Quadrat Method
The
quadrat method orginated with Frederick Edward Clements
(1874-1945) (Pound & Clements, 1898). A
quadrat is a
frame of any shape that can be placed over vegetation so that
cover can be estimated, plant counted or species listed. Quadrats
are used to define sample areas within the study area and are
usually made from strips of wood,
metal or rigid plastic which are tied, glued, welded or bolted
together to form the quarat. It can be helpful to use bolts so
that the quadrat can be dismantled for storage or transport. For
aquatic macrophytes a wood or plastic frame will float and can be
used to sample floating or emergent vegetation on the water
surface. For large quadrats over 4 sq. m folding rulers or string
can be used.
Three factors need to be considered in relation to the use of
quadrats.
- Distribution of plants
- Shape and size of the quadrat
- Number of observations needed to obtain an adequate estimate
of density
Shape
Quadrat are not natural sampling units, and one must always
decide what size and shape of quadrat to use. The spatial pattern
obtained, and the resulting index of dispersion, depends on
quadrat size and shape. The term "Quadrat" strictly means a four
sided figure but in practice this term is used to mean any
sampling unit, whether
square,
rectangular, circular, hexagonal or even irregular in outline.
Although a square is often used, the quadrat shape is unimportant
as long as you know its area.
There are two conflicting problems regarding shape
1. Edge effect: Minimal in a circular quadrat and maximal in a
rectangular one. The ratio of length of edge to the area inside a
quadrat changes as
Edge effect is important because it leads to possible counting
error. A decision must be made every time an animal or plant is at
the edge. For plants or animals that are partly in and partly out
of the quadrat, you have to adopt some reasonable convention, e.g.
- Include plants that are more half in and exclude ones less
than half in
- Include all the edge plants on the north and east side and
exclude all those on the south and west side.
2. Long thin quadrats are better than circular or square ones
of the same area. The reason for this is habitat heterogeneity:
long quadrat cross more patches.
Size
Different vegetation types requires different quadrat sizes.
Vegetation with smaller plants, greater plant density or greater
species diversity need smaller quadrats. Increasing the size of
quadrat generally results in a lower variance in your
observations, but more work in getting them. Numerous studies have
evaluated quadrat size, and no consistent recommendation has been
made about the sizes to use. The sizes most often used are
- 0.01-0.25sq. m - bryophyte, lichens and algae
- 0.25-16 sq. m - grassland, tall herb, short shrub or aquatic
macrophyte
- 25-100 sq. m - tall shrub community
- 400-2500 sq. m - trees
A better approach, if time and resources are available, is to
determine for your particular study the optimal quadrat size and
shape. To do this, you first need to decide what you mean by
"Best" or "Optimal" quadrat size and shape. Best may be defined in
the following two ways:
- Statistically, as the quadrat size and shape giving the
highest statistical precision for a given total sample area
samples or for a given total amount of time or money.
- Ecologically, as the quadrat size and shape that are best to
answer the question being asked. If you are investigating
questions of ecological scale, the processes you are studying
will dictate quadrat size.
But in many cases the statistical criterion is the major
concern.
Number of Samples
The number of samples to take varies from community to
community. Because many species are not distributed randomly,
variation normally is quite high and the number of samples
required is quite large. Frequently the less common species
require a larger number of samples than do the more common
species.
Choosing Samples
Random Sample
A
random sample is one in which every member of the population
i.e., every individual animal or every point of ground has an
equal and independent probability of being included. Quadrats can
be located randomly by constructing two imaginary axes along the
edges of the area, dividing the axes into units, and picking pairs
of units from a
random number table or other ways. The easiest method of
random sampling is one you throw the quadrat with closed eyes,
from above the shoulder level in any direction on the study plot.
We can also usually achieve the same effect more simply by
using the random numbers generated by a calculator or a
computer, or included in books of statistical tables. A random
number table consists of a long series of digits that has been
checked for non-randomness. To use it, simply enter the table in
some way that prevents your exercising choice in the first sample
then simply take the number is same predetermined order such as
left to right. Other appropriate ways of making random decisions
are drawing numbers from hats, flipping coins, rolling dice, etc.,
Stratified Random Sample
All the random quadrats might be clustered by chance in one
section of the area. To avoid this possibility, the area can be
subdivided into roughly equal areas and each section randomly
sampled with fewer quadrats. This is called stratified random
sampling, or restricted random sampling.
