Declaration of Maridee Ann Gregory, M.D.
Public Court Documents
June 7, 1991
17 pages
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Case Files, Matthews v. Kizer Hardbacks. Declaration of Maridee Ann Gregory, M.D., 1991. c98f619c-5c40-f011-b4cb-7c1e5267c7b6. LDF Archives, Thurgood Marshall Institute. https://ldfrecollection.org/archives/archives-search/archives-item/f19666e0-2152-492a-b03a-170983865797/declaration-of-maridee-ann-gregory-md. Accessed November 23, 2025.
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DANIEL E. LUNGREN, Attorney General
of the State of Califorma
CHARLTON G. HOLLAND, III
Assistant Attorney General
STEPHANIE WALD
Supervising Deputy Attorney General
LAN E. VAN
Deputy Attorney General
2101 Webster Street, 12th Floor
Oakland, California 94612-3049
Telephone: (413) 464-1173
Attorneys for Defendant
UNITED STATES DISTRICT COURT
NORTHERN DISTRICT OF CALIFORNIA
No. C 90 3620 EFL
DECLARATION OF MARIDEE
ANN GREGORY, M.D.
ERIKA MATTHEWS AND JALISA
MATTHEWS, by their guardian ad litem Lisa
Matthews, and PEOPLE UNITED FOR A
BETTER OAKLAND, On Behalf of
Themselves and All Others Similarly Situated,
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Plaintiffs, |
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MOLLY COYE, M.D., Director, California
Department of Health Services,
Defendant.
I, MARIDEE ANN GREGORY, declare:
L I am a Doctor of Medicine and a Board Certified Pediatrician. I have
spent my entire professional career since 1965 in the area of maternal and child health.
I was first employed by the State Department of Health Services in 1981 as Chief of
Maternal and Child Health. Since 1987 I have served as chief of the California
Childrens Services Branch within the Department. [ also serve as medical consultant to
the Child Health and Disability Prevention Branch of the Department and have been
the medical consultant in the drafting of program letters regarding lead screening and
1,
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testing matters within the last four or five years.
2 The matters stated below are personally known to me and if called as a
witness I could and would testify competently concerning the same.
3. The Department of Health Services does not dispute the seriousness of
the problem of lead poisoning in children. In fact, as recently as March 12, 1991, the
Department's former Director, Dr. Kenneth Kizer stated that: "Lead poisoning is the
most significant environmental health problem facing California children today, and
insufficient consideration is being given to this potential problem during routine child
health evaluations." What the Department does dispute is whether either the law or
good medical practice requires the actual testing of children’s blood for the presence of
lead in all cases, and particularly very young children in the Early and Periodic
Screening, Diagnostic and Treatment ("EPSDT") Program of the Federal Medicaid
Program (known as the Medi-Cal program in California, and administered by the
Department of Health Services).
4, The Department believes that neither applicable laws nor good medical
practice requires that all EPSDT children receive blood lead tests as a part of the
mandatory screening process. Rather, it is the Department's position that young (i.e.,
under 6 years old) EPDST children should first be screened by their treating physicians
for both the presence of objective medical indications and/or environmental factors
which might indicate the possibility of lead toxicity. If either or both are presenti then
a blood test would be indicated.
3 A blood test is an intrusive procedure which causes some degree of
discomfort, and in the vast majority of cases is simply unnecessary to determine
whether a child is at risk of lead poisoning. Further, there is a significant cost factor
involved in completing a blood test which must be considered in an age of limited
1. CDHP Provider Information Notice #91-6, included as Exhibit C in the
Exhibits In Support Of Plaintiffs’ Motion For Partial Summary Judgment.
2
3
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resources, although the Department has been absolutely clear in its communications
with physician/providers that the cost of a blood test for lead is a covered cost in the
Child Health and Disability Prevention Program (see the penultimate paragraph of
CHDP Provider Information Notice #91-6). The message the Department sends to
physicians is that blood lead tests should be given to young EPSDT children whenever
and wherever medically indicated and that cost is not a factor -- good medical
judgment is.
6. While it is recognized that certain pediatricians advocate universal blood
lead testing for young children, that position is not universally shared. On March 3,
1987, the American Academy of Pediatrics published its Statement On Childhood Lead
Poisoning in its journal Pediatrics? While recognizing as an ideal the concept of
universal blood lead testing, the Statement recognized that ". . . the incidence of lead
may be so low in certain areas that pediatricians may prudently consider their patients
to be at little risk of lead toxicity . . "/ and set out priority guidelines to assist
pediatricians in deciding whether the need for a blood lead test was indicated.
