Lead Chromate Pigments - A

Literature Survey on

Environmental and Toxic

Effects

I

M. A. Post and P. G. Campbell

Center for Building Technology

National Engineering Laboratory

National Bureau of Standards

Washington, D.C. 20234

February 1980

Prepared for Federal Highway Administration

Offices of Research & Development — - ^ Washington, D.C. 20590

QC

100

.056

NO.80-1974

1980
I

I

* ^

I
NBSIR 80-1974

LEAD CHROMATE PIGMENTS - A

LITERATURE SURVEY ON

ENVIRONMENTAL AND TOXIC

EFFECTS

M. A. Post and P. G. Campbell

This report is an updated version of the one appearing as Appendix A

in Report No. FHWA-RD-78-1 Nontoxic Yellow Traffic Striping.

Center for Building Technology

National Engineering Laboratory

National Bureau of Standards

Washington, D.C. 20234

February 1980

Prepared for Federal Highway Administration

Offices of Research and Development

Washington, D.C. 20590

U.S. DEPARTMENT OF COMMERCE, Philip M. Klutznick, Secretary

Luther H. Hodges, Jr., Deputy Secretary

Jordan J. Baruch, Assistant Secretary for Science and Technoiogy

NATIONAL BUREAU OF STANDARDS, Ernest Ambler, Director
I’P-
ABSTRACT

Lead Chromate Pigments - A Literature Survey on Environmental and Toxic Effects

by M. A, Post and P. G. Campbell

In connection with an evaluation of the performance of possible alternative yellow

pigments j a literature search was made on the toxicity and environmental effects

of lead chromate pigments. The literature reveals that workers in chromate plants

in the U. S., Europe and Japan have had a high incidence of lung cancer as well as other respiratory ailments. Further, reports on the biologic interactions of

chromium show that chromium in its hexavalent state (chromate, dichromate) penetrates body membranes such as skin and the walls of red blood cells and is subsequently reduced to the trivalent state and complexed with organic molecules. While

the carcinogen in the chromate manufacturing process has not been identified, animal

experiments have shown that calcium chromate can produce cancer in rats. Information

is presented on sources of chromium in air and water pollution. Also, the pollution

aspects of lead and chromium in storm water runoff and as street surface contaminants

are reviewed.

Key words: Air pollution; chromite ore; environmental effects; lead chromate

pigments; storm water runoff; toxicity; water pollution.
Table of Contents

Page

1. INTRODUCTION 1

2. MANUFACTURING PROCESS OF CHROMATE PIGMENTS 2

3. EFFECT OF CHROMATES ON WORKERS IN THE MANUFACTURING

PROCESS 3

4. EFFECTS OF LEAD-CONTAINING SPRAY- APPLIED PAINTS ON

PAINTERS WORKING IN CONFINED AREAS 9

5. BIOLOGICAL INTERACTIONS OF CHROMIUM AND CHROMATES 14

6. ANIMAL STUDIES WITH HFJCAVALENT CHROMIUM 15

7. AIR POLLUTION STUDIES RELATING TO CHROMIUM 18

8. WATER POLLUTION STUDIES RELATING TO CHROMIUM IN

RUNOFF FROM STREETS 21

9. STREET CONSTRUCTION MATERIALS AND SURFACE CONTAMINANTS

AS SOURCES OF CHROMIUM 25

10. CALCULATION OF POSSIBLE CONTRIBUTION OF YELLOW TRAFFIC

STRIPING TO LEAD AND CHROMIUM CONTENT OF ROADWAY

PARTICULATES 28

11. CONCLUSIONS 29

12. REFERENCES 32
1.0 INTRODUCTION

This report Is the result of a literature survey carried out in connection with

an evaluation of the performance of yellow pigments which might be possible alternatives to lead chromate for use in traffic paints, i.e., paints used for highway

striping. In this part of the project, the focus was on the toxicity and environmental effects of lead chromate pigments.

At the present time, lead chromate pigments are the only yellow pigments used in

traffic paints. Concern about their use is apparent from the recent warning given

by the Dry Color Manufacturer’s Association to pigment manufacturers and their

customers as to the possible carcinogenic effects of certain chromate pigments [1]*

A computer search of the Medline, Toxline and Chemical Abstracts data bases was

performed. From this search, the bulk of the references was obtained. The NTIS

(National Technical Information Service) was also used and EPA (Environmental Protection Agency) reports were searched. In addition. Chemical Titles, World Surface

Coatings Abstracts, Journal of Oil and Colour Chemists Association, American Paint

Journal, Journal of Paint Technology, Paint and Varnish Production, Paint Manufacture, Canadian Paint and Finishing, and Pigment and Resin Technology were consulted

2.0 MANUFACTURING PROCESS OF CHROMATE PIGMENTS

Before discussing the results of a literature search on the effects of chromates on

the human body, a description of the manufacturing process for lead chromate is

presented.

* Numbers in brackets refer to references at the end of this paper.

1
The principal lead ore is the sulfide. Lead ores are first concentrated by a series

of flotation processes to remove the zinc sulfide and the gangue materials. The

concentrated ore is then roasted in air to convert most of the sulfide to the oxide.

The lead oxide is dissolved in nitric acid to form lead nitrate. The solution must

be slightly acid, otherwise hydrolysis occurs and basic nitrates are precipitated.

The process is described by Nebergall and Schmidt [2] and the reactions are:

The principal chromium ore is chromite. The chromite is roasted with sods , with

or without lime, and the sodium chromate is leached out with water [3]. If sodium

dischromate is used in the production of lead chromate, this is produced from the

solution of sodium chromate by reaction with dilute sulfuric acid. Wormald [4]

described the process where solutions of sodium chromate or dichromate are produced

in individual tanks. The lead nitrate solution is added and lead chromate is precipitated. The lead chromate pigment is collected in the filter press, washed, dried

and milled. The reactions involved are:

2 PbS + 3 O

2

2 PbO + 2 SO2

( 1 )

PbO + 2HNO3 PB(N03>2 + H

2 O

+ NO3 + H2O ^ Pb(0H)N03 + H'*’

( 2 )

(3)

2 Cr203 + 4 Na2C03 + 3 O

2

-*• 4 Na2Cr04 + CO 2 (4)

(Roasting of chromate ore with soda ash)

Pb (N03)2 + Na2Cr04 > PbCr04 + 2NaN03

(Medium chrome yellow pigment)

(5)

or

2 Pb (N03)2 + Na 2 Cr20 y + H

2 O - 2 PbCrO^ + 2 NaN03 + 2 HNO3

Light chrome yellow pigments are produced as follows [13]:

( 6 )

2 Pb (N03)2 + Na 2 Cr04 + Na2 S 04 > PbCrO^ . PbSO^ + 4NaN03 . (7)

2
3.0 EFFECT OF CHROMATES ON WORKERS IN THE MANUFACTURING PROCESS

European, American and Japanese reports have discussed the effects of chromate pigments on workers Involved in the manufacturing process. Enterline [5] cites the

work of Machle and Gregorius as the earliest published epidemiological investigation

of respiratory tract cancer among chromate workers in the U.S. Machle and Gregorius

[6] studied the mortality experience of workers in seven U.S. plants engaged in the

extraction of chromium from chromate ore. Enterline lists a table showing annual

mortality rates for six of these plants. For the period 1943-1947, chromate workers

were dying of cancer of the respiratory tract at a rate over twenty times that for

oil refinery workers. Enterline also cites the work of the U.S. Public Health

Service (USPHS) in its study of the same six chromate plants for the period 1940-

1948 [7] Nearly 29 times as many deaths from respiratory tract cancer were reported

as would have been expected based on mortality rates of U.S. males. In a Litton

Industry study [8] compiled by Sullivan, the authors, commenting on the same USPHS

study, stated there were 470.8 deaths/100,000 in the chromate industry as compared

with 16.7/100,000 of the same age group in the U.S. This study reported that an

examination of the bodies of chromate workers showed that they had acumulated

appreciably higher concentrations of chromium than the general population. It also

mentioned the findings of Baetjer [9] who stated that an examination of the lung

tissues of these workers indicated that carcinogenic tissues were not always associated with the higher concentrations of chromium. The Litton study concluded that

individual susceptibility plays an important role in cancer induced by chromium

compounds. As cited by Enterline [5], a later study on three chromate-producing

plants by the University of Pittsburgh was the only study in which workers were

examined after leaving the Industry. From 1200 chromate workers there were 69 cases

of respiratory cancer. Enterline [5] stated further that the old chromate-producing

3
plants upon which the American epidemiological data were based had been either dismantled or completely rebuilt. He concluded that for the plants which remain it is

too early to tell whether the changes made have completely eliminated the excess

respiratory tract cancer. Utldjian [10] discusses two plants engaged in chromate

production. One plant produced sodium dichromate from chromite ore, while the second

plant produced chromic acid and basic chromic sulfate from the sodium dichromate.

