Document 06Qb8qrdONxrbMYqmJrZgpmLR
TESTIMONY OF RICHARD J. HUGHES Vice President of Union Carbide Corporation
Before Department of Labor Occupational Safety and* Health
Administration Vinyl Chloride Occupational Exposure Standard
Hy name is Richard J. Hughes. I am Uhion Carbide's Chemicals and Plastics Vice President, and I have served with the Company for over 25 years in this area. I intend to present the position of the Company, a New York Corporation with headquarters, at 270 Park Avenue in New York City, with respect to the proposed OSHA standard on vinyl chloride, 29 CFR Part 1910, Section 1910.93g. We are and have been for 38 years a substantial manufacturer of polyvinyl chloride homopolymer and copolymer resins from vinyl chloride gas or monomer. Uhlon Carbide helped develop the monomer in 1938, but we no longer make it ourselves. In other Corporate divisions, we are also a substantial user and fabricator of various products from the polyvinyl chloride resin.
Our interest in the development of a workable standard has coincided with the initiation of OSHA proposals for such action. We submitted a position paper on March 5> 197^ to the preliminary OSHA hearings on this matter held in Washington before Administrative Law Judge Gordon J. Myatt in which we stated that:
While we saw no need for a temporary emergency standard, where no emergency existed, vie welcomed the initiation of the regular
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rule-making procedure under Section 6 (b) of the Act, in which we are now participating, because it afforded a highly useful oppor tunity to investigate and review thoroughly and objectively the potential problems of vinyl chloride monomer handling practices in industry. We were concerned that standards would be set without proper exploration of all phases of the matter. The institution and conduct of the present hearing accorda with our stated objectives.
Our position in this situation is four-fold and may be summarized as follows:
1. There is no medical evidence provided by OSHA or NIOSH to justify the proposed OSHA standard of no detectable level of exposure, which evidence is required by statute. The evidence, set forth below, shows no need of such a restrictive limit.
2. We accept the temporary standard of 50 parts per million exposure level as safe. We support the SPX position as to
s lower levels of exposure. In fact, no tangible evidence has been presented at the present hearings that proves any lesser exposure is unsafe to humans.
3. We accept as a goal, a program to do whatever is technologically feasible to further reduce employee exposure to vinyl chloride.
4. We have an alternative proposal for OSHA, since we are sensitive to this problem and do not wish merely to be negative, as follows:
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We recoMend that OSHA proceed to establish a uniform regulatory work practice standard as suggested in draft language carefully prepared by Mr. R. N. Wheeler, Jr., and reviewed by many others. Some of the principles that appear therein have already been reflected in the proposed standard; others have not. We have already submitted it to OSHA on June 27, 1974 at this hearing, with
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the strong recommendation that it be carefully considered in the final rule-making. We have also submitted on the same date numerous com ments on the proposed OSHA rule, which reinforces our view that it should be replaced with the standard we suggest.
We take this position for the simple reason that there has been no demonstration whatever that worker exposure to vinyl chloride monomer is hazardous at low levels of airborne concentration. Our own experience tends to document this contention. Little or no benefit or potential benefit to employees from over-stringent regu lation has been shown, and industry statements and evidence on the economic impact of such action should cause concern over the continued ability of the producers tocontinue to operate.There is no legal warrant whatever, as the courts have already ruled, for establishing a standard at levels which no evidence supports. The OSHA statute permits court approval of a standard promulgated by the Department only if it is buttressed by substantial evidence on the record as a whole. Associated Industries v. Department of Labor, 437 Fed. 2d 342 (CCA2, 1973).
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We do agree, of course, that our goal should be, wherever possible, to limit the exposure of employees by adoption of those engineering techniques and administration which are feasible. We agree that we should do whatever we can to install all technically feasible controls, and to continue to adopt safe and progressive work practices. Our concern, however, is that goals and legal requirements are two different things. A regulation should not presently require that which is achievable only in the future after the attainment of knowledge and technology that we do not yet have.
It should be emphatically stated that OSHA's proposed permanent standard cannot possibly be met through application of any known technology today, regardless of cost. In short, industry does not know how to comply with the recommendation. Adoption of the proposal as law would face the industry with the clear choice of either: (l) requiring its employees exposed to the extremely low levels of concentrations to wear clothing and respirators which are dangerous; cumbersome; uncomfortable; and resentment-building; which cause losses of employee productivity that will average up to 50 percent or more; and engaging in costly and time-consuming administrative monitoring, surveillance and record keeping; or (2) simply stopping production of the resin altogether with all the consequences that would ensue in the market place.
