Document OzRkwN60veNoOBzN9pLjNb8KQ
Preface
.v r
Chapter I Introduction
Chapter II He thods
Chapter III The Sources of Lead Absorption in the Modern Community
Chapter IV The Absorption and Excretion of Lead in Primitive Life
Chapter V The Magnitude of Clinically Significant Exposure to Lead Compound
Lead Absorption and Lead Excretion in the Lead Trades
Chapter VI
An A^raisal of the Lead Hazards associated with the Distribution and Use of Gasoline containing Tetraethyl Lead
Chapter VII
Certain Considerations in the Prevention! Diagnosis and Treatment of Lead Poisoning
index
Chapter I Introducti on
The usefulness of lead and its compounds in many fields of human
activity has gi^en them a unique place among the materials and products
ymtfa of early arts and crafts, and of modern industry. Thus ample oppor
tunity has been afforded for the demonstration of their poisonous proper
ties. The insidiousness in the development of lead poisoning, the appar
ent capriciousness of its occurrence, and the variety of its clinical
formsi have joined to
the curiosity of investigators, and to stimu
late their efforts in the interpretation and the mitigation of this
occupational menace. And yet a degree of vagueness as to the physiolog
ical activities of lead compounds maintains a lively interest in the
subject, this being heightened by the fact that whereas the means of
prevention of poisoning have steadily improved, new uses for lead-bearing
materials have developed at a more rapid pace, involving'an flosoe increas
ing number of occupations and persons in the hazards of lead exposure.
Indeed, the number of generally distributed commodities which contain
q-uantity.o# lead has become so great that some degree of lead expos
ure has been carried into the everyday life of all persons.
The investigations which are the subject of this volume derive
their importance chiefly from the fact that
K'E 0014430
source of information as to the mag nitude of the lead exposure intrinsic in modern life* They began in 1924 when it became apparent that the previously limited distribution of gasoline containing tetraethyl lead might develop into a commercial activity of very wide propor tions. The experience of those who had developed and dis pensed this fuel up to that time indicated that there was no acute or immediate danger, but the possibility existed that prolonged exposure to small amounts of lead under the conditions arising from the distribution and use of the com modity, might cause a significant accumulation of lead in the tissues of many persons in the industry and in the community at large. It is not my purpose, here, to discuss all the work which has been carried out in this laboratory or elsewhere, in the study of this hygienic problem. Much of the information bearing on the subject is readily available to those v/ho are interested. However, one phase of our work has resulted in the discovery of facts which are of such significance .as to justify their detailed presentation both In relation to the original question at issue, and to the larger problem into which it has come to be merged.
Periodic investigations have been made to determine the extent of the lead exposure associated with leaded gaso line, by the careful study of selected groups of persons who have experienced the longest and most severe.exposure to the conditions established by its use. Kehoe and Edgarv carried out the first observations of this type in 1924-25. Late in
.2/ 1926, J. P. Leaked and his associates in the United States
0014431
Public Health Service, following a program outlined by a commitel
teeAappointed by the Surgeon General, investigated the matter
further and extended the number and type of subjects observed.
This laboratory fiBB made three further studies, in the winter months of 1926-2*3^ 1927-28v^ and 1929-30 respectively, the first
two having been made the subject of detailed reports to the i-MicidL
United States Public Health Service, and to tne inaustry in
volved. None of the data have been put into such form as to
be generally available.
The primary purpose of these investigations could not
be served
by attempting to detect evidences of lead in
toxication in exposed persons. Rather, it seemed imperative to
anticipate
such developments by determining whether
'si-tsO '" -"i whleh might eventually^S^nduce lead intoxication.
KA w ,
.-,A
) / jr kL r ' j f
//WJ
' *
i's f^:-T c ong tanlKrclatoiohship Utftween tlJ^1 fl\Le"0'P> aba or m apt
\S ~ '
itionr -or. Uetlvden tn4 Uiuuunt in-the tioouos ant
tto-rntfl , n.f nrrrirM-ffn.
nnl.ytlirnl. nfaftariyntH nrn on Ithn
_M|. ------ -| i - . t
')U*vu*evc*Xt
bland mljJitP'IniHrnrr T'nn'nin'nmynf absorbed1 'SWfid. Jr, it-
might be,, that some
1 w^^ekhrngaaLjmt r-BUB.6ptlb3re-o--e-lini<
Vi-A.W
eal observation (Wwalar be found to vary with the magnitude of
lead absorption, as for example, the microscopic changes in .the
(SCs
blood. Lacking
Information on these points
Tsmp&rtXT
i<r 0014432
-suLiu
ftoooffla ary to combine
clinical W
l o w iu UJHj u s
uX1 aiuJJtlSBBffi
Varied groups of subjects with, known and unknown exposure
o lead compounds. In short, nothing less than a comprehen
sive examination of 'iStKSBSSSBSBBBSSSBBHm^ the physiological
subject of Investigation.
several years
:i have been devoted to such ef-
forts^ :
:-a demonstrated
that the normal
individual in the United States, experiencing no industrial
exposure to lead compounds. Is excretsu^f measurable quantities
of lead in both the faeces and.urine. The first observations
Indicative of this *swere reported by Kehoe, Edgar,
Thamann and SandersY The facts as to faecal excretion were
verified by Leake^ and his associates shortly afterward.
They have been established
LAj>-
by the extension of our observations to several groups of a/
carefully selected normal subjects^. Francis and his associ
CO ates, as well as Millel^have CO
the existence of a
similar 'M fnnf 1 nn in England. Vnr^nci,..jT^rmpn V? .8/ .9/ 1CL-o Eadham and Tayloir, Cooksey and Walton , and Tannahill^^, o
have obtained like results in Australia, while Fretwurst and L^-C*J /uiy-^ ^
Hertz'xTbave reported similar findings in Germany We^, as X -i
well as others^, have shown, further, that the rate of lead
excretion In faeces and urine varies with the magnitude of
lead exposure to such a degree as to differentiate* groups of
workers in the lead trades from.each other and from the non-
industrialized population. These facts have led to the fur
ther investigation of the conditions of exposure to lead
both in the lead trades and in the community at large. With-
out f^-frraotthgfin any wry ?y>nm. the importance of the original
problem, the study of the lead absorption of the general popu
lation has claimed an increasing amount of attention. This
has become the more necessary since those persons who have .
had the most severe and prolonged exposure to the hazards of
leaded gasoline^fail
to differentiate themselves
from unexposed persons, on the basis of their lead excretion
or any other factor. Whether this is due to the limitations
of the methods of observation or whether it is the result of
an insignificant magnitude of the leaded-gasoline
factor in the total picture, can be determined satisfactorily
only by the
of the several sources
which contribute to the absorption of lead by the average
normal man. By the same process one may hope to obtain some
evidence as to whether such lead absorption is now or is like
ly to become significant in relation to the public health.
Thus a number of problems have presented themselves,
as the direct outgrowth of what may appear to have been a
simple experimental study. Certain specific questions may be
formulated as matters &J
orest, as follows:
1. What are the sources of the lead absorbed by the average normal man in the modern American community?
KET 0014434
J*vJJLj^-iteu^,
3* Are., the-^o the result of modern industry and
.4 'Jt commerce, or aj3toihey> tij u j l li*A~*t !fTTSTrnivai
flPffgs* condi
tion^ of life on a lead-bearing planet, or are both factors
active?
Are there evidences of an increase in lead ex
posure as a consequence of the distribution of leaded gaso
line, or of any other commodity or factor of modern origin?
bx&J~C&i. CXstuAsa.iL&i}- 1~Pl
T
The mothoda which have been employed ^ and -feho re
sults which have been obtained in answer to these questions,
are dealt with In the chapters which follow. 7&J nd&J
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Bibliography
Kehoe, Robert A., and. Edgar, Graham: A Study of the Hazards Associated with the Sale and Distribution of Ethyl Gaso line. Printed report to United States Public Health Ser vice and Ethyl Gasoline Corporation, June 1925.
2/ Leake, J. P. and others: The Use of Tetraethyl Lead Gasoline In its Relation to Public Health. U.S. Public Health Bulletin No. 163, 1926.
y
Kehoe, Robert A. and others; A Study of the Health Hazards Associated with the Distribution and Use of Ethyl Gasoline Printed Report to United States Public Health Service and Ethyl Gasoline Corporation, May 1927.
Bibliography (cont)
4 Kehoe, Robert A. and others; A Study of the Health Hazards Associated with the Distribution and Use of Ethyl Gaso
line. Printed report to United States Public Health Service and Ethyl Gasoline Corporation, April 1928.
Kehoe, Robert A.} Edgar, Grahami Thamann, Frederick; and Sanders, Lester; The Excretion of Lead by Normal Per sons. J. Am. Med. Assn., 87; 2081, (1926)
Francis, A. G., Harvey, C. O., and Buchan, J. L.; The Determination of Small Quantities of Lead, with Special Reference to Urine and Biological Materials. Analyst, Sy.' 12-S^ December 1929.
Tm. fyc-wttMt </
ui
Millet, Horace:^J. Biol. Chem., 83:265, (1929)
Badham, Charles* and Taylor, H# B.: Studies in Industrial
Hygiene, No. 7, Lead Poisoning, Report of Director Gen
eral of Public Health, New South Wales^for year 1925,
Sydney, (1927).
'~~
9 Cooksey, T., and Walton, S. G.; Electrolytic Determination of Lead in Urine, Analyst? .February 1929.
Tannahill, R. W.; The Excretion of Lead by Mine Workers at Broken Hill. Med. Jour. Australia 1; 201, (1929).
11
Fretwurst, Fritz j and Hertz., _kvt u
Quantitative Deter
mination of LTTad in Faeces and Urine and Its Signifi
cance in Making a Diagnosis of Lead Poisoning, ArchXriyg.,
1J.0W4X ;i 15, (1930).
--, f 'At
*y ' 'N '-'.v fc*---v*
IZ
Kehoe, Robert A., narnrd^ TTVhaiommafinnnn,. Fredericr>kV ; fTPhVieA TE>x1ycnr.TetiHoftnn noff Lead, J. Am. Med. Assn. 92; 1418, (1929).