Systematic Sample
Taking samples that have some sort of systematic or regular
arrangements. For example sample plots may be located every 100
meters along a line. Thisis simpler than random sampling but bias
will be present if the pattern of sampling is picking up some
pattern in the distribution.
Estimation of Cover, Frequency and Height
Cover or Coverage: Defined as the percentage of
quadrat are beneath the canopy of given species or group.
Percentage cover can be estimated by eye. Visual estimates can be
made of the cover of the species either in the sample plots or in
the whole study area. Different measures can be used. The simplest
is the classification Dominant, Abundance, Frequent, Occasional,
and Rare (DAFOR). These classes have no strict definition and you
must decide on your own interpretation.
Vegetation is often layered, so percentage cover values can
sum to more than 100%. So it is useful to divide the vegetation
into layers and present the cover estimates separately each layer.
Frequency: Defined as the percentage of total
quadrats which contains at least one rooted individual of a give
group or species.
Height: The height of a plant is defined as the
length of the main stem above the ground level.
Lundy Island Grassland Classifications
It is difficult to identify the Lundy grassland plants down to
species level in the field. We can identify some of the grasses by
using our identification manual. The samples of plants can be
collected from the field and it can be identified here by
consulting the experts. However, the plants are classified into
following groups. They are Grasses & Sedges, Broad leafed herbs
(forbs), and Shrubs.
Grass: Generally have long, narrow parallel-veined
leaves inserted distichously on a round hollow stem. Open
grasslands fall conveniently into three height groups viz., high
(or tall) (6-8ft or more), medium (2-5ft) and short (less than 2).
Grasses can be divided into four groups. They are
Fine leaved grass: Grasses which have thin
needle like leaves mostly deep green
Blade leaved grass: Grasses with leaves that
look like a blade i.e., broad and flat.
Tussocks: A tuft of grass looking like a grass
heap.
Rushes: Grasses which have hollow stems that
look like a pipe, with a white inner coating.
Broad leafed herb or Forb: A non-woody plant, or at
least one which is not woody above the ground level. It is
classified into two categories i.e.,
Rosette: Any plant with its leaves radiating
outwards as a circular cluster from a short stem at soil level.
Further these can be classified into short and tall rosettes.
Prostrate: Describing a plant that grows flat
upon or closely along the ground.
Shrubs: A woody plant not having a main trunk but
several main branches. In general shrubs are smaller than trees.
Two types will be seen on Lundy. They are
Gorse: Shrubs which have needle like leaves and
it is spiny.
Heather: Shrubs which have needle like leaves
but are not spiny.
Identifying the impact of grazing
Over grazing can be identified by a low number of tussocks,
short grass height and more rushes, rosette, and prostrate herbs,
and less heather. Gorse is thick and looks like a cushion.
In less grazed areas, more tussocks can be seen. The height
will be high and there will be fewer rushes and more heather.
Gorse is not thick and gaps can be seen between plants.
References
- Barbour, M.G., Burk, J.H., and Pitts, W.D. (1980).
Terrestrial plant ecology. London: Benjamin/Cummings Publishers.
604pp
- Bookhout, T.A. (Ed). (1996). Research and management
techniques for wildlife and habitats. Maryland: The Wildlife
Society. 740pp
- Brewer, R., and McCann, M.T. (1982). Laboratory and field
manual of ecology. London: Saunders College Publishers. 269pp
- Krebs, C.J. (1989). Ecological methodology. London: Harper &
Row Publishers. 654pp
- Pound, R., and Clements, F.E. (1898). A method of
determining the abundance of secondary species. Minn. Bot.
Studies 2: 19-24.
- Sutherland, W.J. (1997). Ecological census techniques a
handbook. Cambridge: Cambridge University Press. 336pp