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September 9, 1999 - A public lecture by Dr Shankar
Prasad, |
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community health adviser to the Chairperson,
California Air Resources Board on `Translating Health Concerns into Air Quality
Regulations: Lessons from California |
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Role of Regulations,
Advisories, and Notifications in Improving Air Quality
Shankar B. Prasad, M.B.B.S.
Community Health Advisor
California Air Resources Board
Sacramento, California
In California, state and local entities are responsible for controlling emissions from
stationary and mobile sources to meet federal and state ambient air quality standards
(AAQSs) to protect human health and welfare. In an effort to protect individuals from
adverse air pollution impacts, local air pollution control agencies (e.g., South Coast
AQMD) routinely issue health advisories and public notifications when air pollutant levels
are expected to exceed preset threshold levels for criteria pollutants and toxic air
contaminants, respectively. The success of advisory and notification programs is evident
from the changes in activity patterns in schools, and from reductions in toxic pollutant
emissions from many facilities. Guidelines for these programs have been developed in
consultation with various state (Office of Environmental Health Hazard Assessment (OEHHA)
and ARB) and federal agencies, cities, schools, the public-at-large, consumer interest
groups, and the regulated community.
California is a state of great diversity and size spanning an area of
about 156,000 square miles. For purposes of managing the geographically distinct air
quality problems across the state, California is divided into 35-air pollution control
districts, where an individual air basin may encompass administrative areas of one or more
county governments. Without question, the most severe air pollution problem occurs in the
South Coast Air Basin (SoCAB), which is commonly known as the Los Angeles Basin. In this
regard, federal and state AAQSs for ozone, carbon monoxide (CO), and PM10 are routinely
exceeded in the SoCAB. In 1997, the maximum 1-hr average ozone concentration recorded in
the SoCAB was 0.205 ppm, with 144-days exceeding the state AAQS (0.09 ppm) and 64-days
above the federal AAQS (0.12 ppm) (Table 1). For CO in 1997, the maximum 8-hr average
concentration was 17.1 ppm, with 16 and 12-days recorded above the state (9.0 ppm) and
federal (9 ppm) AAQSs, respectively. The highest 24-hr average PM10 concentration in 1997
was 224 :g/m3, with 54-days exceeding the state standard (50 :g/m3) and 6-days over the
federal standard (150 :g/m3). The sizeable improvements in ambient air quality observed in
the SoCAB are largely the result of an aggressive air pollution control program to reduce
emissions of both criteria pollutants and toxic air contaminants from stationary and
mobile sources.
Table 1. Selected Air Quality
Values for Ambient Ozone, PM10, and CO
in Californias South Coast Air Basin
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----- Ozone ----- |
----- PM10 ----- |
----- CO ----- |
Year |
Max
1-hr (ppm) |
Days
Above 0.09 ppm |
Max
24-hr (:g/m3) |
Days*
Above
50 :g/m3 |
Max
8-hr (ppm) |
Days Above 9.0 ppm |
1980 |
0.490 |
210 |
--- |
--- |
25.8 |
98 |
1982 |
0.400 |
198 |
--- |
--- |
21.3 |
71 |
1984 |
0.340 |
209 |
--- |
--- |
19.7 |
73 |
1986 |
0.350 |
217 |
--- |
--- |
19.7 |
56 |
1988 |
0.350 |
216 |
289 |
65 |
27.5 |
66 |
1990 |
0.330 |
185 |
475 |
65 |
16.8 |
47 |
1992 |
0.300 |
190 |
649 |
52 |
18.8 |
32 |
1994 |
0.300 |
165 |
161 |
58 |
18.2 |
28 |
1996 |
0.239 |
141 |
162 |
51 |
17.5 |
23 |
1997 |
0.205 |
144 |
227 |
54 |
17.1 |
16 |
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* PM10 is sampled on a 1-day in six basis; value is
an estimate of number of days that the state standard is exceeded in one year |
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In the mobile source arena,
the ARB has targeted two main parameters to control emissions from motor vehicles: exhaust
emission levels from on-road motor vehicles and the properties of motor fuels. From
light-duty motor vehicles (e.g., cars and small trucks) without tailpipe controls (i.e.,
pre-1968), emissions of hydrocarbons, nitrogen oxides (NOx), and CO are 10.6, 4.1, and 84
g/mile, respectively. Over the ensuing 26-years (Table 2), improvements in emission
control technologies and vehicle durability enabled the ARB to adopt Low Emission
Vehicle standards in 1994. These standards called for low and ultra-low emission
vehicles that have to be certified to meet tailpipe emission standards that were < 1%
for hydrocarbons, ~4% for NOx, and 2-4% for CO of the emission levels from pre-1968 motor
vehicles.
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Model Year |
Hydrocarbons (grams/mile) |
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Pre-Control |
10.60 |
4.1 |
84.0 |
1968 |
6.30 |
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51.0 |
1971 |
4.10 |
4.0 |
34.0 |
1972 |
2.90 |
3.0 |
34.0 |
1975 |
0.90 |
2.0 |
9.0 |
1977 |
0.41 |
1.5 |
9.0 |
1980 |
0.39 |
1.0 |
9.0 |
1993 |
0.25 |
0.4 |
3.4 |
1994 TLEV* |
0.125 |
0.4 |
3.4 |
1994 LEV |
0.075 |
0.2 |
3.4 |
1994 ULEV |
0.040 |
0.2 |
1.7 |
1994 ZEV |
0.000 |
0.0 |
0.0 |
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* TLEV (Transitional Low Emission Vehicle);LEV (Low Emission Vehicle);
ULEV (Ultra Low Emission Vehicle);
ZEV (Zero Emission Vehicle) |
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The achievement of
increasingly stringent tailpipe standards could not have been achieved without
improvements in motor fuels. Over the same time span, the ARB has also adopted a suite of
regulations to tighten the specifications of gasoline sold for use in motor vehicles
(Table 3). Since 1991, with the adoption of Phase 2 of the California Reformulated
Gasoline (CaRFG) Program, stringent limits were placed on Reid Vapor Pressure (RVP),
sulfur, aromatic, and olefin levels, along with the phase-out of leaded gasoline.
