaries, saltmarshes, and tidal flats would not exist. Therefore not only do natural processes erode the coastline they also seem to battle their own processes by providing a natural buffer to their own actions Currently a number of councils in the South are working alongside the Environment agency to formulate the Western Solent and Southampton Water Shoreline Management Plan, the SMP. Saltmarshes are an important part of the Shoreline management plan because they are abound in this local area. Recent studies have shown that the saltmarshes of the Western Solent and Southampton Water are eroding. Throughout the SMP it is recommended that the saltmarshes be monitored and, as far as possible, maintained, for both their nature conservation and coastal defence importance. An overall Saltmarsh management strategy to preserve these important natural landforms is also presented within the Shoreline Management Plan. The Solent forum is working alongside the Sea Level Rise workshop at the University of Portsmouth. One of the three main research priorities of the workshop is to look into the managed retreat of saltmarshes. This obviously indicates how important the participating councils and the environment agency believe saltmarshes to be as a means of defence against coastal erosion. Earlier in our presentation Neil briefly mentioned that the BBC News web page recently featured an article by Dr David Whitehouse. In this article Dr. Whitehouse addressed research by the Rutherford Appleton laboratory in Oxford, which provided evidence for an increasingly energetic Sun. The importance of this is that solar magnetism is closely linked with sunspot activity and the strength of sunlight reaching Earth. This increase could have produced warming in the global climate, a theory that is supported by Professor Eugene Parker of the laboratory for Astrophysics and Space Research at the University of Chicago. With the principal threats to saltmarshes including rising sea levels and the changes in coastal nearshore profiles then the increasingly energetic Sun perfectly illustrates just one example of the natural origin of retreating saltmarshes. Around 15,000 years ago, ice sheets started melting (as has happened hundreds of times over the past couple of million years), and sea level rose rapidly around the world. Sea levels 'plateaued' about 6,000-4,000 years ago, at perhaps a metre or two higher than today's sea level. What has happened since then is that the ocean basins have slowly dipped under the extra weight of the postglacial meltwater, this has dragged the sea level back down a bit. This 'mid-Holocene optimum' was also a slightly warmer world, global ice volume was slightly less, and given the warmer temperatures the ocean water was slightly thermally expanded. So the higher mid-Holocene sea level was the effect of a combination of natural events. These higher sea levels obviously destroyed many saltmarshes, however as we can see by the abundance of saltmarshes today, they have excellent powers of recovery. Therefore, unless our ancestors of 15,000 years had ago ran big cars and had large factories, which fossil records seem to suggest they didn’t, then we, Group J can accurately state that saltmarshes have been forced to retreat before by natural processes and it is the same natural processes that are forcing them to retreat again. Question 1 Ruth Pratt [Group H] A conservative estimate from Tooly and Jelgersma in 1992 stated that sea level is rising by 3.8 mm per year. This increase in sea level is due to an increased global temperature, which causes thermal expansion of sea water and the melting of polar ice sheets. Ice cores show that temperature patterns are closely related to the level of carbon dioxide in the air. Due to the burning of fossil fuels, the concentration of carbon dioxide in the atmosphere has augmented over the years, an increase mirrored by global temperature. Humans also release many other greenhouse gases, such as methane, CFCs, nitrous oxide and sulphur dioxide into the atmosphere. Is it your opinion that the anthropogenic inputs that contribute to global warming are outweighed by natural causes? Answer 1 Andrew Teuma The Wash, an area of about 70 miles along the East coast of England from Skegness to Hunstanton, has a crustal subsistence rate of 0.91m per year. This is due to the continual down tilting of S.E. Britain caused by the former Devonian ice sheet fore bulge, which once covered and forced down Northern Britain. This rapid, isostatically related sea level rise rate, along with the increase erosion rate due to rise in storm frequency has overtaken the marsh’s aggradation rate. This has lead to a reduction rate of salt marsh area of 4% per annum along the East Coast. Anthropogenic causes, including increased green house gas emission leading seawater thermal expansion and water displacement due to