SIGNIFICANT HAR^, LEVELS FOR CARBON MONOXIDE
                   DRAF
   U.S.  ENVIRONMENTAL DROTECTION AGENCY
                 JULY 1380

-------
                  SIGNIFICANT HARM LEVELS FOR CARBON MONOXIDE

     "Significant harm levels" for criteria pollutants are those ambient
concentrations of the pollutants associated with specific adverse health
effects which create "an imminent and substantial endangerment to the health
of persons."
     As stated in the Federal Register, Vol. 40, No. 162, p.  36333, August 20,
1975:
          Life threatening or permanently disabling exposures are clearly
          serious threats to health.   Reversible but acutely incapacitating
          health effects also would be sufficiently disturbing to the
          general public to require remedial action.  It is our opinion
          that both of these do, in fact, constitute "significant harm."
     In 1971, the following "significant harm level" was established for
carbon monoxide (CO):
                         50 ppm	 8-hr average
                         75 ppm 	 4-hr average
                        125 ppm 	 1-hr average
     The purpose of this paper is to identify adverse health effects, which
have been documented in scientific journals, associated with exposure of
humans to levels of CO which may cause significant harm.
Health Effects of Carbon Monoxide
     Health effects of CO are presently thought to be caused primarily by a
reduction in the ability of the blood to transport oxygen (02) and a consequent
interference with biochemical utilization of 02 in tissues.   The toxicity of
CO is due to strong coordination bonds formed between CO and the iron atoms in
hemoglobin (Hb).  Carbon monoxide and Hb interact in the blood to form carboxy-
hemoglobin (COHb).

-------
 The  attraction  between  CO  and  Hb  is  more than 200 times stronger than the
"attraction  between  Q~ and  Hb and  effectively eliminates the binding site from
 the  normal  transport of O^.  Myoglobin  also  exhibits  a very strong affinity
 for  CO;  however,  muscle impairment  has  not yet been clearly demonstrated.
      All  humans have some  level of  CO  in their circulatory systems.   The
 normal catabolism of Hb results in  endogenous levels  of between 0.3 to 0.7
              2
 percent  COHb.    Levels  above this can  normally be assumed to result from
 exogenous sources.   It  is  important  to  note  that high variability in COHb
 concentrations  is commonly found  between individuals  both for endogenous COHb
 production  and  for  COHb concentrations  resulting from exposure to similar
 ambient  CO  levels.  This is demonstrated by  the effect of exercise on COHb
 levels as shown in  Table 1.
      Health effects which  have been  attributed to CO  exposure at or near
 significant harm levels include:  (1)  aggravation of  angina pectoris,
 intermittent claudication,  and peripheral  arteriosclerosis;  (2) decreased
 exercise capacity in normal persons  and in patients with chronic obstructive
 pulmonary disease,  angina  pectoris,  intermittent claudication and peripheral
 arteriosclerosis; (3) changes  in  heart  functioning and possible impairment;
 (4)  reduced birth weight;  and  (5) impairment of vigilance,  visual  perception,
 manual dexterity, ability  to learn,  and performance on complex sensorimotor
 tasks, such as  driving.   The above  health  effects are summarized in  Table  2
 along with  references and  the  ranges of specific levels of CO exposure
 associated  with the health effects.
      Presently, the scientific community recognizes two general  classifications
 of health effects associated with CO exposure.   These are cardiovascular effects

