Philip Morris
Review 890000 Alice Hamilton Lecture Lead and Human Health:Background and Recent Findings
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- 2025545673-6381 Risk Analysis in Occupational and Environmental Health 910904 - 910906
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- 2025545872-5881 How Do Cancer Risks Predicted From Animal Bioassays Compare with the Epidemiologic Evidence? the Case of Ethylene Dibromide
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- 2025546047-6062 Limitations to the Use of Employee Exposure Data on Air Contaminants in Epidemiologic Studies
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- 2025546146-6149 Risk Assessment in Environmental and Occupational Health Risk of Alar (Daminozide)
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- 2025546163-6168 Daminozide Special Review Technical Support Document - Preliminary Determination to Cancel the Food Uses of Daminozide
- 2025546169 Daminozide / Udmh
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- 2025546174-6175 A Movie Star Pares the Apple Industry
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- 2025546226 Epa Moves to Reassess the Risk of Dioxin Urged on by the Scientific Community, Epa Is Developing A New Model for Estimating Dioxin's Risk
- 2025546227 US Government Orders New Look at Dioxin the Environmental Protection Agency Is Evaluating Data From the Past Decade That Suggest Dioxin's Toxicity May Be Overestimated. A Risk Assessment Model Based on Biological Mechanism Is Being Drawn Up.
- 2025546228-6235 Dioxin Toxicity: New Studies Prompt Debate, Regulatory Action New Data on Dioxin's Effect on Humans, A Clearer Picture of the Cellular Events It Precipitates, and New Animal Toxicity Studies May Provide Epa with A Firm Basis for Regulation
- 2025546236-6250 the Regulation of Gene Expression by 2,3,7, 8-Tetrachlorodibenzo-P-Dioxin
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- 2025546276-6281 the Long-Term Effects of Exposure to Low Doses of Lead in Childhood An 11 - Year Follow-Up Report
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- 2025546357-6362 Communicating Risk Under Title III of Sara: Strategies for Explaining Very Small Risks in A Community Context
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- 2025546369-6370 Too Many Rodent Carcinogens: Mitogenesis Increases Mutagenesis
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- 2025546374-6378 Health and Safety Risk Analyses: Information for Better Decisions
- 2025546379-6381 Telling Reporters About Risk Dealing with Reporters Needn't Be the Least Agreeable Part of the Job.
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ENVpRONMENTAL ttESEA,iCH Sl, 1-24 (1990)
REVIEW
1989 Alice Hamilton Lecture'
Lead and Human Health: Background and Recent Findings
MORTON LIPPMANN
New York University Medical Center, lrtstitr+te ojG'itviromttenta! Medicine,
Tuxedo, New York 10987
Received March 22, 1989
This paper, prepared in tribute to Dr. Alice Hamilton on her 120th birthday, reviews her
pioneering studies of occupational lead poisoning and its control, her IarYely unheeded
warnings about the possible consequences of widespread lead exposure to the general public
through the use of leaded fuel, and the results of recent studies of human exposure to and
health effects of tead in the general environment. Evidence is presented for dose-related
non-threshold effects for children with blood lead concentrations below 25 µgldl for a
variety of effects including verbal IQ; mental development; physical size; and age at phys-
ical m1'lestones such as first steps, hearing thresholds, and postural sway. For adults, various
studies have produced associations between blood pressure and blood lead concentrations
below 35 p.gfdl, suggesting possible etfects on cardiovascular health. Wlu7e the biological
rnechanisms responsible for these effects remain poorly understood, recent and current
efforts to reduce exposure to kad by the virtual elimination of lead in psoline and food
packaging show that we have learned one of Dr. Harulton's important kst:ons, i.e., that the
most effective means of reducing excessive exposures are through control of the enviroit-
ftlental smiSrces. e H90 Asadamic Press, inc.
