- •Types of ecosystems -
- •Coastal ecosystem –
- •1. Basic idea:
- •2. Significance and importance:
- •Ecological significance of the coastal plain in west bengal
- •Significance of the field study and its relation to coastal ecosystem
- •Conservation strategies of the coastal ecosystems
- •Climate of talsari
- •Brief topography of talsari
- •Method of the study and procedures
- •Procedure
- •Discussions about the vegetation and flora
- •The following data can be recorded for each quadrate
- •The data recorded from our quadrates
- •Chart on overall quadrate data
- •Calculation on species abundance Abundance– It is the community refers to the no. Of individuals of that species per unit area. It is calculated by –
- •Calculation on species frequency Species frequency – this involves calculating the percentage of quadrates that contain each plant species.
- •Method of the study
- •Further cheaklist on avifauna in talsari and their scientific name and range habitant
- •Photos avifauna studied at coastline area
- •Avifauna observed in the estuarine area is given as follows:-
- •A brief about crab
- •Ecology
- •Behavior
- •Significance of presence of claws in the body of crab
- •Objective of the study
- •Observations
- •Discussion about crab behavior
- •6 Crab interaction
- •7 Walking movement of crabs
- •Observations
- •Observations
- •Ecosystem analysis in details
- •Conclusion
- •Hoopoe bird (Upupa epops)
- •Bibliography
Method of the study and procedures
To study the floral and vegetation diversity, we chose the QUADRATE STUDY method.
A quadrate is a small plot used in ecology and geography to isolate a standard unit of area for study of the distribution of an item over a large area. While originally rectangular, modern quadrates can be rectangular, circular, irregular, etc.,. The quadrate is suitable for sampling plants, slow-moving animals (such as millipedes and insects), and some aquatic organisms.
When an ecologist wants to know how many organisms there are in a particular habitat, it would not be feasible to count them all. Instead, he or she would be forced to count a smaller representative part of the population, called a sample. Sampling of plants or animals that do not move much (such as snails), can be done using a sampling square called a quadrate. A suitable size of a quadrate depends on the size of the organisms being sampled. For example, to count plants growing on a school field, one could use a quadrate with sides 0.5 or 1 meter in length.
Quadrates are typically areas of dimensions ranging from 1×1 ft to 4×4 ft and to the maximum 5×5 ft.
Procedure
The fixed point is first determined by a stone throwing by our coordinator.
It is then made prominent with a branch in the form of a stick and placed accordingly.
Now areas are formed of 1×1 ft to 4×4 ft by extending the other point i.e. the boundaries but keeping the fixed point as it is.
The various plants falling under the quadrates are then noted down.
A
TYPICAL DIAGRAM OF QUADRATE STUDY
Remark :- It is to reminded that when a 4×4 dimension is reached and if no new species intrusion takes place then that is considered as the least quadrate .5×5 dimension is created just to check saturation and confirmation of no new species intrusion.
For avifaunal study we have used Line Transect Method.
A transect line can be made using a nylon rope marked and numbered at 0.5m, or 1m intervals, all the way along its length. This is laid across the area you wish to study. The position of the transect line is very important and it depends on the direction of the environmental gradient you wish to study. It should be thought about carefully before it is placed. You may otherwise end up without clear results because the line has been wrongly placed. For example, if the source of the pollutant was wrongly identified in the example given above, it is likely that the transect line would be laid in the wrong area and the results would be very confusing. Time is usually money, so it is worth while thinking about it before starting.
A line transect is carried out by unrolling the transect line along the gradient identified. The species touching the line may be recorded along the whole length of the line (continuous sampling). Alternatively, the presence, or absence of species at each marked point is recorded (systematic sampling). If the slope along the transect line is measured as well, the results can then be inserted onto this profile.
For crab study we have been arranged in a line few distance away from the crab habitant so that we can easily spot the crabs without disturbing them.
OBSERVATIONS
A total of 3 types of quadrate sets were made and then studied/analyzed.
TYPE 1 – COASTLINE AREA
TYPE 2 –MID COASTLINE AREA
TYPE 3 –ESTUARINE AREA
OF THE FOLLOWING QUADRATES [Q=QUADRATES]
Q1 TO Q4 LIES IN COASTLINE AREA
Q5 TO Q8 LIES IN MID COASTLINE AREA
Q9 TO Q12 LIES IN ESTUARINE AREA
SPECIES Serial no. |
Q 1 |
Q 2 |
Q 3 |
Q 4 |
Q 5 |
Q 6 |
Q 7 |
Q 8 |
Q 9 |
Q 10 |
Q 11 |
Q 12 |
DENSITY [total no. of individuals of the species in all quadrates ÷no. of quadrates in which that surveyed] |
Abundance =( total no. of individuals in all quadrates) ÷( no. of quadrates in which the particular species is found] |
Frequency (in %) = (no. of quadrates in which species occurred ) divided by (the total no. of quadrates studied ) x 100
|
1 CASUARINA SP |
1 |
0 |
0 |
4 |
1 |
1 |
0 |
0 |
0 |
0 |
0 |
0 |
2.333 |
3.5 |
66.66 |
2 OPUNTIA SP |
0 |
0 |
1 |
1 |
0 |
0 |
0 |
0 |
1 |
2 |
0 |
0 |
2 |
3 |
66.66 |
3 CALOTROPIS SP |
0 |
1 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0.33 |
1 |
33.33 |
4 AZADIRACHTA INDICA |
1 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0.33 |
1 |
33.33 |
5 SUEDA MARITIMA |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
1 |
0 |
0.33 |
1 |
33.33 |
6 SPINIFEX LITTOREUS |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
1 |
2 |
1 |
3 |
33.33 |
7 GRASS |
4 |
5 |
5 |
4 |
5 |
3 |
2 |
9 |
0 |
0 |
0 |
0 |
12.33 |
18.5 |
66.66 |
8 OTU 1 |
1 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0.33 |
1 |
33.33 |
9 OTU2 |
0 |
0 |
0 |
1 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0.33 |
1 |
33.33 |
10 OTU3 |
0 |
0 |
0 |
2 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0.66 |
2 |
33.33 |
11 OTU4 |
0 |
0 |
0 |
1 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
|
0.33 |
1 |
33.33 |
12 OTU5 |
0 |
0 |
0 |
2 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0.66 |
2 |
33.33 |
13 OTU6 |
0 |
0 |
0 |
0 |
0 |
1 |
0 |
0 |
1 |
0 |
0 |
0 |
0.66 |
1 |
66.66 |
14 OTU7 |
0 |
0 |
0 |
0 |
0 |
1 |
2 |
0 |
0 |
0 |
0 |
0 |
1 |
3 |
33.33 |
15 OTU8 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
2 |
0 |
0 |
0 |
0 |
0.66 |
2 |
33.33 |
PHOTOS
CALOTROPIS SP. UNKNOWN GRASS SPECIES [GSP1]
UNKNOWN GRASS SPECIES [GOTU2] NEEM
CASUARINA SP OPUNTIA SP OPUNTIA SP
OPUNTIA SP. UNKNOWN PLANT SPECIES [SP1]
UNKNOWN PLANT SPECIES [OTU2] UNKNOWN PLANT SPECIES [OTU3]
UNKNOWN PLANT SPECIES [OTU4] UNKNOWN PLANT SPECIES [OTU5]
UNKNOWN PLANT SPECIES [OTU6] UNKNOWN PLANT SPECIES [OTU7]
UNKNOWN PLANT SPECIES [OTU8] SPINIFEX LITTOREUS
CALOTROPIS SPECIES UNKNOWN SPECIES 10
OPUNTIA SP CASUARINA SP
