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Subject: Known Carcinogen: Chromium and Certain Chromium Compounds
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Known Carcinogen: Chromium and Certain =
Chromium Compounds
KNOWN CARCINOGEN:
CHROMIUM AND CERTAIN CHROMIUM COMPOUNDS
CARCINOGENICITY
There is inadequate evidence for the =
carcinogenicity of=20
chromium (7440-47-3) and most trivalent chromium compounds in =
experimental=20
animals. There is sufficient evidence for the following hexavalent =
chromium=20
compounds in experimental animals: calcium chromate (13765-19-0), =
chromium=20
trioxide (1333-82-0), lead chromate (7758-97-6), strontium chromate =
(7789-06-2),=20
and zinc chromate (13530-65-9) (IARC V.2, 1973; IARC V.23, 1980; IARC =
S.4, 1982;=20
IARC S.7, 1987). Calcium chromate produced bronchial carcinomas after=20
implantation of an intrabronchial pellet in rats and injection-site =
sarcomas=20
after intramuscular implantation in rats and mice and after intrapleural =
injection in rats. Bronchial carcinomas were produced in rats after=20
intrabronchial implantation of strontium chromate and zinc chromate.=20
Injection-site sarcomas were produced in rats and mice after =
intramuscular,=20
intrapleural, and subcutaneous injections of chromite ore, strontium =
chromate,=20
chromium trioxide, lead chromate, and zinc chromate, but few or no =
sarcomas were=20
induced by barium chromate (10294-40-3), sodium chromate (7775-11-3), =
sodium=20
dichromate (10588-01-9), or chromic acetate (1066-30-4).=20
An IARC Working Group concluded that there were no adequate data =
available to=20
evaluate the carcinogenicity of chromium and trivalent chromium =
compounds in=20
humans; however, they also concluded that there was sufficient evidence =
for the=20
carcinogenicity of hexavalent chromium compounds in humans (IARC S.7, =
1987). An=20
increased incidence of lung cancer has been observed among workers in =
both the=20
bichromate-producing industry and chromate-pigment manufacturing. There =
is=20
evidence of a similar risk among chromium platers and chromium-alloy =
workers.=20
The incidences of cancers at other sites may also be increased in such=20
populations. However, a clear distinction between the relative =
carcinogenicity=20
of chromium compounds of different oxidation states or solubilities has =
been=20
difficult to achieve. Recent studies of chromate-pigment makers and =
users,=20
chrome platers, welders and chrome-alloy foundry workers have shed some =
light on=20
this problem. For chromate-pigment makers and users, respiratory cancer =
excesses=20
have usually been found. Chromium pigments are usually hexavalent and =
commonly=20
include zinc, lead, or strontium chromate. Chrome platers have also been =
found=20
to have excess lung cancer. Stainless steel welding involves the =
greatest=20
exposure to hexavalent chromium, as well as to nickel, and one study of=20
chromium-nickel alloy foundry workers showed a statistically significant =
excess=20
of lung cancers. (For a discussion on the carcinogenicity of metals, see =
the=20
Introduction, p. viii).=20
PROPERTIES
Chromium is an odorless, steel-to-semi-grey, lustrous =
metal=20
available as crystals or powder (99.97% purity). It is insoluble in hot =
and cold=20
water, nitric acid, and aqua regia, but reacts with dilute sulfuric acid =
and=20
hydrochloric acid. Calcium chromate occurs in the form of yellow =
monoclinic=20
prisms. It is soluble in cold and hot water and reacts with acids and =
ethanol.=20
Chromium trioxide is odorless, dark-purplish-to-red-rhombus crystals =
that are=20
deliquescent. It is soluble in alcohol, ethanol, sulfuric acid, and =
nitric acid.=20
When heated to decomposition, chromium trioxide emits smoke and =
irritating=20
fumes. Lead chromate occurs as yellow or orange monoclinic crystals that =
are=20
insoluble in water, acetic acid, and ammonia but are soluble in acid and =
alkali.=20
Lead chromate, when heated to decomposition, emits toxic fumes of lead. =
Basic=20
lead chromate is a red amorphous or crystalline powder. It is insoluble =
in hot=20
and cold water, reacts with most acid and alkali but not with acetic =
acid or=20
ammonia, and emits very toxic fumes of lead when heated to =
decomposition.=20