INTRODUCTION
The invitation to present the second Alice Hamilton lecture led me to reread her
autobiography (Hamilton, 1943) FxpdoriRg the Dangerous Trades (Fig. 1) which,
in turn, led me to select lead's effects on human health as the focus of this lecture.
The systematic study of lead poisoning among industrial workers which Dr. Ham-
ilton performed so well, virtually single-handedly, in Illinois in 1910 led her, and
those she influenced, to new careers in occupational medicine and worker health
protection. Her emphasis on exposure prevention through the application of en-
gineering controls to process technology gave powerful impetus to the develop-
ment of the fieid of industrial hygiene in this country.
Dr. Hamilton was personally persuasive. She had to be. As she has written:
Our procedure in the Illinois survey and in the work that I carried on later for the Federal
government was completely informal. We had no authority to enter any plant, we had no
instructions as to which we should visit, we simply explored the state. When we found a
place which seemed to belong in our field, we asked permission to enter it. Never were we
refused, never did 1, at kast, meet with anything but courtesy in those very early days.
t Presentation: National Institute for Occupational Safety and Health, Cincinnati, Ohio. February
27, 1989.
0013-9351/90 S3.®0
Cor.1rijht C 1990 b> Academie Prcu. Inc.
All rijht- of ttproductioo in an> fam rcscrveE.

MORTON LIPPMANN
EXPLORING THE
DANGEROUS TRADES
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Fto. 1. Frontispiece and titk page of Erplosinj the Dangerous Trodes.
As Dr. Hamilton noted, however, it was usually difricult to convince manage-
ment that the conditions and exposures she observed were sufficient to warrant
controls. As a good example she cites the following:
... the National Lead Company ,.. had several white-lead and tead-oxide works in and
near Chicago. I visited them and found much dangerous work;oing on in alt of them. One
ogthe vicepresidents, Edward Cornish, later president, came to Chicago and I went to see
him in the Sangamon Street works. He was both indignant and incredulous when I told him
I was sure men were being poisoned in those plants. He had never heard of such a thing;
it could not be true; they were model plants. He went to the door and shouted to a passing
workman to come in. "Did the lead ever make you sick?" he demanded. The man, a badly
scared Slav stammered. "No, no, never sick." "Any other men sick?" demanded Mr.
Cornish. "no, no, all good." and the poor man escaped quickly. "There", said Mr. Cor-
nish, "you see!" "But I do not see: " I answered. "Your men are breathing whitekad dust
and red lead and litharge and the fumes from the oxide furnaces. They are no different from
other men; a poison is a poison to them as it is to any man." He thought a moment and then
he said, "Now, see here. I don't believe you are right, but I can see you do. Very well then,
it is up to you to convince me. Come back here with proof that my men are being leaded
and I give you my word I wTll follow all your directions, even to employing plant doctors."
It was not an easy task I faced, tncking down actual, proved cases of lead poisoning
among men who came from the Serbian, Bulgarian, and Polish sections of West and
Northwest Chicago, and Kere known to the employing office only as Joe. Jim. or Charlie,
with no record of their street and number! It meant digging up hospital records, for I had
to be sure of the diagnosis. then a search for the home, and finally an interview with the
wife to discover where the man had been working, for of course no hospital interne ever
noted where the victim of plumbism had acquired the lead. Hospital history sheets noted

LEAD AND HUMAN HEALTH 3
carefully all the facts about tobacco, alcohol, and even coffee consumed by the leaded man,
though obviously he was not suffering from those poisons; but curiosity as to how he
became poisoned with lead was not in the interne's mental make-up.
In the end I was able to present Mr. Cornish with authentic records of twentytwo cases
of plumbism severe enough to require hospital care. He was better than his word. Begin-
ning with the SanYamon Street works, he went on to reform all the plants in the Chicago
region, and this meant dust and fume prevention, often by methods which had never before
been worked out. There were no models to follow: the engineers faced new problems. As
each was solved, Mr. Cornish sent the blueprints to the plants in other states and later on.
when I visited these, invariably I found the same changes being introduced. I had told Mr.
