Document OEE0ypKby4jyyDMjZkRmEeDyX
V
HEALTH HAZARDS AND OCCUPATIONAL DISEASES
JAMES W. HAMMOND HUMBLE OIL & REFINING COMPANY
HOUSTON, TEXAS
Action of Hazardous.-Substances
1. Irritants
2. Asphyxiants
3. Volatile drugs and druglike substances
a. Primary irritants
b. Primary anesthetics
c. Anesthetics with systemic effects on the
liver and kidneys
d. Anesthetics with systemic effects on the
blood-forming organs
e. Anesthetics with systemic effects on the
nervous system
f. Substances whose anesthetic action is
observed by more severe systemic effects
4. Inorganic and organometallic substances
a. Acute poisons
b. Chronic poisons
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HEALTH HAZARDS AND OCCUPATIONAL DISEASES - outline continued
Preventive Measures 1. Job Study and Analysis
2. Process and Operations Study 3. Materials Study 4. Sampling and Measurements 5. Using Results of the Survey
a. Do exposures exist in the plant? b. What is the significance of the exposures? c. What can we do about them? The Survey as a Basis for Controls They must 1. Protect the man 2. Not interfere with his work 3. Be acceptable to the worker 4. Be reasonable and practical 5. Not cost too much. Several basic control techniques are.1. Isolation 2. Substitution 3. General ventilation 4. Local exhaust ventilation 5. Personal protective equipment
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HEALTH HAZARDS AND OCCUPATIONAL DISEASES - outline continued
Emergency Action 1. Remove victim to fresh air 2. Give proper first aid 3. Take care of the eyes
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4. Proper treatment of clothing Conclusion
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HEALTH HAZARDS AND OCCUPATIONAL DISEASES
JAMES W. HAMMOND ' HUMBLE OIL St REFINING COMPANY
HOUSTON, TEXAS
Action of Hazardous Substances Hazardous substances encountered in the petroleum
industry can cause local irritation, systemic poisoning or occasionally both. Some are sensitizers and a few have or have been suspected to have carcinogenic properties. Damage to health may result if a person is exposed to a sufficient quantity of any of these substances for a sufficient time. In acute poisoning, the quantity is usually relatively large and the exposure time short. In chronic poisoning, the exposure time is generally long and repeated while the quantity is relatively low, often being so low that the individual may be unaware of any exposure at the time. With most sensitizers, the first few exposures may cause no reaction; but once a person becomes sensitized, reactions may occur from contact with verysmall quantities for very short periods of time.
The wide variety of hazardous substances used or handled permits only a very broad classification of their toxic or hazardous properties. Factors other than inherent toxicities often determine the type and severity of their effects. For example, acute benzene poisoning has a different clinical picture than chronic poisoning by this same chemical.
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And while ethyl alcohol is somewhat more toxic than methanol,
the latter is much more dangerous when ingested because of
its slow rate of metabolism. Sometimes the physical state and
physical properties of a substance determine to a large extent
the nature and severity of its action on the body. Most skin
irritants are liquids and in many cases the degree of local
irritation has no relation to their systemic toxicities as is
the case with kerosine. Differences in viscosities sometimes
are the determining factor in the type of injury. The aspiration
hazard from a low viscosity substance like kerosine is quite
different and more severe than that from a higher viscosity
product like medicinal mineral oil. The solubility of an
irritant gas influences to a large extent the part of the
respiratory tract that is affected. Ammonia, which is very
soluble in water irritates the nose and throat primarily while
nitrogen dioxide, being much less soluble, acts mainly on the
tissues in the lungs.
Various classifications of hazardous substances have
been proposed but none are completely satisfactory. Henderson
and Haggard developed a classification for gases and volatile
liquids which is based to a large extent on the acute effects of
inhalation with less emphasis on chronic effects. The matter
of skin absorption, skin and eye irritation, carcinogenicity,
sensitization, allergic reactions, were purposely excluded.
Henderson and Haggard grouped gases and volatile substances
into these four categories:
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1. Irritants are substances which when inhaled
produce injury to the air passages or lungs, or both. Some
irritant gases and vapors also are systemic poisons but their
local effects overshadow any systemic effects that may occur
after exposure. The more soluble ones can also be expected to
cause eye irritation. Examples are: ammonia, chlorine, sulfur
dioxide, ozone, phosgene, acrolein.
2. Asphyxiants exert their action in one of three
ways: by reducing the amount of oxygen available for breathing,
by preventing oxygen transport by the blood, or by preventing
utilization of oxygen by the tissues. The quantities of these
gases necessary for them to act varies widely. Large volumes
of gases such as nitrogen, hydrogen, methane, must be present
before the oxygen content of the air becomes sufficiently low
to be unsafe to breathe. Such gases are classed as simple
asphyxiants. With other gases such as carbon monoxide and the
cyanogen compounds, particularly-hydrogen cyanide, only very
small amounts are needed to cause asphyxiation. These gases are
called chemical asphyxiants. Carbon monoxide reduces the amount .
of oxygen available to the tissues because of its much greater affinity for hemoglobin as compared to that of oxygen. The
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cyanogens prevent the tissues from using oxygen, even though it
may be delivered to them in adequate amounts.