In the plant producing the dlchromate, the incidence of death from lung cancer was

18 times normal. There were no lung cancer cases in the second plant. There has

been no mining of chromite ore in the U.S. since 1961 because higher grade ore can

be purchased from foreign countries at lower cost. Bldstrup and Case [11] reported

that, from 723 workers in three chromate plants in Great Britain, there were twelve

deaths from lung cancer compared with 3.3 expected on the basis of the total populations. Enterline commented that the difference between this study and [11] previously

cited studies of workers in the U.S. is striking and may be due to better working

conditions or to a shorter follow-up period in the study by Bidstrup and Case.

Oettel et al. [12] discussed the statistics concerning lung cancer among workers in

a small chromate factory in Ludwlgshafen. They mentioned that the pathologist,

Hanser, in Ludwlgshafen, reported that, of 16 cases of lung carcinoma which occured

between 1921 and 1928, five came from a chromate operation^ The exposure times for

the chromate workers were 5-27 years. The regular induction time for lung carcinoma

was estimated to be 20-30 years. However, these workers had also handled quinones

which are very carcinogenic. Oettel et al. said it appeared that chromates caused

lung cancer primarily in combination with other cancer-causing products as in the

case of smokers. No more chromates are manufactured there.

4
Capodagllo et al. [13] reported that workers exposed continually to chromates had

modules of insoluble powder in the lung. Respiratory problems attributed to hexavalent chromium were laryngitis, chronic bronchitis, and elevated incidence of

tumors in the respiratory tract after a period of exposure to production of

dichromates from chromates from 5 to 27 years. Eighty-eight people, 22-58 years

of age, were examined. No statistics on the number of fatalities were given.

Renovation of the air circulatory system was followed by an outstanding decrease

in dust pollution.

Pica [14] and Hartogensis and Ziehlhius [15] carried out toxicity studies on lead

chromate but their primary concern was lead rather than chromate toxicity.

Pica [14] reported that lead poisoning is one of the hazards workmen face in ceramic

dye factories. The reason is that basic lead chromate (PbCrO^.PbO) is a raw material

for a red ceramic dye. Examinations were performed on 161 men, 16-62 years of age,

who had been working in a ceramic dye factory for 1-21 years. Clincial and laboratory results from men engaged in different phases of work were tabulated. Workmen

engaged in fusing and sifting of the raw material were found to be subject to the

greatest risk. An abstract of Pica's paper is given by Campbell and Mergard in the

EPA publication “Biological Aspects of Lead." [16]

Hartogensis and Zielhuis [15] discussed the effect of exposure to lead chromate dust

on 26 male workers in two pigment factories. Seven workers were exposed to less

than 0.1 mg Pb/m^ (Group A), five to 0.1-0. 2 mg Pb/m^ (Group B) and fourteen to

greater than 0.2 mg Pb/m^ (Group C). The hemoglobin (Hb) level was clearly subnormal

in Group C. The authors conclude that the maximum allowable concentration (MAC)

for lead chromate should be 0.1 to 0.2 mg Pb/m^, using the Hb decrease as a criterion.

5
They said that, because the same MAC had been established for other lead pigments,

the toxicity for all lead pigments, both soluble and Insoluble was similar. An

abstract for the paper by Hartogensis and Zlelhuls is given by Campbell and Mergard

in the EPA publication "Biological Aspects of Lead." [17]

A report translated from Japanese summarizes lung cancer statistics for workers in

a chromate plant in Japan [18]. The chromate factory was in operation from 1936-

1973. Of a total of 554 workers, 133 were exposed to chromates for ten years or

more. Of the 133, ten cases of cancer occured; four were lung cancer and, six,

cancer of the bronchial tubes.

A later report [19] discusses lung cancer in a chromate factory in Japan for the

period 1972-1976. Ten patients with lung cancer were among workers in a chromate

factory. Four additional cases were found through death certificates and medical

records. Most of these were smokers and all were men. The average duration of

exposure to chromates was 24 yedrs. The primary sites of the cancer were in the

large bronchi in the ten patients. The cell type was squamous (scale-like) in seven

patients and small anaplastic (having high reproductivity) in three. The incidence

(person per year) calculated from the number of employees, duration of factory

activity, number of cancer patients and shortest duration of labor period simong

the patients was 657.9 per 100,000 compared to 13.3 per 100,000 in Japan as a whole.

Fraumeni [20] discussed chemical carcinogenesis in man due to industrial exposure

and cited the work of Machle and Gregorius, Baetjer, Bldstrup and Case in their

j

I studies of the cancer hazard among chromate workers. He said than an elevated |

I risk of lung cancer had been linked to the chromate pigment industry in Norway [21]. |

1 The risk was not Increased among chromite-ore miners but only among workers producing >

i and processing chromium compounds.

6
Langard and Norseth [21] conducted a study of bronchial cancer among workers in a

small company in Norway which produced chromate pigments. The company had employed

133 workers from the time production started in 1948 until the end of 1972. The

study was conducted on 24 workers who had been exposed to chromate dust for more

than three years. Three of these workers developed lung cancer. One had been

employed for six years and had been exposed to both lead and zinc chromate pigment.

The other two had been employed for eight years and had been involved in the manual

mixing of solium dichromate. Two of the three workers were smokers. The authors

commented that it was difficult to judge to what extent the smoking habits of two of

these workers may have contributed to their lung cancers.

A follow-up study of mortality among workers at three English chromate pigment factories was performed by the Division of Epidemiology, Institute of Cancer Research

[22]. Two factories made both lead chromate and zinc chromate and workers were

exposed to both substances. The third factory made only lead chromate. Workers

were, for the purposes of this survey, classified by degree of exposure to chromates.

Work in the "dry” departments where pigments were ground, blended and packed was

classified as high. Medium classification covered work in the less dusty "wet"

compartments where precipitates were washed, pressed and stove-dried. In the low

classification, there was only slight exposure to chromates, e.g. most laboratory

jobs, painting, bricklaying. In the two factories producing both lead and zinc

chromate, there was a marked excess of lung cancer deaths. These occured among

workers within 5-25 years after the first exposure even if employed for as little

as one year. Under conditions prevailing at the third factory since 1946, lead

chromate appeared not to have caused lung cancer deaths. In the author’s opinion,

7
the results suggest that the manufacture of zinc chromate may involve a lung cancer

hazard, although Improved working conditions at one factory appear to have controlled

this hazard from about 1955.

In the National Academy of Science (NAS) study on chromium [23], the authors discussed the work of W. C Hueper on occupational respiratory tract cancer. Heuper

had a history of 187 cases of cancer in which the workmen handled chromates. Only

seven of these 187 did not have cancer of the lung. The study cited Hueper who

found that, in 123 cases of lung cancer in chromate workers around the world, cancers

were not of any single histologic type. There were 46 squamous-cell carcinomas, 66

round-cell carcinomas and 11 adenocarcinomas. One of the conclusions of the NAS

study was that the carcinogens present in the chromate manufacturing process have

not been identified.