-------
                TABLE 1.   PERCENT COHb AS A FUNCTION OF CO EXPOSURE

                       PERCENT COHb BASED ON COBURN EQUATION3
CO
(ppm)
5.0
9.0
15.0
20.0
25.0
35.0
50.0

Resting
0.6
0.7
1.0
1.1
1.3
1.6
2.2
1
Moderate
Exercise
0.6
0.8
1.1
1.4
1.6
2.1
2.9
Exposure Time (Hours)
2 4
Resting
0.
0.
1.
1.
1.
2.
3.
7
9
3
6
9
5
5
Moderate
Exercise
0.7
1.0
1.5
2.0
2.4
3.2
4.5
Resting
0.8
1.2
1.8
2.3
2.8
3.8
5.2
Moderate
Exercise
0.8
1.3
2.0
2.6
3.2
4.5
6.3
Resting
0.
1.
2.
2.
3.
4.
7.
9
4
2
9
6
9
0
8
Moderate
Exercise
0.9
1.5
2.4
3.1
3.8
5.3
7.6
% COHb at
Equilibrium
Based on
Haldane
Equation
0.9
1.6
-
3.5
-
-
8.2
Assumed conditions:   Alveolar ventilation rates:   resting = 10 L/min,
                        moderate exercise = 20 L/min (equivalent to 3
                        mph walk on level ground or light industry or housework);
                        hemoglobin - 15 g/100 mL (normal); altitude = sea level;
                        endogenous COHb level =0.5 percent.

-------
    TABLE 2.   ESTIMATED HEALTH EFFECTS LEVELS FOR CARBON MONOXIDE  EXPOSURE
     Effects
  COHb concen-  .
tration, percent5
    References
Passive smoking aggravates            1.8-2.3
angina pectoris

Decreased exercise capacity           2.5-3.0
in patients with angina pec-
toris, intermittent claudica-
tion, or peripheral arterio-
sclerosis

Impairment of vigilance tasks         3.0-7.6
in healthy experimental subjects
Decreased exercise performance        3.0-4.9
in normal persons and in
patients with chronic obstructive
pulmonary disease

Increased angina attacks for
freeway travel

Changes in heart functioning
and possible impairment


Linear relationship between COHb
and decreasing maximal oxygen
consumption during strenuous
exercise in young healthy men

Statistically significant diminu-     5-17
tion of visual perception, manual
dexterity, ability to learn, or
performance in complex sensorimotor
tasks (such as driving)
     3.8-8.0


     3.9-5.0



     5-20
                         Aronow, 1978
                         Anderson et al., 1973
                         Aronow and Isbell, 1973
                         Aronow et al., 1974
                         Aronow and Rokaw, 1971
                         Horvath et al. ,  1971
                         Groll-Knapp et al., 1972
                         Fodor and Winneke, 1972

                         Aronow and Cassidy, 1975
                         Aronow et al., 1977
Aronow et al., 1972
Aronow et al., 1974
Ayres et al.,  1969
Ayres et al.,  1970

Ekblom and Huot, 1972
Horvath, 1975
Dahms et al.,  1975
Seppanen, 1977

Bender, et al., 1971
Schulte, 1973
O'Donnell et al.,  1971
McFarland, 1973
Putz et al., 1976
Salvatore, 1974
Wright et al.,  1973
Rockwell and Weir, 1975
Rummo and Sarlanis, 1974
 The physiologic norm (i.e., COHb Levels resulting from the normal metabolic
 breakdown of hemoglobin and other heme-containing materials) has been
 estimated to be in the range of 0.3 to 0.7 percent.

-------
 and central  nervous  system  effects.  There  has  been  evidence  presented  that  CO
 toxicity may be,  at  least in  part,  due  to non-hypoxic  inhibition  of  oxidase
 enzymes;   however, this  has not yet been clearly  demonstrated or  accepted  by
 the scientific  community.
•Cardiovascular  Effects
                                                                                4
      Cardiovascular  failure is the  leading  cause  of  death  in  the  United States.
 What  portion of these deaths  can  be directly  or indirectly attributed to CO
 exposure remains  uncertain.   It has been stated that a large  segment of the
 population over forty, possibly as  large as one-half,  may  have sufficiently
 defective  cardiovasculatures  to be  susceptible  to adverse  health  effects
 associated with CO concentrations commonly  found  in  urban  air.
      It  is well  documented  that persons suffering from angina pectoris  will
 experience early  onset of pain from angina  attacks after an 8-hr  equivalent
                                                                              6-9
 exposure to CO  concentrations of  15 to  18 ppm (2.5 percent COHb)  and exercise.
 This  effect is  thought to be  the  result of  an oxygen debt  caused  by  a defective
 cardiovasculature in conjunction  with a reduced blood  02 supply.  This  blood
 OP  supply, which  is  inversely related to CO exposure,  will  continue  to  decrease
 as  CO concentrations increase.
      Studies conducted at ambient CO concentrations  sufficient to achieve  COHb
 levels of  5-10  percent have shown changes in  myocardial metabolism and  possible
 impairment.   '     As a result of  studies in which 26 men between  the ages  of
 41  and 60  were  exposed to 100 ppm of CO for four  hours, it was suggested "that
 exposure to low,levels of CO  may  worsen myocardial ischemia,  impair  myocardial
 function and enhance development  of arrhythmias during exercise in a large
 segment  of the  population	"    Other results suggest that  COHb concentrations
 of  5  percent interfere with oxygen  delivery to  the myocardium.    Carbon

-------
monoxide not only hastens development of atherosclerosis but has a sufficiently
damaging effect on myocardial tissue to worsen the effects of coronary occlu-
sions.18'19
     At significant harm levels for CO, it could be expected that persons who
otherwise might have been considered normal could begin to experience adverse
health effects caused by CO exposure.   Those individuals who have a pre-exist-
ing oxygen debt (e.g., anemics, asthmatics, angina patients, fetuses) will
very likely find their conditions exacerbated at these CO levels.  Although
the extent to which any individual is affected depends upon the physiology,
exercise and exposure patterns of that person, it can be stated that an 8-hr
exposure to 50 ppm CO (7-8 percent COHb) would create adverse cardiovascular
effects in a large segment of the U.  S. population.
Central Nervous System
     Health effects associated with.the central nervous system (CNS) do not
begin to consistently appear in most individuals until equivalent 8-hr expo-
sures of 35-40 ppm CO (5 percent COHb) are experienced.  Early studies suggesting
effects at levels as low as 2.5 to 3 percent COHb have not been replicated and
are not presently considered to reflect the level of effect for the CNS in
                   20 21
normal individuals.  '
     Many studies have documented an impairment of vigilance in healthy experi-
                22 23 24
mental subjects.   '  '    In one study, the impairment was due to exposure of
subjects to levels of CO (average 26 ppm and peak 111 ppm) found while driving
                 2?
in urban traffic.    It was suggested that persons who sustain increases in
COHb saturation of more than about 2 percent to 3 percent may become less
effective in coping effectively with unexpected events and more likely to
perform routine tasks in an inefficient manner.

-------
     Significant decrements were found in several measures of vigilance in a
simulated driving task following exposure of subjects to levels of CO sufficient
                               25
to produce 6 to 8 percent COHb.     Even at levels as low as 3.4 percent COHb,
                                                              26
it was shown that the ability to drive safely may be impaired.
     Numerous other studies suggest a significant diminution of visual perception,
manual dexterity, and ability to learn after CO exposures resulting in 5
                           07-33
percent to 10 percent COHb.       The implications of such effects should be
evident.
     The long-term exposure impacts have not yet been well characterized for
the CNS.   Studies have not been performed and published for persons with
impaired cerebrovasculatures.   However, the reduction in vigilance and manual
dexterity associated with significant harm levels of CO may result in an
increase in automobile accidents and in job-related or household accidents.
The reduction in ability to learn may begin to play an important role in
hindering the learning process of school children exposed to significant harm
levels of CO.
Conclusions
     The present significant harm standards appear to adequately protect
normal individuals in the United States.  However, there may be groups
constituting a significant portion of the population of the United States
with extensive cardiovascular or cerebrovascular damage.  Individuals in these
groups may show adverse health effects below significant harm levels.
     In comments by the Senate Committee on Public Works, the Committee stated
that "emergency authority is necessary to provide for immediate, effective
action whenever air pollution agents reach levels of concentration that are
associated with:  (1) the production of significant health effects,

-------
(2) incapacitating body damage, or (3) irreversible body damage in any



significant portion of the general populations.   The term "significant portion



[was] not intended to exclude sensitive elements of society such as asthmatics,



but only those groups of particularly susceptible persons for whom other



precautionary measures should be taken.   Secondly, the emergency situation


                                                                         34
exists whenever there is any perceptible increase in the mortality rate."