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3. Volatile drugs and druglike substances have
one physiological effect in common, that of inducing anesthesia,
although with some the action may be obscured by some other
systemic effects. Some of them are also irritating to surface
tissues. Depending on the concentration present, the depth
of anesthesia will range from mild symptoms to complete loss of
consciousness and death. In very high concentrations death may
be due to asphyxiation. Henderson and Haggard subdivided these
substances into six subclasses:
a. Primary irritants. Those with sufficiently
strong irritant properties to prevent absorption of any apprec
iable amounts or to obscure the effects of absorption. Some
of the ketones, ethers, alcohols, and esters are in this sub
group.
b. Primary anesthetics. No marked effect other
than anesthesia and no serious systemic effects from prolonged
exposure. Examples are hydrocarbons of the paraffin, olefin, and
acetylene series, nitrous oxide, ethers.
c. Anesthetics with systemic effects on the liver
and kidneys. The chlorinated hydrocarbons belong to this subgroup.
d. Anesthetics with systemic effects on the
blood-forming organs. Of the aromatics and alkyl aromatics,
benzene is the only one that affects the blood-forming organs.
It has been established that the alkyl aromatics such as toluene
and the xylenes do not have this effect.
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e. Anesthetics with systemic effects on the
nervous system. Included in this subgroup are ethyl alcohol,
methyl alcohol, esters of organic acids, carbon disulfide.
f. Substances whose anesthetic action is
observed by more severe systemic effects. These are substances
whose predominant action is the "nitrite effect" like the alkyl
nitrites and alkyl nitro-substitution products or those which
convert oxyhemoglobin to methenoglobin with relatively little
"nitrite effect" such as nitrobenzene, aniline and toluidine.
4. Inorganic and organometallic substances.
In this group there is a large number of substances with a wide
variety of compositions and actions which do not fit into an;7
of the other three groups. Examples which show this wide variance
are mercury vapors, tetraethyl lead, nickel, iron, and cobalt
carbonyls, and hydrogen sulfide. This latter gas also has
irritant properties resembling those of chlorine though less intense
Immediate death from hydrogen sulfide is due, however, to its
.
systemic action. The occasional delayed death one or two days
after exposure to this gas may be the result of its irritant action on the respiratory passages. -P--r--e--v---e--n--t--i-v--e----M---e---a--s-u---r-e--s-
Selection of the proper preventive measures to avoid health damage requires a detailed knowledge of the handling or
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use methods of the hazardous substance as well as a knowledge of
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its physical and toxicological properties. Today, containers
of many hazardous substances have precautionary labels. An
adequate label will name the hazardous component, state the
toxicological effect, outline the preventive measures and
the emergency action to be followed in the event of exposure.
All precautionary instructions on such labels should be followed.
A detailed* description of the precautionary measures for all hazardous substances is not feasible in this general
review. However, a summary of the more common ones that
relate to the various types of potential exposure follows:
1. Job Study and Analysis
The kind of work a man does is certainly important in
relation to environmental factors that may influence his health.
Many times in the course of a periodic survey a job study and
analysis must be done. This is necessary to determine exposure
time, work habits, and related items. In some situations a
mere change in work procedure may mean the difference between
exposure and no exposure. Intermittent operation of a process
and accompanying job requirements may be important in terms of
exposure time, and ultimately in the kind of control measures
required.
2. Process and Operations Study
. Closely related to the job study is the study of process
or operations. A good working knowledge of all operations in
the plant is essential. This includes both manufacturing or
process as well as mechanical work. This information tells us
the source of those factors of concern to health.
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the materials that go into a process, what happens to them, and
how they may come in contact with the worker. The same general
information must be developed for physical factors, such as
noise and radiation. A process study is necessary also in terms of how
controls can be applied. Many times these involve engineering
features which may influence or limit design of controls. *
3. Materials Study
The majority of environmental exposures result from
process or related materials being liberated into the plant
atmosphere. Therefore, information on the physical, chemical,
and toxicological properties of these is of great importance.
In the periodic survey, all materials for each operation
should be listed. The chemical and physical properties should be
studied. If the process is one in which chemical reactions can
occur, new or side products should be studied in the same fashion.
The toxic properties of a material is of even greater
importance. If an exposure to a material is to be evaluated,
its toxicity must be known. Witho?jt this information there is
little ground for a quantitative appraisal of exposure.
