testing-for-distribution-and-abundance

Testing for distribution & abundance

• The distribution of a species describes how it is spread throughout the ecosystem

• The abundance of a species is the number of individuals of that species

• The distribution and abundance of a species in an area can be assessed using different practical methods:

  • Frame quadrats

  • Line and belt transects

  • Mark-release-recapture

Frame quadrats

• Some ecosystems are very complex with large numbers of different species of different sizes

• For the sake of logistics, sampling is often used to estimate the distribution and abundance of species

• When carrying out sampling, square frames called quadrats can be used to mark off the area being sampled

• Quadrats of different sizes can be used depending on what is being measured and what is most suitable in the space the samples are being made in

  • These are usually made of wood or metal and measure 25 cm × 25 cm, 50 cm × 50 cm or 1 m × 1 m

• Quadrats must be laid randomly in the area to avoid sampling bias

  • This random sampling can be done by converting the sampling area into a grid format and labelling each square on the grid with a number

  • Then a random number generator is used to pick the sample points

• Once the quadrat has been laid on the chosen sample point the abundance of all the different species present can be recorded

Results from quadrats

• The results from the quadrats can be used to calculate the predicted frequency and density of a species within an area

• Species frequency is the probability that the species will be found within any quadrat in the sample area

  • The number of quadrats that the species was present in is divided by the total number of quadrats and then multiplied by 100

  • For example, if bluebells were found in 18 out of 50 quadrats the species frequency would be (18÷50) x 100 = 36%

• Species density indicates how many individuals of that species there are per unit area

  • The number of individuals counted across all quadrats is divided by the total area of all the quadrats

  • For example, if 107 bluebells were found across 50 quadrats that are 1m² each the species density would be 107/50 = 2.14 individuals per m²

• It can sometimes be difficult to count individual plants or organisms. When this is the case percentage cover of the species within the quadrat can be estimated instead

  • The quadrat is divided into 100 smaller squares

  • The number of squares the species is found in is equivalent to its percentage cover in that quadrat

  • For example, if grass is found in 89 out of 100 squares in the quadrat then it has a percentage cover of 89%

Line and belt transects

• Throughout some areas, there can be changes in the physical conditions

  • For example, there may be changes in altitude, soil pH or light intensity

• When investigating the species distribution in these kinds of areas, systematic sampling is more appropriate

• Methods using transects can help show how species distribution changes with the different physical conditions in the area

  • A transect is a line represented by a measuring tape, along which sample are taken

• For a line transect:

  • Lay out a measuring tape in a straight line across the sample area

  • At equal distances along the tape record the identity of the organisms that touch the line. For example, every 2m

  • This produces qualitative data

• For a belt transect:

  • Place quadrats at regular intervals along the tape and record the abundance of each species within each quadrat

  • This produces quantitative data

Mark-release-recapture

• The methods above are only useful for stationary organisms

• Different methods are required for estimating the number of individuals in a population of mobile animals

• The mark-release-recapture method is used in conjunction with the Lincoln Index

• For a single species in the area:

  • The first large sample is taken. As many individuals as possible are captured / collected, counted and marked in a way that won’t affect their survival

  • They are returned to their habitat and allowed to mix randomly with the rest of the population

  • When a sufficient amount of time has passed another large sample is captured

  • The numbers of marked and unmarked individuals within the sample are counted

  • The proportion of marked to unmarked individuals is used to calculate an estimate of the population size

  • The formula for the calculation is:

• Where:

  • N = population estimate

  • n₁ = number of marked individuals released

  • n₂ = number of individuals in the second sample (marked and unmarked)

  • m₂ = number of marked individuals in the second sample