Indeed, it is not too much to say that the OSIIA-proposed levels of exposure are unattainable, and unenforceable in practice
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especially where non-continuous monitoring is adopted, even if such monitoring is faithfully carried out. One problem lies in the expected employee resistance to its effectuation, as a practical matter. It also would be simply impossible in many cases to ascertain whether a detectable level of vinyl chloride monomer has appeared in a given area, especially if, as occurs with most excursions, it would persist for only short periods of time.
Since no evidence that advanced engineering and modified production practices could ever achieve operations meeting a nondetectable level of vinyl chloride in the work-place air, the proposed standard will require, as a practical matter, all personnel in any restricted area to make 100 percent use of respirators at all times or for a major portion of the work day. Union Carbide holds that It is Impractical and unsafe for employees to work regularly and routinely with respirators such as are required by the proposed standard. Considerable persuasive testimony has already been presented to this same effect at this hearing. The use of respirators should be considered only as a temporary practice when atmospheric levels of monomer rise above the permitted maximum and should be required only until corrective measures have been taken to bring the level of vinyl chloride down to or below the permitted maximum. As to respirator use, we submit that:
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1. Due to current configuration of our plants, the fact that batch processing is employed, and the state of technology, the practical effect of the proposed permanent standard will be to require employees to wear respirators 100 percent of their time spent in the regulated area as described by the work standard.
2. It is difficult to imagine that workers in regulated areas would be willing to remain employed under these untenable conditions. Heat exposure; lack of mobility; severe limitations on communications with fellow workers; and the physical burden of respirator equipment will greatly lower employee morale over an extended period.
3. Workmen restricted by respirator equipment can precipitate safety problems due to awkwardness; limited ability to move to and from a unit due to emergency; restrictions on visibility; and fatigue from carrying and dragging cumbersome equipment.
4. Certain maintenance and operating tasks cannot be accomplished physically when a respirator is worn. The radius of activity is severely limited by length of hose, number and location of air supply outlets, and the weight and bulk of the respirator support apparatus. Moreover, the requirement of constantly check ing supply source and hose to ensure operability is a burden.
Union Carbide has devoted much research, engineering, and production talent to bring its existing polyvinyl chloride
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plants simply to meet the present standards and, thus, to minimize the time employees in the restricted areas need wear respirators, as required by the standard now in effect. We have uncovered no engineering approach to reduce vinyl chloride emissions to a non detec table level. Relief from the standard that employees be required to wear respirators 100 percent of their time spent in the regulated area must come from the setting of practical levels of permitted monomer exposure.
The actual hazard, moreover, that is posed by any exposure of employees to vinyl chloride monomer is in fact a very limited one. It is always useful therefore to define what we are guarding against. Insufficient attention has to date been given to that simple fundamental; and the proposed standard itself avoids coming to grips with the matter. Instead, it attempts to settle the question by effectively forbidding all detectable exposure. Clearly this is ''safe", but it hardly answers the problem. Indeed, it
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seems plainly to contravene the OSHA statute which abjures the Secretary to:
"set the standard which most adequately assures, to the extent feasible, on the basis of the best available evidence that no employee will suffer material impairment of health or functional capacity." 29 USC Sec. 655 (b) (5). The proposed standard hardly complies with that statutory command.
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Yet there does appear to be a hazard to be met; and we agree with meeting it. What that hazard has been shown to be at this point is, that long-term exposure of employees on a continuous basis to vinyl chloride monomer emissions at high concentrations may cause liver angiosarcoma in some cases where inhalation takes place. The proposed standard is unnecessarily restrictive, technically and economically, in terms of such a limited hazard.
At this point, it would be appropriate to define areas where the proposed standard need not go at all. Thus, employees of resin fabricators, or any employee whose only potential contact with vinyl chloride monomer is to resihs or products containing polyvinyl chloride resins whose retained monomer is less than .1 percent by weight, are exposed to no hazard and need no regulatory protection.