4. Sampling and Measurements
In order to put the evaluation of an exposure on a
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quantitative basis, we must know actual levels of exposure. In
other words, "How much of this material is the man taking into
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his body by inhalation?" Therefore, it becomes necessary to measure, as accurately as possible, the amounts of those gases, vapors, dusts, mists, and the like which are in the air the worker is breathing. From this information his daily "dose" can be determined.
From a technical standpoint these measurements involve the collection of various samples and the analysis of these in the laboratory. Physical factors must also be measured. This phase of the periodic survey is time consuming, requires considerable instrumentation, but actually is the heart of any such survey.
5. Using Results of the Survey Generally plant surveys should answer three important questions: . a. Do exposures exist in the plant?
b. What is the significance of the exposures? c. What can we do about them?
The existence of exposures can be determined by relating data from measurements to various standards or reference points and to past experience with the situation at hand. Basically, the same procedure is followed in judging the significance of an exposure. The most common reference points are the MAC values. In passing, it should be pointed out that often more con fidence is written into these values than was the intent when they
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were established. They are basically set up as bench marks
for control purposes and this should be recognized in making
use of them.
What can be done about exposures falls into the
category of controls, which we should discuss separately.
The Survey as a Basis for Controls
When exposures have been defined by survey techniques,
the next basic problem is how they can be controlled. For
control procedures to be acceptable they must meet certain
requirements, such as --
They must 1. Protect the man.
2. Not interfere with his work.
3. Be acceptable to the worker.
4. Be reasonable and practical.
5. Not cost too much.
There are several basic techniques which can be used in controlling
exposures.. They are -
1. Isolation.
2. Substitution.
3. General ventilation.
4. Local exhaust ventilation.
5. Personal protective equipment.
` The United States of America Standards Institute through
its Committee on Acceptable Concentrations of Toxic Dusts and
Gases has also published standards in this area. Formerly these
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standards gave only one value. The USASI standards now recognize
that there are other factors sj ch as a relation between duration
of exposure and concentration. Where applicable for a particular
substance, values are given for ceiling concentrations, eight-
hour time-weighted average concentrations, levels to avoid sensory
responses, ''peaks" and the duration thereof above the acceptable
concentration for continuous exposure.
The reviews in this series contain the ACGIH and the
USASI values, if such exist, for the substance under consideration.
These values should be used and interpreted subject to the
limitationsin the first paragraph of this section. In addition,
it should be kept in mind that because of the wide variation in
individual susceptibility, exposures of an occasional person,
even below the values may cause discomfort, aggravation of a
pre-existing condition or even an occupational disease.
Emergency Action
If because of the failure or inadequacy of the
preventive measures, acute effects occur from exposure to a
hazardous substance a medical emergency may exist. Then the
immediate application of emergency procedures is necessary.
This is not necessary for cases of chronic poisoning.
When a person has been overcome by a toxic gas or
vapor, he should be immediately removed to an uncontaminated
atmosphere. Rescuers should not attempt to do this unless they
have adequate respiratory protection.
10.
If natural breathing has
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been interrupted artificial respiration should be started immediately after removal from the contaminated atmosphere. The various methods of administering artificial respiration are described in API Publication 2017, First Aid Training Guide. The victim should be kept warm and completely at rest.
Eye contact with irritating substances, particularly liquids, requires emergency action. The eyes should be immediately flushed with water for at least 15 minutes and medical attention obtained immediately thereafter. The use of neutralizing solu tions, for example, dilute acetic acid in the case of alkali burns of the eye, is inadvisable. Valuable time may be lost while looking for the bottle of the neutralizing chemical, the strength may have changed from long standing, and sometime the solution may do more harm to the eye than the original irritant. Flushing is best done using an eye fountain but if such a fixture is not available, water from a tap or hose should be used. If there are no sources of water at hand, the person can immerse his head in a bucket of water so that his eyes are in contact with the water. Needless to say, the eyes should be kept open during the flushing operation. Often this will require the assis tance of a fellow worker. It is advisable to train all employees in the proper technique of flushing the eyes.
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Substances which can cause corrosion or immediate
irritation to the skin or systemic effects by reason of skin
absorption should be removed from the skin immediately. The
skin should be flushed with copious amounts of water. Safety
showers for this purpose should be provided in all areas where
there is likelihood of exposure to these substances. Time
should not be taken*to remove clothing or footwear before getting
under the shower; it should be removed while the affected person
is being flushed with water. If a shower is not available,
water from a hose can be used. Agents other than
water may be more effective in removing some substances but
water is useful in any case because its direct mechanical action
will remove even water insoluble substances to a large extent.
In addition, water is usually readily available.