Comish he could never fully protect his men unless he employed doctors to keep strict
watch over their condition, to make at least a brief inspection of each lead worker once a
week. He accepted this recommendation without protest and before our report was pub-
tished there was a medical department in each plant of the National Lead Company in
Illinois. I have met many admirable men in industry throughout these thirtytwo years, but
my warmest gratitude and admiration goes to Edward Cornish.
In commenting on the lack of adequate governmental regulation of occupational
exposures, and the apparently automatic opposition of industry to tighter regula-
tion Dr. Hamilton remarked:
Perhnps it is our instinctive American lawlessness that prompts us to oppose all legal
controt, even when we are willing to do of our own accord what the law requires.
It is clear that Dr. Hamilton was a shrewd and wise observer as well as an
inquisitive investigator and pioneer. It is now also clear that failure to pay close
attention to her farsighted concerns about tetraethyl lead in 1925 has had serious
public health consequences.
The use of organic compounds of lead as antiknock motor vehicle fuel additives
has clearly been the dominant source of a worldwide dispersion of lead into the
environment and into people. Since leaded gasoline was introduced in 1923, it has
increased background levels everywhere, including the Greenland ice cap (Fig. 2).
Several years ago. Rosner and Markowitz (1985) reviewed the public health
controversy over leaded gasoline during the early 1920s. including the role played
by Dr. Hamilton. The following is a selective condensation of their review. The
introduction of leaded gasoline led to a series of fatalities and severe poisonings
among employees of the producing companies in Bayway. New Jersey; Dayton,
Ohio; and Deepwater, Delaware. On the other hand, in February 1924 the Bureau
of Mines concluded that ethyl gas posed no threat to the public on the basis of a
series of toxicological studies it performed in its laboratories with funds donated
by!the industry. In response to the public controversy which ensued, Dr. Ham-
ilton wrote to Surgeon General Hugh Cumming in February 1925 suggesting the
'°desirabiiity of having an investigation made by a public body which will be
beyond suspicion."
In Apr1'1 1925, the Surgeon General announced that he was calling together
experts from business, labor, and public health to assess the tetraethyl lead sit-
uation. The conference convened on May 20, 1925. According to Rosner and
Markowitz, the industry position could be summed up as follows: (1) "leaded
gasoline was essential to the industrial progress of America"; (2) "any innova-
tions entails certain risks"; and (3) "the major reason that deaths and illnesses

4
0.20 F-
0.15
0.04
0
t300 _~ 1750 1800 1850 1900 1950
A.O.
AGE OF SAMPLES
1Fao. 2. Lead concentration, profile in snow strata of Northern Greenland (EPA, 1986).
occurred at their plants was that the men who worked with the materials were
careless and did not follow instructions." The strongest and most authoritative
critic of industry was Dr. Yandell Henderson, a noted physiologist at Yale. The
following are excerpts from Rosner and Markowitz (1985).
He (Henderson) told the conference that lead was a serious public bealth menace that could
be equated to the serious infectious diseases then affecting the nation's health. Unlike
industry spokespeople who defined the problem as one of occupational health and main-
tzined that individual vigilance on the part of workers could solve the problem, Henderson
believed that leaded gasoline was a public health and environmental health issue that
required federal action. He expressed horror at the thought that hundreds of thousands of
pounds of lead would be deposited in the streets of every major city in America. His
warning to the conference of the long-term dangers proved to be an accurate prediction:
"conditions would grow worse so gradually and the development of lead poisoning wt7t
come on so insid'wusly ... that leaded jasoline w9 be in nearly universal use and large
numbers of cars will have been sold ... before the public and the Bovernment awaken to
the situation."
