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Pages (PDF 3 MB) - Otter Specialist Group

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IUCN <strong>Otter</strong> Spec. <strong>Group</strong> Bull. 26(2) 2009<br />

Surveying season<br />

Consideration of season is important in rivers with intermittent water regimes.<br />

As the effect of water level and rain can mask the influence of other variables in otter<br />

sprainting activity, it is important to survey in months that minimize these effects. In<br />

Mediterranean countries that may principally be in the summer and autumn. When<br />

performing single surveys these should not be implemented during the days after<br />

heavy rain or high water level (according to Chanin, 2003, there should be a period of<br />

at least five days without rain before surveying). Also, when dealing with sprainting,<br />

one should take into account seasonal variations in otter sprainting behaviour, which<br />

maybe up to tenfold between seasons (e.g. Kruuk, 2006). So, annual monitoring<br />

schemes should be conducted each year in the same season to diminish otter<br />

sprainting behavioural differences.<br />

Survey length and width<br />

Similarly to river surveys, 600 m transects are a reasonable compromise for<br />

otter regular monitoring, either only to detect otter presence/absence or for more in<br />

depth comparative studies. The survey should be concentrated in the first five metres<br />

from shore of the entire width of the bank flooding area. Nevertheless, for monitoring<br />

otter presence/absence in dams in dry regions, 200m transects are adequate as this<br />

minimises survey time and thus the number of sites to be surveyed per day. However,<br />

this survey length should only be used when more than one site is to be surveyed in<br />

the same reservoir. Alternatively, surveys may be planned to begin with 200m<br />

transects, moving up to a maximum of 600m transects in case no otter signs are<br />

found. Similarly to river surveys, this has the effect of avoiding false negatives.<br />

Number of survey sites<br />

To make it possible to say that otters are present in all of a reservoir, a series of<br />

regularly spaced survey sites, approximately 5 km apart, should be established. This<br />

degree of surveying in depth would give an insight into the otter’s specific habitat use,<br />

such as whether they are present at the point where tributaries run into the reservoir,<br />

or if they use the overall perimeter of the reservoir.<br />

Location of the survey sites<br />

When performing presence/absence surveys, and if proving otter presence in the<br />

entire reservoir is unimportant, the most crucial aspect is choosing the right sites for<br />

surveying. Suitable sites are usually selected by ease of access. Our data suggest that<br />

surveys located in the main inflow of the tributaries into the reservoir (Pedroso,<br />

unpublished data; Sales-Luís et al., 2007) are ideal places to survey. However, it must<br />

be considered that this is not necessarily representative of otter use in the totality of<br />

the reservoir perimeter, particularly when dealing with large reservoirs. To improve<br />

the probability of finding otter signs, surveys should be located on gently sloping<br />

banks, with many suitable potential marking places, near shallow water and beside or<br />

under any existing bridge. The dam wall itself can also be a good place to consider<br />

surveying, providing the wall is not steep and is a short distance from the downstream<br />

river, allowing otters to cross (Figure 4). Furthermore, if surveys are replicated<br />

seasonally, special attention must be given to traditional otter marking places in order<br />

to promote efficiency in detecting spraints.<br />

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