7. On June 4, 1991, I spoke by telephone with Raymond J. Koteras, M.H.A,,
Director of the Division of Technical Committees, of the Department of Maternal,
Child and Adolescent Health of the American Academy of Pediatrics. Mr. Koteras
confirmed to me that, while the matter of child blood lead testing is currently under
review by several Academy committees, the aforementioned Statepgent is and remains
the position of the Academy.
8. The Department believes that its position is consistent with the
requirements of the Health Care Financing Administration's ("HCFA") State Medicaid
Manual (included as Plaintiffs’ Exhibit N) wherein it is stated that a blood lead level
2. A copy of this Statement is attached hereto as Exhibit A.
3. Op. cit, at p. 463.
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assessment is mandatory where age and risk factors so indicate. (Ex. N, at p. 5-14)
The Manual goes on to specifically require that all Medicaid eligibie children ages 1-3
be screened for lead poisoning. However, the Manual section wherein the requirement
to screen is contained also contains several significant caveats concerning testing:
"Physicians providing screening/assessment services under the EPSDT program use their
medical judgment in determining the applicability of the laboratory tests or analysis to
be performed. +. « As appropriate, conduct the following laboratory tests: . . . 1 In
general, use the EP test as the primary screening test." (Ex. N, at p. 5-14 through 3-
15) Clearly, the ultimate decision as to whether a blood lead test should be given has
been left to the determination of the physician.
9. It is the present belief of the Department that universal blood lead:
testing of young EPSDT children is not medically indicated, legally required nor fiscally
prudent.
I declare under penalty of perjury that the foregoing is true and correct.
Executed at Sacramento, California this 6th day of June, 1991.
M hod A ant,
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Committee on Environmental Hazards
Committee on Accident and Poison Prevention
Statement on Childhood Lead ‘Poisoning
1
Lead remains a significant hazard to the health
of American children.’® Virtually all children in
the United States are exposed to lead that has been
dispersed in air, dust, and soil by the combustion
of leaded gasoline, Several hundred thousand chil-
dren, most of them living in older houses, are at
risk of ingesting lead-based paint as well as lead-
bearing soil and house dust contaminated by the
deterioration of lead-based paint. Although the in-
cidence of symptomatic lead poisoning and of lead-
related mortality has declined dramatically,’ data
from targeted screening programs’ and from a ne-
tional survey” show that there are many asympto-
“matic children with increased absorption of lead in
all regions of the United States. It is particularly
prevalent in areas of urban poverty.
hildhood lead poisoning can readily be detected
by_gimple. and_inexpensiy ¢ screening’ technigues;
however, screening is sporadic and in some areas
not available.
Despite wide recognition of the importance of
preventing children’s exposure to lead, state and
federal funding for the screening of children and
for the removal of environmental lead hazards has
diminished in recent years. Thus, pediatricians at-
tempting to address the problem of childhood lead
exposure face serious economic and administrative
obstacles to effective intervention,
This statement reviews current approaches to the
diagnosis, treatment, and prevention of lead poi-
soning, and it recommends steps to reduce the
pervasive impact of lead on children’s health. Some
of these recommendations are addressed to practi-
tioners and others to agencies of state and federal
government. It is important to recognize that vir-
tually all of these preventive steps are after the
fact, Ideally, in keeping with the precepts of pri-
mary prevention, lead should have been prohibited
from ever having become dispersed in the modern
environment.
PEDIATRICS (ISSN 0031 4005). Copyright © 1887 by the
American Academy of Pediatrics.
has been shown conc
BACKGROUND AND DEFINITIONS
Lead has no biologic value. Thus, the ideal whole
blood lead level is 0 ug/dl.. According to the Second
National Health and Nutrition Examination Sur-
vey (NHANES II); conducted from 1876 to 1980,°
the mean blood lead level in American preschool
children was approximately 16 ug/dL. Substantially
lower lead levels are seen in persons remote from
modern industrialized civilization® and in the re-
mains of prehistoric man.