There is no need to be concerned about exposure to the polyvinyl chloride resin as such; it is chemically inert, not only as resin but also in the form of fabricated or mixed product. OSHA's nuisance dust standard with adequate ventilation adequately covers any exposure thereto. We need be concerned solely about the hazard said to result from exposure to the gaseous monomer, either during its own production; or during its reaction with other ingredients which produce the polymers; or retained in the resin and released into the atmosphere.
There has been, moreover, no showing that the monomer in its usual gaseous state causes any deleterious results by contact
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with the skin, nor by Ingestion. The retention of monomer on skin
or clothing is unlikely because the product is volatile and non
adhesive, even where liquid monomer spills occur; a low boiling
point assures such volatility. There could possible be some
absorption through the skin, but the percentage is not known, nor
has it been shown or claimed to have had adverse effects. A limi
tation will certainly pose no greater hazard to the skin than to
the lungs.
So the hazard we need to meet is that of potential
angiosarcoma after long-term inhalation exposure at high concen
trations. Nothing else has been shown hazardous; any other hazard
is simply speculation and nothing more, plainly not the sort of
thing that would support a rule of laitf.
The proposed vinyl chloride monomer exposure standard of
"no detectable level" in polymer operations implies that the health
of workmen will be impaired materially if exposed even to traces of
vinyl chloride. We know of no human or other medical data to sup
port this conclusion. Actually, human experience in polyvinyl
chloride plants operated by Uhion Carbide refutes it completely.
The solvent process
as operated by Union Carbide at
Texas City has remained essentially unchanged as to process, recipe.
(1) This is a process unique to Union Carbide, producing resins suitable for coating use.
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equipment and operating procedure since about 1953. Its vinyl chloride emission are presently the same as has been experienced regularly over the past 20 years. Furthermore, measurements of vinyl chloride, monomer in the workplace air and of exposure of operators to monomer made recently, are representative of the continuing condition since 1953.
Measurements during the first quarter of 1974 established that operators in the polymerization section of this plant were exposed to levels of vinyl chloride approximating 30 parts per million on an eight-hour time weighted average basis. Included in the tasks assigned to these operators is the taking and testing of autoclave samples to determine degree of conversion. During sampling and testing, which occurs four times each shift and requires about eight minutes to complete, workplace environmental levels can range as high as 400 parts per million in the sampling area. (We have taken steps to eliminate the need for this procedure).
Exposure time has been gathered on all of the 54 employees working in this Job at the Texas City plant from 1948 to date. Twenty-four have from one to twelve years work experience on this Job; two employees have had twelve years or more of exposure. No unusual liver function test results have been found based on a recent review of the medical evidence in the records.
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In Union Carbide polyvinyl chloride suspension resin
operations, the business realities since 1965 resulted in improved
efficiencies in conversion' of vinyl chloride monomer to polymer
through modification of operating procedures and plant facilities.
Increases in monomer efficiency (Polymer/Monomer charged x 100)
from 85 percent in 1968 to 96 percent in 1974 at our Texas City
plant have been and are being realized. Improved machinery for
recovering the monomer from vapors released in venting and strip
ping sections accounts for more than half of the improvement which
resulted in significant reductions in monomer emitted into the
workplace atmosphere.
Recent measurements within polyvinyl chloride suspension
operations established that maximum vinyl chloride level's in the
workplace air approximated 30 parts per million time weighted average (eight-hour) at a ceiling of 45 parts per million. Based
on the known improvement in monomer efficiency, it is certain that the vinyl chloride monomer levels in the 1974 workplace environment
are significantly below those of the prior years.'
Here too, health records of employees at Texas City show
no deterioration in the health of the workmen exposed during this
period.
The Union Carbide experience is instructive in another
respect. We operate several plants xvhlch fabricate a variety of
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products from the polyvinyl chloride resin* Monitoring of our resin-handling at our fabrication plants show that the monomer levels (using a gas chromatograph sensitive to 0.15 parts per million) in the air around suspension resins rarely exceed 1 part per million at our calendars; 3-8 parts per million at our Banbury mixers; or an occasional "extreme" excursion to 18 parts per million in rare cases of exposure to the resin in the course of unloading. There has been discovered at those plants, moreover, after a check of employee medical records, not one case of angio sarcoma, nor any other liver or other disorder traceable to vinyl chloride. Many of our employees "exposed" to such concentrations are long-term employees who have worked on these substances for many years.