Leake, J. P. and others; Loc. cit.
Badham, Charles, and Taylor, It. B.: Loc. tit.
Taylor, H. B.: The Determination of Minute Quantities of
Metals in Biological Material Part 1; J. Proc. Roy. Soc.
Hew South Wales, 61: 315 (1927).
)
Francis, A. G.*p!inaT"Report of DepfciW ' Com. on Ethyl
Petrol, Ministry of Health, Great Britain. (1930)
Tannahill, R. W. Loc. cit.
/ Chapter IV
The Absorption and Excretion of Lead In Primitive Life
1/
No information
available as to the natural presence of
1/ lead In human tissues. Nor W it possible to determine whether
or not some quantity of lead la to be regarded as a normal consti-
1/ tuent of the animal organism if observations
confined to in-
dustrialized parts of the earth. On the other hand, it would' seem
that there should be places that have escaped the commercial devel-
/
y/ opments of present day civilization, and && which the opportunities
\/ for lead absorption -are- of the same type as those of primitive men.
A cursory examination of localities which offered some chance for
the existence of such conditions, led to the consideration of Mexico
as a field for experimentation. Certain requirements were set up as .the basis for the selection of specific communities, as follows:
tx (1) -^The conditions of life must be such as to exclude the possibility
of occupational exposure to lead compounds at.any time;
^0 -^here must be complete freedom from such opportunity for lead absorption as would come from the use of lead paints on the outside or inside of dwellings, or on objects of general usu-juu.
-Jfcpjfc UAfe of canned goods, metal containers and cooking utensils, piped water supplies, and machinery of any kind was 4JW,llSWlll,ilij-
f
(3) proximity to cities, or easy transportation facilities to and from highly organized communities constituted a further objection;
K 0014437
t
'
^ning and smelting activities, with special reference to leadcontaining ores, must not be carried on within such a distance as might provide opportunity for contamination of vegetation, surface soil or water supply ^e^employment of firearms, and the inclusion in the diet of game obtained through the use of firearms to any considerable extent, was accepted- qa-reason for exclusion;
& considerable number of people available for study, and willing to provide samples of blood and excreta, as well as articles of food and objects of general use.
\ V ft'V
Persons who-a-aa familiar with
MexicQi oeono-will
/
// recognize how easily many parts of that amazing country meet these requirements^ but~~te-eur-^inchi llie""C0Trdl'trii57r5^^eTQ^^6" c ting 'St ep
to^rousq-considerable'^dbub^a's^^^^
k-vl iK*4
Through the generous assistance of colleagues in the Department of
Public Health of Mexico, it was possible to establish the probable
suitability of several small communities within comparatively short
distances of Mexico City, and after de-k&iled examin^J^fcon ~e- several
9 such villages andjafterjestablishing mutually friendly relationships
\ with the native Mexicans, our doubts were
dispelled* awfr Ex
1 perimental work was undertaken in two pueblos. Since any conclusions
as to the natural occurrence of lead in human beings must depend
wholly upon the absence of artificial opportunities for lead exposure,
some description of these two villages and of life within them is
necessary.
--'*'7* Pueblo de Cachi
a small village of about one hundred
milies, situated on the Mexican plateau^ thirty-one kilometers
\
KE 0014438
northwest of Toluca, in the State of Mexico. At first sight, the vast
expanse of level plain in the region appeared as though uninhabited,*
There were no towns; with' obvious highways leading to them, or^with the
^ , smoke of factories hanging over them.
only evidence of human
existence in the immediate vicinity was furnished by occasional flocks
'of cattle* turkeys and chickens foraging under the care of children.
V^,C^The adobe houses
were
xjaady--f:or---theHiarvest, so^.-that-onlT'^bywstandihg"6h'''a^hi^bek^wul^ther
ofbe^ee-en scattered, at irregular intervals in the
o &** *.']
Or&Jl,
midst of the a&ffiattcwi field of <gMk* From-such'a ventage point one~H
could see -the- church tower and the- tile~roofe-of-Ixtlahuaca to the^dast,
and at a distance of about five kilometers, while to the north^he small
f^n__pf._.J.o.c.o.titlan-was~just- recognizable as a series of-white and red -- specks-.. To--th-e'-south',"and' within two-kilometers
were -the-white chapel" arid the rambling walls of a oomewhet dilapidated hacienda. AVithin-the cornfields of-the village one came upon a tortuous dlt.ch,._in..whlch..a.plentiful supply of turbid water was flowing, since it
Was--the - rainy 'season. . A'-well-worn---path-followed-.the..,sma-U.-~Ganal-and..led tojhe_hpus0Slfc...alX, of. which,...wexe situated-so -as'-to be" conveniently "sUp-"" ^iis^^idh^water for washing clothing, and for every purpose except that
of drinking. The latter was furnished by a deep well over which was an adobe building roofed with tile. A rope, tied to an earthenware vessel,
05 provided the means of drawing the water. Bo-th--men~and~women.~wo.rlced_.in..
co the -f-ields''bu`t''sbme' o'f'''the-women...wer.e._tp. be. se.e.n.washing-clothing.-or
o woQl_._in_.the- stream-~cadding-*-wool, spinning...thread on . crude spmales. or--
o ~rf /
weaving cloth on--simple..looms tied-to-the rooitree~of the -nouse. tana11--
Ux
X ^.chilji.ren.j_.jiuiaer.o.u.s....d.ogs , - and - an occasional^-^maIl--plg--tlod by the 'hind
leg %c> n,_ nj-.i-rfaft oijpupied--the--dorryafd The--singl-e-room"hcuses'~b'Uilt'
of-adobe-blocks, with one door and perhaps another opening for light
contained no furniture. Rush mats were on the floor or hanging on
pegs on the wall./ These took the place of tables, chairs andbeds. A
simple stone hearth without a chimney was in one end, the smoke finding
its way out under the open eaves. Several earthenware vessels of variable
size, a three-legged flat-topped stone and stone roller for grinding
corn, a flat earthenware platter, and a wooden ladle constituted the
culinary equipment.
The occupation.of the men was purely agricultural and pastoral. r.. The only metal implements found in the entire pueblo consist*.ed of sickles
and machetes, these.-.latter'"serving-tne--.peaaefuh,,,,pur-po.se-S-_.of--.husbandry.
There was no game and no hunting, furthermore, the inhabitants had no
firearms. No pottery was made here, nor was there any manufacturing
activity of any kind in the two neighboring towns which provided the
only convenient trading and social contacts with other native groups.
Cachi was poor. Its people had poor clothing and few belong
ings. Nevertheless it was essentially self-sufficient. The people /
r'\i
produced their own food out-of-the-i-r-awn soil. They had corn, beans,
small quantities of barley and wheat, and numerous other vegetable pro
ducts, together with milk, eggs, pork and fowl. They were well fed,
and in general they were healthy. Tne altitude of over eight thousand
ieet provided freedom from excessive heat and tropical insects, but the
warm bright days permitted the growth of vegetation the year r::und. Thus
there was no hunger. Such food as was not required in the village was
sold or bartered for rime, cloth, pottery, mats, sombreros, serapes,
and rebosos. in general, however, very little was produced in excess.
Thus only necessities were procurable, and though tobacco fcfcfe relished
greatly its use was infrequent. Pulque, the fermented land commonly
pu-toeXied-j juice oi one almost ubiquitous magey, was easily available,
and was generally used as a beverage by the men and boys.
There were no highways between Cachi ana the towns in the vicin-
ity.
ln-XacJhi^here were^.n-Q^ecogni-zabl^--road-B---i-ntQ^.lxtxn.h.uaca. TTtr~was-
HE 0014440
usually necessarv^to walk or to ride on a burro or horse to readx.it*
-Xn fliitomobile
flftToaA
o--qttwtrronable outctnm*"> y wn cr.ur^^l-orea--at--axtabuacair"''t:hg-or!-ly^-pfiyei-
*> i cm in
""1*v*'ryXs5Tst.anft ft
on h
drove u b to Cacni,..showing an.-astonishing skill in' goxng-aro und,over ana througn pools of water ana mua.in.the-open plain, t fte--gr-ea-ter-numberof nis medical vi ait,a Duta-Ld^-.Ixt.iamiaca~aTe~Tna'de~~on 'noTsebaQk. Through
the greater part ol.__t.ne year the _ automob.il..e,, ia_.a^.mar3c-o.f-diatlwetTorf,'
rather than an article_oi'..-iitili*y - The Indians walked or trotted, often
carrying-a-load..oi- sticks or-otiier' material-"-several "time-Ef' their' owiT'buik*
i^.e_.o.iuy--xiorse -in tne -village, was.-tne property.,.,pi.,. tne-cniei
ihe visits
the Xnaians to tne^^nexghhari-ag towns were limited
to market aay, ana local or general fiesta days./ The--fbraiefr, whxeh
occurred onee..a w.eek-,--provxa'ed` an 'opportunity-for '-seemg-and-perhaps.
purchasing- or-trading f or articles from the city* - irL..Ixtlahuaca merchants
irom_.Toluca--spread their waresm open-booths along the- streets, while
peopl.e..from the countryside -piled their products around tnem on the
ground .and offered them for sale-or.^.trade Hwever,-the pervading atmos
phere was not that oi a market place but rather that ox a gay bazaar.
The social life of the neighborhood found its chief expression in these
weekly- gatherings, if something could be bought or sold a pretext was.
thus provided- for a day of-visiting and pleasure, in whicn. commercial---
matters were mere incidents.