Strontium chromate occurs as monoclinic yellow crystals. It is soluble =
in cold=20
and hot water and reacts with hydrochloric acid, nitric acid, acetic =
acid, and=20
ammonium salts. Zinc chromate occurs as lemon yellow prisms. It is =
insoluble in=20
cold water and acetone, dissolves in hot water, and is soluble in acid =
and=20
liquid ammonia.=20
USE
In 1987 and 1989, estimated consumption of chromium ferro- =
alloys,=20
metals, and other chromium-containing materials by end use was as =
follows:=20
stainless and heat-resisting steel, 79%; full- alloy steel, 8%; =
super-alloys,=20
3%; and other alloys, 10% (USDOI, 1988, 1990). The steel industry is the =
major=20
consumer of chromium. Chromium is used as an alloying and plating =
element on=20
metal and plastic substrates for corrosion resistance in chromium- =
containing=20
and stainless steels and in protective coatings for automotive and =
equipment=20
accessories. It is also used in nuclear and high-temperature research.=20
Similarly, barium chromate and calcium chromate find use in =
high-temperature=20
applications, e.g., barium chromate in safety matches and pyrotechnics =
and both=20
are used in high-temperature batteries. In 1985, 39% of the chromium =
trioxide=20
produced was used for metal plating and treatment, 44% was used in wood=20
treatment and preservatives, and 11% was exported (Chem. Profile, 1985). =
Chromium trioxide is used in chromium plating and in the manufacture of=20
chromated copper arsenate (NCI DCE, 1985c). Chromium acetate, sodium =
chromate,=20
and potassium chromate are used in the textile industry. Basic trivalent =
chromic=20
sulfate is used in the tanning industry (Leather Industries of America, =
Inc.,=20
personal communication). Chromium compounds are also used as pigments =
(IARC=20
V.23, 1980). Lead chromate is chrome yellow and a component of chrome =
orange and=20
green; chromium trioxide is green cinnabar; and zinc chromate is zinc =
yellow=20
(Kirk-Othmer V.6, 1979). Chromium phosphate, strontium chromate, calcium =
chromate, chromium acetate, and potassium chromate and dichromate are =
also used=20
in pigments. Other uses for chromium and its compounds include organic =
chemical=20
synthesis, photomechanical processing, and industrial water treatment. =
In=20
medicine, chromium compounds are used in astringents and antiseptics =
(Sax,=20
1987).=20
PRODUCTION
Two U.S. firms produced primary chromium chemicals, =
three=20
firms produced chromium-ferro alloys, and four refractory firms produced =
chromite-containing refractories (USDOI, 1990). Chromite has not been =
mined in=20
the United States since 1961. Domestic deposits are small or of low =
grade. The=20
Bureau of Mines has estimated that in 1989 248.6 million lb of chromium =
were=20
produced in the United States and 946 million lb were imported and 35.2 =
million=20
lb were exported (USDOI, 1990). In 1988, 261.8 million lb were produced=20
domestically, 990 million lb were imported, and 30.8 million lb were =
exported.=20
In 1987, it was estimated that 213.4 million lb of chromium were =
produced, 708.4=20
million lb were imported, and 19.8 million lb were exported. Of the =
184.8=20
million lb of chromium produced and 767.8 million lb of chromium =
imported in=20
1986, 77 million lb were exported. In 1985, the United States produced =
187=20
million lb, imported 640.2 million lb, and exported 83.6 million lb of =
chromium.=20
Production of chromium in 1984 was 176 million lb and exports were 72 =
million=20
lb. Imports of chromium rebounded in 1984 after a 55% decrease from 1981 =
to=20
1983. The amount imported in 1984 was 694 million lb while in 1983, 462 =
million=20
lb were imported. In 1983, 154 million lb of chromium were produced of =
which 26=20
million lb were exported. Of the 96 million lb of chromium produced in =
1982, 20=20
million lb were exported (USDOI, 1988; USDOI, 1987). In 1982, 478 =
million lb of=20
chromium were imported, which was over 50% less than the 1.0 billion lb =
imported=20
in 1981. Exports of chromium in 1981 were 104 million lb while in 1980, =
80=20
million lb were exported. The amount of chromium imported in 1980 was =
922=20
million lb (USDOI, 1987; USDOI, 1985). The 1979 TSCA Inventory =
identified a=20