To return to the record at our Texas City plant, there have been 431 employees potentially exposed to vinyl chloride monomer at that location. This group includes all workers that could possibly have been so exposed. In it, there have been a total of 24 deaths since 1948. Not one has occurred from angiosarcoma. The exposure of these workers has, moreover, been lengthy and extensive. Seventy-four of them were exposed for more than 20 years. Ninety-seven were from 10 to 20 years. One-hundred ninety-one were exposed for 1 to 10 years, and 69 for less than one year.
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Exposure levels at Texas City, furthermore, parallel those of many other older plants in Union Carbide and the entire industry.
The memory of many employees attests to the frequent detection of vinyl chloride odor over the years. Levels above the odor threshold were often reached in the early days. A recent test of levels of airborne concentration of vinyl chloride monomer which could be detected by odor was conducted by a panel of seven at our South Charleston, West Virginia plant. It was discovered that none of the panel could detect the monomer by odor at 133; 350; or 680 parts per million. Two of the seven detected it at 1200 parts per million. All seven detected it at i960 and 3800 parts per million. The results support recent statements, including several made at the hearing, that vinyl chloride monomer levels in the past were far higher than thought initially. The limited dispersion of angiosarcoma in evidence found to date must be evaluated in the light of this knowledge.
Union Carbide has also produced polyvinyl chloride at our South Charleston, West Virginia, plant from 1936 to date. At one time, we also made the vinyl chloride monomer there; but dis continued such operations in 1968. After complete review of all available health records of a group of some 550 employees potentially exposed to vinyl chloride monomer at that location, where the early
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exposure levels were far heavier than at Texas City, there have been discovered two cases of angiosarcoma. One employee, deceased in 1968, was exposed for 18 years, from 1944 to 1962, at high vinyl chloride concentrations. The other, still living, was exposed to high and medium high concentrations for approximately 24 years (1944 to 1968). The exposures were continuous over the years.
Yet many other employees plainly and obviously have been subject to the same high exposure levels and have suffered no ill effects therefrom. It is noteworthy moreover, that both reported cases --the only ones discovered out of a total' of almost 1,000 Union Carbide polyvinyl producing employees reviev/ed-- were of individuals exposed in the earlier years of polyvinyl chloride production, when no concern about inhalation of the material was felt necessary. The only problem that arose then was at very high concentrations and was of flammability; employee protection was and is aimed at elimination of that hazard.
At one time, there was a body of medical opinion that felt that vinyl chloride monomer was useful as an ether substitute; other materials proved more adaptable as an anesthetic.
In operating polyvinyl chloride plants, we continue as in the past to give high priority to safe practices that will avoid the development of explosive concentrations of vinyl chloride mono mer in the plant atmosphere and will eliminate ignition sources.
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A defect in performance in this area of safety could lead to massive destruction of life and property. Thus, work practices must be written and carried out with avoidance of explosive concentrations and of ignition sources as the primary safety instruction regard less of exposure of workmen to monomer. As earlier indicated, such considerations did de-emphasize reliance on respirators as a safety device.
We therefore recommend that: (l) higher priority be given in the total safety procedure to isolating leaking pumps; sealing off ruptured lines; closing valves; blowing down autoclaves showing mechanical deficiencies; and taking all actions that will minimize the possibility of catastrophe from explosion and fire than to avoidance of exposure of workmen to even substantial concen trations of vinyl chloride for brief periods; (2) employees must be able to respond to upsets and emergency conditions not hampered by trailing airhoses or the 30-pound weight of a portable back-pack air supply; not immobilized by vapor-impervious clothing; and not cut off from vital communication by limited visibility and limited hearing; (3) it is sensible to accept a brief exposure to vinyl chloride monomer and thus to avoid a larger exposure or a greater hazard.
It is also noteviorthy that concentrations of vinyl chloride monomer have been reduced over the years at the various American
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producing plants, including our own. It is clearly a significant fact for these hearings that not one angiosarcoma case has occurred among the employees of a single one of the United States polyvinyl chloride producers whose operations began in or after 1950- It is also significant that, of the 13 Uhited States cases so far reported, the average exposure of all such employees has been 19 years at high concentrations (i.e. above the odor threshold level) and that most of them had an exposure period i/hose onset antedates 1950* Moreover, the exposures that have resulted in the 13 reported cases occurred at only four of the 36 Uhited States polyvinyl chloride producing plants. There are thus in the Uhited States, 13 monomer producing plants and 32 polyvinyl chloride resin producing plants where no cases have been reported at all.
