Belt transect

From Wikipedia, the free encyclopedia

Belt transects are used in biology to investigate the distribution of organisms in relation to a certain area, such as the seashore or a meadow.[1] It records all the species found between two lines and how far they are for a certain place or area and how many of them there are. An interrupted belt transect records all the species found in quadrats (square frames) placed at certain intervals along a line.

The belt transect method is similar to the line transect method but gives information on abundance as well as presence, or absence of species.[2][3] It may be considered as a widening of the line transect to form a continuous belt, or series of quadrats.

In this method, the transect line is laid out across the area to be surveyed and a quadrat is placed on the first marked point on the line. These marked points should be a set amount of space apart. The plants and/or animals inside the quadrat are then identified and their abundance estimated. Animals can be counted within the quadrat, or collected, while it is usual to estimate the percentage cover of plant species. Cover is the area of the quadrat occupied by the above-ground parts of a species when viewed from above. The canopies of the plants inside the quadrat will often overlap each other, so the total percentage cover of plants in a single quadrat will frequently add up to more than 100%.

Quadrats are sampled all the way down the transect line, at each marked point on the line, or at some other predetermined interval (or even randomly) if time is short. It is important that the same person should do the estimations of cover in each quadrat, because the estimation is likely to vary from person to person. If different people estimate percentage cover in different quadrats, then an element of personal variation is introduced which will lead to less accurate results. Sampling should always be as least destructive as possible and trampling the surrounding area should be avoided when carrying out a survey. Not only is there a risk of damaging the area, but there is also a risk of reducing the population or percentage cover of the species being surveyed.

References

  1. ↑ Hill, David Arnold; Matthew Fasham, Graham Tucker, Michael Shewry and Philip Shaw (2005). Handbook of biodiversity methods: survey, evaluation and monitoring. Cambridge, UK: Cambridge University Press. pp. 219–222. ISBN 0-521-82368-4. OCLC 61439712. 
  2. ↑ Ecological Sampling Methods
  3. ↑ Urban Sampling Methods - Barcelona Field Study Center
This article is issued from Wikipedia. The text is available under the Creative Commons Attribution/Share Alike; additional terms may apply for the media files.