More distant places were visited rarely. Only one of the persons
used as subjects m Cachi, an uld man of seventy, had ever been in Mexico
uity. ne naa traveled the entire distance on loot, dun-ng--t-he-^elebr^rfc-i-cn
hf--.tbe-fiesta"-of->-tne~~virgiH-ox- tiaudilupe
The Rancheria el Colera is a small pueblo near Capulhuac about
twenty-four kilometers southeast of Toluca and approximately fifty kilo
meters from Cachi. Its people and its community life were so similar
0014441
to those of the village previously described that no points of signifi cant differentiation were evident, except that the variety of food mater ials generally used was somewhat greater than that of the people of Cachi. This will be shown in the list of food san pies on which analytical results have been obtained*
No mining or smelting of lead has been carried on in the State of Mexico according to information supplied by the federal Institute of Geology. No deposits of lead ores were known to exist in the vicinity
> of the two villages in which observations were made, though three obsolete documents granting claims for the extraction of argentiferous galena in the town lands of Aquipan, in the extreme south of the state, were found in the Department of Mines. The fate of these attempted mining develop ments is not recorded.
i0014442
n
o !'C'ZK&f&t' sorvation of the activities of the
people in the two communities led to the recognition of only
one opportunity for the artificial introduction of lead into
their food. This came from their use of earthenware utensils,
which will be shown to have been glazed with a lead compound.
Considering the antiquity of pottery and lead glazing materials,
this may not be regarded as a modern phenomenon. Some idea of
Its significance as an early example of the use of lead-contain
ing commodities may be obtained from the data of this study. V v Fifty-three subjects in Cachi, and forty-two in
Colero were selected for study. Each subject was questioned as
to his birthplace, age, occupation, visits away, from the village,
and illnesses. A cursory physical examination was made for the
purpose of eliminating such as were ill, and a determination of
the haemoglobin of the blood by Dare's instrument, a urinalysis,
and blood smears, were made on each subject. Fifty cubic centi C)
meter samples of blood for analysis were obtained from thirty-
four subjects in Cachi. In the collection of these samples
care was taken to avoid any contamination. The syringe
and needles were sterilized in a small metal receptacle heated
by an alcohol lamp. Distilled water had been carried along for
the purpose. After
each sample the syringe was washed
out with well watei^, rinsed in distilled water and boiled in
distilled water. From time to time additional distilled water had
to be added to the sterilizer. At the end of the day's work, the
residual water in the sterilizer containing the non-volatile
accumulations from several sterilizations, was poured into a
sample bottle for preservation and analysis.
KEf 0014443
Gallon jugs for samples of urine and beverages* and quart jars for
faeces and solid food materials, and small bottles for blood and other
small samples had been prepared and sealed in the laboratory in Cincinnati,
and had been shipped by rail to the nearest point* The final lap of their
journey was made on the backs of burros* They were stored in a dry adobe
house, from which they were given out to the subjects for immediate use
and immediate return to the custody of the caretaker# Each subject was
provided with an identification card which showed his name and number, the
jugs and jars having been labeled correspondingly. At first difficulty
was encountered in introducing the idea that the urine samples were to be
provided by single individuals. In some instances the identification cards
were passed to other members of the family of the subject in order to
expedite the conclusion of the work and the obtaining of the fee* ThiB was not so much an intentional deception, as a lack of understanding of
what was desired. When the language difficulties of the situation are
considered, and when some inkling of the absurdity of the entire situation
from the point of view of the Mexican is appreciated, the misunderstanding
is not surprising. On the whole, however, the collection'of the samples -
was satisfactorily accomplished, with only the occasional mishap of mixing. -
the urine of more than one person in a single container. In a few instances
recorded in the data, the samples were so small that they were combined to
make composite samples. The food samples were collected directly into the jars.
Upon the completion of the work, each sample was treated
10 c.c. of 40/ formaldehyde which had been shown by analysis to be free of
lead. The containers were sealed, packed in crates and shipped back to the
Cincinnati laboratory for analysis.
fgsq.. uf..cub luma--
of a member of the laboratory staff. Thus no opportunity was given for the -contamination of any of the materials from the time they left the Mexican village until-they arrived in the laboratory.
f
Cincinnati laboratory for analysis. Through the /Courtesy of
//
customs officials it was possible to have them ^elivered to
the analytical laboratory without breaking the/seal on a
single container,/the customs inspection having been made
in Cincinnati in' the presence of a member of the laboratory staff. Thus no opportunity was given for ihe contamination
j /
of any of the materials from the time they left the Mexican / village until they arrived in the laboratory*---------"711/ " , , .
Tables rfyy. to -wdffiC inclusive^ pruseut l/vi ilula rLho.^-^ojt^Ma^ Soil samples taken at
random in the fields under cultivation (Table Xvl) uniformly show small amounts of lead. Since there had been no opportu nity for surface contamination of the earth by artificial means, these results give some idea of the natural lead con tent of the soil. No doubt there are wide variations in different parts of the earth, but Y/herever soil is produced,_ by the leveling of mountains, some small quantities of lead may be expected to be found. Similarly, the water contains minute traces of lead. Table XV5rI shows that the vegetation
absorbed small amounts of lead.'' ` In the case of prepared foods (Table XBt) it is
necessary to consider the opportunities for the introduction 5
of lead from the use of pottery. Table XVIII demonstrates the load-glazed character of the pottery which was being used generally in the two pueblos. Certain of the animal products, such as eggs, fish, lizards and crawfish were obtained in a raw state and are not to be classified as prepared foods*
K 001.444')
%>-- Table XVI
Lead in Soil and Water
Article
i1 '
CACHI , .
|
COLERO~
! WM Pound j
I/5&d Pound
! O.uantltyi Mgs.
| <*//<,<> , Quantity] Mgs.
ii Ii
-------------j
i j.
Well "*ater (drinking)
1 3600 c c
? (
Water from Stream(washing); 1 3240 c.c.
0.03 0.00
Soil n.
\ ; S <U0
r. zi
Soil i;2 Soil ,3
;r i ,,
-i
6-,^ O.lt
o.ooj/Lj 3900 CC;
0.00
3860 cc
I.C 0 i'.iu
j: -j j . " (.
! 1
|
1
0.03 0.03
/> , ^ 0 0 o3
0.Q09# 0.009it
/.
SC, C 0
o fo
Table XVII Natural Lead In Vegetation Used as Food Materials
Articles
Wheat (dry) Wheat (green) Corn (dry Corn (green) #1 Corn (green) ^2 Corn Stalk (green) #1 Corn Stalk (green) #2 Corn Husks (green) Peas (green) Pea Pods (green) Keans (dry) Beans (Haba) (dry) Beans (Haba) (green) Pods (Haba) (green) Leaves (Haba) (green) Pears (green) Apples (green) Peaches (green) Nopal #1 Nopal 2 Squash (green) Squash Plant Radishes Turnip Leaves Peppers Greens #1 C-reens #2 Capulin (type of cherry)
CACHI
Weight ' Pb.Found PhT^'Q in Gms. Mss* bvYjjzk'
COLERO
Weight Pb.Found Pt^Orr \ * in Gms Mgs
99. 40
146. 40
330..70
161..20
217 .00
; 183 .20
; i 215 .00
' | 227 .20
'
;
273 00 :
116 00 : 175 .00
133 .30
249 .50 : 243 .70
149 .30 214 .40
121 .00
0.04 0.04 0.11 0.05 0.03 0.02 0.01 0.06
0.11
0.03 0.00 0.00
0.03 0.02 0.00 0.01 0.04
p '
] 85 .70
0.00
ti
oJw o.i? o.sr o.
o.tf '0.0JO.tttt
0 .M
o.m 0.00 0.00
o.n 0.05 0.00
o.or-
o-53
0.00
t i
1
* :331.80 !
: 275.00 5i
'
i
S
291.20
; !193.00
i 175.40
213.30
, i256.50 j 283.80
!
: 218.10
\i : 262.80
231.10
: 128.60
i 1 335.60 j 71.20
54.80
221.50
32.00
224.60 ;
80.70 i
215.90 |
0.01 0.02
. 0.03o.O?
0.01
0.0J-
0.01 " -9$0.07 "0.40
0.03 0.04
0.74-
o.42r
0.01
0.04.
0.04
0. f.g
0.01 0.01
0.03 0.01 0.02 0.01 0.00 0.03 0.01 0.00 0.01
0.02^. 0.0%-
0.23 0.03-
o.2
o.p* 0.00 .w
o.6r-
0.00
o.oy-
0014447
Table XVIII f
Lead In Pottery Used by Subjects
Sample
CACRI
Weight in Gms.
Pound
Mgs.
Percent
COLERO
Weight in Gms.
Pound
Mgs.
Percent
Glazed Dish Glazed Dish Unglazed Dish
1.00
8.20
0.82
1.00 1.00 1.00
13.00 12.50
0.10
1.30 1.25 0.01
0014448
Table XXX
&
Lead in Animal Products and Prepared Pood Materials
Articles Atole -(barley-corn juolj Com In Lime Solution Corn ground for Tortillas Bread Tortillas Tamales (corn) Chicken Eggs - Hen and Turkey Boiled Pork Pork Sausage >Lay|& (pork) Beef Chili (with meat) Cheese Dried Pish Fresh Fish Ajolotes (lizard) Craw Fish Common Salt Candy (local type) pulque Aguamiel Wine
CACHI
COLERO
Weight Pb.Found PV)^%U'43 Weight Pb.Found Fb/AlQ'^s
in Gins. Mgs.
in Gms. Mgs.
417.50 445.00
0.00 0.04
0.00 O.oi
409.70 544.00
1.70 0.10
oM
117.20 0.02
0.{$
265.70 0.03
o.f i
73.70 0.07
>45"
119.40 0.07
o.?>
224.80 0.08
o4ur
283.30 0.01
0.04-
419.80. 0.00
0.00
503.40 0.00
0.00
471.50 0.01
0.0%
411.70 0.03
o.of.
492.10 0.00
0.00
73.80 0.02
0.4?
54.70 0.00
0.00
0
gr 1
121.80 0.02
324.40 0.15
O.^fe
84.40 0.00
0.00
26.50 0.04
1>.fc
80.90 0.02
0.24-
207.80 0.02
0 4X5
186.90 0.14
o.fS
204.60 0.21
p.aZ
277.60 0.08
o.l&
3300 cc 0.14
0.04,$Jk
Sample Lost
3760 cc 0.06
Thus any lead found in them is of natural origin. In fact,
only two of the articles listed in Table XIX, show amounts
of lead which indicate the likelihood of significant con
tamination, namely, the pulcue which probably took up some
of its lead from earthenware vessels, and the atole, one
sample of which
grossly polluted with lead. The latter
circumstance may have been due to the unrecognized presence
of small fragments of the earthenware jar In which it had
been kept, since such jars are very fragile.