The conclusion is inescapable that the only hazard of potential angiosarcoma against which protection for employees is currently required is that of long-term exposure to high concentrations of vinyl chloride monomer. A level of exposure based on our recognition of the actual hazard would, we believe implicitly, pose no risk to the health of employees that could be in any way termed abnormal. Any extra limitations required would clearly be unnecessarily burdensome, and add nothing to improving worker health.
This is borne out in the recently issued Taberuhaw-Cooper findings, released May 3* 1974, in which that organization reviewed
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the records of a total of 8,384 polyvinyl chloride-exposed employees of whom at least 1,500 had been exposed for fifteen years or more, and all of whom had had at least one year of exposure prior to December 31, 1972. The findings were that the mortality rate of this group was only 75 percent of what would be expected in a com parable group of the United States male population; and that no cause of death in the polyvinyl chloride group studied showed a statistically significant increase over a comparable non-exposed group; yet all reported United States angiosarcoma deaths of vinyl chloride monomer exposees were found. The only caveat issued by Tabershaw-Cooper was that liver cancer occurred "more often than expected" in "those members of the group with the greatest exposure"; but that several other forms of cancer occurred at lower levels than those normally expected. However, the incidence of occurrence of other forms of cancer was not statistically significant.
A comparable study in Great Britain covering a group of polyvinyl chloride workers completed early in 1973, showed no increased incidence of cancer among the exposed workers, as compared to a control population; yet the British airborne concentrations of * vinyl chloride monomer in 1973 were found to average 150 parts per million; from i960 to 1970, to range from 300 to 400 parts per million; and from 1955 1 i960, 400 to 500 parts per million.
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We also note with approval Dr. Dernehl's testimony reviewing an epidemiological survey whose conduct he oversaw which shows that liver abnormalities in the study group of employees exposed to vinyl chloride are comparable to those of employees in non-exposed control groups. Such a study of human reaction certainly does not suggest any need for an extraordinarily restrictive exposure level.
The only support, indeed, suggested for such restrictions has been studies not of humans but of rats and mice. The results of these studies, taken by themselves, are far from constituting conclusive or exhaustive proof of vinyl chloride monomer's carcinogenic effects at even the exposure levels set by the temporary standard currently in force.
Moreover, the transferability of mice studies to human experience is of dubious value. It is not known, indeed is doubtful, whether humans will react the same as mice to vinyl chloride monomer exposure. The only possible valid data that OSHA should consider in setting regulatory standards is that relating to humans. The wealth of such data confirms our belief that exposure at our recommended level is safe.
We are aware --and acutely so-- of the need of assuring every worker's health and safety. We have been in the forefront of such efforts for many years. Indeed, in 1973> our safety record was one of the best in the industry. Nevertheless, we see no merit
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in OSHA establishing unnecessarily restrictive rules in the light of what we have defined above as the actual known hazard. Where there is no reason for regulation, it is folly to attempt it.
Summarizing our position once again: 1. There is no medical evidence provided by OSHA or NIOSH to justify the proposed OSHA standard of no detectable level of exposure, which evidence is required by statute. The evidence, based on human data, shows no need of any such restrictive limit. 2. We accept the temporary standard of 50 parts per million exposure level as safe. We support the SPX position as to lower levels of exposure. No evidence has been presented at these hearings to prove any lesser exposure is unsafe to humans. 3. We accept as a goal a program to do whatever is technologically and economically feasible to further reduce employee exposure to vinyl chloride. 4. Since we are sensitive to the problem and do not wish merely to be negative, we have submitted an alternative proposal for an OSHA standard. There is merit in imposing limits on the vinyl chloride monomer and polyvinyl chloride manufacturers along the lines we have suggested. We believe that appropriate employee protection can result from their adoption.
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APPENDIX TO TESTIMONY OF RICHARD J. HUGHES
Vice President - Union Carbide Corporation Comments on Proposed Vinyl Chloride Occupational Exposure Standard and
Proposed Substitute Work Practice Standard The following comments with respect to specific provisions of the proposed standard are set forth. Each comment applies to the particular subsection of the proposed standard unless otherwise noted on the sense of the comment makes clear that It has broader application. The language of the section referred to is not repeated in the commends for the sake of brevity.
