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ENVIRONMENTAL ASSESSMENTS AND RELATED IMPACTS
BACKGROUND
This author has previously written on the subject of environ-
mental assessment by outlining its typical content require-
ments, as well as the types of expertise that are required in
the preparation of an Environmental Impact Statement(EIS).
The author has also discussed some of the problems associ-
ated with the EIS process and has provided some sugges-
tions in improving the quality of EIS documents. This paper
examines the role of the EIS at the project level, where ulti-
mately, most decisions of project approvals or denials are
made in the 1990s by municipal reviewers rather than by
state or federal agencies.
INTRODUCTION
With the advent of the National Environmental Policy Act
(i.e., NEPA) in 1969, the requirements for environmen-
tal impact reporting was originally restricted by the Act to
Federal projects, or projects subsidized in whole or in part by
Federal funding. Since NEPA, many states and municipali-
ties have developed their own environmental impact require-
ments to aid in the review of projects under their jurisdiction.
As a result of the above evaluation, which has coincided
with a general decentralization of power under the Reagan
administration, the approval or denial of proposals often rest
with local review of the environmental impacts of the spe-
cific project regardless of its funding source (i.e., public or
private). The evolution of ultimate decision-making at the
local level is inevitable when one considers that the most
potentially noxious sitings (e.g., nuclear power plants,
resource recovery facilities, airports, etc.) would be accepted
more critically by municipalities serving as potential host
communities than by state or federal entities. Since environ-
mental standards promulgated at the federal and state levels
can be adopted or be made more restrictive at the municipal
level, the opportunity presents itself for municipalities to uti-
lize local environmental impact ordinances to tightly regulate
land-use development within their boundaries. Even in cases
where states have the power to “force” sitings in munici-
palities in order to insure the health and well being of all its
constituents, most have tried, for political reasons, to justify
their positions through an environmental review process,
which, in many cases, has caused extensive delays and/or
total abandonment of such sitings. As such, the preparation
and presentation of environmental impact statements at the
municipal level have often become the most critical element
in the consideration and fate of many development projects.
VARIATION IN EIS REPORTING AT THE
MUNICIPAL LEVEL
The quality of EIS reporting at the municipal level often
exhibits tremendous variations for one or more of the fol-
lowing reasons:
1) The expectations of municipalities relating to EIS
documentation varies from it merely being a for-
mality with the application process to the docu-
ment being a pivotal component in the approval
or denial of the project. In municipalities where
growth is encouraged and variances to the zone
plane are given consideration with regularity, the
environmental impact statement requirements may
be minimal. In contrast, in municipalities which
practice “no-growth” policies and/or rigidly pro-
tect their zone plan, the review and critique of the
EIS often is used as a weapon for denial or delay
of applications.
2) The assessment ordinances, as promulgated, often
allow too much subjective interpretation insofar
as EIS preparation is concerned. Examples are as
follows:
a. Normally there are no regulations specified for
the preparers of component portions of the EIS
to be identified or to provide their credentials
pertinent to the sections they have prepared.
b. There generally are no guidelines to provide
the applicant with information as to the extent
of documentation required to deem an EIS
“complete” for submission purposes.
c. Specific environmental quality standards to
be maintained are often either not specified
in the ordinances, or are written in qualitative
rather than quantitative terms. This encourages
assessors to respond to environmental issues in
qualitative terms rather than to conduct proper
monitoring programs to establish baseline
data, project thereon the added impact of the
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