Until recently, whole blood lead levels as high as
30 ug/dL were considered acceptable. However, dis-
turbances in biochemical function are demonstrable
at concentrations well below that figure. For ex-
ample, inhibition of 3-aminolevulinic acid dehy-
drase, an enzyme important to the synthesis of
heme, occurs at whole blood lead levels below 10
pg/dL."® Also, the enzyme ferrochelatase, which
converts protoporphyriti to heme, iz inhibited in
children at a blood lead concentration of approxi:
mately 16 pg/dL; thus, elevations in erythrocyte
protoporphyrin above normal background become
evident at blood lead levels above 16 ug/dL.? In
addition, depression of circulating levels of 1,25-
dihydroxyvitamin D (the active form of vitamin D)
is seen at blood lead levels well below 25 g/dL, 2%
Neuropsychologic dysfunction, characterized by
reduction in intellizence and ‘alteration in | a Behiavio or,
usively to occur in agympto-
matic children w Sn Rs Tead levels at
The results of clinical and epidéiislogic ‘studies
conducted in the United States,” Germany,” and
England" indicate clearly that blood lead levels
below 50 ug/dl. cause neuropsychologic deficits in |
asymptomatic children. Recent clinical and exper:
imental studies suggest that neuropsychologic dam-
age may be produced in children with blood lead
levels below 35 pg/dL.}®
Short stature, decreased weight, and diminished
chest circumferanre have recently been found in
analyses of dite From the NHANES II survey to be
significantly associated with blood lead levels in
American children younger. than 7 years of age,
62400757821
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after controlling for age, race, sex, and nutritional
status. Although the effects are small, the results
are statistically robust,’
In light of these data, an expert Advisory Com-
mittee to the Centers for Disease Control (CDC)
has determined that a blood lead level of 25 ug/dL
or above indicates excessive lead absorption in chil-
dren and constitutes grounds for intervention.’
Increased lead absorption was previously defined
by & blood lead level of 30 ug/dL. Furthermore, the
CDC committee has now defined childhood lead
poisoning as a blood lead level of 25 ug/dL in
association with an erythrocyte protoporphyrin
leval of 85 ug/dL or more.’ The Academy concurs
in these definitions. Also, the Academy anticipates
that as evidence of the low-dose toxicity of lead
continues to develop, these definitions will be low-
ered still further.
PREVALENCE OF LEAD POISONING
Data from NHANES II® indicate that between
1876 and 1980 the national prevalence of blood lead
levels of 30 pg/dL or higher was 4% among Amer-
ican children 6 months to 5 years of age. Applying
this rate to US census data, it may be estimated
that, between 1976 and 1980, 780,000 American
preschool children had excess levels of lead in their
blood. In the NHANES II data, there was wide
disparity in the prevalence of elevated blood lead
levels between black children (12%) and white chil-
dren (2.0%) irrespective of social class or place of
residence. A similar disparity was noted in mean
blood lead levels, which were 21 xg/dL in black
preschool-aged children and 15 pg/dL in white chil-
dren of the same age. Prevalence rates for elevated
blood lead levels were highest among families in
densely populated urban areas and in those with
incomes of less than $15,000 per year. However, it
should be noted that cases of lead poisonings were
found also in families of higher income and in rural
settings.
Between 1976 and 1980, the average blood lead
level in Americans of all ages decreased from 15.8
to 10.0 ug/dL according to the NHANES I1.* This
decrease coincided with a reduction in the use of
lead additives in gasoline. Additional factors in this
_ reduction may have included a simultaneous reduc-
tion in the lead content of foodstuffs, the impact of
targeted screening programs in high-risk areas, and
an increase in public awareness of the hazards of
lead.
SOURCES OF LEAD
Environmental Sources
Lead is ubiquitous. A natural constituent of the
ey
earth’s crust, lead may be found in drinking water,
soil, and vegetation. Its low melting point, mallea-
bility, and high density, as well as its ability to form
alloys, have made lead useful for myriad purposes,
--Many of these uses (eg, rediation shields, storage i
batteries) are not intrinsically dangerous, However,
when lead is used for purposes other than intended ~3§
(eg, burning of storage battery casings), when it is
incorrectly applied or removed (eg, improper use of
lead ceramic glazes, burning and sanding of old
leaded paint), when it is disseminated rather than
reused (combustion of lead additives in automotive
fuels), or when it ie improperly discarded, lead
‘enters the human environment in potentially haz- #
ardous form.
For purposes of estimating risk to children, pad
sources may be categorized as low, intermediate,
and high dose (Table 1).