Currently, levels of sulfur in gasoline are capped at 30 ppm by weight, RVP at 7.0 psi,
and aromatics at 22.3 % by weight. The mandated reductions in fuel aromatic and olefin
contents has the added benefit of reducing emissions of two major toxic air contaminants
benzene and 1-3, butadiene. |
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Table 3. Chronology
of Gasoline Fuel Regulations in California |
Year |
Parameter(s) Controlled |
1971 |
RVP, Bromine Number |
1975 |
Sulfur, Manganese, Phosphorus |
1976 & 1982 |
Lead |
1990 |
Phase 1 California Reformulated Gasoline (CaRFG)-- RVP, Lead Phase-Out,
Deposit Control Additives |
1991 |
Phase 2 CaRFG -- Winter Oxygenates |
1994 |
Phase 2 CaRFG Predictive Model |
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To address emissions from
heavy-duty vehicles, which primarily utilize diesel, recent efforts have focused on
reformulating diesel fuel and lowering emissions from trucks and buses. Of special concern
is the reduction of particulate emissions, which have been designated as a toxic air
contaminant by the State of California.
For stationary sources, criteria pollutant emissions from major industrial facilities
largely occurred in the 1970s. Since 1987, efforts have focused on reducing
emissions of toxic air contaminants through the adoption of control measures including
those to reduce benzene emissions from gasoline service stations (adopted in 1987) and
perchloroethylene emissions from dry cleaners (adopted in 1993). Other measures have been
adopted to limit emissions of metals (e.g., hexavalent chromium, arsenic, cadmium, and
nickel), ethlene oxide, and dioxins.
To warn the general public in California about the health risks posed by criteria
pollutants, local air pollution control agencies like the South Coast AQMD make regular
predictions of air quality conditions and issue health advisories on a daily basis. Health
advisories serve to provide the public with information on air quality conditions in
different areas within an air basin. Qualitative terms such as good, moderate, or
unhealthful are used to inform the public that air pollution levels have exceeded
predetermined thresholds that could lead to adverse health impacts such as the impairment
of lung function (resulting in a decrease in breathing capacity and exercise tolerance),
excess coughing, or headache. For example, a good ozone day is characterized
as a day in which the maximum 1-hr average ozone concentration is no greater than 0.12
ppm. At this maximum concentration, no reported adverse health effects are known to occur
based on present knowledge. On moderate days, ozone concentrations may reach
levels that are harmful to sensitive sectors of the general population like school
children, the elderly, and people with heart and lung disease. When ambient levels are
projected to reach concentrations that are harmful for these sectors of the population, a
cautionary statement is issued to recommend changes in activity patterns at schools, such
as to limit or avoid outdoor activities.
For toxic air contaminants, chronic exposures are associated with higher lifetime cancer
risk, and the State of California recognizes the cancer-causing potential of a suite of
airborne contaminants (e.g., diesel particulate, benzene, perchloroethylene, and
1,3-butadiene). Because emissions of toxic air contaminants from stationary sources could
be higher in surrounding areas, public notifications, to inform the public living in the
vicinity of major source of airborne toxics, are required by law under Assembly Bill 2588
known as the Hot Spots bill. The aim of the notification process is to trigger
action by facility operators to inform the people living near the facilities of the risk
from toxic emissions released by the facility. Whenever the risk posed by the release of
air toxics exceeds a predetermined level deemed as unsafe by a local air pollution control
agency, the facility must notify the public of the risk posed by the emissions release. In
the SoCAB, no existing facilities are allowed to exceed a maximum individual cancer risk
(MICR) of 25 in a million (i.e., 2.5 x 10-5) or a hazard index of 3.0. If they exceed this
limit, emissions must be reduced in order to continue operations. The requirement for a
public notification applies to all facilities with a MICR of 10 in a million (10-5), a
hazard index > 1 for toxic air contaminants, or a hazard index > 0.5 for lead.
Different thresholds are applicable to new facilities or sources undergoing modification.
In the last three decades, California has made tremendous progress in reducing emissions
of criteria and toxic pollutants using the command-and-control approach. While the
ARBs long-term programs to reduce emissions from motor vehicles and toxic hot
spots has played a major role in achieving the air quality improvement, the issuance
of public notifications and health advisories has also been a contributing factor to
improving environmental quality. By informing the public that criteria pollutant levels
may reach unhealthful levels, the public-at-large has the information needed to make
informed decisions as to what they can do to change their activity pattern and reduce
personal exposure to those pollutant stressors. The levels at which notifications are
issued is critical insofar as keeping residents living near toxic pollutant sources
informed of the risk they face in their daily lives. However, because of the amount of
effort required to issue public notifications and the inference that they may be bad
neighbors, many facilities have opted to reduce their emissions below threshold
values, thereby eliminating the need for issuing a public notification. In this regard,
the public notification process has indirectly led to voluntary reductions in the amount
of toxic pollutants emitted in California.
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Press
Release |
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