Dr. Hamilton agreed with those opposed to tetr.ethyl lead. At the conference she ex
pressed her belief that the environmental health issues were far more important than the
occupational health and safety issues, adding that she doubted that any effective measures
could be implemented to protect the general public from the hazards of widespread use of
leaded gasoline. "You may control conditions within a factory; ' she said, "but how are
you going to control the whole country?" In an extended commentary after the conference
on the issues that it raised, Hamilton stated, "I am not one of those who believe that the
use of this leaded gasoline can ever be made safe. No lead industry has ever, even under
the strictest control, lost all its dangers. Where there is lead some cases of lead poisoning
sooner or later develops, even under the strictest supervision."
Most public health professionals did not agree with Henderson and Hartulton, however.
Many took the position that it was unfair to ban this new gasoline additive until definitive
proof existed that it was a real danger. In the face of industry arguments that oil supplies
were limited and that there was an extraordinary need to conserve fuel by making com-
MORTON LIPPMANN
t.

LEAD AND HUMAN HEALTH 5
bustion more efficient, most public health workers believed that there should be over-
whelming evidence that leaded gasoline actually harmed people before it was banned. Dr.
Henry F. Vaughan, president of the American Public Health Association, said that such
evidence did not exist. "Certainly in a study of the statistics in our large cities there is
nothing which would warrant a health commissioner in suying that you could not sell ethyl
gasoline," he pointed out. Vaughan acknowledged that there should be further tests and
studies of the problem but that "so far as the present situation is concerned, as a health
administrator I feel that it is entirely negative."
Despite the widespread ambivalence on the part of public health professionals and the
opposition to any curbs on production on the part of industry spokespeople, the public
suspicions aroused by the preceding year's events led to a significant victory for those who
opposed the sale of leaded gasoline. At the end of the conference, the Ethyl Corporation
announced that it was suspending the production and distribution of leaded gasoline until
the scientifc and public health issues involved in its manufacture could be resolved. The
conference also called upon the Surgeon General to organize a blue ribbon committee of
the nation's foremost public health scientists to conduct an investigation of leaded gasoline.
Among those asked to participate were David Edsall of Harvard University, Julius Steiglitz
of the University of Chicago. C: E. A. Winslow of Yale University and the American
Public Health Association. For Atice Hamilton and other opponents of leaded;asoline, the
conference appeared to be a major victory for it wrested from industry the power to decide
on the future of an important industrial poison, and placed it in the hands of university
scientists. "To anyone who had followed the course of industrial medicine for as much as
ten years; " Alice Hamilton remarked one month after the conference, "this conference
marks a great progress from the days when we used to meet the underlings of the great
munition makers (during World War I) and coax and pl-.ad with them to put in the pre-
autiotnry measures . . . This time it was possible to bring together in the office of the
Surgeon General the foremost men in industrial medicine and pubGc health and the men
who are in real authority in industry and to have a blaze of publicity turned on their
dehberations."
As a result of their study, the committee concluded seven months after the conference
that "in its opinion there are at present no good grounds for prohibiting the use of ethyl
gasoEine ... provided that its distribution and use are controlled by proper regulations."
They suggested that the Surgeon General formulate specific regulations with enforcement
by the states. This group saw their study as only an interim report, to be followed by longer
tange follow-up studies in ensuing years. In their final report to the Surgeon Genetal, the
cornmittce warned: 'it remains possibk that if the use of leaded gasoline becomes wide-
spread conditions may arise very different from those studied by us which would render its
use tnae of a hazard than would appeu to be the case from this investigation. Longer
experience may show that even such slight storage of lead as was observed in these studies
may lead eventually in susceptible individuals to recognizable or to chronic degenerative
diseases of a less obvious character."
Recognizing that their shon-tetm investigation was incapable of detecting such danger,
the committee concluded that further study by the government was essential: ln view of
such possibilities the committee feels that the investigation begun under their direction
must not be allowed to lapse ... It should be possible to follow closely the outcome of a
more extended use of this fuel and to determine whether or not it may constitute a menace
to the health of the general public after prolonged use or other conditions not now foreseen
...`!i he vast increase in the number of automobiles throughout the country makes the
study of all such questions a matter of real importance from the standpoint of public health
and the committee urges strongly that a suitable appropriation be requested from Congress
for the continuance of these investigations under the supervision of the Surgeon General of
the Public Health Service."