Low-Dose Sources. These sources of lead inclide
air, food, and drinking water, Together, these
sources, which have accounted for an average esti-
mated blood lead concentration of approximately
10 ug/dL in the recent past, probably now account “3
for a blood level concentration of about 6 ug/dL.
Mean ambient air lead concertrations currently ki:
average less than 1 ug/m® of air, although in areas ps
near lead smelters, concentrations may be she,
tially higher,
Average dietary intake of lead increases fc 20 Ee
#g/d during early infancy to 60 to 80 pg/d by & to
8 years of age.’ Except in isolated areas, it would. :
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6240075422
appear that the majority of public drinking water ¢% 5
supplies in the United States have a lead concen-.
tration of less than 20 pg/dL. However, these data
may be misleading if, as iz generally the case, the
water samples have been obtained from the distri-
bution plant prior to the distribution of water
through a plumbing system that contains lead 4
pipes. The lead solvency of drinking water can be
reduced by reducing acidity of water supplies and
by abandoning the use of lead-based solder at pipe
joints in new and replacement plumbing, Commu.
nities with excessive lead in water have successfully
used each of these remedial approaches. i
TABLE 1. Common Sources of Lead
Low dose
Food
Ambient air
Drinking water
Intermediate dose
Dust (housshold)
Interior paint removal
Soil contaminated by automobile accident
Industrial sources
Imprope® temoval of exterior paint
High dose
Interior and exterior pat
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" Intermediate-Dose Sources. These sources in-
£5 clude dust and soil in children’s play areas. Dust
BY: ond soil are contaminated principally by automo-
IB tive exhaust and by the weathering and deteriora-
gi tion of old lead paint (both interior and exterior).
Bi Although background soil lead contaminants in
BF rural areas are generally less than 200 ppm, concen-
£ trations of lead in urban soil can exceed 3,000 ppm.
BF: In industrial areas where lead smelters have been
3 situated (eg, El Paso, TX; Kellogg, ID), the lead
“content of dust can, however, exceed 100,000 ppm,*®
.- thus producing significant elevations in children’s
© blood lead levels. Each increase of 100 ppm in the
lead content of surface soil above a level of 300 ppm
SY is associated with a mean increase in children's
3 whole blood lead levels of 1 to 2 pg/dL. When dust
. and soil are the only sources of exposure to lead,
fk symptoms are rarely encountered, although lead
{38 toxicity may occur. Soil lead may, however, be
E. extremely difficult to abate, and chronic low-grade
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ingestion may continue undetected even after a
child has come to medical attention. The proper
site for disposal of lsad waste, such as lead-contam-
&. inated soll, is a hazardous waste facility that has
38. been approved by the US Environmental Protec-
tion Agency. |
= High-Dose Sources. These sources are those in which the concentrations of lead are sufficient to
produce acute and potentially fatal illness, Lead-
based paint on both the interior and exterior sur-
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faces of housing remains the most common high.
dose source of lead for preschool-aged children. It
continues to be the experience of most pediatricians
that virtually all cases of symptomatic lead poison-
ing and blood lead levels greater than 70 ug/dL
result from the ingestion of lead paint chips.
Lead-based paint is still widespread. A 1878 US
census survey found that 8 million of the 27 million
occupied dwellings in the United States, which had
t been built prior to 1940 when use of lead-based
pain: was common,” were deteriorated or dilapi-
dated. An additional 22 million dwellings were built
between 1940 and 1960, and 75% of these units are
estimated to contain lead-based paint. Nationally,
according to the 1978 census survey of housing, 8%
of rental units have peeling paint.
Although the use and manufacture of interior
lead-based paint declined dramatically during the
1950s, exterior lead-based paint continued to be
available until the mid-1970s and is still available
for maritime use, farm and outdoor equipment, road
stripes, and other special purposes. Thus, potential
for domestic misuse of lead-based paint continues
to exist. Manufacturers could voluntarily decrease
the lead content of interior paint until 1877, when
the US Consumer Product Safety Commission en-
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acted regulations banning the sale in interstate
commerce of paints for exposed interior and exte-
rior residential surfaces containing more than
0.06% lead by weight in final, dry solid form.
A previously unforeseen, but increasingly recog-
nized, danger is that of improper removal of lead-
based paint from older houses during renovation
or, ironically, during cleaning to protect children.
