During this study trip we also recorded data concerning various aspects that might relate to tourist impact on the dune ecosystem and the Bay.

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SECTION 2

Methodology

During this study trip we also recorded data concerning various aspects that might relate to tourist impact on the dune ecosystem and the Bay. These data were all primary and included those aspects listed below. Secondary data was obtained by researching Internet sites.  

To achieve the Primary Data 

The group carried out a number of different surveys

  1. In assessing tourist impact on the dunes the group chose at random eight different sites along footpaths. At these different sites the group measured the width of the footpath by laying down a meter rule or measuring tape across the path. Subsequent to these measurements, the group then also estimated the amount of vegetation cover within a 5m radius of that point on the path and similarly counted the number of pieces of litter within the same radius. Finally a visual estimate of the distance from the beach was made.

  1. In assessing the impact of tourism within the Bay, the group moved to the entrance of the dunes and its car park to carry out a car park survey, simply by counting how many cars were in the car park.

  1. A traffic survey was also planned, but on the day little traffic was present and so this survey was not conducted.

  1. The group also took time to take several photographs of tourist impact on the village. (unfortunately I have none to present)

To achieve the Secondary Data

The objective of the Internet research was to find supporting data on the extent and effects of tourism in the area. Sites visited included:

 

Survey Results

The results obtained during the site surveys are given in Tables 2:1 and 2:2 below.

Footpath Survey Results Table 2:1                                        

Car Park Survey Results Table 2:2                                                  

Analysis of Results

The results above have been plotted on a series of graphs, Figures2:1 to2:4, in order to provide and assess various elements of data and any relationships that can be established.

  • Footpath width/Location - (Figure 2:1). Whilst there is no definite relationship, the observations, apart from site five, do suggest that the closer to the beach the wider the footpath. A minimum footpath width of two meters on average might be present.

  • Footpath width/Vegetation cover - (Figure 2:2). Up to a width of four meters there is scatter in the results, vegetation cover varies between sixty and one hundred percent After attaining a footpath width of six meters the vegetation cover appears to be much lower, around twenty to forty percent.
  • Footpath width/Litter present - (Figure 2:3).  Half of the footpath sites had no pieces of litter.  Of the sites that had litter, three sites had two pieces and one had five pieces. There was not much litter at the sites.
  • Litter present/Location - Table 2:1 above clearly shows there is no relationship of the amount of litter with distance from the beach. Similarly there is no apparent relationship with the number of pieces of litter and footpath width. Graphs have not been plotted.

        


Spearman’s Rank test

A Spearman’s Rank test has been compiled to see whether there is a clearer relationship between the widths of the footpath, and the amount of trampled vegetation, which were observed.

This calculation has been based upon a ranking assuming that the wider the path the less likely is vegetation in the vicinity to be trampled i.e. people would stick to the wider footpath. Looking at this final number we can see that there is a weak negative relationship, because the number is below 0 and not close to -1. Therefore there is a poor relationship but it is actually the opposite of what was anticipated. The relationship shows that more trampling occurs alongside the wider path. This result is consistent with my general observation from Graph (Fig 2:2).

It is difficult to make conclusions, as it is possible that narrow footpaths might well be extended to greater width as time goes on and more people use the path. However it is also possible to suggest that as the footpath becomes wider more people will congregate or walk side by side thereby increasing the loss of vegetation and in turn increasing the width. The graph (Fig 2:4) seemed to indicate that this latter situation might be emphasized when the footpath width exceeded four meters. More data would be needed to confirm or disprove this latter and all observation.

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Effects of Tourism

Effects on the dunes ecosystem by walkers and trampling

Oxwich Bay has a diversity of vegetation and flora such as marram grass, bracken, birch trees, sea spurge etc. The area is very popular with ramblers/walkers and there is a walk that cuts through Oxwich Bay via reserve.

Human beings are a problem because they trample on the vegetation, which then dies allowing the sand to blow away, causing a blow- out.  These effects can be managed by keeping the tourists off the dunes. Fences can be used to isolate areas or footpaths used to keep people in ...

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