The results of industrial exposure to mixed chromite and chromate compounds have

been summarized by Utidjian [10]. These Included dermatitis, perforation of the

nasal septum, inflammation of the lining of the eyelids and cancer of the lung.

Deichmann and Gerarde [24] stated that the results of the skin contact with hexavalent chromium compounds (chromates, dlchromates) may be dermatitis and slow-healing

ulcers. They warned that prolonged or repeated inhalation of mists or dusts will

result in perforation of the nasal septum. They indicted chromates as a group of

chemicals capable of Inducing pulmonary carcinoma in man.

Rauscher [25] commented that there was a direct relationship between lung cancer

and cigarette smoke and other Inhalation hazards. He defined these as asbestos.

8
chromates and radioactive materials. Grawey [26] stated that, "the strong supportive

data for a relationship between hexavalent chromium and lung cancer come from

chromate-producing industries, not from chromic acid exposures."

4.0 EFFECTS OF LEAD-CONTAINING SPRAY-APPLIED PAINTS ON PAINTERS WORKING IN

CONFINED AREAS

Neronskii [27] reported the effect of lead-containing spray applied paints on

painters. These men were spray painters employed in an auto factory. The lead

O content of the air in the workroom was 0.004 to 3.452 mg/m (greater than 0.01 in

96.7% of the samples), and solvent vapor concentrations were benzene 0.02 to 0.45

mg/H, toluene 0.02 to 0.32 mg/S,, and naphtha solvent 0.04 to 0.71 mg/S,. The aromatic

hydrocarbon content of the air exceeded permissible levels in 67.9% of the cases.

Physical examinations were performed on 216 painters whose duration of employment

ranged from several months to twelve years. Of these 9.7% showed signs of chronic

lead poisoning. The signs of chronic effects of benzene and its homologs were

also observed. The author concluded that health hazards were caused not only

by the lead pigment but by the solvents in the paint. To elimate these health

hazards, he recommended that lead-free paints be substituted for the lead-containing

paints and that solvents other than benzene and its homologs be used.

Ankerst and Weimer [28] discussed hazards in the enamel industry. Listed among the

toxic raw materials were red lead oxide, lead carbonate and lead silicate. The

authors cited the lethal dose of lead as between 11 and 27 g. They warned that

daily inhalation of approximately 1 mg of lead would result in abdominal and muscular

pain, paralysis and liver damage. The authors said that, while lead compounds have

been largely eliminated as raw materials in the enamel industry and precautionary

9
measures have been taken where they are still used, the complete exclusion of lead

compounds should be implemented; they said that the introduction of lead-free pottery

shows this to be feasible.

Zielhuis [29] discussed the toxicity, on the basis of existing literature, of many

raw materials used in the paint industry-binders, pigments including lead pigments,

driers, solvents, diluents and plasticizers. The work has carried out as an aid to

dermatologists involved in treating skin diseases caused by these substances. He

stated that, before 1930, lead poisoning was the most serious disease for painters.

He mentioned the hygienic precautions which were gradually introduced. These were

washing hands before eating, not sanding old paint residues or surfaces, using

paste pigments instead of powders and using a respirator when burning off paint.

He quoted the work of Oltramare who described two cases of lead poisoning in which

two workmen removed lead paint by sanding without wearing masks. For painters using

paints containing chrome yellow or chrome green pigments, the only forms of poisoning

have been related to the skin. Cases of erosion of the nasal septum caused by

chromic acid and chromate dust occur only in pigment factories and not in paintproducing or paint-using industries. Zielhuis said that this was because the precautions taken against lead poisoning were sufficient to prevent chromate damage

to the nose and skin. The danger of lung cancer which was present in Industries

working with chromite ore and with pigments "was probably” not present for people

who produce and use paint.

Two methods of spray painting without using compressed air for atomizing the paint

have been utilized. One method, employs hydraulic pressure alone ("high-pressure

method") and the other hydraulic pressure and heating the paint to reduce the

viscosity ( "heat-wlth-pressure method"). Proper ventilation for both of these

10
methods had been a source of much concern to industrial hygienists. A study was

conducted by Berghout [30] to indicate the health, safety and fire hazards associated

with the use of these methods. The primary objective was to determine whether an

air velocity of less than 150 ft/min (76 cm/sec) could be applied in the ventilation

control of spray booths, the extent of the health hazard being used on the concentration in the breathing zone of mist containing lead or zinc chromate pigment and

vapor from the thinner. Vehicle spraying with lead-bearing paint by the "highO pressure method" produced lead concentrations averaging 2.5 mg/m at air velocities

O of 105 ft/min (53 cm/sec) and 3.5 mg/m at 130 ft/min (66 cm/sec). Vehicle spraying

with lead-bearing paint by the "heat-with-pressure method" produced concentrations

averaging 4.4 mg/m at 62 ft/min (31 cm/sec) and 0.5 mg/m at 105 ft/min (53 cm/sec).

Missile container spraying with lead-bearing paint by the "high-pressure method"

produced concentrations of lead averaging 2.3 mg/m at 62 ft/min (31 cm/sec) and

O 3.3 mg/m at 105 ft/min (53 cm/sec) by the "heat-with-pressure method. Open shop

spraying of vehicles by the "high-pressure method" produced lead concentrations

averaging 3.2 mg/m"^ and solvent vapor concentrations of 590 ppm. Using the "heatO wlth-pressure method," lead concentrations average 5.9 mg/m and solvent vapor

concentrations averaged 800 ppm. The air velocities were not determined. From the

results obtained on analysis of air samples during spraying operations, the author

concluded that, at low rates of ventilation in vehicle spraying, personnel required

the protection of paint-spray respirators; also at air velocities less than 100

ft/min (51 cm/sec), dangerous concentrations of explosive vapors were recorded.

For missile container spraying, a ventilating rate of at least 150 ft/min (76

cm/sec) was required, and higher when bottom sides were sprayed. In open-face

booths, a ventilating rate of at least 150 ft/min (76 cm/sec) should be maintained.

Results in open shop spraying of vehicles Indicated danger from every standpoint.

11
A report on a survey of 50 paint plants by the Cleveland Bureau of Industrial

Hygiene to determine the amount of lead exposure, showed the value of adequate

ventilation [31]. Lead paints were manufactured in 28 plants on a routine basis.

A few other plants made several batches a month. In one plant, 1600 lbs (726 kg)

of a combination of lead and zinc pigments was used in paint formulation several

times a week. Analysis of air samples taken in the area where workmen were emptying

bags of these pigments showed an excess of 8 mg Pb/m'^. There was only one reported

case of lead poisoning which resulted in the death of the workman but the anonymous

author said there were undoubtedly many cases which were never reported. After

local exhaust ventilation was installed in this plant, air samples taken from the

O same area were found to contain 0.16 mg Pb/m"^. In plants where exposure had been

much greater, with installation of ventilation, lead reduction was even more pronounced. Abstracts of reference 22 through 26 are given in "Biological Aspects of

Lead." [32].

A health hazard evaluation determination was conducted by NIOSH at the Peabody

Gallon Corp, Unlsteel Body Division, Lima, Ohio [33]. It was determined that

employees were exposed to potentially toxic concentrations of lead in association

with spray painting operations at this plant. Employee exposure to lead was in

excess of the federal occupational health standard for eight hour time-weighted

average exposure of 0.2 mg/m"^. It was concluded that employee exposure to chromium

did not appear to be excessive. As reflected by total airborne paint particulate

concentrations, spray painting employees were exposed to excessive levels of paint

overspray. In interviewing the employees it became obvious that they had not

been properly instructed in the wearing, function and maintenance of their respiratory

protective equlpunent. It was also recommended that filters in spray booths be

12
changed frequently and where possible, spray painting should be conducted so that

the painter sprays toward the booth filters. Booths where large objects are painted

should be equipped with additional exhaust ventilation.

