Methods of EIA
By Advanced Environmental Engineering
http://mjcetce455.blogspot.com/2017/04/methods-of-eia.html
Listed below are the important methodologies for assessing the impacts of any developmental activity on the environment:
These methods might vary from:
The change in EIA is moving away from a simple listing of potential impacts to complex modes involving identification of feedback paths leading to higher order impacts as compared to the easily visible first order impacts involving uncertainities. This approach can be considered as an overall management technique requiring differentkinds of data in different formats along with varying levels of expertise and technological inputs to accurately forecast the results of any planned development.
Ad hoc methods indicate broad areas of possible impacts by listing composite environmental parameters (Ex: flora and fauna) likely to be affected by the proposed activity.
These methods involve assembling a team of specialists who identify impacts in their area of expertise. Here, each parameter is considered separately and the nature of impacts (long term or short term, reversible or irreversible) are considered.
These methods give a rough assessment of total impact while giving the broad areas and the general nature of possible impacts. In this method, the assessor relies on an intuitive approach and makes a broad-based qualitative assessment. This method serves as a preliminary assessment and helps in identification of important areas like:
Types of Ad hoc method are:
This method is very simple and can be performed without any training. It does not involve any relative weighting or any cause-effect relationship.
It provides minimal guidance for impact analysis while suggesting broad areas for possible impacts. Moreover, it does not even state the actual impacts on specific parameters that will be affected.
The drawbacks of this method are listed below:
In this method, environmental factors are listed in a structured format by giving importance weightings for factors and application of scaling techniques for impacts of each alternative.
Checklists are strong indicators of impact identification. They effectively garner the attention and awareness of their audience. Impact identification is a fundamental function of an EIA. Checklists may be:
However, the scaling and weighting methods are subjective and hence pose the danger of imparting equal importance to every impact. Another defect observed by critics is that numerical values assigned to impacts can be derived on the basis of expert knowledge and judgement alone.
Scaling and weighting checklist techniques quantify impacts reasonably well although they use subjective extimates. However, they make no provision for assessing dynamic probabilistic trends or mitigation, enhancement and monitoring programmes. These methods cannot identify higher order effects, impacts and interactions.
Simple and descriptive checklists simply identify the possible potential impacts without any rating regarding their relative magnitudes.
Scaling and weighting checklists remove decision making from the hands of decision makers while they impart a single number to various inherently different impacts and this aspect prevents the decision maker to consider the possibility of trade-offs.
In checklist method, the impacts are tabulated in the form of cells with information either in the descriptive form that gives information regarding possibility or potential existence of an impact whereas in the scaling or weighing methods the magnitude or importance of impact is given. Sample checklists or weighing methods used in EIA are shown below:
The advantages of this method are:
Disadvantages of this method are:
This methodology provides a framework of interaction of different activities of a project with potential environmental impacts caused by them. A simple interaction matrix is formed when project actions are listed on one axis (usually vertical) and environmental impacts are listed along the other axis. This technique was pioneered by Leopold et al in 1971. It lists about 100 project actions and about 88 environmental charateristics and conditions. An example of this matrix is shown below:
Similarly, a sectoral matrix is shown below:
The disadvantages of this method are listed below:
The advantages of the network method are:
The disadvantages of this method are:
The advantages of this method are:
The disadvantages of this method are: