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 ------- |