![]() | Conducting Environmental Impact Assessment in Developing Countries (United Nations University, 1999, 375 p.) |
![]() | ![]() | 4. EIA methods |
![]() | ![]() | 4.3 Matrix |
A most noteworthy matrix presentation essentially improves the communication between the impact analysts, decision makers, and the public. In the symbolized matrices, symbols are used to capture the understanding of the impacts.
Environmental impacts may be described by words such as "important'' or "significant''. These subjective, qualitative words are difficult to deal with because their interpretation depend on cultural values and specific circumstances. Even when quantitative data are available, they must be gauged against some standard and often there is none or at least none widely accepted. There are, however, some useful guides for ranking impacts or assessing impact assessment.
There are several factors that must be taken into account when assessing the significance of an environmental impact arising from a project. The factors are interrelated and must not be considered in isolation. For a particular impact some factors may carry more weight than others, but it is the combination of all the factors that determines significance.
An example is to use abbreviations and scales, e.g., S for short term and L for long term or 10 to denote a very high order of the impact and 1 to denote almost negligible impact, etc. In this way, a symbolized matrix becomes a combination of descriptive and numeric scales. There are, however, some useful guides for the grading or classification of impacts. These are listed below:
Table 4.1 Environmental matrix for a quarry
Phase |
Development action |
Social |
Physical |
Biological |
Planning |
Consents, district plan, EIS timetable |
Law, regulation, public participation, employment, land values,
alternative sites, justification, risks and anxieties,
cultural/historical |
Location of access road |
Water table effects on adjacent land |
Engineering design |
Design of quarrying plan, resolve environmental factors, evaluate
options |
Landscape effects |
Design of quarry, restoration plan |
Design of drainage system, including sediment traps to protect
water quality in the river |
Construction |
Access road, drainage system, site crushing plant, energy supply,
traffic discharge, stormwaters, silt, sewage, site staff facilities |
Cultural/historical, safety, noise, vibrations, effect on farm
animals |
Disposal of stripping, stability, nuisance, landform noise,
blasting, drilling |
Sedimentation, surface water pollution |
Operation |
Stripping overburden, drilling, blasting, excavation, crushing,
loading, traffic, review and adjust environmental measures |
Landscape, farm animals, noise/vibration/dust, emissions,
safety/risk, staff facilities, working environment |
Landscape effect |
Progressive restoration plan, sedimentation, surface water
pollution |
Termination |
Remove plant, check stability, replace topsoil, plant ground
cover, maintenance |
Safety, landscape restoration |
|
Maintain and monitor sediment traps |
• Sign of the impact
Positive or negative. This is
unfortunately not that simple.
• Magnitude
This is defined as the probable severity of
each potential impact. Will the impact be irreversible? If reversible, what will
be the rate of recovery or adaptability of an impact area? Will the activity
preclude the use of the impacted area for other purposes? The answer to these
questions may be difficult and may have to be speculated on a subjective basis.
The size often depends on the source release, mitigation measures adopted, if
any, and the assimilative capacity of the receiving environment, etc.
• Type of change: reversible or
irreversible
Irreversibilities always command attention because they signal a
loss of future options. Species extinction, severe soil erosion, and habitat
destruction are examples of irreversible changes. Pollution of groundwater is
often irreversible because of its slow movement. Urbanization of agricultural
land is virtually impossible to undo once the land use trend has begun.
• Prevalence
This is defined as the likely eventual
extent of the impact as, for example, the cumulative effect(s) of a number of
stream crossings. Each one taken separately might represent a localized impact
of small importance and magnitude but a number of such crossings could result in
a widespread effect. Coupled with the determination of cumulative effects is the
remoteness of an effect from the activity causing it. The deterioration of fish
production resulting from access roads could affect subsistence fishing in an
area many miles away, and for months or years after the project activity has
ceased.
• Duration and frequency
The significance of duration and
frequency is reflected in the following questions. Will the activity be long
term, short term, or sporadic? If the activity is intermittent, will it allow
for recovery during inactive periods?
• Risk
This is defined as the probability of serious
environmental effects. To accurately assess the risk, both the project activity
and the area of the environment affected must be well known and understood.
• Importance
This is defined as the value that is
attached to an environmental component in its present state. For example, a
local community may value a short stretch of river for bathing or a small swamp
for hunting. Alternatively, the impacted component may be of regional,
provincial or even national importance.
• Mitigatability
Are solutions to problems available?
Existing technology may provide a solution to a siting problem expected during
construction of an access road, or to bank erosion resulting from a new stream
configuration.
• Understanding
For example, if an access road is to
cross a stream and the assessor does not know the extent of use of that stream
(for fish spawning, fish migration, subsistence fishing, river transport, etc.),
then the impact would be classed as unknown. Similarly, the nature of the river
crossing (ford, bridge, ferry, or causeway) may not yet have been planned and so
the significance of the environmental impact of that crossing is therefore
unknown.
The assessment of significance is best done by holding at least two group discussion meetings involving interdisciplinary expertise.
The most frequently used presentation of a comparison of alternatives is a matrix, in which +, 0 and - show how each alternative affects the different environmental aspects. This can be a useful way to provide a quick overview of the differences between the alternatives.
• the impacts of each alternative are evaluated against a reference (usually the existing situation); or
• for each alternative, it is shown how it contributes to the environmental objectives; or
• the impacts of each alternative are compared with the preferred alternative.
+ + and - - give extra possibilities for differentiation.
In each case it is important that the significance of the symbols is properly defined. If necessary, a reference should guide the reader to more ample information (Table 4.2).
Table 4.2 Example of plus/minus matrix on the theme "Why does the proposed activity improve the soil condition?"
|
Existing situation |
Proposed activity |
Process alternative |
Environmentally most friendly |
Air |
0 |
|
|
0 |
Soil |
0 |
+ |
+ |
+ |
Surface water |
0 |
|
0 |
0 |
Waste |
0 |
+ |
+ |
+ |
Noise |
0 |
- |
- |
- |
Safety |
0 |
(-) |
(-) |
(-) |
Nature |
0 |
0 |
0 |
0 |
Energy |
0 |
- |
0 |
+ |
Costs |
0 |
- |
- |
- |
Legend: - deterioration compared to the existing situation; + improvement; 0 no difference; (-) insignificant deterioration.
Table 4.3 Numeric matrix lending a quick but factual overview
|
Lead concentration in air
(μg/m3) |
NOx emission
(μg/m3) |
Noise level at periphery area (dB(A)) |
Hazardous waste produced tons/year |
Alternative 1 |
0.8 |
35 |
55 |
2674 |
Alternative 2 |
0.7 |
20 |
50 |
2350 |
Background level existing situation |
1.0 |
80 |
43 |
- |
Predicted background level 2005 |
1.2 |
110 |
45 |
- |
Environmental standard |
1.5 |
100 |
55 |
- |