biodiversity Flashcards
biodiversity and how it is assessed
Biodiversity can be thought of as a study of all the variation that exists within and between all forms of life
Biodiversity looks at the range and variety of genes, species and habitats within a particular region
It can be assessed at three different levels:
-The number and range of different ecosystems and habitats
-The number of species and their relative abundance
-The genetic variation within each species
Biodiversity is very important for the resilience of ecosystems, in that it allows them to resist changes in the environment
ecosystem or habitat diversity
This is the range of different ecosystems or habitats within a particular area or region
If there is a large number of different habitats within an area, that area is likely to have high biodiversity
-A good example of this is a coral reef. They are very complex with lots of microhabitats and niches to be exploited
If there are only one or two different habitats within an area, that area is likely to have low biodiversity
-Large sandy deserts typically have very low biodiversity as the conditions are basically the same throughout the whole area
species richness
An ecosystem such as a tropical rainforest that has a very high number of different species would be described as being species-rich
-Species richness is the number of species within an ecosystem
Species richness is a measure of the number of different species within a given area
An area with a greater number of species will have a greater species richness
For example, a tropical rain forest has a very high number of different species so it would be described as being a species-rich area
However, species richness can be a misleading indicator of diversity as it does not take into account the number of individuals of each species
species evenness
Species diversity includes the number of different species in an ecosystem, and also the evenness of abundance across the different species present (known as species evenness)
The greater the number of species in an ecosystem, and the more evenly distributed the number of individuals from each species, the greater the species diversity
For example, an ecosystem can have a large number of different species but some species may be very rare (may only have a few individuals) in that particular ecosystem.
As a result, the ecosystem does not necessarily have high species diversity
stability in ecosystems
Ecosystems with high species diversity are usually more stable than those with lower species diversity as they are more resilient to environmental changes
For example in the Pine forests of Florida, the ecosystem is dominated by one or two tree species. If a pathogen comes along that targets one of the two dominant species of trees, then the whole population could be wiped out and the ecosystem it is a part of could collapse
genetic diversity
The genetic diversity within a species is the diversity of alleles and genes in the genome of species
Although individuals of the same species will have the same genes they will not necessarily have the same alleles for each gene
how is genetic diversity measured
Genetic diversity is measured by working out the proportion of genes that have more than one form (allele) and how many possible alleles each gene has
genetic differences within the same species
There can be genetic differences or diversity between populations of the same species
These differences may arise because the two populations occupy slightly different ranges in their habitat and so are subject to slightly different selection pressures that affect the allele frequencies in their populations
genetic diversity within a single population
Genetic diversity can also be observed within a single population
Genetic diversity in a species is important as it can help the population adapt to, and survive, changes in the environment
The changes could be in biotic factors such as new predators, pathogens and competition with other species
Or the changes could be through abiotic factors like temperature, humidity and rainfall
limitations of genetic diversity
Genetic diversity is limited in populations that are very small or isolated
Inbreeding in small, isolated populations leads to a high proportion of individuals being homozygous (e.g. AA to aa) for many genes, resulting in lower genetic diversity
This can mean that genetic diseases caused by recessive alleles can become more common in these populations
sampling to determine biodiversity
Measuring the different levels of biodiversity within an ecosystem can be challenging
Finding out which species live in an ecosystem and the size of the populations requires the identification and cataloguing of all organisms present to build a species list
This is possible for areas that are very small or where the species are very large like trees
However, for larger and more complex ecosystems like rainforests, it is simply impossible to find, identify and count every organism that exists there
When this is the case, different samples of the area can be taken and used to make an estimate for the total species numbers in the area
sampling
Sampling is a method of investigating the abundance and distribution of species and populations
There are two different types of sampling:
Random
Non-random
random sampling
In random sampling, the positions of the sampling points are completely random or due to chance
This method is beneficial because it means there will be no bias by the person that is carrying out the sampling that may affect the results
When a sampling area is reasonably uniform or has no clear pattern to the way the species are distributed then random sampling is the best choice
non random sampling
In non-random sampling the positions of the sampling points are chosen by the person carrying out the sampling
There is a possibility that the person choosing could show bias towards or against certain areas
Individuals may deliberately place the quadrats in areas with the least species as these will be easier and quicker to count
This is unrepresentative of the whole area
what is random sampling used to estimate
Some ecosystems are very complex with large numbers of different species of different sizes
For the sake of logistics, random sampling is often used to estimate the distribution and abundance of species
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
quadrants
When carrying out sampling, square frames called quadrats can be used to mark off the area being sampled