Torches, heat guns, and sanding machines are par-
ticularly dangerous because they can create a lead
fume.? Sanding not only distributes lead as & fine
dust throughout the house but also creates small
particles that are more readily absorbed than paint
chips. The greatest hazard in paint removal appears
to be to the person doing the “deleading” and to
the youngest children in the dwelling. There mdy
be significant morbidity. Persons who perform this
work should comply with the standards for occu-
peational exposure to lead which have been devel
oped by the US Occupational Safety and Health
Administration. Pregnant women, infants, and
children should be removed from the house until
deleading is completed and cleanup accomplished.
Proper cleaning of the dust and chips produced in
deleading must include complete removal of all
chipping and peeling paint and vacuuming and
thorough wet mopping, preferably with high-phos-
phate detergents. This waste must be discarded in
& secure site,
Another previously unrecognized hazard lies in
sandblasting. This technique is commonly used to
remove lead from exterior surfaces, There are no
standardized safeguards. Recent case reports of lead
poisoning among sandblasters underscore the haz-
ard. ® Sandblasting creates large amounts of lead-
laden dust and debris which, if improperly disposed
or not properly removed, redouble the hazard,
Uncommon Sources (Table 2)
Additional lead sources include hobbies such as
artwork with stained glass and ceramics, particu-
larly when conducted in the home. Folk medicines
TABLE 2. Uncommon Sources of Lead
Metallic objects (shot, fishing weight)
Lead glazed ceramics
Qld toys and furniture
Storage battery casings
(Gasoline sniffing
Lead plumbing
Exposed lead solder in cans
Imported canned foods and toys
Folk medicines (eg, azarcon, Greta) -
Legged glass artwork
Cosmetics
Antique pewter
Farm equipment Na
SENT BY:NHelLP ® piel
used to treat gastrointestinal ailments may contain
lead and mercuric or arsenical salts. Recent reports
have noted lead poisoning from use of azarcon (lead
tetroxide)* and Greta (lead monoxide) among Mez-
ican-Americans and from use of Pay-loc-ah, a
Chinese folk remedy,” among Hmong refugee chil-
dren. Cosmetics (ceruse, surma, or kohl), particu-
larly those from Asia, may contain white lead or
lead sulfide®” and have caused severe lead poison-
ing. Another source of lead is improperly soldered
cans, particularly those containing acidic food-
stuffs. Food should not be heated in such cans, as
heating increases the dissolution of lead. Pediatri-
cians should realize as a practical matter that the
lead content of imported earthenware toys, medi-
cines, or canned foods cannot readily be regulated,
In addition, antique toys, cribs, and utensils may
have a significant lead’ content. ;
Lead-glazed pottery is a. potential source of Toad
in food and drink. If not fired at high temperatures,
lead may be released from the glaze in large
amounts when such pottery is used for cooking or
for storage of acidic foodstuffs. Also, if pottery
vessels are washed frequently, even & properly fired
glaze can deteriorate, releasing unsafe levels of pre-
viously adherent lead.” Sporadic cases of f plumbism
have been traced to lead-glazed pottery.” :
Among the oldest sources of lead in America is
antique pewter. Food should not be cooked or stored
in antique pewter vessels or dishes. Although un-
common, many of the above sources have been
essociated with severe, symptomatic, and even fatal
lead poisoning.
Finally, a number of cases of lead poisoning have
been reported among the children of workers in
smelters, foundries, battery factories, and other
lead-related industries. ®®¥ These workers can bring
home highly concentrated lead dust on their skin,
shoes, clothing, and automobiles. This source of
exposure can be avoided by providing showers at
work, by providing workers with a change of cloth-
ing, and by having clothing laundered at the work-
place.
In summary, it can be inferred from the
NHANES II data that most children in the United
States with increased lead absorption have been
exposed to low-dose or to intermediate-dose lead
sources. Four percent of children have blood lead
levels in excess of 30 pg/dL, but only 0.1% have
levels exceeding 50 pg/dL.?
ROUTES OF ABSORPTION
Ingestion is the principal route of lead absorption
in children. Because of the high density of lear
ingestion of surprisingly small quantities may pro-
duce toxic effects. A lead paint chip weighing only
‘480 EADY POIGSOINIMM
TY
1 g (approximately 1 em’ in surface area) and
containing 5% lead by weight will deliver a potential
dose of 50 mg (50,000 ug); by comparison, the safe
upper limit for daily intake of lead by children is 5
g/kg of body weight. Because ingestion of such
chips ie not uncommon, it might be expected that
large numbers of children would have symptomatic
lead poisoning. However, most ingested chips are
swallowed whole or in large pieces, rendering much
"of the lead contained in them unavailable for ab-
sorption.