5 / & > ~y /
)
Tables XX, XXI, XXII, XXIII, and XIV, display
the lead findings in the two groups of subjects. Only eleven
of the thirty-two blood samples showed the presence of lead,
and In these the quantities were small, but measureable.
because of the minuteness of the quantities of lead^which
were at the lower limit of analytical estiras-tfoon, the entire
volumes of the last five positive and the last three negative
samples as finally prepared for the colorimetric determination,
were preserved for re-examination. ^Twenty-three samples had
been completed and the solutions had been discarded before
this procedure was decided upon. The two sets of combined
samples were evaporated down to the required amounts for
colorimetric comparison and a re-estimation of the total lead
was made. This same process was employed in checking the
quantities of lead In all other types of samples, the results appearing In Table X^IV. Thus, despite the
quantities of lead Involved in the entire series of analyses,
there can be no doubt of the presence of lead where it Is
reported to have been found.) It is certain that the lead
UP' 00144b 0
Distribution of Subjects According to Lead In the Blood
Lead in Milligrams per 100 Gms. Blood
Number
Percentage
0.00 0.01 - 0.02 0.03 - 0.04 0.05 - 0.06 0.07 - 0.08 0.25
21 6 2 1 1* 1*
65.6 18.8
6.3 3.1 3.1 ' 3.1
Total
32 100.
Jy.-VIA, J-ii'S.-Oy'-1 &YAj &x }, AI -1' iJIviX'v
L{
Table XJCI
JfrJ b,Cu.
Distribution of Subjects According to Amounts of Lead
he Urine
CO'.'BITTED GROUPS
CACITI
COLERO
-or-
'pw Liter of Urine number Percentage number Percentage Number Percentage
0 0.009 0.010 - 0.019 0.020 - 0.029 0.030 - 0.039 0.040 - 0.049 0.050 - 0.059 0.060 - 0.069 0.070 - 0.079 0.080 - 0.089 0.090 - 0.099 0.100 - 0.109 0.110 - 0.119 0.120 - 0.129
37 45.7 19 45.2 18 46.2 26 32.1 10 23.8 16 41.0 10# 12.4 8* 19.0 2 5.1
4 4.9 2 4.8 2 5.1 3 3.7 2 4.8 1 2.6
1## 1.2
1* 2.4
Totals .
81 100.00 42 100.00 39 100.00
.. Mean (f>:r>h 10 u' v1 y^-j
Standard Dev+*k.
Jo. 012 0. ooc% +0.0105
lo. 01^8 o,. ooiz. 0.0114
JoToE37 \to.oo\o 0.0095
* These include two composite samples made up of the urines of two groups of children. Omitted in calculation of mean.
KF 0014452
Distribution of Subjects According to Milligrams of Lead per Gram Ash of Faeces
COT/EIHFD g r o u p s
CACHI
COLERO
fj * <i Humber Percentage Number Percentage Humber Percentage
b
0 1
0.019
28 36.9
0.020 - 0.039
21 27.6
0.040 - 0.059
13 17.1
0.060 - 0.079
5 6.6
0.080 - 0.099
4 5.3
0.100 * 0.119
0.120 - 0.139
2 2.6
14
16
0.18 - 0.199 .
i
1.3
20
22
24
0.26 - 0.279 0.28 - 0.299
i 1.3 a'
1 1.3
19 9 6 4 o
JQr~ -0-
47.5 22.5 15.0 10.0
5.0
&ve~
9 12
7 1 2
2
^rh--*
1
drd
1 1
25.0 33.3 19.5
2.8 5.5 dr'**-' 5.5
2.8
2.8 2.8
Totals
Kean
s 7"d ..... -...........-
76 100.0
JoToSS? 41 U i +10.0280
40 100.0 36 100.0
IU UOv-)p 0 rwgfr- ;0.039,
'0. Wo. oosy
+0.0243 ..........
0.0312
^Omitted in calculation of the mean
tfF 0014453
Table XXIII Distribution of Subjects According to Lead Found In Faeces
^M^*?**
I
' _...
COt,-BINED GROUPS )
CACHI
) COLERO
dumber Percentage / Number Percentagetlj^
........................................................................................
0
' ix o - 0.019 0.020 - 0.039 0.040 0.059 0.060 - 0.079 0.080 - 0.099 0.100 - 0.119 0.120 - 0.139 0.140 - 0.159 0.160 - 0.179 0.180 - 0.199 0.200 - 0.219 0.220 - 0.239 0.240 - 0.259 0.260 - 0.279 0.280 - 0.299 0.30 - C1.319 0.40 - c1.439 1.00 -
8
10.5
6
. 15.0 ...
2
5.5
7 9.2 5 12.5 2 5.5
9
11.8 '*
8
20.0
1
2.8
7 9.2 5 12.5 2 5.5
4 5.3 2 5.0 2 5.5
9
11.8
4
10.0
5 13.9
7 9.2 1 2.5 6 16.7
6 7.9 1 2.5 5 13.9
2 2.6 2 5.0 0 0.0
3 4.0 2 5.0 1 2.3
3 4.0 2
o
lO
1 2.8
1 1.3 0 0.0 1 2.8
3 4.0 1 2.5 2 5.5
2 2.6 0 0.0 2 5.5
0 0.0 0 0.0 0 0.0
1 1.3 1 2.5 0 0.0
3 4.0 0 0.0 3 8.3'
1 1.3 0 0.0 1 2.8
Totals
76 100.0 40 100.0 36 100.0
ttfean
0, 2 oSy 0.0741
0. oo 77
0.0725
fe.130 O-.-0083--
0' 0 0^3 0.0700
# Omitted in calculation of the means
K 0014454
Table XXIV
to
Summation of Analytical Results as Compared to Amounts Obtained
by Composite Analyses
Description
CACHI
CGLERO
Sum of
:j Sum of
Clumber Individ-
Number Individ
of ual Composite} of ual Composite
Samples Findings Analysis:!Samples Findings Analysis
filood^Samples -/Pos. 5* . BfeaOfiH&Sbgs -(I'Jee... 3;:-..
A-Vivwt " Jjrlne--Strmplee - ; Neg. ! 3* foMU4-Postf 12
0.05 0.00 0-78 0.00 1.02
0.08 0.00 0.85 0.00 1.02
32 7
36
1.41 ,.........1.51
0.00
0.00
i . ...
6.15
5.75
Fo-od'"Ssmples
Total
-f Pos. ! 19 17
i 72
0.97 0.00
2.82
________ .... ...... ................ i
0.93
|
i
\
0.04 !
34 9
3.17 0.00
2.92
118 10.73 . . ......
2.97 0.06
10.29
* Material from other samples was discarded*when..Individual analyaA-o -b^-pl an -a^o-.
## Only three negative results were obtained on faecal samples. The `mat-e-r-ia.-l-^vgs1 dlucsn.'ded"bofore-the..adoption 1 of the po-do-oomposih^siiauLyeee.
K 0014455
found by analysis was in the blood as withdrawn from the
veins of the subjects, for any suspicion that contamination
may have occurred is oompjjsbflAy dispelled by the fact that
the three samples of residual distilled water from the
sterilizer
failed to show traces of lead.
Table -5&T1 detailing the analytical results obtained
on the urinary samples, shows the mean values of the lead ex4 >"u
cretion per liter of urine for each group as well as; the com-
bined group of subjects. Here, again, the results were low
but the volumes of the individual samples were so large that
the amounts of lead generally found .-were within the limits of
accurate measurement. The volume of the average sample was
over three liters, many being four, and only a few less than
two liters. The accuracy of estimation of the smaller amounts
is attested by the result of the composite analysis which
appears in Table "}&. The urinary excretion of lead is of the
same magnitude in the two groups of subjects, as shown by the tihd'JJJ
meanSfy Despite the comparatively small numbers of subjects the
means are so stable as to indicate only a small variability in
the experience of the subjects as regards lead absorption. The
excretion of lead in terms of milligrams of lead per gram of
ash in the faeces, (Table XXII); shows a slightly greater
variability, but the two groups of subjects are similar in
x this regard, and may not be differentiated statistically.,/ A ^comparison of these mean values with those obtained from the
study of the medical student (cf. Tables VlX^and VIII), brings
out the surprising fact that they are of the same order of
K 0014456
magnitude. Evidently the ingestion of lead by persons living under
these natural and primitive conditions, is not widely divergent from
that, experienced by certain individuals in an American city. The
evidence provided in Table XXIII leads to the same condlusion. The
quantities of lead actually found in the samples reach a mean value
of 0.108 milligrams of lead for the entire group of subjects. On the
whole, the single samples represent not more than one day's alimentary
output, while the lead content may be assumed to be something less than
lhat ingested during the previous day. In these terms the mean daily
ingestion of lead amounts to a little more than one tenth of a milli-
gram of lead. This value of 0.108 midtiigrannr in^ the liexiaan subjects
is to be compared with the value of 0.187 arrived at by similar
methods in the case of American subjects. A slightly different basis
of comparison may be made by calculating the mean daily output of
lead in both urine and faeces. Assuming that the mean lead content
of the faecal samples constitutes the alimentary excretion for a day,
and that approximately two liters of urine are voided daily, the
average Mexican excretes approximately 0.14 milligrams of lead per
V
day, as compared to 0.33 milligrams for the American. The unavoidable
conclusion to be drawn from these facts is obvious. Despite all the
opportunities for the artificial contamination of food materials with
lead in American cities, a large proportion of lead which is ingestdd
by the average American is derived from natural sources.
