| 
     | 
     | 
    
      
          | 
       
      
         | 
       
      
        
          
              | 
            September 9, 1999 - A public lecture by Dr Shankar
              Prasad, | 
           
         
         | 
       
      
        | community health adviser to the Chairperson,
        California Air Resources Board on `Translating Health Concerns into Air Quality
        Regulations: Lessons from California     | 
       
      
         | 
       
      
        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 
              | 
           
          
            
              
                |   | 
                -----  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 | 
               
             
             | 
           
          
            * 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   | 
           
         
         | 
       
      
         | 
       
      
        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.  
          | 
       
      
         | 
       
      
        
          
             | 
           
          
            
              
                | Model Year | 
                Hydrocarbons (grams/mile) | 
                 | 
                 | 
               
              
                | Pre-Control | 
                10.60 | 
                4.1 | 
                84.0 | 
               
              
                | 1968 | 
                6.30 | 
                --- | 
                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 | 
               
             
             | 
           
         
         | 
       
      
        * TLEV (Transitional Low Emission Vehicle);LEV (Low Emission Vehicle);
        ULEV (Ultra Low Emission Vehicle);  
        ZEV (Zero Emission Vehicle) | 
       
      
         | 
       
      
        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.   | 
       
      
         | 
       
      
        
          
            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 | 
               
             
             | 
           
         
         | 
       
      
         | 
       
      
        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. 
          | 
       
      
         | 
       
      
        | Press
        Release | 
       
     
     |