glacial rebound together with terrestrial water redistribution, have increased global sea levels. However it is near impossible to put a figure to the rate of increase due to human causes. The present maximum rate quoted is 20mm per year. Even this maximum rate of increase is relatively small when compared to the local sea level rise due the crustal subsistence on the East Coast. Some sources doubt that human activity has a significant influence on global sea level. Current research into global magnetic flux, which is directly related to sunspot activity and therefore global insulation, could prove that the increase in sea level rise rate in the last century could be related purely to sun spot activity. With these facts is it possible to claim anthropogenic factors dominate in causing salt marsh regression along the East Coast of England? Question 2 Phillip Parker [Group H] Saltmarsh retreat in the last 50 years in SE England has been 40% since 1973. Average loss over the whole of the UK has been 22% between 1978-88, equalling 6 500ha in 15 years (Pye 1995). In relation to Benacre Broad, Suffolk ‘Coastal Defence and environment: a guide to good practise F Burd and J Perthwick’ [Case study 5 of your essay], can you justify that a lack of coastal management to a rapidly receding coastline around Suffolk will have any beneficial consequence to the prevention and overall long-term conservation of the Broad, in respect to the receding shingle bar. As a result can you prove that without anthropogenic intervention the Broad is likely to survive in the long-term as a brackish water environment, causing the die back of reed beds and lagoonal invertebrates, thus reducing biodiversity of the area? Answer 2 Richard Stokes The case study of Benacre Broad is not an example of a lack of coastal management. A managed retreat scheme was put in place, based on experiences at other sites of successful natural retreat in the Broads area. The initial cause of the managed retreat scheme mentioned was cost – it was deemed too expensive to provide hard defences to that area of coastline, and so the opening of a channel in the existing deteriorating defences was made, to reopen existing creeks and allow the gradual Question 3 Ruth Pratt [Group H] The present position of many of the coastal defences on the southeast coast of Britain are not sustainable due to sea level rise. In areas of low urban and industrialisation, an economically viable option is that of managed retreat. Managed retreat is basically abandoning the area and letting natural processes occur. This scheme will cause the loss of many habitats, which has wide economic and environmental implications. If the sea level continues to rise, do you think managed retreat is the best option, as erosion will continue until it reaches some solid, non-erodable feature? Answer 3 Vicky Stedall Managed retreat is currently the most natural process being used as a coastal defence system. By creating saltmarshes we provide a situation that erodes slowly as it is in virtual equilibrium with the sea. Wave action is also reduced due to the natural slope of the marsh. Currently sea walls around the UK are expensive to maintain and only divert the erosion to another area. They may be worthwhile for saving current human habitats from erosion but only those in immediate danger require such drastic protection. If we use saltmarshes to protect our coastlines we benefit in a number of ways. 1. They are cheaper to install and they maintain themselves. 2. They are attractive. 3. They provide good natural reserves for wildlife The general worry is that allowing the land to be converted into salt marshes forces the country to lose agricultural land. In reality a large number of agricultural land is laid to rest each year because the country produces too much farming produce. It is clear that some of this land could be used for managed retreat providing farm owners with compensation. In February 2000, the government brought a 750-acre farm called Abbots Hill on the Essex coastline. The plan is to destroy the 500-year-old seawall, which is in great need of repair, allowing over 200 acres of the farm to become saltmarsh. They believe that this will slow the rate of erosion while creating a good wildlife habitat. So in answer to your question, in my opinion Managed retreat is the best option currently available to us. Admittedly without a sea wall erosion will continue to occur possibly until it hits a hard substrate, however this would have occurred naturally and with the use of managed retreat we can slow this process dramatically. Finally, I believe that it is surely better to slow down erosion than to prevent it in some areas only for it to damage others areas more. OC2.07 Group J 8 UK salt marshes in retreat: anthropogenic versus natural origin Page 13 of
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