A classification of the Mexican subjects on the basis of 1 ' rc.
their ages, as portrayed in Table XXV, shows that a large number
of children were included in the groups. An opportunity is thus
afforded for the comparison of these children with the adults of
their own type, and with American children. Table XXVI gives the
analytical data for children up
KEF 0014457
Table Distribution of Subjects According to Age
;e in Years
5-9 10 - 14 15 - 19 20 - 24 25 - 29 30 - 34 35 - 39 40 - 44 45 - 49 50 - 54 55 - 59 60 - 64 65 - 69 70 -
Totals
Combined Groups
30 13
7 4 14 6 6 4 1 2 2 3 1 2
95
Cachi
16 2 4 2 8 5 5 2 1 1 2 2 1 2
53
Colero
14 11
3 2 6 1 1 2 0 1 0 1 0 0
42
HE 0014458
Table XXVI
; jrt.'.'uV-'-'A
Distribution of Children
to Lead Found in Faeces, Lead in
Milligrams per Gram Ash of Faeces, and Lead In Milli
grams per Liter of Urine
j (Number of Subjects as Number of Subjects as Number of Subjectsj Lead Findings ijto Lead Found to Faeces to Lead In Mgs/Gm Ash to Lead to Kgs/L. Urine
Milligrams ` jCachi Colero Combined Cachl Colero Combined Cachl Colero Combir
:;i?,G - 0*019
2
0.020 - 0*039
2
0*040 - 0.059 ; 4
0.060 - 0.079 / 2
0.080 -0.099 L 1
0.10. - 0.119
0.12 - 0.139
0.14 - 0.159
0.16 - 0.179 0.18 - 0.199
0.20 - 0.219
0.22 - 0.239 0.24- 0.259
0.26 - 0.279
24
1 2
1 1 11
5......... 5............... 10
9* .....12# _ 21#
11
Totals
12 15 27
Means
(Combined
.k '
/*>
S. D.
______ 'J Groups!) 10.0881
____ :z:::z.xK,^orx +0.0712
12 15
27
foTosSe _o~o6s-- '~0 Zo'bsz 0.0409
* Only six of these are nil, two from Cachl and four from Colero. ^Calculated after a wider distribution of findings.
K 0014459
to nine years of age. The numbers of subjects are too small
to permit statistical treatment of the individual groups,
but the means for the total number of children from the two
Ll-CUA
villages are stable. The means are not gbi-fM-Ly dif
ferent from those of the entire groups to justify calcula
tions on the adults alone. On the other hand, the urinary
>
lead excretion of these children is significantly, lower than-
that of the American children, though their faecal excretion,
while considerably lower, is not significantly so from a
statistical point of view. The importance of the observa
tions on the Mexican children arises from the fact that it
is not necessary to consider the possibility of any sources
of lead ingestion external to their pueblo. They had spent
their entire lives up to that time in the immediate vicinity
of $heir native village.
The examination of blood smears made from these
subjects establishes a fact which is of some consequence
in relation to lead absorption. Much discussion has con-
/vl IS
t/ ceitted itself with the question of whether stippling of the
erythrocytes occurs in normal persons. Table XXVII answers
the question conclusively and affirmatively. There can be
no question of any relationship between significant lead
absorption and the presence of stippled erythrocytes in the
blood of these subjects. On the other-hand, there is a
difference in the people of the two villages in
this regard. For some unexplainable reason a considerable
proportion of the blood smears from Cachi show numbers of
stippled erythrocytes which would be generally regarded as
-'
KF 00I44G0
Table XXVII Distribution of Subjects ae to Stippling of Erythrocytes
Number of Stlppledj
CACHI
COLERO......... 1
Erythrocytes per 1
1----------------------- -
50 Fields
= Number Percentage Number 'Percentage
i
______ 0, 3......... . . ; 28.... ....... A JJ_... .38 ,, ..!.....9/ .5........
4- 7 .8 1! 12 - 15
12 ;3
3
?o-0 sj~ ;. _
{ o+*4 i
i1
4.3 . l.z
16 - 19 20 - 23 24 - 27
5 '
1
1
n\
/.7- : 1
LI ^
28 - 31 32 - 35 36 - 39 40 - 43 44 ** 47 50 - 53 54 - 57 74 * 77
Total
3
1
1
2 ..............
60
o. 0
1.7-
!> 7-
l> jj n \\
wVIt t, II n a 1; |j 1
3.3 _ /(>D
h: >'): 42
'
2.1 / >''J
K 0014461
' ......
Table XXVIII Distribution of Subjects According to Haemoglobin of Blood
Haemoglobin Reading(Dare)
CACHI
Humber
Percentage
65 - 69 70 - 74 75 - 79 80 - 84 85 - 89 90 - 94 95 - 99 100 -
Totals
P' 3 17 13 15 9 1 1
59
5.1 28.8 22.0 25.4 15.3
1.7 1.7
100.
of diagnostic significance, under conditions of lead exposure. The smears from Colero were mostly negative, and uniformly low. The presence of secondary anemias in the inhabitants of Cachi might be expected to produce such a result. However, the subjects in both villages were healthy, and the haemo globin determinations in Cachi, shown in Table XXVIII, do not suggest the existence of any considerable incidence of anemia. Furthermore, there is no correlation between the amount of stippling and the haemoglobin reading. These facts lead to the conclusion that stippling occurs as a normal phenomenon^ of unknown physiological significance. This statement of fact must not be interpreted as a denial of the practical value of blood examinations in the case of workers in the lead trades. Data which will be shown later demonstrate the im portance of such observations in obtaining presumptive evidence of lead absorption. Nevertheless, considerable caution must be exercised in drawing conclusions from such information, even under the most suggestive conditions.
0014463
Chapter III The Sources of Lead Absorption In the Modern Community
The uniform occurrence of lead in the excreta of normal individuals indicates a general distribution of lead compounds in the normal human environment. The quantities of lead in the urine are so small as not to be demonstrable by the analytical methods employed by most of the earlier investigators. Thus, there is no adequate basis for an assumption that this is a phenomenon of modern life. Evidences to the contrary are to be found in certain observations of the lead content of food
J/ and drink. As early as 1881, Gau-fc ierv determined the lead content of many food materials, by satisfactory chemical methods,
and concluded that the average Frenchman was ingesting approxi
mately half a milligram of lead daily. In his opinion the prin- .
v/ clpal source of lead
jUt*!** cooking utensils and preserving
cans.. Other facts, mostly of a fragmentary character, tend to demonstrate that such factors were not the only ones involved.
Fuller reference to these matters will be made later. But it
need not follow that present conditions are the same qualitatively or quantitatively. The modern technique of handling food is very different from t'-at of the ninjeenth century, while many other matters of everyday life have seen revolutionary changes. There ? fore it is necessary to examine(thejconditlons in the modern com
munity in some detail.
K 0014464
/
2
We have chosen to approach this question by a less laborious method than that of systematically studying the lead content of foods and other materials with which the individual has contact. It appeared more advantageous and more interesting from a physiological point.of view, to ob serve human subjects under certain sharply defined variations In environment, thereby obtaining simultaneous information as to the environmental factors and the response to them, A study of the lead excretion of infants and children was made on the possibility that the limited length and quality of their experience might be associated with an obvious limita tion of their contacts with lead. Observations on adults under carefully controlled conditions supplied further variants,
1. Lead Excretion in. Infants and Children.
Children were taken at random from various services in a
children's hospital, WydL';f_- care to exclude such as were sus
pected or known to have had exposure to lead compounds or a
history of pica. Those with acute illness v/ore also avoided. In
so far as it was possible, samples of urine and faeces were col-
looted directly into the containersIn some instances this
could not be done. The precautions taken were such as to avoid
the likelihood of contamination of the materials with any lead- j
bearing materials.
yv
Table Jy shows the ages, the gounds for admission to the
hospital, and the lead findings in this group of children^
>/ the mean values for the excretion of lead in
^ g 0014465.
n..... f>!5i
\
.. V>-V
rt o3> V'<? f- 080 Jt. 'P0&:?{&
0~,QZ*f
03 -'.oS'q Oi _,<?<?? .
W-./t? fZ- /</#
/S' 7?
/S-/2o<f
z
Jo <?
.6'
3. % /
3r
*
O i -2
-fe . ^U, 6
' O% /O' /#
/<?/ 2. ;0 '
4.._
T -.-vX. JH* '
i/ ;s -.<?
0
/h 3&'
sJV ^/r
ga 3k
V31/ / -
TY A,OJ +
3V
r
,2o3
lor - c^arfovs
3V
>3'X
co CO
~ k*2> '3 V
- V*1^7V ; ~
T*
**< r~
o o
0^ _ (21 i*
V3<f
fO 3c
,47Y-Vq '0V-$9
%30M. -] '<-,' 0,02oa
r11 Dmnn 111
f?r -.
,00^0%
S./S. - 10.043*1
S.ySoCfSt /
P.2. . Y 0.00 Sag
Table TJ Lead Excretion in Normal Children
Hospital Identifi cation Ho*
Description of Case or
Diagnosis
0-4 'L tjw*
LEAD IN FAECES LEAD IN URINE
Mgs Mgs/Gm Found Ash
Mgs. Found
Mgs./ Liter
. 90 245 . 970 V 2130 2330 2504 - 2582 2783 2375 3043 3091 3119 3337 3377 3387 3528 3531 3532 3604 3691 3695 3698 3703 3706 3726 3763 3779 3780 3846 3866 3874 ' 3887 3901 3967 4020 4026
Orthopedic Treatment
9
Chorea
8
Cardiac Lesions
7
Fo-St " 0 j* erctf t v< .
5
Cardiac Lesion
10
Orthopedic Treatment
12
Convalescent Polio-
.4
Orthopedic Treatment
4
Convalescent Fracture
4
`Astragalectomy
9
Osteomyelitis
11
Post-appendectomy
7
Eczema
1
Chronic Appendicitis
14
Osteomyelitis
7
Mastoiditis
6
Dietary Regulation
0.6
Oesophageal Stricture
7
Chorea
11
Post-anpendectomy
11
Osteomyelitis
10
Post-appendectomy
12
Anemia (type?)