In view of what we now know about the health effects of low levels of lead in
the body, it is quite unfortunate that the further investigations called for by the

6 MORTON LIPPMANN
Surgeon General's committee did not take place for more than four decades,
during which lead was spread far and wide in quantities which the committee
could hardly have envisaged. For example, in 1970, when lead use in gasoline
peaked, 252,654 metric tons were used and the total consumption over the period
1929-1983 was 6,635,059 metric tons. Of this, approximately 10% was retained in
the engine oil, 15% deposited in the exhaust system, 35% emitted as submicrome-
ter-sized aerosol, and 40% emitted as > 10-µm particles (EPA, 1986).
REVIEW OF HUMAN EXPOSURE AND HEALTH EFFECTS
Quoting once again from Dr. Hamilton's Exploring the Dangerous Trades:
Lead is the oldest of the industrial poisons except carbon monflxide, which must have
begun to take its toll soon after Prometheus made the gift of fire to man. In Roman days,
lead poisoning was known, for Pliny the Elder includes it among the "diseases of slaves,"
which were potters' and knife grinders' phthisis, lexd and mercurial poisoning.
ThrouYhout all the centuries since then men have used this valuable metal in many ways,
and from time to time an observant physician has seen the results and described them,
notably Ramazzini in the eighteenth century, and early in the nineteenth century the grtat
Frenchman, Tanquerel des Planches. It is a poison which can act in many different ways.
some of them so unusual and outside the experience of the ordinary physician that be fai7s
to recognize the cause. I could never feel that I had uncovered all the cases in any com-
munity, no matter how small, even after I had talked with all the doctors and gone through
the hospital records, for some doctors would not pronounce a case to be due to lead
poisoning unless there was either colic or palsy, which is as if he refused to recognize
alcoholism unless there were an attack of delirium tremens.
It is true that a severe attack of co6c is the most characteristic symptom of lead poisoa-
una, and palsy-usually in the form of wristdrop-is the one most easily recognized, but
there are many other manifestations of this protean malady, as every physician knows
today. Thirty years ago it was not hard to f nd extremely severe forans, such as could come
only from an exposure so great as to seem criminal to us now, but which then attracted no
attention.
Dr. Hamilton was writing about the situation as of 1942. By then, as now, overt
clinical symptoms of lead poisoning only occurred when available knowledge
about lead toxicity and exposure control are not taken into account. In 1970, 3
months after Dr. Hamilton passed away, the federal Occupational Safety and
Health Act (OSHA) was passed. This led, in 1971, to the adoption of an interim
Permissible Exposure Level (PEL) of 200 µg/ms for lead dust in air. In 1979, a
permanent OSHA standard was implemented. It specified a PEL of 40 µg/m3. as
well as a blood lead concentration limit of SO µgldl.
More subtle health effects, resulting from exposures below the PEL, are known
to occur and were addressed by the Environmental Protection Agency (EPA) in
preparing the 1978 National Ambient Air Quality Standard (NAAQS) of 1.5 µg/m3
as a 3-month average. While EPA has completed its latest criteria document for
lead in ambient air (EPA, 1986), it has not yet proposed a revised NAAQS.
However, concern about low-level lead exposure has led EPA to propose, on
8/18l88, a maximum contaminant level goal (MCLG) for drinking water of zero
(CFR 53 (160) 31516). EPA is also considering regulating lead as a carinogen, as
a toxic component in incinerator ash, and as a leachable constituent in Superfund
sites.