In addition to these comments, the appended Work Practices standard contains other recommendations for changes in language for the regulation for which comments were not deemed, necessary, or the suggested change was self-explanatory.
1. Sections (a) (1) and (2).The application and scope of the standard is very fair from clear, unnecessarily harsh and probably un nforceable as a practical matter. Particularly must the point of process at which the exemption of fabricated products therefrom applies be made more precise and specific. In addition, as more fully set forth below, the standard need not and should not apply to all working areas at all times but only where a high probability of release of vinyl chloride gas in excess of the suggested limits in fact takes place. Transfer pipelines, roadways, storage places
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the recommended exposure level figure set forth in the Work Practices standard recommendation.
6. Subsections (b) (8) and (9) The definition of "exposure11 is too broad, as is the failure to limit the term "emergency" to releases of large quantities of vinyl chloride monomer.
7. Subsection (b) (10) The term "fabricated product" should be changed to ^exclude and exempt polyvinyl chloride and fabricated product with a retained monomer content of not greater than 1/10 of 1 percent by weight. This is consistent with.our recommendation elsewhere made for exemption of the fabricators entirely, and would serve to clarify the otherwise murky dividing line between included and excluded operations.
8. Subsection (c) The reference to the College of American Pathologists is totally unclear and unnecessary for regulatory purposes. It should be eliminated.
9. Subsection (d) The requirement of a regulated area is unclear, particularly with respect to the physical extent of such an area. Obviously, the airborne concentrations of vinyl chloride will be greatest at the point of actual release and will diminish directly with the distance from that point. No allowance for that fundamental fact is made in Item (d). Moreover, a regulated area should not include an area where polyvinyl chloride is located
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which does not in fact release levels of monomer greater than the standard exposure levels. There is no need to make an entire plant, or an area where the resin is packaged, stored or used, or a rail line, or plant road, or pipeline into a regulated area, as the language here requires. Only those places where the probability of exposure above standard is high need to considered. We should like to expand further on this problem in a supplemental memo, as an appendix to this testimony.
10. Subsections (d) (2) and (3) Provision should be made for access to regulated areas and the keeping of records for other than employees of the employer. Records should not be required for individuals who only occasionally or infrequently enter such areas.
11. Section (e) The entire monitoring section is objected to as confusing and unclear. It is not understandable what is meant to "monitoring ... with a confidence level of 95 percent". Moreover, the method of monitoring is not set forth; Is should be not area monitoring in any case but breathing zone monitoring for employees in the regulated areas. These same objections would apply to the provisions regarding regulated areas and monitoring as well as respirator protection. We will submit an appendix hereto expanding further on this point.
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12. Subsection (e) (3) (ill) The term "observer" should be defined and this section should not permit such individuals to do other than monitoring when observing; moreover, observers should be required to provide their own equipment, etc. Unrestricted presence of observers could hamper and impede production operations.
13* Section (f) is objected to. It should be changed to require provision for protection only in the event of discovery of airborne concentrations which may result in exposure in excess of the standard. The term "detectable level" should be eliminated from this and the various other sections of the regulations where it is used and should be replaced with the above exposure level figure.
14. The term "feasible" engineering controls and work practice methods in Subsection (f) is totally unclear. Its provis ions, moreover, ere keyed to the proposed exposure limits of "no detectable levels". Thus, the entire section should be rewritten where such limits are not recommended. The provision of Subsection 4 hereof is unenforceable as well as being meaningless. This entire section on engineering controls and work practice methods should be redrafted. The same objection is made to the provision herein covering tests for equipment leaks and emissions. We submit an appendix here as well.
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15. Section (g) The requirement of respirators should be applied only in the event that airborne concentrations of greater than 50 parts per million in the regulated are are detected. We have already commented at length on the hazards, costs and produc tion loss that use of respirators involves. Use of such respirators should not be forbidden in situations where "feasible" engineering controls or v?ork practice methods are suggested. This limitation conflicts with the rest of the provisions of the standard.
16. The entire Subsection (h) as well as Subsection (b) (13) on protective clothing are objected to because no evidence exists that vinyl chloride is a hazard to employees other than by inhalation. The only possible useful protective clothing is, moreover, impervious, which carries with it many other problems of employee discomfort and health hazard, especially if worn for an eight-hour day. Skin contact with vinyl chloride has never been determined to represent a hazard and therefore no warrant exists for "protecting" an employee against that peril which does not xist. Removal of protective clothing in entering^ leaving the area is unnecessarily burdensome. Moreover, there is no authority in the Act for a standard to require an employer to pay for or provide such protection. Finally, even as written, both sections are wholly unclear and require considerable redrafting even if it is determined to retain them.