total of 11 producers producing 91 million lb of chromium and 12 =
importers=20
importing 6.2 million lb of chromium in 1977 (TSCA, 1979).=20
In 1986, 3.9 million lb of zinc chromate, reported as zinc yellow, =
and 39.2=20
million lb of lead chromate, reported as chrome yellow and orange, were=20
produced. In 1985, 4.42 million lb of zinc yellow, and 41.4 million lb =
of chrome=20
yellow and orange were produced (USDOC Inorganic, 1987). In 1985, the =
following=20
chemicals were imported: 9.8 million lb of chromic acid, 403,447 lb of =
chrome=20
green (lead chromate), 6.4 million lb of chrome yellow, 3.0 million lb =
of=20
chromium oxide green, 862,465 lb of strontium chromate, and 3.5 million =
lb of=20
zinc yellow (USDOC Imports, 1986). In 1985, 731,941 lb of chromic acid =
were=20
exported (USDOC Exports, 1986). In 1984, the production of chrome yellow =
and=20
orange was 46.8 million lb, and of lead chromate, as chrome green, was =
16.5=20
million lb (USDOC Inorganic, 1987). In 1984, the United States imported =
105,569=20
lb of chrome green, 5.1 million lb of chrome yellow, 393,529 lb of =
strontium=20
chromate, 2.4 million lb of zinc yellow, and 4.9 million lb of chromic =
acid=20
(USDOC Imports, 1985). In 1983, production of chrome yellow and orange =
was 43.1=20
million lb and production of chrome green was 10.4 million lb. In 1982, =
40.8=20
million lb of chrome yellow and orange and 8.6 million lb of chrome =
green were=20
produced (USDOC Inorganic, 1987; Chem. Prod., 1983a). The 1979 TSCA =
Inventory=20
reported that in 1977, 10 companies produced 74,000 lb of calcium =
chromate and 2=20
companies imported 6,000 lb; 10 companies produced 11.6 million lb of =
lead=20
chromate and there were 3 importers; 6 companies produced 555,000 lb of=20
strontium chromate and 9 firms imported 124,500 lb. Also reported in the =
TSCA=20
Inventory was that 199,000 lb of zinc chromate and 6 companies imported =
7.2=20
million lb. The CBI Aggregate was less than 1 million lb barium chromate =
and=20
between 1 million and 100 million lb for zinc chromate (TSCA, 1979).=20
EXPOSURE
The primary routes of potential human exposure to =
chromium and=20
certain chromium compounds are inhalation, ingestion, and dermal =
contact.=20
Chromium (in the form of unidentified chromium compounds) is widely =
distributed=20
in air, water, soil, and food. In trace amounts, its trivalent form may =
be an=20
essential ingredient in the diet. The entire population is possibly =
exposed to=20
some of these compounds, but the levels of exposure vary. Hexavalent =
chromium=20
(chromium (VI)) compounds are of greater health concern than trivalent =
chromium=20
compounds (chromium (III)), but hexavalent compounds are readily reduced =
to=20
trivalent forms in the presence of organic matter.=20
NIOSH has found that certain forms of chromium (VI) are =
noncarcinogenic; they=20
are the monochromates and dichromates of hydrogen, lithium, sodium, =
potassium,=20
rubidium, cesium, and ammonium, and chromium (VI) oxide (chromic acid =
anhydride)=20
(NIOSHb, 1979b). The National Occupational Hazard Survey, conducted by =
NIOSH=20
from 1972 to 1974, estimated that 2.5 million workers were possibly =
exposed to=20
chromium and its compounds in the workplace (NIOSH, 1976). NIOSH =
estimated that=20
175,000 workers were potentially exposed to chromium (VI), which is =
produced=20
principally from chromite ore (NIOSHb, 1979b). The National Occupational =
Exposure Survey (NOES) (1981-1983) estimated that a total of 115,788 =
workers,=20
including 3,101 women, were potentially exposed to chromium; 6,339 total =
workers=20
were potentially exposed to chromite ore (NIOSH, 1984). The NOES also =
estimated=20
that a total of 196,725 workers, including 31,444 women, were =
potentially=20
exposed to hexavalent chromium (VI) compounds (barium chromate, calcium=20
chromate, chromium trioxide, lead chromate, strontium chromate, and zinc =
chromate). Occupational airbone chromium concentrations have declined=20
significantly during the past decades because of improved emission =
controls.=20
Occupational exposure occurs mainly from stainless steel production and =
welding,=20
chromate production, chrome plating, ferrochrome alloys, chrome pigment, =
and=20