LEAD AND HUMAN HEALTH 7
For infants and small children, significant body burdens of lead can be acquired
from ingested soil and paint chips. Household dust and garden soil, especially in
urban areas can be greatly enriched in lead from the fallout of airborne particles
from motor vehicles burning leaded fuels. Another major source in older homes is
paint flakes and chips containing lead-based pigments. It has been illegal to use
such pigments in interior paint for more than 50 years, but there are large inven-
tories within older buildings which can be readily mobilized and dispersed during
maintenance and renovations. ATSDR (1988) indicates that 40 million households
in the United States contain hazardous quantities of leaded paint.
Yaffe et al. (1983) reported that the isotopic ratios of lead in the blood of
children were close to the average lead ratios of paints from exterior walls and to
the lead ratios of surface soils in adjacent areas where the children played. Their
data suggest that the lead in the soil was derived mainly from weathering of
leaa-based exterior paints, and that the lead-contaminated soil was a proximate
source of lead in the blood of the children.
As shown in Fig. 3, the most significant contributors to current body burdens of
lead include direct air inhalation, inhalation or direct ingestion of settled dust, and
the ingbstion of food and water. Some old housing stock has lead pipe which can
elevate potable water concentrations substantially. Lesser, but still significant,
elevations can occur in water delivered via modem copper and brass pipe due to
leaching of lead from the solder in the joints. Foods can be enriched in lead from
a variety of sources. Lead in the air can deposit on leafy vegetables and fruits and
IN REO
t
B100Q --~ n~
~
UYER
KIDNEY
A( )X
Ftc. 3.
FECES UR1NE
BONES
Pathways of lead from the environment to and within man (EPA. 1986).

~ MORTON LIPPMANN
leave residues which are ingested. Lead in the soil can be incorporated into the
growing plant. Canned foods can also extract lead from solder used to seal the
can.
Lead exposures and blood lead levels among the general population have de-
clined substantially in recent years. The most substantial reduction has been due
to the switch from leaded to unleaded gasoline as motor vehicle fuel. This had an
immediate effect on air lead (Fig. 4) and a parallel reduction in average blood lead
(PbS) concentration which lagged by -3 months (Fig. 5). The lag occurred be-
cause most of the tailpipe lead reached people indirectly through exposure to
resuspended soil and through incorporation into foodstuffs. Further reductions
have occurred as the food packaging industry has reduced the use of solder in
cans. Table I from the 1986 EPA Criteria Document summarizes the contributions
to lead in blood from the major sources for 2-year-old children in the early 1980s.
RECENT HEALTH EFFECTS FINDINGS
The literature on human exposures to lead and their health effects is volumi-
nous. The 1986 EPA criteria document was published in four volumes containing
1336 pages. This discussion will be limited to the more descriptive research rel-
ative to low-level population exposures and the chronic health effects associated
with such exposures. In most cases, this limits the review to studies of the asso-
ciations between exposure and health effects in humans, since the low-dose ef-
fects of interest have seldom been seen in animal toxicology studies conducted at
higher levels of exposure. The disturbing implication that conventional animal
J
2°r ~
® t t t t t t t t t o~
1975 1977 1979 1981 1983
CALENDAR YEAR
Ftrr. 4. Lead consumed in gasoline and ambient lead concentrations. 1975-1983 (EPA. 1986).

LEAD AND HUMAN HEALTH
16
9
9
1976
1977
1976 1979" 1980
YEAR
FtG. S. Parallel decreases in blood lead values observed in the NHANES 11 Study and amounts of
lead used in gasoline during 1976-1980 (EPA. 1986).
toxicology provides little useful information about some 'serious human chronic
health issues is a subject for another paper and will not be discussed further here.
The effects that have been associated with blood lead (PbB) concentrations <40
µg/dl will be the main focus of this selective review. These include the effects of
prenatal and early childhood exposures on physical and neurobehavioral devel-
opment of children, and the influence of chronic low-level exposure on cardio-
vascular function in adults. These low-exposure-related effects are of interest in
relation to both occupational and general environmental exposures. The effects in
young children may be due to exposures in utero of working mothers (Wang et al.,
1989), and to lead brought into the home on work clothing of family members with
occupational exposures (Baker et al., 1977; Kaye et al., 1987; Wang et al., 1989).