5
Post-appendectomy
13
Otitis media - nephritis 12
Arthritis
6
Post-appendectomy
12
Convalescent Fracture
12
Alkaptonuria
0.25
Convalescent tonsillectomy 8
Post-appendectomy
11
Convalescentfburn
6
Mastoiditis
15
Chorea
8
Orthopedic Treatment
7
Tonsillectomy
8
0.30 0.27 0.27 0.10 0.38 0.61 0.05 2.22 0.62 0.14 0.42 0.10 0.37 0.09 0.53 0.21 0.26 1.57 0.29 0.45 0.14 0.41 0.43
0.17 0.10 0.23 1.28 0.24 0.23 0.60 0.39 0.24 0.23 0.70 0.90
0.06
0.17
C.09
0.08
0.03
0.11
0.03
0.23
0.10
0.13
0.08
0.20
0.005
0414
0.31
0.11
0.14
0.06
0.07
0.10
0.08
Nil
0.13
0.11
0.07
0.20
0.03 . 0.24
0.06
0.13
0.05
0.18
0.03
0.13
0.19
0.04
0.11
0.37
0.05
0.24
0.01
0.12
0.06
0.17
0.14
0.10
0.22
0.03
0.17
0.01
0.18
0.07
0.13
0.15
' 0.29
.0.05
0.15
0.15
0.11
0.11
0.20
0.04
0.05
. 0.06
0.03
0.03
0.23
0;11
0.13
0.11
0.09
0.17 0.06 0.09 0.08 0.07 0.08 0.09
0.13
0.07
0.06 Nil 0.08 0.18 0.08 0.07 0.09 0.11 0.02
0.07 0.11
0.07
0.05 0.04 0.08 0.17 0.07 0.04
0.09 0.10 .0.39 0.12 0.03
0.04 0.11
0.12 0.10
! . . ( <t (..,
X/,; 7 W I|r r.f- . ` ^ 1 1
tfg 0014467
O,0$G 1 o>oo~ 1 o.
0
6
o. o$lf o.
5
the faeces and urine. The calculation of faecal excretion in terms of the total ash Is not entirely justified on a physiologi cal basis, for reasons which will appear later. However, it is a reasonably satisfactory arbitrary basis for quantitative com parison. In this case it is necessary to use some such means^ for the reason that the faecal, samples are not comparable on a. time base.
The constancy in the lead excretion in these children is sufficient evidence of the general and unavoidable character of exposure to lead compounds. Moreover, the magnitude of their lead excretion as compared to that of adults suggests either that lead is excreted more readily by thepung, or that time Is not an important factor in influencing the extent of absorp tion under present conditions of exposure to lead compounds.
It is worthy of note that none of these children showed symptoms which gave even the vaguest suggestion of lead intoxica-
^ Cue tion. One of them had been breast-fed from birth. Thus the possible sources of lead must be extended to include the suck ling period and the gestation period. Accordingly the lead content of human milk was investigated in a limited manner. The results obtained may not be regarded 3 a representative cross section of the normal situation. They merely demonstrate that the ingestion of lead from this source may and does occur.
The milk was obtained by manual expression, each subject having been instructed by visiting nurses in the matter of clean liness and general technique. The several small samples were collected and delivered fresh to the laboratory, where they were kept until a considerable volume had been obtained from each
0014468
Table Y Lead Content of Human Milk
ubject No.
1 2 3 4 5
Volume of Milk in c.c.
Lead Pound in
2031
! !
0.05
1936
0.10
2306
0.09
1230
0.04
2853
Nil
K" 0014469
4
o subject. All'"of; the subjects were housewives, with entirely
negative histories in such matters as occupational exposures
Y to lead, recent illnesses, and recent*sources of medication.
>/ Table %. presents the results of the analyses.
Our data on lead absorption during gestation
confined
\/ to
obtained on experimental animals, under variable condi
tions of lead exposure. As such"tfcy
not apply to the
present matter except in so far as
that lead absorp
' Os.
tion in the pregnant animal is associated with lead absorption
by the foetus. However,
furnish/.; presumptive evidence that
human beings may be born with lead in their tissues.
V-'
i-
"h'-N >
* - hA '
.J~ A , -i ;i.' i -f, t
1
' r\ * :* A -.i, i /
2. Lead Ingestion and Lead Excretion in a Normal Adult.
h a healthy medical student v/as selected as a subject for
,v '
1 VAJ uV ',Ltdaily observations over a long period of time. His understanding
of the character of the problem provided the intelligent care
/ and cooperation' for prolonged study. He kept a diary of his A activities and movements about the city and the College of Medi
cine, in which he also recorded his food intake together with its
source. Except for specific instructions from time to time, he
selected his food according to his own wishes, and but for condi
tions imposed for experimental reasons, his entire life was that
of a normal junior in the College of Medicine.
The results obtained over a period of a year are graphi
cally illustrated in Figures 1 to 7.
0014470
H
Fig. 1. Lead Excretion in a Normal Subject
The blocks represent consecutive daily observations. The small
solid black blocks at the top indicate lead determinations on sam
ples of 50 c.c. of blood. They do not extend into the field of the
graph for the reason that the quantities of lead found were insuf
ficient for accurate measurement. The upper section illustrates
the urinary findings, the stippled area indicating volume of urine,
the solid block the lead found in mg3. In the lower section the
cross-hatched portions represent lead found in the faeces, while
the solid blbck gives the lead In mgs. per gram of ash In the
I:
faeces. The dotted line records the average levels of faecal ex- '
cretion of lead for the periods over which it extends.
The observations made from the fifteenth to twentieth days inclusive have been omitted on account of acci dental loss of the urinary samples for this period.
K 0014471
iH i& r m of Lead
Fig. 2. Lead Excretion in a Normal Subject The blocks represent consecutive daily observations as an
uninterrupted continuation of Fig. 1.
0014472
Three matters- of special note may be seen in Figure 1. ` ad
The urinary excretion at the start is almost negligible, but A
when an increase in urinary volume is brought about by in
creased water intake it becomes significant, though variable
from day to day* The faecal excretion starts out on a much A
higher level than the urinary, and is subject to wider varia
tion. It is clear that theye variations are not referable
entirely to variability of the mass of material excreted, for
if such were the case the milligrams of lead per gram ash of
faeces -would be much more nearly constant. (The weight of
ash is not an entirely- reliable measure of the quantity of
faeces, but experience has shown it to be the most generally
satisfactory manner of expressing quantity.)
Figure 2 shows the introduction of two changes in the
activities of the subject. He was instructed to discontinue
the two quarts of milk which it had been his daily custom to
take*1^--*rTTTly. A slight brief rise in the urinary excretion
of lead coincides with the day of discontinuance of milk. The
faecal excretion also, shows an elevation, with irregularly
*
spaced,very high peaks. That neither of these changes
di
rectly due to the elimination of milk from the diet will appear
later.
Then daily vigorous exercise was carried out for three
weeks. There is a definite rise in the urinary excretion, with
resumption of the former level on the cessation of exercise.
On the basis of the preceding rate of urinary excretion one
would certainly ascribe this change to the influence of exercise
tiers of Urine
Pig# 5. Lead Excretion in a Normal Subject
The blocks represent consecutive daily observations as an
uninterrupted continuation of Figures 1 and 2*
* This result of 0#14 mg. is an entirely ab normal one. The concentration of lead in the sample is 0.22 mg. per liter, and is higher than any obtained in the entire series of observations. Without doubt it. is due to the contamination of the sample in some manner.
0014474
However, a similar rise in the urinary excretion of lead, without a corresponding change in the experimental procedure, as shown in Figure 3, casts considerable doubt upon the validity of such an enterpretation. In fact the general level of urinary excretion is notably high during the entire period represented in Figure 3. The explanation of this sit uation may be found by examining the faecal output of lead from the begin ning of the observations through Figure 3. Beginning with the 54th day of observations (Fig. l) and continuing up to the 149th day (Fig. 3) there is a maintained high level of faecal lead excretion such as is not shown in any other normal period of the study. This suggests the existence of a factor which is so much larger than any other in its influence upon lead excretion in both faeces and urine as to completely mask the effects of other experimental measures. This factor is assoc-ia-ted-wi-th the quan tity and quality of ingested food. It may be noted that the faecal excretion of lead shows wide
7 Footnote: The very high figure obtained on the 124th day is entirely
\! unlike any other result obtained during the entire study, and ljencejis
probably in error. This figure of 0.14 mg. in 630 c.c. of urir^e repre-
> sents a concentration of 0.22 mg. of lead per liter of urine. Such la
conc; entration Ii is not/- found in the urines -of norm al sub jects, anpiL/ litldoes
\
1/
*
- .
k ./
!\
not occur agaip in/this subject, even when lead was adim-flistered for\
\
\j
:/
! \/
*'
\/
<,
,i
f
experimental purposes. It must .be the result/of contamination of the
sample at some point in its collection or analysis.
Kf 001447b
fluctuations from day to day, without any exact correspondence
with the daily level of urinary lead excretion# On the whole,
however, periods of several days in which the faecal-excretion
is high, are associated with corresponding high periods of
urinary lead output# The significance of the wide fluctuations
as well as the generally large magnitude of the faecal excre
tion becomes apparent in the observations shown in Figure 4#
Thus it is only necessary to point out that the notes kept by
the subject indicate that for the periods of time represented
in Figure 2 and the first half of Figure 3, the food intake
was practically doubled $
-f the period shown in
Figure 1. This was the result of longer working hours, shorter
hours of rest, and changes in food sources# During the obser
vations of Figure 1 the subject was at rest# At the beginning
of Figure 2 he began to exorcise daily to a moderate degree.
On September 1st (Fig. 2) he began working on the hospital
obstetrical service, being on call day and night# At the same
time he took vigorous exercise by playing tennis through the
greater part of the afternoon. On September 15th he began
working on the hospital receiving ward. During this period
vaccination against typhoid fever resulted in a severe reaction
(first Injection) with an evening temperature of 103 F. on J-
v -two successive days# On September 23 regular classes in the
Medical College began, with the necessity for establishing a
new routine. During this entire period the gross solid food
intake was high not only as a result of activities, but also
as a consequence of the discontinuance of two l^uarts of milk
daily which had been an important, item of diet previously#
KE 0014476
Just how much direct effect on the lead excretion was
produced by the discontinuance of milk and by exercise cannot
be determined* A glance at the high findings during the ab
sence of milk from the diet and at the lower results coinci
dent with a return to the use of milk suggests a cause and
effect relationship. In terms of the observations and con-
elusions of Aub and his associates , this might bo thought to
denote a steady depletion of the calcium stores of lead in
the body, with the simultaneous elimination of greater amounts
of lead during a period of low calcium intake, with an exactly
opposite effect during a period of higher calcium absorption.