tanning industries. Occupational exposure is due to the soluble and =
insoluble=20
fractions of chromium (III) and chromium (VI), depending upon the =
industry. The=20
typical concentration ranges of chromium (VI) in these industries are: =
stainless=20
steel welding, 50-400 =B5g/m3; chromate production, 100-500 =B5g/m3; =
chrome plating,=20
5-25 =B5g/m3; ferrochrome alloys, 10-140 =B5g/m3; and chrome pigment, =
60-600 =B5g/m3.=20
In the tanning industry, exposure is almost exclusively to soluble =
chromium=20
(III), typically in the range of 10-50 =B5g/m3 (ATSDR, 1989h). ACGIH has =
designated the following threshold limit values (TLVs) as 8-hr =
time-weighted=20
averages (TWAs) for chromium compounds, as chromium: 0.5 mg/m3 for =
chromium (VI)=20
compounds, and 0.05 mg/m3 for lead chromate, water soluble chromium (VI) =
compounds, and certain water insoluble chromium (VI) compounds (ACGIH, =
1986).=20
The general population can be exposed to chromium through the air, =
water,=20
soils and food. Chromium has been detected in at least 386/1,777 sites =
on the=20
National Priorities List (ATSDR, 1989h). The Toxic Chemical Release =
Inventory=20
(EPA) listed 929 industrial facilities that produced, processed, or =
otherwise=20
used chromium in 1988 (TRI, 1990). In compliance with the Community=20
Right-to-Know Program, the facilities reported releases of chromium to =
the=20
environmental which were estimated to total 9.9 million lb. The =
atmospheric=20
chromium concentration in the United States is typically < 0.01 =
=B5g/m3 in=20
rural areas and 0.01-0.03 =B5g/m3 in urban areas. In the United States =
it was=20
calculated that 64% of the atmospheric chromium emissions, which =
originate from=20
coal, contain 1.5-54 ppm chromium (Merian, 1984). It is been reported =
that tap=20
water contains 0.4-0.8 =B5g chromium/l (ATSDR, 1989h). The chromium =
concentration=20
in rivers and lakes is usually between 1 and 10 =B5g/l (Merian, 1984). =
The earth's=20
crust and rocks contain about 100 ppm chromium; soils contain, on the =
average,=20
about 400 ppm (Merian, 1984). Typical chromium levels in most fresh =
foods are=20
low. Chromium has been detected in vegetables, fruits, grains, and =
cereals at=20
concentrations between 20 and 50 =B5g/kg (ATSDR, 1989h). CPSC =
investigated the=20
potential hazard to consumers from chromium-containing inks, printed =
products,=20
and nonprinted consumer products. Although chromium was present in some =
inks=20
used in printed products, the levels found in the final products did not =
warrant=20
further investigation.=20
REGULATIONS
In FY 1982, an evaluation was made of exposure to =
chromium=20
from nonprinted consumer products. EPA regulates chromium and its =
compounds=20
under the Clean Water Act (CWA), Comprehensive Environmental Response,=20
Compensation, and Liability Act (CERCLA), Resource Conservation and =
Recovery Act=20
(RCRA), Superfund Amendments and Reauthorization Act (SARA), and Toxic=20
Substances Control Act (TSCA). CERCLA establishes reportable quantities =
(RQs)=20
for chromium and some chromium compounds. RCRA and SARA subject chromium =
and its=20
compounds to report/recordkeeping requirements. The EPA has proposed a =
maximum=20
contaminant level goal (MCLG) and maximum contaminant level (MCL) of 0.1 =
mg/l=20
for total chromium because no evidence suggests the hexavalent chromium =
is=20
carcinogenic by ingestion. EPA's Carcinogen Assessment Group includes 10 =
chromium compounds on its list of potential carcinogens. FDA regulates =
the use=20
of chromium as an indirect food additive and the use of chromium oxide =
in drugs=20
and cosmetics. NIOSH recommends an exposure limit of 1 =B5g/m3 for =
carcinogenic=20
hexavalent chromium compounds. For noncarcinogenic chromium compounds, =
it=20
recommends an exposure limit of 50 =B5g/m3 as a 10-hr time-weighted =
average (TWA).=20
OSHA adopted an 8-hr TWA permissible exposure limit (PEL) of 0.5 mg/m3 =
for=20
chromium (II) and chromium (III) compounds and l mg/m3 for chromium =
metal; for=20
chromic acid and chromate, the ceiling is 0.1 ppm. OSHA regulates =
chromium and=20
certain chromium compounds under the Hazard Communication Standard, and=20
hexavalent chromium compounds as chemical hazards in laboratories.=20