A health hazard evaluation was also conducted by NIOSH at the Harris Structural

Steel Co., Piscataway, N.J. [34]. Bridge girders were painted with lead silico

chromate paint which was applied by airless spray. Prior to painting, the girders

were prepared by workers who cleaned and ground each girder. From the analysis

of air samples, the exposure of the spray painter to lead was judged to be great

enough to cause adverse health effects, if unprotected. Exposure to chromium and

iron was judged to be at safe levels. The following recomendations were made (1)

Workers performing spray painting with lead paint should have their blood analyzed

for lead annually or urine analyzed for lead semi-annually, (2) an approved respirator

should be used by spray painters while painting with lead silico chromate paint

(Bureau of Mines Schedule 21B), (3) workers should wash hands and face thoroughly

before eating and no food beverages or tobacco should be permitted in the work

area, (4) workers should be provided with clean work clothes on a daily basis

with thorough showering after work before changing into street clothes.

Walgren [35] listed the solubility of chromium yellow light pigment and chromiun

yellow medium pigment in "hydrochloric acidic water" with a pH of 3 and 1 and

"assumes that the risk of poisoning would depend upon getting the soluble pigments

down to the stomach." He said the risk of release is considerably lessened by the

encapsulating film surrounding the pigment grains in the paint and therefore the

lead pigment powder and paint with lead pigment should be distinguished. He cited

the normal lead content in the blood as between 0.1-0. 5 ppm.

13
5.0 BIOLOGICAL INTERACTIONS OF CHROMIUM AND CHROMATES

The authors of the National Academy of Science study on chromium [36] stated that

chromium is an essential trace element for humans and animals. Hexavalent chromium

is a strong oxidizing agent which reacts readily with organic matter in acidic

solution while being reduced to the trivalent form. The NAS authors said that the

well known toxic action of chromates was due largely to ths oxidizing action.

Hexavalent chromium also had the property of easy penetration of biologic membranes.

These two properties distinguished hexavalent chromium from the trivalent form which

is much less toxic.

The authors stated that all the biologic interactions of chromate should result in

reduction to the trivalent form and later coordination to organic molecules. Hexavalent chromium is reduced within human skin to the trivalent state by methionine,

cystine and cysteine. Chromates penetrate the red blood cells, are reduced to

the trivalent form and bound to hemoglobin, resulting in a stable tagging of the

red blood cells. The author stated that there was some evidence that chromium

could exist in other valence states but there was no evidence that they played a

role in biologic systems. They concluded that chromium in biologic material rapidly

attained the trivalent form. Hansen [37] said that, while small quantities of

chromium are essential, larger concentrations are toxic. Inhalation is the main

way of absorbing it. The toxicity depends on the valence state of the metal. Generally speaking, the metal itself is Inactive. The greatest risk is from hexavalent

chromium which is toxic for all body cells. He commented on reports which told of

a high incidence of lung cancer where exposure to hexavalent chromium had occurred.

He stated that normal blood levels of chromium were 1.05-5.5 yg/100 ml.

14
6.0 ANIMAL STUDIES VTLTH HEXAVALENT CHROMIUM

The National Academy of Science study [36] reported on the work of Feldman [38] who

found that all hexavalent chromium injected intravenously into rats was rapidly

reduced. The same reduction occurred when hexavalent chromium was added in vitro

to rat tissues. The NAS authors also mentioned the work of Laskin, Kuschner and

Drew [39, 40] who tested the carcinogenic properties of the chromate ore roast

residue, calcium chromate, chromic chromate, chromic oxide and chromic trioxide.

Their technique consisted of using a very small capsule made of tine steel wire

mesh which was impregnated with the test chemical, and mixed in equal parts with

cholesterol. "This capsule was attached permanently with a fishhook to the inner

wall of the lower-lobe bronchus of the test rat in such a way as not to cause

obstruction." Six of the 100 rats exposed to calcium chromate developed squamouscell carcinoma of the bronchus and two of them developed adenocarcinoma. One of

the 100 rats developed squamous-cell carcinoma when exposed to roast residue. All

other compounds were without effect. The tumors were invasive and some metastasized (spread to other parts of the rat). Mean duration for exposure of the six

carcinomas caused by calcium chromate was 540 days and the duration for the two

adenocarcinomas were 366 and 609 days.

The NAS authors included the work of Roe and Carter [41] who tried repeated intramuscular injections of calcium chromate in arachls oil for a 20 week period and

produced sarcomas at the point of injection. These tumors were invasive but did

not metastasize.

Nettesheim et al. [42] reported results on experiments with mice exposed for 5 hrs/

day, 5 days/week for their lifetime to fine calcium chromate dust (70% of particles

smaller than 0.3 ym) , at a concentration of 13 mg/m . Control mice were exposed

15
to filtered air. The mice developed pulmonary adenomas at an earlier age than

control mice and had four times as many tumors. This work was also discussed by the

NAS authors. They said also that it had been demonstrated that, in experiments

with rats, invasive sarcomas (fleshy tumors) could be produced locally by implantation of a relatively insoluble hexavalent chromium compound in a medium that holds

the chemical in contact with the area. They considered it much more significant

that production of squamous-cell (scale-like) carcinoma of the bronchus in rats

had been produced by local implantation of calcium chromate in cholesterol pellets.

They concluded that, although calcium chromate was the specific chromium compound

responsible for cancer of the bronchus in rats, it would be "premature to say that

only this form of chromium can exert a carcinogenic effect."

Enterline [5] stated that "recent animal experiments suggest that the carcinogenic

agent in the old chromate producing plants was calcium chromate." He stated that

further epidemiological studies were needed to verify this.

A Midwest Research Institute study [43] on lead paint ingestion consisted of feeding

studies in which rats were fed rat chow mixed with different concentrations of

lead-containing paints as 0.1% of their diet. Used in the study were a control

paint with no lead, paints containing 0.08% lead octoate, 0.53% lead octoate, 2.05%

lead octoate, 0.42% lead chromate, 1.95% lead chromate, 12.43% lead chromate, 66.05%

lead carbonate, and NBS lead paint (11.92% lead carbonate). Rats were examined

after 4, 8 and 13 weeks. Both the 66.05% lead carbonate and the NBS lead paint

produced the signs of lead poisoning in rats, i.e., decrease in red blood cells,

and significant Increases in blood, kidney, bone, liver, and brain lead. With the

16
other formulations, the only evidence of toxicity was in the rats fed the 12.43%

lead chromate. This consisted of an increase in blood lead without other signs

of poisoning.

Lead chromate was investigated for its carcinogenic potential in both rats and mice

in a study performed at the Institute of Chemical Biology, University of San

Francisco [44] . Results show that this compound is a potent carcinogen in rats when

administered Intramuscularly (l.m.). Sixty four percent of the animals treated

developed malignant tumors at the injection site. Three renal carcinomas were also

found after i.m. treatment with lead chromate. Since lead powder is a comparatively

weak carcinogen in rats, whether given orally (p.o.) or i.m., the authors suggest

that the combination of lead and chromium (also a weak carcinogen) in lead chromate

accounts for the high carcinogenic activity of this compound in rats. Swiss albino

female mice could not tolerate the same high dose level as the rats. At the lower

dose administered to the mice, no tumors were detected. The mechanism of the action

of lead compounds as renal carinogens is unknown, but porphyrin metabolism is

disturbed.

Ninety-day feeding studies were conducted using 6-month-old beagle dogs to determine

the toxicologic effects and tissue residues resulting from ingestion of lead-containing pigments [45]

.