Conclusion
An adequate program for the protection of the health
of employees includes both industrial hygiene control and
medical supervision. Industrial hygiene procedures include
evaluation of the work environment by surveys and inspection,
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selection of the proper control measures, and periodic surveys and studies to ascertain if operations have changed and if control equipment is functioning properly. Medical supervision
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includes preplacement physical examinations in order to avoid
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possible exposure of persons with certain pre-existing conditions to certain hazardous substances. Periodic physical examinations at proper intervals should be made to detect early symptoms of occupational disease and to determine the adequacy of existing control methods.
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APPENDIX I. Group I. Solvents.
Solvent
TLV
Evpn. er/tlv
(ppm) rate ratio
n~ Amyl alcohol Butylcellosolve o- & p- Cresol Diacetone alcohol o- Dichlorobenzene Diisobutyl ketone Ethyl alcohol Isoamyl acetate Methyleye1ohexanol Methylcyclohexanone Phenol
100 50 5 50 50 50
1,000 100 100 50 .5
34 6 1
14 15 16 340 12
2 17
0.6
0.34 0.12 0.20 0.26 0.30 0.35 0.34 0.12 0.02 0.34 0.16
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APPENDIX I. Group II. Solvents
Solvent
TLV (ppm I
Evpn. rate
Acetone Amyl acetate Aniline n- Butyl acetate n- Butyl alcohol Chlorobenzene Cyclohexanone Dichloroethyl ether Diethylaminoethanol Ethanolaraine Ethylbenzene Heptane Isobutyl acetate Isobutyl alcohol Isopropylbenzene Methylamyl acetate Methylamyl alcohol
Methylamyl ketone Kethylbutly ketone
1,000
1,160
100 '
62
54 150 100
100 45
75 75
50 23
15 11 '
10 . 15
3' 1
100
91
500 386
150 174
100 '
80
50 .
57
50 47
25 33
100 40
100 87
ER/TLV
ratio
1.16 0.62 0.80 0.67 0.45 1.00 0.46 0.73 1.50 0.33 0.91 0.77 1.16 0.80 1.14 0.94 1-45 0.40 0.87
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appendix I. Group II. Solvents.
Solvent
TLV Evpn. ER/TLV
iPPffi)- rate
ratio
Kethylcyclohexane
500 320
n- Octane
500 336
3- Pentanone (diethyl ketone)
200 275
n- Propyl acetate
200 276
n- Propyl alcohol
200 110
Toluene
'
200 240
1,2,3* Trichloropropane 50 39
Xylene
100 63
0.64 0.67 1.36
1.36 0.55 1.20 0.76 0.63
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--- MfcT
APPENDIX I. Group III. Solvents,
Solvent_______ ________ ___
TLV Evpn. ER/TLV ... toml rate ratio
2- Butanone (MEK)
Cyclohexane
Cyclohexene
Dimethylformamide
Dioxane
Ethyl acetate
Furfural
n- Hexane
Isopropyl acetate
Methylisobutyl ketone
Nitropropane
ri- Pentane
2- Pentanone
Perchloroethylene
200 300 300
10 100 400
5 500 250 100 100 1,000 200 100
57 2 720 597 *7 311 615
9 1,000
500
. 165 ISO
2,860 320 280
2.86 2.40 1.99 1.70 3.11 1.54 1.80 2.00 2.00 1.65 1.80 2.86 1.60 2.80
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APPENDIX I. Group IV. Solvents
Solvent
TLV Evpn. ER/TLV
(ppm) rate
ratio
Acetic anhydride
5
Acetonitrile
40
Allyl alcohol
2
Benzene
25
Carbon disulfide
20
Carbon tetrachloride
10
Chloroform
50
1,2 Dichloroethylene
200
Diethylamine
25
Diemethyl sulfate
1
Ethyl bromide
200
Ethylenediamine
10
Ethylene dibormide
25
Ethylene dichloride (1,1) 50
Ethyl ether
400
Methyl acetate
200
Methyl alcohol
200
Methyl chloroform
350
Methylene chloride
500
Methyl formate
100
46 9.20
579 14.50
100 50.0
630 25.2
2,260
113.0
1,260
126.0
1,160
23.2
1,656
8.2
1,596
63.8
4,151 4,151.0
4,557
22.8
1,015
101.5
656
26.2
1,160
23.2
3,300 _
6.3
1,180
5.9
610 3.1
1,577
4.5
2,750
5.5
4,080
40.8
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APPENDIX I. Grout? IV. Solvents.
Solvent
TLV w
1- & 2- Nitropropane
25
Propylene dichloride
75
Pyridine
5
1,1,2,2, Tetrachloroethane 5
T etrahydrofuran
200
Triethylaraine
25
Trichloroethylene
100
Evpn. ER/TLV rate _ratio_
125 5.0 530 7.1 156 31.6
65 13.0 600 4.0
451 16.0 620 6.2
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