United States
                             Environmental Protection
                             Agency
                     Office of Water
                     4601
            EPA811-F-95-003e-T
                  October 1995
                             National Primary Drinking
                             Water Regulations
                             Benzo(a)pyrene
  CHEMICAL/ PHYSICAL PROPERTIES

  CAS NUMBER: 50-32-8

  COLOR/ FORM/ODOR:
    Pale yellow needlelike crystals, FAINTLY
    AROMATIC

  M.P.: 179-179.3° C     B.P.: >360°C

  VAPOR PRESSURE: >1 mm Hg at 20° C

 . DENSITY/SPEC. GRAV.: 1.35at15°C
OCTANOL/WATER PARTmoN (Kow):
  Log Kow = 6.04

SOLUBILITY: 0.0038 mg/L of water at 25°
 • C; very low solubility in water

SOIL SORPTION COEFFICIENT:
  Log Koc =6.6 to 6.8; very low mobility
  in soil

ODOR/TASTE THRESHOLDS:  N/A
BlOCONCENTRATION FACTOR:
  BCFs range from <1 to 2675 in fish;
  expected to bioconcentrate in aquatic
  organisms which are unable to metabo-
  lize it.

HENRY'S LAW COEFFICIENT: .
  N/A; volatilization not significant

TRADE NAMES/SYNONYMS:
  3,4-Benz(a)pyrene; BaP; BP
DRINKING WATER STANDARDS
  MCLG:      zero mg/L
  MCL:   .    0.0002 mg/L  -
  HAL(child):  none

HEALTH EFFECTS SUMMARY
  Acute: EPA has found polycyclic aromatic hydrocar-
bons (PAHs)  similar to benzo(a)pyrene to potentially
cause the following health effects from acute exposures
at levels above the MCL: red blood cell damage, leading
to anemia; suppressed immune system.
  Drinking water levels which are considered "safe" for
short-term exposures have not been established at this
time.
  Chronic: Benzo(a)pyrene has the potential to cause
the following health effects from long-term exposures at
levels above the MCL: developmental and reproductive
effects.
  Cancer; There is some evidence that benzo(a)pyrene
has the potential to cause cancer from a lifetime expo-
sure at levels above the MCL.

USAGE PATTERNS
  Benzo(a)pyrene is one of a group of compounds called
polycyclic aromatic hydrocarbons (PAHs), or polynuclear
somatic hydrocarbons (PNAs). They are not produced
or used commercially but are ubiquitous in that they are
formed as a result of incomplete combustion of organic
materials.
               RELEASE PATTERNS
                 PAHs are found in exhaust from motor vehicles and
               other gasoline and diesel engines, emission from coal-,
               oil-, and wood-burning stoves and furnaces, cigarette
               smoke; general soot and smoke of industrial, municipal,
               and domestic origin, and cooked foods, especially char-
               coal-broiled; in incinerators, coke ovens, and asphalt
               processing and use.
                 There are two major sources of PAHs in drinking water:
               1) contamination of raw water supplies from natural and
               man-made sources, and 2) leachate from coal tar and
               asphalt linings  in water storage tanks and distribution
               lines. PAHs in raw water  will tend to adsorb  to any
               particulate matter and be removed by filtration before
               reaching the tap.
                 PAHs in tap water will mainly be due to the presence
               of PAH-containing materials in water storage and distri-
               bution systems. Though few data are available for esti-
               mating the potential for PAH release to water from these
               materials, there are reports that levels can reach 0.01 mg/
               L with optimum leaching conditions.

               ENVIRONMENTAL FATE
                 Released benzo(a)pyrene is  largely associated with
               particulate matter, soils, and sediments. Although envi-
               ronmental concentrations are highest near sources, its
               presence in places distant from primary sources indi-
               cates that it is reasonably stable in the atmosphere and
               capable of long distance transport. When released to air
               it may be subject to direct photolysis, although adsorption
               to particulates apparently can  retard this process. It may
October 1995
         Technical Versioni
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also be removed by reaction with ozone (half-life 37 min)
and NO2 (half-life 7 days), and an estimated half-life for
reaction with photochemically produced hydroxyl radi-
cals is 21.49 hr.
   If released to water, it will be expected to adsorb very
strongly to sediments and particulate matter. It will not
hydrolyze. It has been shown to be susceptible to signifi-
cant metabolism  by microorganisms in some natural
waters without use as carbon or energy source, but in
most waters and in sediments it is stable towards biodeg-
radation. BaP will be expected  to undergo significant
photodegradation near the surface of waters. Evapora-
tion may be significant  with a predicted half-life of 43
days. However, adsorption to sediments and participates
may significantly retard  biodegradation, photodegrada-
tion, and evaporation.
   If released to soil it will be expected to adsorb very
strongly and will not be expected to leach to the ground-
water.  However,  its presence in some groundwater
samples indicates that it can be transported there by
some mechanism. It will not hydrolyze, and evaporation
from soils arid surfaces is not expected to be significant.
Biodegradation tests in soils have resulted in a wide
range of reported half-lives: 2 days to 1.9 yr. Based on
these values and the apparent lack  of a significant
competing fate process, biodegradation may be an im-
portant process in soils.
   Benzo(a)pyrene is expected to bioconcentrate  in
aquatic organisms that can not metabolize it.  Reported
BCFs include: Oysters, 3000; Rainbow trout, 920; Blue-
gills, 2,657; zooplankton, 1000 to 13,000. The presence
of humic acid in solution has been shown to decrease
bioconcentration. Those organisms which lack a meta-
bolic detoxification enzyme system, tend to accumulate
polycyclic aromatic hydrocarbons. For example, BCFs
have been found to be  very low (<1) for mudsuckers,
sculpins and sand dabs.
   Human exposure will  be from inhalation  of contami-
nated air and consumption of contaminated food and
water.  Especially high exposure will occur through the
smoking of cigarettes and the ingestion of certain foods
(eg smoked and charcoal broiled meats and fish).
         OTHER REGULATORY INFORMATION
         MONITORING:
         FOR GROUND/SURFACE WATER SOURCES:
           INITIAL FREQUENCY-  4 quarterly samples every 3 years
           REPEAT FREQUENCY- If no detections during initial round:
                         2 quarterly per year if serving >3300 persons;
                         1 sample per 3 years for smaller systems
         TRIGGERS - Return to Initial Freq. if detect at > 0.00002 mg/L

             /
         ANALYSIS:
         REFERENCE SOURCE             METHOD NUMBERS
         EPA 600/4-88-039             525.1; 550; 550.1


         TREATMENT:
         BEST AVAILABLE TECHNOLOGIES
         Granular Activated Charcoal
             \

         FOR ADDITIONAL INFORMATION:
         * EPA can provide further regulatory and other general information:
         • EPA Safe Drinking Water Hotline - 800/426-4791


         4 Other sources of lexicological and environmental fate data include:
         • Toxic Substance Control Act Information Line - 202/554-1404
         • Toxics Release Inventory, National Library of Medicine - 301/496-6531
         • Agency for Toxic Substances and Disease Registry - 404/639-6000
October 1995
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