The pigments were lead carbonate, light chrome yellow (80%

lead chromate & 20% lead sulfate), medium chrome yellow (lead chromate), primrose

chrome yellow (60% lead chromate & 40% lead sulfate), and molybdate orange (80%

lead chromate, 15% lead molybdate and 5% lead sulfate). Groups of four dogs of

each sex were fed each pigment at dietary levels of either 2000, 5000 or 20,000

ppm. Early signs of lethargy, anorexia (loss of appetite), dehydration and emaciation

followed by hyperirritability, disorientation, motor ataxia and convulsions preceding

17
death were seen in animals fed 2000 ppm or greater of lead carbonate, 5000 ppm

or greater of light chrome yellow, primrose chrome yellow or molybdate orange and

20,000 ppm of medium chrome yellow. All the chemicals tested produced decreased

hemoglobin concentration and altered erythrocyte morphology, although the level

of exposure to produce these changes varied considerably. Also Involved were

pathologic changes of the kidney and cell changes. These occurred with all five

pigments. The most severe lesions with the shortest period of onset occurred

with lead carbonate. It was concluded that although the biological effects produced

by the five chemicals were similar, the quantitative aspects (dose needed to produce

the changes) are quite different.

7.0 AIR POLLUTION STUDIES RELATING TO CHROMIUM

Magee [46] said that there were large number of different chemicals known to cause

cancer in experimental animals but relatively few for which there was convincing

evidence of carcinogenic activity in man. He quoted a list by Hueper of recognized

carcinogens. This list included asbestos, arsenic, chromium, nickel, benzene, some

aromatic amines, coal tar pitch, soot, and mustard gas.

Woolrich [47] commented that "the principal harm done by the less desirable metals

is that they tend to displace physiologically desirable elements belonging to the

same periodic group. Barium and berylium inhibit absorption of calcium and strontium displaces calcium. Some elements accumulate with age, notably aluminum,

barium, tin, and titanium but do not normally reach dangerous levels. Some such

as chromium and vanadium are retained in the lungs in insoluble form.”

18
Shakman [48] stated that high levels of chromium were found in the air of heavy

industrialized areas. Chromium also occurred in water supplies as a minor contaminant. It occurred abundantly in tobacco smoke. Shakman commented on the variation

in the uptake of chromium from the soil by plants. Corn rejected hexavalent

chromium. Tobacco, on the other hand, selectively absorbed it.

According to Dreisbach [49], the fatal dose of a soluble chromate such as potassium

chromate, potassium dichromate or chromic acid was approximately 5 g. The threshold

limit value (TLV) for chromium (determined as chromic oxide) in air was 0.1 mg/m^.

The authors of the Litton Industry report [50] stated that the exact sources of

chromium in air pollution were not known. The possible sources cited are the

metallurgical Industry, chromate-producing industry, chrome plating, burning of

coal and the use of chromium chemicals such as fuel additives, corrosion inhibitors,

pigments, tanning agents, chromium mordants in the textile industry, fungicides,

wood preservatives, and rust inhibitors in cooling-tower recirculating water systems.

Other sources of chromium pollution are from asbestos, welding rod fumes and cement

o dust. In 1964, atmospheric concentrations of total chromium averaged 0.015 yg/m^

q and ranged as high as 0.0350 pg/m^. No evidence of damage by airborne chromium

to animals or plants had been found [51].

The NAS authors stated that the concentration of chromium in the ambient air of large

q industrial cities of the U.S. usually ranged from 0.01 to 0.03 yg/m"^ and in nonurban

q areas it was less that 0.01 yg/m [52]. The concentration of chromium in the soil

varied from tracers to 250 ppm as CrO^ although concentrations as high as 3900 ppm

had been reported in the literature. The total chromium intake per day by man had

19
been estimated as 5 to 115 pg in food and water and 0.04 to 0.08 pg in air. There

were no known harmful effects from the chromium in the ambient air or from dietary

intake.

Linton et al [53] have established that toxic trace elements such as As, Be, Cd, Cr,

Mn, Ni, Pb, Sb, Se, Tl, V and Zn are being discharged in the atmosphere in association

with particles emitted from fossil fuel combustion and conversion. It has also

been shown that the specific concentration of many of these elements (in micrograms

per gram of fly ash) increase with decreasing particle size in fly ash derived from

coal combustion. Consequently, the highest trace element concentrations are encountered in small particles which most readily pass through control devices, which

remain suspended in the atmosphere for long periods and which deposit in the

innermost regions of the human respiratory tract when inhaled. These results are

of real significance because they show that conventional bulk analyses provide a

poor measure of the actual concentrations of many toxic trace elements that are

in effective contact with the external environment of a particle.

The American Standards Association (ASA), now called the American National Standards

Institute (ANSI), American Conference of Governmental Industrial Hygienists (ACGIH)

and Occupational Safety and Health Administration (OSHA), have all set limits for

chromium concentration in air of industrial plants [54]. For all three the limit

O for chromic acid and chromates, as CrO^ is 0.1 mg/m"^; for AGGIH and OSHA, the

limit for chromium as soluble chromic and chromous salts as Cr is 0.5 mg/m , chromium

O metal and Insoluble salts as Cr, 1.0 mg/m , and for ACGIH some insoluble chromates

0.1 mg/ . The National Institute of Occupational Safety and Health has Issued

recommended limits for hexavalent chromium [55]. Those chromium compounds which are

considered as non-carclnogenlc are the monochromates and dichromates of H, Li, Na,

20
K, Rb, Cs, NH^, and Cr'*’^ oxide (chromic acid anhydride). All the rest are considered

to be carcinogens. For carcinogens, the maximum allowable concentration is 25 yg

Cr /m as a time weighted average exposure for up to a 10 hour work day, 40 hour

work week. For non-carcinogenic compounds, the maximum allowable concentration as

I r o determined by a 15 minute sample is 50 yg Cr °/m^.

8.0 WATER POLLUTION STUDIES RELATING TO CHROMIUM IN RUNOFF FROM STREETS

Sarter and Boyd [56] discussed pollution aspects of storm water runoff in an EPA

report. They stated that the street surface runoff for the hypothetical city

following one hour storm [0.5 inch (1.27 cm) of rain] would contribute considerably

more pollution load than the city’s sanitary sewage during the same time. They

defined a hypothetical city as one having a population of 100,000 people, total

land area of 14,000 acres (5,666 hectares), land-use distribution of 75% residential,

5% commercial, and 20% industrial. It has 400 curb miles (644 curb km) of streets

(tributary to receiving waters) and a sanitary sewage output of 12 x 10^ gal/day

(4.54 X 10^ i/day). The streets are cleaned (intentionally or by rainfall) every

5 days.

The calculated quantities of pollutants which would enter the receiving waters of

a hypothetical city from the street surface runoff following a one-hour storm were

compared with pollutants from raw sanitary sewage and are listed below. The metals

were analyzed to determine total quantity, not specific chemical form. From the

data given by Sarter and Boyd, table 8.1 was prepared.

Sarter and Boyd [56] also determined the metal content of street surface contaminants

for seven selected communities. These were San Jose, Phoenix,, Milwaukee, Baltimore,

Seattle, and Atlanta. The weighted averages in ib/curb mile (kg/curb km) for metals

21
were as follows: chromium 0.11 (0.03); copper 0.20 (0.06); zinc 0.65 (0.18); nickel j

0.05 (0.014); mercury 0.073 (0.02); lead 0.57 (0.16). Total heavy metals per curb

mile was 1.6 lb (0.45 kg/curb km). The sampling was random. They could not determine

the time period for accumulation of the contaminants. The authors commented that the

fact that the weighted average of the total heavy metal was as high as 1.6 Ib/curb

mile (0.45 kg/curb km) was "rather alarming."

I Sarter and Boyd stated that the sources of the street surface contaminants included

pavement, motor vehicles, atmospheric "fallout," vegetation, runoff from adjacent

land areas, litter, spills, and anti-skid compounds. The contaminants included

asphaltic and portland cement, their various products of decomposition and aggregate

materials. Also included were small amounts of road marking paints, crack fillers

and expansion joint compounds. On a weight basis, aggregate materials accounted

for the largest contribution of materials from the pavement.

Sarter and Boyd commented that one of the most important findings of their study

was that a great portion of the pollution potential was associated with the fine

1 solids fraction of the street surface contaminants. Very fine silt-like material j

I (less that 43 microns) accounted for only 5.9% of the total solids. It also |

I accounted for over 1/2 of the heavy metals, nearly 3/4 of the total pesticides, 1/4

| of the oxygen demand, and 1/3 to 1/2 of the algal nutrients.