Quadrats are square frames made of wood or wire
They can be a variety of sizes eg. 0.25m2 or 1m2
They are placed on the ground and the organisms within them are recorded
They can be used to measure the distribution and abundance of plants or slow-moving animals
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
sampling bias with quadrants
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 or percentage cover of all the different species present can be recorded
other techniques/ equipment that can be used
Sweeping nets: these are large, strong nets with a fine material (very small holes) that are used to catch flying insects and insects that live in long grass by sweeping the net back and forth through the grass
Pitfall traps: these are cans or jars that are buried in the ground that are used to catch ground-dwelling (often nocturnal) insects and other invertebrates as they fall into the trap
Pooters: these are small plastic or glass containers with two tubes sticking out that are used to suck up small insects and other small invertebrates. The first tube is placed over the insect and the second tube is used by the scientist to create suction
Tullgren funnel: these are funnels with a light bulb above and a container below that are used to collect invertebrates that live in leaf litter or soil. The leaf litter or soil is placed in the funnel and the light and heat forces the invertebrates to move down until they drop into the container
Kick-sampling: this technique is used to catch freshwater invertebrates living in streams or rivers. A net in placed on the stream-bed so that the water is flowing into it and the stream-bed just above the net is churned up by the scientist (using their foot) for a set period of time. The invertebrates are carried by the stream into the net
non random sampling types
Random sampling is not always possible or may take an impractically long time. In these cases, non-random sampling may be more suitable
There are three main types of non-random sampling:
Opportunistic sampling
Stratified sampling
Systematic sampling
opportunistic sampling
Opportunistic sampling involves picking and choosing sampling locations based on various non-random factors. For example, students on a field trip may be told they can only collect samples from locations that are nearby, easy to reach, and safe
stratified sampling
Stratified sampling involves matching the number of sampling locations in a particular habitat with the relative proportion of area that habitat covers in the whole area being studied.
For example, if 10% of a dense woodland being sampled is actually made up of grassy clearings, then 90% of the sample locations should be in the woodland habitat and 10% in the grass habitat
systematic sampling
Systematic sampling is used when there is a clear change in the physical conditions across the area being studied
For example, there may be changes in altitude, soil pH or light intensity
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
line transect
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
belt transect
For a belt transect:
-Place quadrats at regular intervals along the tape and record the abundance or percentage cover of each species within each quadrat
-This produces quantitative data
method for choosing sample sites
Mark up a grid on a map or a to-scale drawing of the area being studied and label the grid with coordinates
It is important that the area is big enough to get a representative estimate for the specific habitat/ecosystem
Use a random number generator to choose a set of coordinates
This is done to avoid sampling bias which could lead to over or under-estimation (either subconsciously choosing areas that are easier to access or that look like they contain individuals)
getting measurements from quadrants
The contents within quadrats can be counted using different measurements
Population density, percentage cover and species frequency are all different ways of counting and recording the number of different species and individuals present within a quadrat
calculating population density
Place a quadrat at the generated coordinate
Count the number of individuals in each quadrat
Use a running mean to determine the number of quadrats required to get a representative sample:
Calculate the mean number of individuals per quadrat for the first two quadrats found, then the mean of the first three, then the mean of the first four and repeat until there is no further significant change in the mean
calculating the estimated population size
To calculate the estimated population size for the whole area or habitat, divide the whole area by the area of one quadrant, then multiply this value by the mean number of individuals per quadrat
calculating the abundance of a species using percentage cover
Usually used for plants
Place a grid quadrat (a square frame split into 100 smaller squares) at this coordinate
Each square of a grid quadrat is equivalent to 1% cover
Count the number of squares in each quadrat within which the species occupies over half the square
If 30 squares contain the species, the percentage cover is 30%
This method is subjective and therefore the same person should make the estimate for all samples to control this variable
calculating the abundance of a species using frequency
Place a frame quadrat at multiple coordinates generated
Count the number of quadrats that contain the species
If 3 out of 10 quadrats contain the species the frequency is 30%
species destiny
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
percentage cover
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%
precise frequency
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%
limitations of using quadrats
Quadrats and transects can only be used for sessile and immobile species (eg. plants and slow-moving animals)
Some species can be counted to find their abundance but others that are very small or in high numbers require abundance to be calculated using percentage cover or frequency techniques
The frequency technique shows how common a species is but it does not give information on the estimated number of individuals or the size of the population
distribution of species
Percentage cover and frequency, when used together, give a good picture of the distribution of a species
If a species had a high mean percentage cover but a low frequency it would suggest the species lives in groups in preferred areas of the habitat
This can be used to answer questions such as: does the species prefer light or dark and wet or dry areas etc.