Encyclopedia of Environmental Science and Engineering, Volume I and II

(Ben Green) #1

330 ENVIRONMENTAL ASSESSMENTS AND RELATED IMPACTS


the site. This often leads to time consuming and costly litiga-
tion between applicants and their design professionals.
The analysis of traffic-induced noise and air quality
impacts in environmental assessment reporting has been
conducted in most reports since the passage of NEPA.
Normally, many attendees at public hearings are confused
about the logarithmic nature of decibel levels (the stan-
dard noise descriptor) and how multiple sources of sound
are added in terms of decibels. In addition, they generally
do not have the technical background to assess results gen-
erated from noise and air pollution mathematical models
often employed by professionals preparing assessments.
However, the public, over the last thirty years, have dem-
onstrated an increasing tendency to voice more concerns at
hearings related to noise and air quality issues, and quality
of life issues as a whole.
In addition, because traffic noise generation by vehicles
on public highways, and rail and aviation noise generation
are not normally regulated by municipalities, and further,
because the agencies which regulate rail and aircraft noise
have less stringent or no standards of compliance at resi-
dential property lines (or properties in the case of aircraft)
compared to typical municipal noise ordinances, noise gen-
eration from these sources is being challenged more often
by the public.
In populated and well developed communities, the
remaining parcels to be developed are often situated in close
proximity to rail lines, airports and heavily traveled high-
ways. Lastly, society is trending toward greater longevity,
and noise and air pollution more adversely affect senior citi-
zens than the rest of the general population. As such, credible
assessment reporting in the disciplines of noise and air qual-
ity, as well as providing meaningful mitigation techniques in
site design and orientation for residential applications pro-
posed in proximity to major potential noise and air quality
generators are critical for one to be successful in convincing
an often cynical public.
Lastly, the air quality standards promulgated for mobile
source (i.e., traffic) pollutants in the Clean Air Act of 1970,
with the exception of ozone (which is generated about
equally by mobile and stationary air pollution sources) have
remained unchanged, yet most urban areas, where air pol-
lution generation is normally at the highest levels, have
remained in compliance over the period in question. This has
occurred despite a major increase in driver registration and
vehicular miles traveled on US highways since 1970, due in
major parts to technological advances (e.g., catalytic muf-
flers since the mid 70s, which have reduced vehicular emis-
sions to offset population growth. However, in the United
States in the near future, we will be challenged with the need
to find alternative fuel sources for vehicles which generate
less air pollutants if we are to remain in compliance with
the Ambient Air Quality Standards promulgated in 1970 for
mobile source pollutants.
In summary, issues such as wetlands delineation, air pol-
lution and traffic-induced noise must be given serious atten-
tion in assessment reporting for applications to be approved

by reviewing bodies. Increased public awareness on how
effectively to critique decision-making methodologies and
basic assumptions associated with mathematical models
employed in conjunction with assessment preparation is
placing an increased burden to defend properly their appli-
cation in the reporting process.

RISK ASSESSMENT REPORTING AND ASSOCIATED
STRATEGIES

If an application involves a project which can (or may) be
deemed as a potential threat to life, limb or property result-
ing from its construction and/or operation, reviewing agen-
cies will normally require a risk assessment to be prepared
in addition to an environmental assessment. The function of
a risk assessment is to quantify (where possible) the risk of
death, injury and potential loss of personal property asso-
ciated with the worst-case scenarios that can be perceived
occurring on the subject site. Typically, risk assessors are to
prepare their assessment utilizing the principle of Murphy’s
Law that “all that can go wrong, will!” All aspects of the
operation on the site, including transportation, handling,
storing, processing of the product involved and related
by-product generation and disposal must be considered, and
probabilities of risk quantified (based upon industry practice
and history) for each phase of the operation on an annual
basis.
For all aspects of risk considered, one assesses the
so-called “safe separation distance” (SSD) from the site
should a particular failure mode occur either on the site or
by transmission from the site (e.g., vapor dispersion of a
product or by-product). If potential sensitive receptors are
located within the SSD, then those cumulative risks from all
potential modes associated with the site in question must be
quantified. For parcels located beyond the SSD, the risks are
considered negligible.
Once a potential risk is quantified for a particular site,
mitigations to the risk can be investigated, based on the pro-
posed implementation of mitigating factors for the subject
site and the historical value based on industrial experience
related to their effectiveness in reducing risk. Examples of
mitigating factors may include the following: availability
of fire-fighting capability on the site or within a short dis-
tance of the site, accident history of the particular company
involved, training of personnel on site, etc. Generally, a
value between 0 and 1 is assessed for each mitigating factor,
which is then multiplied by the cumulative risk probability
for the proposal. This, in essence, produces a reduced prob-
ability of risk.
The risks associated with the proposal are typically
compared to the “normal risk” to which individuals are
subjected in conducting their daily lives. To develop such
a perspective, published annual fatality statistics due to
accidents (vehicular, aircraft, drowning, lightning, elec-
trocution, falls, etc.) are available from all industrialized
nations which, based on total population statistics, can be

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