-------
REFERENCES


 1.   1970 Clean Air Act, Section 303.

 2.   Coburn, R. F., R. E. Forster, and P. B. Kane.  Considerations  of  the
     physiological and variables that determine the blood carboxyhemoglobin
     concentration in man.  J. Clin. Invest. 44:1899-1910,  1965.

 3.   Goldbaum, L.  R., T. Orellano, and E. Oergal.  Mechanism of  the toxic
     action of carbon monoxide.  Ann. Clin. Lab.  Sci. 6:372-376,  1976.

 4.   National Center for Disease Control, U.S. Environmental Health Services
     Division.  Occupational exposure to CO in selected rural work  environments.
     Atlanta, GA,  1973.

 5.   Transcript of CASAC CO Subcommittee meeting  January 30-31,  1979.  (Office
     of General Counsel and ECAO)

 6.   Aronow, W. S.  Effect of passive smoking on  angina pectoris.   N.  Engl. J.
     Med. 299:21-24,  1978.

 7.   Aronow, W. S., and S. N. Rokaw.  Carboxyhemoglobin caused by smoking
     non-nicotine cigarettes:  effects in Angina  Pectoris.  Circulation
     44:782-788, 1971.

 8.   Anderson, E.  W., R. J. Andelman, J. M. Strauch, N. J.  Fortuin,  and
     J. H. Knelson.  Effect of low-level carbon monoxide exposure on onset and
     duration of angina pectoris:  A study on 10  patients with ischemic  heart
     disease.  Ann. Intern. Med. 79:46-50, 1973.

 9.   Aronow, W. S., C. N. Harris, M. W.  Isbell, S. N. Rokaw, and  B.  Imparato.
     Effect of freeway travel on angina  pectoris.  Ann. Intern. Med. 77:669-676,
     1972.

10.   Aronow, W. S., J. Cassidy, J. S. Vangrow, H. March, J. C. Kern, J.
     R. Goldsmith, M. Khemka, J. Pagano, and M.  Vawter.  Effect  of  cigarette
     smoking and breathing carbon monoxide on cardiovascular hemodynamics on
     anginal patients.  Circulation 50:340-347, 1974.

11.   Aronow, W. S., E. A. Stemmer, and M. W. Isbell.  Effect of  carbon monoxide
     exposure on intermittent claudication.  Circulation 49:415-417, 1974.

12.   Aronow, W. S., and M. W. Isbell.  Carbon monoxide effect on  exercise-induced
     angina pectoris.  Ann. Intern. Med. 79:392-395, 1973.

13.   Aronow, W. S., and J. Cassidy.  Effect of carbon monoxide on maximal
     treadmill exercise:  A study in normal persons.  Ann.  Intern.  Med.  83:496-499,
     1975.

-------
14.   Aronow, W. S. ,  J. Ferlinz, and F. Glauser.   Effect  of  carbon  monoxide on
     exercise performance in chronic obstructive  pulmonary  disease.   Am.  J.
     Med.  53:904-908, 1977.

15.   Ayres, S. M., H. S.  Mueller, J. J. Gregory,  S. Giannelli,  Jr.,  and J.  L.  Penny.
     Systemic and myocardial hemodynamic responses  to  relatively small  concentra-
     tions of carboxyhemoglobin (COHb).  Arch.  Environ.  Health  18:699-709,
     1969.

16.   Knelson, J. H.   Discussion of the Carbon Monoxide Standards for the
     Federal German Republic:  lr\:  Carbon Monoxide - Origin, Measurement,  and
     Air Quality Criteria.  VOI Berichte No. 180, 1972,  pp.  120-124,  Pro-
     ceedings of the Colloquium Held in Dusseldorf October  28-29,  1971.
     Reprinted from Staub Reinhalt.  Luft 32(4),  April 1972.

17.   Ayres, S. M., S. Giannelli, Jr., H. Mueller.  Myocardial and  systemic
     responses to carboxyhemoglobin.  Ln:  Biological effects of carbon
     monoxide, R.  F.  Coburn, ed.  Ann. N.Y. Acad. Sci. 174(Art. l):268-293,
     October 5, 1970.

18.   Astrup, P.  Some physiological and pathological effects of moderate
     carbon monoxide exposure.  Br. Med. J. 4:447-452, 1972.

19.   Astrup, P.  Carbon monoxide, smoking and cardiovascular disease.
     Circulation 48:1167-1168, 1973.

20.   Beard, R. R., and G. A. Wertheim.  Behavioral impairment associated with
     small doses of carbon monoxide.  Am. J. Public Health  57:2012-2022,  1967.

21.   Beard, R. R., and N. W. Grandstaff.  Carbon  monoxide and human  functions.
     In:  Behavioral  Toxicology. B. Weiss and V.  G. Laties, eds.,  Plenum
     Press, New York, 1975.   pp. 1-26.

22.   Horvath, S. M.,  T. E. Dahms, and J. F. O'Hanlon.  Carbon monoxide  and
     human vigilance.  A deleterious effect of  present urban concentrations.
     Arch. Environ.  Health 23:343-347, 1971.

23.   Groll-Knapp,  E., H.  Wagner, H. Hauck, and  M. Haider.   Effects of low
     carbon monoxide concentrations on vigilance  and computer-analyzed  brain
     potentials.  Staub Reinhalt. Luft 32:64-68,  1972.

24.   Fodor, G. G., and G. Winneke.  Effect of low CO concentrations  on
     resistance to monotony and on psychomotor  capacity.   Staub Reinhalt. Luft
     32:46-54, 1972.

25.   Rummo, N., and K. Sarlanis.  The effect of carbon monoxide on several
     measures of vigilance in a simulated driving task.  J.  Saf. Res. 6:126-130,
     1974.

26.   Wright, G., P.  Randell, and R. J.  Shephard.  Carbon monoxide and driving
     skills.  Arch.  Environ. Health 27:349-354, 1973.

27.   Bender, W., M.  Gothert, G. Malorny, and P. Sebbesse.   Effects of low
     carbon monoxide concentrations in man.  Arch. Toxicol.  £7:142-158,  1971.


                                     10

-------
28.   Schulte, J.  H.   Effects of mild carbon monoxide intoxication.  Arch.
     Environ. Health 7:524-530, 1973.

29.   O'Donnell, R.  D.,  P. Chikos, and J. Theodore.  Effect of carbon monoxide
     exposure on human sleep and psychomotor performance.  J. Appl. Physio!.
     31:513-518,  1971.

30.   McFarland, R.  A.,  W. H. Forbes, H. J. Stoudt, J. D. Dougherty, T. J. Crowley,
     R.  C. Moore, and T.  J.  Nalwalk.  A Study of the Effects of Low Levels  of
     Carbon Monoxide upon Humans Performing Driving Tasks.  Final Report.
     Harvard University,  Guggenheim Center for Aerospace Health and Safety,
     Boston, MA,  May 1973.

31.   Putz, V. R., B. L. Johnson, and J. V. Setzer.  Effects of CO on Vigilance
     Performance.  Effects of Low Level Carbon Monoxide on Divided Attention,
     Pitch Discrimination, and the Auditory Evoked Potential.  DHEW (NIOSH)
     Publication No. 77-124, U.S. Department of Health, Education, and Welfare,
     National Institute of Occupational Safety and Health, Cincinnati, OH,
     November, 1976.

32.   Salvatore, S.   Performance decrement caused by mild carbon monoxide
     levels on two visual functions.  J. Saf.  Res. 6:131-134, 1974.

33.   Rockwell, T. J., and F. W. Weir.  The Interactive Effects of Carbon
     Monoxide and Alcohol on Driving Skills.   Ohio State University Research
     Foundation,  Columbus, OH, January 1975.

34.   Library of Congress, Committee on Public Works, U.S. Senate.  A Legislative
     History of the Clean Air Amendments of 1970, Committee Print Serial No.
     93-18, January 1974.
                                     11

-------