Depression of dissolved oxygen was one of the most significant detrimental effects

a pollutant could have on receiving waters. Subtantlal loads of oxygen demanding

substances could lead to fish kills, foul odors, and slime growth. Heavy metals

I were of concern because of their potential toxicity to various biological forms.

Also they destroyed the bacteria necessary in the activated sludge process. !

{

i1 22
Table 8.1

Settleable plus suspended

solids

Biological oxygen

demand (BOD)

Chemical oxygen

demand (COD)

Kjeldhal nitrogen

Phosphates

Zinc

Copper

Lead

Nickel

Mercury

Chromium

Total coliform

bacteria (org/hr)

Street Surface Runoff

(following 1 hr storm)

Ib/hr kg/hr

560,000 254,016

5,600 2,540

13,000 5,897

880 300

440 200

260 118

80 36

230 104

20 9

29 13

44 20.

4,000 X 10^°

Raw Sanitary Sewage

lb /hr kg/hr

1,300 590

1,110 499

1,200 544

210 95.3

50 22. 7

0.84 0.38

3 0.17 0.08

3 0.13 0.06

1 0.04 0.02

1 0.27 0.12

0 0.17 0.08

460,000 X 10^°

23
The authors, is discussing the heavy metals, said that zinc and lead had the

heaviest loadings, chromium and nickel the lightest. These trends were borne out

in all the cities tested. The arithmetic mean for lead was 0.68 lb/ curb mile (0.19

kg/curb km) and for chromium 0.12 Ib/curb mile (0.033 kg/curb km). For all metals

except mercury, loading intensities (in Ib/curb mile) were heaviest in industrial

areas and lightest in commercial areas. The loading intensities for lead in street

surfaces ranged from a low of 0.030 Ib/curb mile (0.008 kg/curb km) (Tulsa) to

a high of 2.0 Ib/curb mile (0.56 kg/curb km) (San Jose). There was a strong tendency

for lead to be associated with solids of a small particle size range. Nearly 90%

of the total lead found was with particles smaller than 246 microns. It was not

known whether the lead existed in a compound whose particles were of this size

or if the lead was adhering to particles of this size. The USPHS drinking water

standards limit lead to 0.05 ppm. Chromium was not found in substantial quantities

in street surface contaminants. Loading Intensities ranged from 0.0033 Ib/curb

mile (0.0009 kg/curb km) (Tulsa) to 0.45 Ib/curb mile (0.126 kg/curb km) (Baltimore).

The USPHS drinking water standards limit hexavalent chromium to 0.05 ppm but state

no limit for the trivalent forms. Limits of 100 ppm for fisheries and 5 ppm for

Irrigation water have been recommended.

Additional work on the analysis of street surface contaminants was carried out by

Pitt and Amy [57]. They concluded that industrial and commercial land use areas

have the greatest content (mg/kg of heavy metals). They found that the metals

associated with street runoff were 100 to 1000 times greater that the sewage metals

on a slug load basis (Ibs/hour) and from 10 to 100 times on a concentration basis

(mg/l). However, the metal content of a street runoff was usually not sufficient

to cause noticeable reductions in biological treatment efficiency in plants handling

24
combined sewage-storm water drains. The solubilities of heavy metals in a simulated

receiving water environment (dechlorinated tap water) were low, most being less than

10% of the available metal. Elemental composition of street surface contaminants

determined by mass spectrographic analysis showed the following concentration for

chromium and lead:

Residential Industrial Commercial

Chromium 200 mg/kg 500 mg/kg 100 mg/kg

Lead 2000 mg/kg 5000 mg/kg 5000 mg/kg.

In terms of Ib/curb mile (kg/curb km) the concentrations of chromium and lead

were as follows:

Residential Industrial Commercial

Chromium 0.240 (0.067) 1.4 (0.394) 0.029 (0.008)

Lead 2.4 (0.676) 14 (3.94) 1.4 (0.394)

9.0 STREET CONSTRUCTION MATERIALS AND SURFACE CONTAMINANTS AS SOURCES OF CHROMIUM

As mentioned previously, street surface contaminants and construction materials

contain appreciable amounts of lead and chromium. Amy et al. [58] mentioned special

additives used in deicers as causing pollution problems. Chromate and phosphate

additives, used as corrosion inhibitors, had been found in high quantities. A study

of snow-melt collections conducted in the Minneapolis-St . Paul area showed values

of up to 1.7 mg/ £. of hexavalent chromium.

Shaheen listed the sources of chromium and lead and also the amounts of wg/g found

on analysis of these "pure" materials. (See Table 21, reference 59). The sources

of chromium were as follows:

25
1. Wear from metal plating, rocker arms, crankshafts and rings

2. Gasoline - 15 yg Cr/g

3. Asphalt pavement - 357 yg Cr/g

4. Concrete - 93 yg Cr/g

5. Rubber - 182 yg Cr/g

6. Diesel fuel - 15 yg Cr/g

7. Brake linings - 2200 yg Cr/g

8. Brake fluid - 19 yg Cr/g

9. Cigarettes - 71 yg Cr/g

10. Area soil - 36 yg Cr/g

The sources of lead were as follows:

1. Wear from babbitt metal bearings

2. Gasoline - 663 yg Pb/g

3. Motor oil - 9 yg Pb/g

4. Transmission fluid - 8 yg Pb/g

5. Antifreeze - 6 yg P

6. Undercoating - 116 yg Pb/g

7. Asphalt pavement - 102 yg Pb/g

8. Concrete - 450 yg Pb/g

9. Rubber - 1110 yg Pb/g — lead oxide is used as a filler in tires

10. Diesel fuel - 12 yg Pb/g

11. Brake linings - 1050 yg Pb/g

12. Brake fluid - 7 yg Pb/g

13. Cigarettes - 492 yg Pb/g

26
Traffic paints were not considered in the preparation of these lists. As will be

seen from the following calculations, they should not be ignored. In our laboratory

formulated yellow traffic paint, there are 69 g of lead chromate in 595 g of dry

paint. The lead chromate is 95.5% PbCrO^.

X 207.21/323*22 = 0.071 g Pb/g of dry paint

^595^^" ^ 52.01/323.22 = 0.018 g Cr/g of dry paint

Paints complying with Federal Spec. TT-P-115C had a lead chromate content of 2.52

Ib/gal (0.30 kg/l) compared to our laboratory formulated paint with 1.36 Ib/gal

(0.16 kg/i). Their Pb and Cr concentrations would be 0.071 x 2.52/1.36 = 0.131

g Pb/g of dry paint and 0.018 x 2.52/1.36 = 0.033 g Cr/g of dry paint.

An article by H. V. Warren, an abstract of which appeared in reference [60],

discussed the relationship between geology and health. A portion of the abstract

is as follows:

"Warren cites Alien-Price's epidemiological studies on cancer in West

Devonshire, England, which showed a striking difference in the cancer

rate in the different parishes of West Devonshire. He stated that the

water supply was the only factor which could account for this difference

Hillman, whose paper apparently had not been known to Alien-Price, had

found an abnormally high content of Pb, Hg, Sn, Cu, and Zn in trees and

soil of this area and high Pb concentrations in twigs and leaves of trees

growing in the proximity of Pb-Zn deposits. Howe (1961) reported clearly

varying epidemiological patterns for some types of cancer and implicated

Pb, Zn and polluted water in causing gastric cancer. There was a wide

variation in content of Pb and other metals in rocks and soils."