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17. The same objection applies to Section (1) Hygiene Facilities and Practices; showers and change rooms are unnecessary where protective clothing is unnecessary for example, where poly vinyl chloride powder is being handled. Showers could be made available, but should not be required.
18. Subsection (.1) (S) (iii) is self-contradictory. As a practical matter, liquid vinyl chloride monomer is rarely met; it volatizes too fast; has a low boiling point; and releases quickly. There will be only a freeze burn if spilled on skin, at worst.
19. Subsection (.1) (3) for the first time mentions the "fire hazards" of vinyl chloride. It does not specify any protective steps but leaves that to the imagination. However, this entire standard is aimed at preventing the alleged carcinogenic impact of vinyl chloride, and should not be confused by the interjection of other problems; if such problems deserve regulation they should be thoroughly reviewed and not left to a mere casual allusion without substance or meaning.
20. The signs and labels Section (k) should be reworded to accord with the attached comments, as set forth in the appended Work Practices standard.
21. Subsection (l) There are no procedures here set forth applicable to maintenance and decontamination. They need to be
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developed, and specified in such a way as to protect employees against actual hazards. The language here is vague and excessively general; it does not set forth, in short, a standard or a regula tion which the employee must meet but confines itself to mere phraseology.
It would be much better to avoid this entire problem and simply rely on requiring adherence to the appropriate exposure levels as distinguished from saying that "something has to be done" regardless of what those levels are. This section is unduly restrictive where it has any meaning at all.
Note here the suggestions in the attached Work Practices standard recommendation.
22. Section fm) The same comments as made in Section (1) apply here. The reliance of the rule should not be on.unnecessarily restrictive regulation but adherence to the exposure levels required. The means of adherence need not be specified in such a way as to proliferate the chance of technical violations without real substance.
23* Subsection (n) is confusing and unnecessary unless the intent of the standard is to permit handling of polymer outside a regulated area. If that is the intent, it is in hopeless conflict with the rest of the standard.
24. Section (nO The handling of polymers is normally not a hazard since the resin generally does not release vinyl
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chloride in any quantity without the application of heat. This section should he applicable only in the event levels of airborne concentration in the area of the polymer resins exceeds 50 parts per million.
25. Subsection (o) A medical surveillance program similar to that provided under OSHA's carcinogens standards should be required of employees assigned to regulated areas as set forth in this standard. Medical exams should be made mandatory for such employees, not merely be given as an "opportunity" which can be rejected. There should be no requirement that the employe^ must pay the entire cost thereof. That is no part of this regulation, and is contrary to the Act.
26. The reporting provision of Section (q) needs rewording. In many cases it is impossible to specify the amount of vinyl chloride monomer "released". In many other cases, release of vinyl chloride in an area where employees "may be exposed" is impossible to ascertain. (Reporting of incidents should be required only where carcinogens exceed the standard level of exposure. A great deal more precision in this and in many other sections of the proposed standard Is needed.
We would substitute and add to these sections with our own recommended work practices document which far more readily reflects industrial realities. This document is appended hereto.
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for small amounts, rail yards, waste treatment facilities and oth r peripheral areas clearly should be excluded from the concept of regulated area. The regulation should not be drawn so as to include an entire plant virtually automatically.
2. Subsection (b) (2) This section appears to impose upon an employer the responsibility for employees other than his own. This is contrary to the specific language of the Act itself and is unauthorized. It should be reworded so as to cover author ized persons as well as employees of the employer.
3. Subsection (b) (h) The definition of "contaminated" is far too ambiguous and broad. It should not cover any material "capable of releasing vinyl chloride monomer" but should be restricted to a product which releases in fact an amount of vinyl chloride gas into the work place air in excess of stated limits. This provision also conflicts with Section (a) (2) and is presumptively unenforceable.
4. Subsection (g) (5) The definition of "decontamination" should be changed as set forth In the appended work practices standard. There is no need to decontaminate all fabricated items, as this language would require.
5. Subsection (b) (6) The term "detectable level" should be eliminated from the definition in Section (b) since it is relevant in the light of other suggested changes; it should be replaced by
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