Obviously, fatiguing exercise would be expected, to increase
the first effect. As a matter of fact, Either of these in-
fluences q .m ho
to have bean exerted
any Important"
because of the ovGr*^\AW^*^y gjy&a&ejp effect of the
on o.'
amounts of
The lead content of the food, as shown in Figure 4, was obtained by having the subject collect an exact duplicate of every meal during the period of such observations. For the greater part of the entire period of food analyses, no attempt was made to determine the lead content of specific foods. The entire bulk of three meals was treated as a single sample and analyzed, each meal having been collected in a quart glass jar. Because of the laborious character of the analytical work, such analyses were purposely omitted in the Initial periods shown in Figures 1, 2 and 3. W now v/ished to study accurately the influence of administered lead on the rate of excretion. A
0014477
double purpose was thus served in beginning the food analysis on the same date that we began to administer lead.
On the day indicated by the first small arrow, the subject was given 1 mg. of lead as a solution of lead chloride in 50 c.c. of distilled water not less than half an hour before the noon meal. Every day for ten days the dose was repeated in the same manner, the oonclusibn of this period being marked on the graph by the second small arrow. The response to this small dose was immediate in the case of the urinary excretion, v with a twenty-four hour lag in the faecal excretion. The urinary excretion may be seen to remain high during the period of experimental ingestion of lead and for four days thereafter. The faecal lead excretion, on the contrary, dropped off to a * normal level in forty-eight hours, i.e. as soon as the alimen tary tract emptied itself of unabsorbed lead.
The third small arrow indicates the termination of the time period for which the calculations of the inset table were made
Figure 5 carries on the daily observations without a break in continuity, showing the effects of the daily ingestion co of 5 mg. of lead in the form of the chloride, for six days. The first .two small arrows delimit the period of lead adminis o tration, while the third marks the end of the time over which the data of the inset table were obtained. The three plateaus X in the graphic representation of the lead in the food of the subject arise from the fact that for these three periods, the J weeks supply of each article of food was combined into a single sample for analysis. The total lead found in all such samples was spread evenly over an area which represents the entire week.
.1^ Agair.0 the response of the urinary excretion was prompt, and again It was sustained, this time for a longer period than that shown when the dose was smaller. The faecal excretion dropped off ftolalmost) its normal level in forty-eight hours, just as before, (The faecal excretion of lead during the period
of ingestion and for two days thereafter is so large as to re quire a very much increased area for its graphic representation. For this reason the trend of the results has been indicated and the exact quantity of lead found has been noted at the top of the incomplete block.^
The results set forth in these two figures are so cleancut as to require little clarification. They are so significant, however, as to justify-some emphasis. First, the quantity of lead in the food is remarkably high. There was no reason to doubt.the occurrence of lead in certain foods, but the discovery of amounts sufficient to explain the entire lead excretion of our subject, except during the periods of lead administration, was entirely unexpected. Second, the daily intake of lead is exceedingly variable.. Indeed so great is the variation that it is impossible to interpret^hanges in the rate of lead excretion/' except as this factor Is adequately controlled. The matter will be given fuller consideration later, but it must be stressed, here, that the observations of Aub and his associates, as well
rT as,others, on the factors which influence the excretion of lead must be reviewed critically with this variable in mind. This is especially necessary since the general acceptance of their conclusions rests largely upon the uncertain evidence of the varying lead content of the faeces under various experimental
conditions* Another consideration of importance relates to the propor
tion of ingested lead which passes through the alimentary tract
unabsorbed. Optimal conditions ware present for the absorption
of the administered lead, in that a dilute solution was taken at
a time when there was the least opportunity for chemical reaction
with the gastric contents. Yet slightly less than half the lead
administered during the first period was absorbed, while more
than two-thirds was eliminated unabsorbed during the second
period. These observations furnish an explanation of the well
recognized fact that heavy exposure for a short period of time
is likely to be less injurious than a lighter exposure for a
longer time. It may be calculated that If one milligram per day
wsre taken for thirty days our subject would have absorbed not
less than fifteen milligrams, while In six days at five milligrams
a day he actually absorbed only nine milligrams. Thus if the same Ar, if?;
total quantities of lead wane administered, the absolute quantity
absorbed would
greater
small daily dosage ^ given over
a longer period of time.
The sensitivity of the level of urinary excretion to the
magnitude of absorption is also sharply indicated here. During
the first period of administration, the subject apparently did
not absorb more than half a milligram of lead per day. Yet
the urinary excretion was measurably increased. However, in the
subsequent period, the daily absorption was in excess of one
milligram per day, and, though there was a definite rise in the
urinary excretory rate, yet there
no distinct increase in
rate over that of the previous period. That is to say -thfrt^the
KE- 0014480
f
M
Mt
ii
__
L* s
I''l-Ecq
iU(\"K, M.
ill
Jt
M
HZ.
M
HI
Calcium Lactate zg uis. Daily ^jj
Mftatioii Ammonium Chloride iz g w . Daily
30 1931
Pig* 7. Lead Excretion in a Normal Subject The blocks represent consecutive daily observation as an uninterrupted continuation of Figures 1, 2, 3, 4, 5, 6*
t< 0014481
excretory rate is not substantially altered by differences in absorption
of this magnitude. Nevertheless the period of heightened lead excretion
is prolonged under the influence of the increased absorption. This
latter fact is especially significant when it is observed that the lead
in the blood during the two periods is not changed within the limits of
sensitivity of the method oi observation. What obviously occurred was
that the absorbed lead was so distributed in the tissues of the body as
to increase their content without producing a corresponding degree of
change in the concentration of lead in the blood* or the urine. Thus
the period required for the elimination of the increased quantity in the
tissues was prolonged*
In Figures 6 and 7 the observations on this subject were concluded*
three hundred and fifty four days having elapsed during the study. The
study of the lead in the food was discontinued as shown in Figure 6.
Figure 7 shows a period of three weeks of increased calcium intake* and
another similar period in which twelve grams of ammonium chloride were
administered daily* with an intervening period oi one week, neither
procedure resulted in any noticeable effect upon the excretory rate. It
may be seen that the lead content of the food diminished considerably
toward the end of our period of study. The maintained low level of faecal
excretion suggests -chat the ingested iead remained low during the remainder
of the study, furthermore * the urinary excretion of lead was almost
negligible during the period represented in these two figurws. xables
YXI and VIII show the frequency distribution of the resultB in milligrams
per gram of ash in the faeces, and per liter oi urine* together with
the calculated means^ for ^these items. Jne,percentage of negative,
__the
mean' value of lead per liter of urine,
is_unhouD.t,,eai.y- due~an"'pahV"to^ the'` r`aet'''that"'the' urine was^ collected in
twenty-four hour ^samples* the volumes of which in many instancea-were less
than~-one--liter. ..ouch quantities-..obtainedjfrom normal subjects .frequently
K'fc 0014482
Table VII
Distribution of Urinary Samples g to Lead In Milligrams per Liter
Milligrams of Lead Per Liter of Urine
Humber
Percentage
too.
.o .o
-3 t9
*1
0 - .009 .01 - .019 .02 - .029
.039 .049 .05 - .059 .06 - .069 .079 .089 .09 - .099 .10 - .109 .11 - .119 .22
179 44 33 16 16 7 5 3 1 2 1 2 i*
57.9 14.2 10.7
5.2 4.9 2.4 1.6 1.0
.3 6 .3 .6 .3
oCO
Totals
309 100.
Mean ~ 0.017 3 0.001 S.D. = 0.003
^ Omitted In calculation of mean.
KT 001
Table VIII
Distribution of Faecal Samples afi- to Lead In Milligrams per Oram of Ash
Milligrams of Lead '
Per Gram of Ash
Humber
0 _ .009 .01 - .019 .02 - .029 .03 _ .039 .04 - .049 . .05 - .059 .06 - .069 .07 - .079 .08 - .089 .09 - .099 .10 - .109 .11 - .119 .13 -
52 95 75 38 27 20
7 3 2 3 2 1 1
Totals
326
Percentage
16.0 29.2 23.0 11.7
8.3 6.1 2.1
.9 .6 .9 .6 .3 .3
100.
Mean s 0.027 0.00(2 S.D. = 0.020
KE" 0014484
fail__io^~ahow--amtmfh""~of lead vihich'are-- capabl-e-^1---accurate-quant-i tative
o&t4mation* j?'or thls..reasun'--nolr~i'e8S''*tlian^two lTters'lLs-'des-irabl'e'f wr
the--purp.o.s_e,,Q.f, each observation in a - 3tuny-ox--tme^normal'excretion of
lead ine conaixions of _tiie_l-Qregoing--ohsep^ii^d^ne-"were"d'eTied--wi-th'-a
full recognition tnat tne.limitations of'the analytical methods would
develap._arLjLncrea9e&. importance in dealing with the samples of urine*
Ihxs--mat-ter--is_of- mu-ch-less-signlf jcance--i-n--the--ease--of-the--faecal earn-
pte.s_f or,,_thereason..that-i^e-l-arger^u'antities''df'lead'prtrs-erilrxeduce
the-proportional analytical error,
mrnpattnii-tr^Ty inw
value of the mean excretion of lead in milligrams per gram of ash is
.ovide-n-o^--1-ewer, ra^eluf-^ead^xeret-ron--than `irs* `weBBtew-iir- normal sub
jects. (Cf. Tables XIII and XIV) The combined facts indicate that during
the latter periods of the experiment* the subject had relatively little
lead in his tissues, that he absorbed little from day to day, and that
consequently he excreted very little. The importance of the information presented in the foregoing
figures is heightened by certain further considerations. Thus if the day-to-day variations in the lead content of the food are leveled by
calculating the mean daily intake of lead, and if the da ly excretion
of lead in thefaeces and urine, exclusive of the periods of elevation
occasioned by the experimental administration of lead, are calculated,
the results are somewhat surprising. Tables IX, X and XI show respect
ively the frequency distributions of daily lead in food, urine, and
faeces, with the calculated means, while Table XII compares daily
ingestion and daily excretion. It i3 seen that the ingested lead is
approximately equivalent to that which is. excreted in the urine and
faeces combined, the differences between their mean values being
insignificant, statistically*
' KEf 0014485
Table Djj
ttccrulb*^
Distribution of Dally Food Samples -as to Lead Content
H O
CO
Milligrams of Lead Found in 24 Hrs.