27
10.0 CALCULATION OF POSSIBLE CONTRIBUTION OF YELLOW TRAFFIC STRIPING TO LEAD AND

CHROMIUM CONTENT OF ROADWAY PARTICULATES

We have made a calculation of the possible contribution of yellow traffic striping

to lead and chromium in roadway particulates. In doing so, the following assumptions have been made: (1) there is complete erosion in 1 year, (2) traffic striping

is applied at a rate of 100 ft^/gal (2.45 m^/*") at a wet film thickness of 15 mils,

and (3) the paint stripe is 4" (10.1 cm) wide. (4a) The traffic paint has the

lead chromate content of Fed. Spec. TT-P-115C or 2.52 lb lead chromate/gal (0.30

kg/^). (4b) The traffic paint has the lead chromate content of our laboratory

formulation of 1.36 lb lead chromate/gal (0.16 kg/^). (5) The purity of the lead

chromate is 95.5% PbCrO^.

One gallon (3.785 *") of yellow traffic paint would be needed for 300 ft (0.09 km)

of a 4" (10.1 cm) wide stripe, (0.333 x 300’ = 100 ft^). It would take 17.6 gal

(66.6 *") to paint a strip one mile long (1.6 km), (5280/300 = 17.6 gal/mi).

(a) 17.6 X 2.52 x 0.955 x 207.21/323.22 = 27.15 lb Pb (12.31 kg) eroded in one year or 0.52 Ibs/week/curb mile (0.15 kg/wk/curb km).

17.6 X 2.52 X 0.955 x 52.01/343.22 = 6.81 lb Cr (3.09 kg) eroded in one year or 0.31 Ibs/wk/curb mile (0.037 kg/wk curb km).

(b) 17.6 X 1.34 X 0.955 x 207.21/232.33 = 14.43 lb Pb (6.54 kg) eroded in one

' year or 0.28 Ibs/wk/curb mile (0.079 kg/wk/curb km).

| 17.6 X 1.34 X 0.955 x 52.01/323.22 = 3.62 lb Cr (1.64 kg) eroded in one ! year or 0.07 Ibs/wk/curb mile (0.020 kg/wk/curb km). i

1

Shaheen demonstrated (see Table 2, reference 61) the significance of traffic-related )

I roadway deposits to urban water pollution. He stated that traffic-related heavy

j

f metals constituted the most serious contaminant from the stormwater source when

j compared with sewage. For example, close to 100% of the lead entering urban receiv-

|

I Ing water was from traffic-related sources. He said the most serious emission was

|

the traffic-related asbestos deposited on roadways and discharged as an air pollutant.^
I Shaheen also commented on the effect of curb height upon the amount of material

j

i collected from the roadway. The amount of dust and dirt collected along the roadway

i smaller than 3.5 mm particle size increases with curb height up to 15 to 20 inches

j

j (38 to 51 cm). He said his data showed that considerable quantities of the smaller

i

j size particles became airborne and were carried over the curbs to areas adjacent to

the roadways. Lead, zinc and rubber were found to be considerably higher during

j warm weather while other heavy metals were deposited at a relatively uniform rate

j throughout the year. This was attributed to greater tire wear at higher ambient

1 temperatures. He further commented that quantitative recovery of particulates

from the roadway could be achieved by careful vacuuming of the roadway followed

by a separate collection of a water flush of the street surface. The average percent

of total lead in the water flush was 4% (std. dev. 2%). The average percent of

total chromium in the flush portion was 17% (std. dev. 15%. These measurements

were taken in the Washington, D.C. area.

11.0 CONCLUSIONS

Based upon a survey of the literature, the following conclusions may be made:

I

I

I

j

1. Reports from Germany, Japan, England, France, Sweden, Norway, and

j Italy as well as the U.S.A. emphasize the high incidence of lung

cancer and other respiratory diseases among workers involved in

j the manufacture of chromates.

I 2. According to the National Academy of Science report on chromium,

the carcinogens present in the chromate manufacturing process

I

! have not been identified.

29
3. Hexavalent chromium is toxic for all body cells. The USPHS limits

its concentration in water to 0.05 pm. The NIOSH limits concentration

in working areas to 1 yg Cr /m .

4. In animal studies, calcium chromate was found to produce cancer

in rats.

5. No harmful effects from chromium metal in the ambient air are known.

Chromium is an essential tract element.

6. The USPHS drinking water standards limit lead to 0.05 ppm.

7. Water pollution from storm water runoff is considerably higher than

from sanitary sewage. Traffic-related heavy metals, including lead

and chromium, constitute the most serious contaminant for the storm

water sources.

8. The fine solids fraction of street surface contaminants accounts

for a great portion of the pollution potential.

It was noted that the literature search showed several gaps in information on

lead and chromium in environment. Among these were:

“ The exact sources of chromium in air pollution are not known, although

several possible sources were cited.

® The contribution of yellow traffic paint striping to the lead chromium

content of roadway particulates, stormwater runoff, or of areas adjacent

to roadways is not known.

“ No work has been reported on the measurement of lead chromate in the

ambient air during the application of leaded traffic paint. (This

30
is surprising in view of the high incidence of lung cancer among workers

in chromate pigment plants and of lead poisoning among spray painters

employing lead paints in auto factories).

f These gaps may suggest areas for future study.
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481, D.C. Health & Co., Boston, 1957.

3. Udy, Marvin J. , "Chromium" Vol. 1, pp. 267-270, Reinhold Publishing Corp.,

New York, 1956.

4. Wormald, George, "Treatise on Coatings," Vol. 3, Pigments, Part I, pp. 316-

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5. Enterline, Philip E., "Respiratory Cancer Among Chromate Workers," Journal of

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pp. 1114-1127, Reprint No. 2882, August 1948.

7. Federal Security Agency, "Health of Workers in Chromate Producing Industry,

A Study." U.S. Public Health Service Publication No. 192, Washington, D.C.,

U.S. Government Printing Office, 1953.

8. Sullivan, R. M. , et al., Litton Industries, Inc., "Air Pollution Aspects of

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32
11. Bidstrup, P. L. and Case, R. A. M. , "Carcinoma of the Lung in Workmen in the

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33
19. Chasakl, Y., Abe, S., Kimura, K. , Tsumeta, Y., Mikami, H. , and Murao, M.

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32 , pp. 62-65, Feb. 1975.

22. Davies, J. M. "Lung Cancer Mortality of Workers in Chromate Pigment Manufacture

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124-6, 1963.

34
29. Zlelhuis, R. L. (Paint and Health. I, II, III.) Verfkroniek 30, pp. 178-80,

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30. Berghout, C. R. (Army Chemical Center, MD), "Spray Painting Without Compressed

Air," Archieves of Environmental Health 1^, pp. 53A-9, 1960.

31. Annonymous: "Cleveland Paint Factories Install Ventilation to Protect Workers

from Lead," Occupational Health 12 , p. 44, March 1952.

32. Campbell, Irene R. and Mergard, Estelle, G., "Biological Aspects of Lead:

An Annotated Bbliography" Parts I and II, Abstracts Nos. 2771, 2498, 3146,

3165, and 3091, Environmental Protection Agency, May 1972.

33. U. S. Department of Health, Education and Welfare, National Institute for

Occupational Safety and Health, Cincinnati, Ohio "Health Hazard Evaluation

Determination Report No. 73-47-172.

34. U. S. Department of Health, Education and Welfare, "National Institute for

Occupational Safety and Health, Cincinnati, Ohio 45202. Health Hazard

Evaluation Determination Report No. 73-99-108.

35. Wallgren, Per-Ake, "The Effect of Hazardous Materials on the Human Body,"

Farg Och Lack pp. 47-51, 1972.

36. Committee on Biologic Effects of Atmospheric Pollutants, Division of Medical

Sciences, National Research Council, "Medical and Biologic Effects of Environmental Pollutants-Chromium," pp. 23-24 and 73, National Academy of Sciences,

1974.

37. Hansen, J. C., "The Toxicology of Some Heavy Metals," Ugeskrift fur Laeger

136 , No. 16, pp. 853-8, 1974.

38. Feldman, F. J., "The State of Chromium in Biological Materials," Federal

Proceedings 27, p. 482, 1968 (abstract).

35
39 . Kuschner, M. and Laskin, S., "Experimental Models in Environmental Carcinogenesis," American Journal of Pathology, 64 , No. 1, pp. 183-6, July 1971.