TABLE I
C_ ONTRltiUTiONS FROM VARIOUS MEDIA TO BLOOD LEAD LEVELS (µL!dl) OF U.S. CHILDREN
(AGE - 2 YEARS): BACKGROUND LEVELS AND INCREMENTAL CONTRlBUT1oNS FROM AdR
Air 1ead. µ;4as
Saurce 0 0.25 0.50 0.75 1.00 1.23 1.50
BackSramd-oon-air
Food. w2ter, and beveraps
2.37
2.37
2.37
2.37
2.37
2.37
2.37
Dust 0.30 0.30 0.30 0.30 0.30 0.30 0.30
SuhtoW . 2.67 2.67 2.67 2.67 2.67 2.67 2.67
BacEcSmnd-asr
Food. Kater, and beverates
1.65
1.63
1.63'
1.63
1.65
1.65
1.65
Ingested dust (with Pb
_'deposited from air)
0.00
1.37
3.09
4.70
6.27
744
9.40
Inhaled air 0.00 0.50 1.00 1.50 2.00 2.50 3.00
Total 4.32 6.39 11.41 10.52 12.59 14.66 16.72

10 MORTON LIPPMANN
Table 2 shows PbB levels in children of workers from a Colorado plant making
capacitors and resistors (Kaye et al., 1987).
IVerarobeftavioral and Developmental Effects in Children
The 1986 EPA criteria document on lead contains a thorough critical review of
the literature on the neurobehavioral effects of chronic lowlevel lead exposures in
children. While various maladaptive behaviors, neuropsychological deficits, and
neuroanatomical changes have been associated with chronic exposures to rela-
tively low concentrations of lead, no single mechanism appears sufficient to ac-
count for the diverse effects. It is more likely that lead acts at several cellular and
subcellular sites. Lead readily enters the brain and appears to be selectively
deposited in the hippocampus and cortex as well as in nonneuronal elements that
are amportant in the maintenance of "blood-brain barrier" functions. Once de-
posited, lead is retained in the brain for long periods of time even after external
exposure ceases and PbB levels decline. These spatial and temporal patterns of
brain lead accumulation correspond to neurobehavioral and morphologic abnor-
malities associated with lead exposure. The sensitivity of the brain during the
period of maximal brain growth and differentiation in the first 2 years of life tends
to magnify the severity of the long-term consequences.
Low PbB levels may contribute to behavioral disorders, such as attentional
deficits and distractibility in essentially normal children not diagnosed as hyper-
active. A study by Bellinger et al. (1984) suggests that measures of classroom
performance may show long-term effects of early lead exposure. Silva et al. (1986)
found similar results on 11year-old children. Winneke et al. (1983) found that
behavioral and attentional deficits as rated by teachers (e.g., disordered class-
room activity, restless, easily distracted, not persistent, does not follow direc-
tioas, low overall functioning) were significantly associated with children's tooth
and'PbB levels, which was consistent with the earlier association reported by
Needhmatt et a!. (1979). The 1986 EPA criteria document has interpreted the
Winneke et al. (1983) study, which also assessed lead-induced deficits in IQ and
other psychometric tests, as showing overall neurobehavioral deficits at PbB
levels possibly.below 30 µg/dl.
In addition; lead levels in young children have been consistently associated,
TABLE 2
BLOOD LEAD IN LEAD WORlCERS* CHILDREN, !v AGE STIUTA`
Blood lead (µg/dl)
AXe category (years) Exposed mean (rantt) Unexposed mean (range)
<6 t3.4(4-23) 7.1 (1-13)
6-10 4 11.1 (3-22) 7.0 (5-9)
> 11 :/ E.0 (1-22) 5.0* (2-i l)
Atl ages 10.2 6.2
Statistically significant (P < 0.001) between exposed and uncxposed groups, Student's test.
° Kaye et ol.. 1987.