- a - .049
.05 - .099 - .149
,15 - .199 ,20 w* .249 .25 - .299 .30 - .349 .35 - .399 .40 - .449 ,45 .499
Totals
Number
13 16 > 33 24
9 5 4 0 0 2
105
Percentage 12.4 14.3 31.4 22.8 8.6
3.8
1.9 100'
Mean = 0.147 0.006
S.D.
0.086
0014486
Table
:
Distribution of Twenty-Four Hour Samples of Urine to Lead Content
Milligrams of Lead Pound In 24 hrs.
0 - .019 02 - .039 04 - .059 06 - .079 08 - .099 10 - .119 12 - .139 14 - .159
Totals
Number
172 74 30 17 8 6 1 1
309
Percentage
55.7 24.0
9.7 5.5 2.6 1.9 0.3 0.3 100
Mean 0.027 * 0.001 S.D. 0.02S
K f 0014487
Table XX
Distribution of Twenty-Four Hour Samples of Faeces to Lead Content
Milligrams of Lead Found In 24 hrs.
Number
Percentage
1!
O CO
o >.CM
0 - .049 .05 - .099 .10 - .149 .15 - .199
.249 .25 - .299 .30 - .349 .35 - .399
.449 .45 - .499 .50 - .549
.82 Totals
46 62 79 58 33 15 18
5 2 4 2
i* i*
326
14.1 19.0 24.2 17.8 10.2
4.6 5.5 1.6
.6 1.2 0.6 0.3 0.3
100
Mean - 0.151 * .004 S.D. z 0.100
* These two aberrant results are not Included in the calculation of the mean value#
KiT 0014488
Table XII
Comparison of Mean Dally Lead Ingestion with Mean Dally Lead Excretion
.Mean Daily Intake of Lead
Mean Daily Excretion of Lead:
In Urine
0.027
.001
In Faeces
0.151 + .004
Mean Daily Excretion of Lead
(Arrived at by calcula tion from the actual data of combined uri nary and faecal excre tion from day to day.)
0.147 t .006
0.178 0.172 004
*K 0014489
If the facts are examined in still another manner the same conclusions are evident. Thus if the periods of experimen tal administration of lead are eliminated, the subject- excreted 48.95 mg. of lead in the faeces, and 6.00 mg. of lead in the urine, a total output of 64.95 mgs., in 329 days. During a period of approximately one third of this time (105 days) over
>
which food analyses were made, he ingested approximately 15 mgs. of lead in his food.
It is difficult to escape the conclusion that substan tially the entire lead interchange of the subject is to be explained by the occurrence of lead in his food. Certainly there can be no other factor of any important magnitude, though undoubtedly some small amount was contributed by drinking water and by other occasional contacts with lead. Prom this it follows that lead was not accumulating in the tissues except for short periods. Thus periods in which excretion exceeded intake alternated with periods in which excretion was less than intake, these effects being brought about by variations in activity, in water intake, in diet, - in short by a number of conditions well within the limits of normal physiological behavior.
K 0014490
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001 4B2
3. Lead Excretion in Various Groups of Normal Subjects.
Prolonged daily observations on u m hnglu subject^
yield information as to the variations in lead excretion attend
ant upon the changing circumstances in the life and activities
of a single individuals, A study of random samples of excreta
from a large segment of the population might be expected to
demonstrate a somewhat wider range of variability not only as
the consequence of greater variation in environment and activity,
but also because of differences in the physiological attributes
of different individuals. Thus the investigation^of a large and
representative group of persons who experience no occupational ;
exposure to lead compounds, Joy the method of random sampling,
should present a fairly adequate cross-sectional picture of the
lead excretion of normal man under present conditions. Incident
ally one may determine thereby, whether or not
'
who has been studied in detail represents
the average type of normal individual. Several groups of subjects have been studied in the
above manner. Medical students, with no previous occupational exposure to lead compounds, form the background for fixing the status of the one subject previously discussed. A number of persons selected from a much larger group of workmen because of their complete freedom from occupational lead exposure, constitutes an additional normal group. Still another group Is made up of workmen with no lead exposure at the time of observations, but
Table XIII
Distribution of Subjects According to Milligrams of Lead per Gram of Ash In the Faeces
Medical Students with No Lead Expo sure at Any Time
Number Percentage
Other Persons with No Lead Expo sure at Any Time
Number Percentage
Persons with Questionable or Slight Exposure in an Earlier Period
Number Percentage
0 - 0.029 0.03 - 0.059" 0.06 - 0.039 0.09 - 0.119 0.12 - 0.149 0.15 - 0.179 0.13 - 0.209 0.21 - 0.239 0.24 - 0.269 0.27 - 0.299 0.30 - 0.329 0.33 - 0.359 0.36 - 0.33 0.39 - 0.419 over 0.42
Totals
15 34.1 9 20.4 8 18.2 6 13.6 2 4.5
1 2.3 1 2.3
1 1* 44
2.3 2.3 100.00
4 8.7 10 21.7 13 28.3
7 15.2 5 10.9 1 2.2
2 4.3
1 2.2
1 2.2 2* 4.3 46 100.00
21 29.6 16 22.6 13 18.3
8 11.3 5 7,0 5 7,0
1 1.4
1 1.4 1* 1.4 71 100.00
Mean Probable Error Standard Dev.
0.06^`r 0.007' 0,071;
0.098: 0.006 0 0$0
0.072 0.005 0.06$::
* Excluded in calculation of mean
K? 0014494
r. l Table
6>
Distribution of Subjects According to Milligrams of Lead per Liter of Urine
A4AU4 fj* Ua, Ua^ML
Medical Students with No Lead Expo sure at Any Time
Number Percentage
Other Persons with No Lead Expo sure at Any time
Number Percentage
Persons with Questionable or Slight Exposure in an Earlier Period
Number Percentage
0 - 0.029 0.03 - 0.059 0.06 - 0.089 0.09 - 0.119 0.12 - 0.149 0.15 - 0.179 0.18 - 0.209 0.21 - 0.239 0.24 - 0.269 0.27 - 0.299 0.30 - 0.329 0.33 - 0.359 0.36 - 0.389 0.39 - 0.419 0.42 Totals
9 14
9 8 1 1 1
1*
44
20.4 ol .8 20.4 18.2
2.3 2.3 2.3
2.3
100.00
7 15.9 11 25.0 11 25.0
5 11.4 3 6.8 1 2.3 3 6.8
3* 6.8 44 100.0
8 11.3 24 33.8 22 31.0
6 8.5 2 2.8 3 4.2 2 2.8
4# 5.6 71 100.00
Mean
Probable Error
Standard Dev.
0.067' +0.005* 40.047
0.076" +0.005; *o.o$o
*069 +0.OOo 40.041
^Excluded in calculation of mean
Kf
0014495
with an occupational history which did not permit of the certain
exclusion of slight exposure at some previous time* The excre
tion of lead in the faeces and urines of these groups, and the
calculated mean values for these factors, are presented in Tables
XIII and XIV.
The three groups of subjects are so nearly identical as
to be indistinguishable by any statistical means. On the other
hand the medical student who was the subject of the prolonged
study does not fit into any one of them, statistically, since
there is a significant difference between his mean lead excretion o
and that of each of them. This'^brings) us-to recognize the im
portance of the somewhat limited diet of the subject in question.
As a matter of choice and habit, this student ate somewhat sparing-
a,
ij*. and introduced little (variety into his choice of food, ^Thie-^
uj iv-Cuit-c*
Viav
'caused) his lead intake (to be) less than that of the average person.
A further difference, affecting only the mean urinary excretion
of lead, has been previously pointed out, in that the analytical
error was somewhat enhanced by the smaller size of the urinary
samples. It is clear, therefore, that although more detailed
and specific Information was obtained in the study of the one sub
ject, a more accurate measure of general experience, as regards
lead absorption and lead excretion. Is to be found In the observa
tions made on the larger number of subjects. Thus the mean lead
excretion of normal persons In the United States, with no occupa
tional exposure to lead compounds, is seen to be of the general
magnitude of 0.07 milligrams per liter of urine, and 0.07 to 0.09
milligrams per gram ash of faeces. If the average urinary excre-
0014490
\P
the average normal American excretes approximately .rd of a milligram of lead per day.
sad as a Contaminant of Pood and Drink. "'
JtuiM Tr
.`he presence of lead in the normal food supply/roquiree--
`onsideration of many possible sources for its origin. In
to leave as little as possible to conjecture, large samples
'h*sr4J i JLK-t<S
igle common food materials mse collected ever- a -three1 weeks
(1 in the course of tbs obenvn felons1 on tho-medloal studfent
The results of -eu^h, analyses, are
.ated in TableSXV, in which the actual weight of food examined,
the actual amounts of lead found are given as a basis for the
ulation of the concentrations of lead. The data are largely
_____ -explanatory, but certain matters merit further discussion.
J" ^"
wl'-:'-!1
``(1) Lead Is found In all
food materials studied,/without;
regard, forj the variety or complexity of the processes of prepara
tion and distribution.
(2) The quantity of lead in articles derived from grain and In dttmhu^
most meats is quite small and would not be found except for
delicate methods of analysis carried out on large quantities of
material.
is^jjjagenc|a^ixi ^owrn^wveTre'l a'
'the--eaae*--
HE 001 449V