40. Laskin, S., Kuschner, M. and Drew, R. T. , "Studies in Pulmonary Carcinogenesis," pp. 321-350. In M. G. Hanna, Jr., P. Nettesheim and J. R. Gilbert,

Eds. Inhalation Carcinogenesis. AEC Symposium Series 18, Oak Ridge, Tenn.,

United States Atomic Energy Commission Division of Technical Information, 1970.

41. Roe, F. J. C. and Carter, R. , "Chromium Carcinogenesis. Calcium Carbonate

as a Potent Carcinogen for the Subcutaneous Tissues of the Rat" British

Journal of Cancer pp. 172-6, 1969.

42. Nettesheim, P. M*» Hanna, M. G. , Jr., Doherty, D. G. , Newell, R. F., and

Heilman, A., "Effects of Chronic Exposure to Artifical Smog and Chromium

Oxide dust on the Indicence of Lung Tumors in Mice,“ pp. 305-320. In M. G.

Hanna, Jr., P. Nettesheim and J. R. Gilbert, Eds. Inhalation Carinogenesis,

AEC Symposium Series 18 Oak Ridge, Tenn., U.S. Atomic Energy Commission,

Division of Technical Information, 1970.

43. Midwest Research Institute, "Lead Paint Ingestion Study," National Paint and

Coatings Association, Inc., Washington, D.C., 1974.

44. Furst A., Schlauder, M. , Sasmore, D. P. "Tumorigenic Activity of Lead Chromate",

Cancer Research 3^ (5), pp. 1779-1783.

45. Chrlstofano, E. E., Kennedy, G. L. , Gordon, D. E. Kepllnger, M. L. & Calandra,

J. C. , Hercules, Inc., Wilmington, Delaware; and Industrial Bio-Test

Laboratories, Inc., Northbrook, Illinois "Toxicity of Lead Chromate Pigments

and Tissue Residues Following 90 days feeding to Beagle Dogs", Toxicology and

Applied "Pharmocology , 37^, No. 1, p 161, 1976.

46. Magee, P. N. , "Carcinogens in the Environment," Proceedings of the Royal Society

of Medicine," 67, No. 8, pp. 741-3, 1974.

36
47. Woolrlch, Paul F., "Occurrence of Trace Metals in the Environment - An

Overview," American Industrial Hygiene Association Journal 3^, No. 5, pp.

217-226, 1973.

48. Shakman, Robert A., "Nutritional Influences on the Toxicity of Environmental

Pollutants," Archives of Environmental Health, p. 197, 1974.

49. Dreisbach, Robert H. , "Handbook of Poisoning: Diagnosis and Treatment,” 8th

ed. , p. 201, Lange Medical Publications, 1974.

50. Litton Industries, Inc., "Air Pollution Aspects of Chromium and Its Compounds,

pp. 1, 19-25, PB 188 075, National Technical Information Service.

51. Ibid, p. 36.

52. Committee on Biologic Effects of Atmospheric Pollutants, Division of Medical

Sciences, National Research Council, "Medical and Biologic Effects of

Environmental Pollutants-Chromium," pp. 107-108, National Academy of Sciences,

1974.

53. Linton, R. W.; LOH, A; Natusch, D. F. S.; Evans, C. A. Jr; Williams, P.

"Surface Predominance of Trace Elements in Airborne Particles", Science 191 ,

852-4 1976.

54. Committee on Biologic Effects of Atmospheric Pollutants, Division of Medical

Sciences, National Research Council, "Medical and Biologic Effects of

Environmental Pollutants-Chromium", pp. 90-91, National Academy of Sciences,

1974.

55. NIOSH Criteria for Recomended Standard. 1. Occupational Exposure to Cr (VI),

HEW Publication No. (NIOSH) 76-129.

56. Sarter, James D. and Boyd, Gall B, "Water Pollution Aspects of Street Surface

Contaminants," EPA-R2-7 2-081 , pp. 2-4, 27-31, 50, 68, 74-76, 136-7. Nov. 1972

37
57 . Pitt, Robert E. and Amy, Gary, "Toxic Materials Analysis of Street Surface

Contaminants,” EPA-R2-73-283, pp. 1, 12, 17, August 1973.

58. Amy, Gary; Pitt, Robert; Singh, Rameshawar; Bradford, Westly; and La-Graff,

Michael, "Water Quality Management Planning for Urban Runoff," EPA-440/9-75-004

Sect. 3, p. 2, December 1974.

59. Shaheen, Donald G. , "Contributions of Urban Roadway Usage to Water Pollution,"

EPA 600/2-75-004, p. 72, April 1975.

60. Campbell, Irene R. and Mergard, Estelle G. , "Biological Aspects of Lead: An

Annotated Bibliography" Part 1, p. 478, Environmental Protection Agency, May

1972.

61. Shaheen, Donald G. , "Contributions of Urban Roadway Usage to Water Pollution,"

EPA 600/2-75-004, p. 5, April 1975.

38
NBS-114A (REV. S-7B)

U.S. DEPT. OF COMM.

BIBLIOGRAPHIC DATA

SHEET

1. PUBLICATION OR REPORT NO. 80-1974

5« tilt's Accession No,

4. TITLE AND SUBTITLE

Lead Chromate Pigments - A Literature Survey on Environmental and Toxic Effects

5. Puhlication Date February 19^

6 . Performing Organization Cede

7. AUTHOR(S)

M. A. Post and P. G. Campbell

8. Performing Organ. Report No.

9. PERFORMING ORGANIZATION NAME AND ADDRESS

NATIONAL BUREAU OF STANDARDS

DEPARTMENT OF COMMERCE

WASHINGTON, DC 20234

J.O».^ojfect/Task/Work Unit No. 4615455

11. Conti act/Grant No. FHWA No. P.O. 5-4-0188

12. SPONSORING ORGANIZATION NAME AND COMPLETE ADDRESS rsfreer, City, state, ziP)

Office of Research and Development

Federal Highway Administration

U.S. Department of Transportation

Washington, D.C. 20590

13. Type of Repoit & Period Covered

14. ^nsOrlng Agency Code

15. SUPPLEMENTARY NOTES

r I Document describes a computer program; SF-185, FIPS Software Summary, is attached.

16. ABSTRACT (A 200^word or leas factual summary of most significant information. If document includes a significant bibliography or

literature survey, mention it here.)

In connection with an evaluation of the performance of possible alternative yellow

pigments, a literature search was made on the toxicity and environmental effects of

lead chromate pigments. The literature reveals that workers in chromate plants in

the U.S., Europe and Japan have had a high incidence of lung cancer as well as other

respiratory ailments. Further, reports on the biologic, interactions of chromium

show that chromium in its hexavalent state (chromate, dichromate) penetrates body

membranes such as skin and the walls of red blood cells and is subsequently reduced

to the trivalent state and complexed with organic molecules. While the carcinogen

in the chromate manufacturing process has not been identified, animal experimen'ts

have shown that calcium chromate can produce cancer in rats. Information is

presented on sources of chromium in air and water pollution. Also, the pollution

aspects of lead and chromium in storm water runoff and as street contaminants are reviewed.

17. KEY WORDS rs ix to twelve entries; alphabetical order; capitalize only the first letter of the first key word unless a proper name;

separated by semicolons)

Air pollution; chromate ore; environmental effects; lead chromate pogments; storm

water runoff; toxicity; water pollution.

18. AVAILABILITY ®Unlimited Q For Official Distribution. Do Mot Release to NTIS

[7] Order From Sup. of Doc., U.S. Government Printing Office, Washington, DC

20402, SD Stock No. SN003-003-

Order From National Technical Information Service (NTIS), Springfield, VA. 22161

19. SECURITY CLASS

(THIS REPORT)

UNCLASSIFIED

20. SECURITY CLASS

(THIS PAGE)

UNCLASSIFIED

21. NO. OF

PRINTED PAGES

42

22. Price

$6 .00

USCOMM-DC
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