Several recent studies have reported the effec-
tiveness of normal hand-to-mouth activity ass e
means for the transfer of lead-laden dust from the
environment into children ®* True pica (the in-
discriminate ingestion of nonfood substances), al.
though still an important risk factor,* need not/be
present.
Inhalation is the second major route of lead ab.
. sorption for children. Lead absorbed by way of the
lungs contributes in additive fashion to the total
body lead burden. The efficiency of respiratory
absorption depends on the diameter of airborne
lead particles, For most common lead aerosols of
mixed particle size, it has been estimated thet be. -
tween 30% and 50% of total inhaled lead is con-
tained in particles of sufficiently small diameter
02400757824
(lesz than 6 um) to be retained in the lungs and
absorbed. Larger particles deposit in the nose,
throat, and upper airways where they are cleated
by ciliary action and then are either expectorated
or swallowed.
PREDISPOSING FACTORS
Factors known to increase susceptibility to lead
toxicity include nutritional deficiencies and age-
related oral behavior (with or without pica) (Table
3).
Animas] and humen studies” have shown that
deficiencies of iron, calcium, and zinc all resultiin 3
increased gastrointestinal absorption of lead. of fo og
particular concern is the effect of lack of iron,” ;
because the prevalence of iron deficiency in infancy .
is at least 156% and may be higher. % Iron deficiency, }
even in the absence of anemia, appears to be the’
single most important predisposing factor for in-
creased absorption of lead, Conspicuous examples :
of nutritional iron deficiency include-breest<fed in-:
fants and “milk babies” who may receive little food ;
TABLE 3. Predisposing Factors for Lead Poisoning |
Nutritional deficiency of iron, calcium, TINE |
Sickle cell digease
Young age
Hand-to-mouth activity, including pica hy :
Metabolic disease \ a
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level, erythrocyte protoporphyrin level, or both.
woh .
E other than milk until 12 to 18 months of age. In
k the presence of iron deficiency insufficient to pro-
duce anemisa, gastrointestinal absorption of lead is
increased severalfold.
SCREENING
Screening for lead poisoning is sporadic. Methods
used have included determination of blood lead
8 cell for
Hs in high-
0 guide the interpretation of screening re-
«sults, the CDC has developed a series of guidelines
(Tables 4 and 5).
The erythrocyte protoporphyrin determination
provides a sensitive and inexpensive screen for both
increased lead absorption and iron deficiency, two
of the most common preventable health problems
in childhood; elevation in the erythrocyte proto-
porphyrin level can reflect iron deficiency before
anemia becomes clinically evident. There is increas-
ing interest, therefore, in adopting the erythrocyte
protoporphyrin determination as a screening tool
for both problems, particularly because it is more
sensitive to iron deficiency than the hematocrit.™
Both capillary tubes and filter paper have been
"used for obtaining screening samples. Capillary
tubes are cumbersome but have the advantage of
providing sufficient blood for concomitant lead de-
TABLE 4. Zinc Protoporphytin by Hematofluorometer:
Risk Classification of Asymptomatic Children for Prior-
ity Medical Evaluation®
Blood Lead E
{ug/dL) Protoporphyrin
(ug/dL)
35 36-74 75-174 >176
Not done 1 t + t
<24 I Ia Ia t
25-48 Ib II III ITI
50-69 § III II Iv
=70 § 5 IV IV
* Diagnostic evaluation is more urgent than the classifi-
cation indicates for (1) children with any symptoms
compatible with lead toxicity, (2) children younger than
+ disposition reshona more complete medical and labora-
"86 months of age, (3) children whose blobd lead and
ervthrocyteprotoporphyrin levels place them in the upper
part of a particular-class, (4) children whose siblings are
in a higher class. These guidelines refer to the interpre-
tation of screening results, but the final] diagnosis and
tory ¢ ofthe child,
t Blood leadtest-needed to estimate risk. i
+ Ervthropoietic. protoporphyria. Iron deficiency may
cause elevated erythrocyte protoporphyrifidevels up to
300 ug/dL, but this is rare. a
§ In practicgzthis:;combination of results is not generally
observed: if3¥- is observed, immediately retest with whole
blood.
® F32+12 Th Ll
TABLE 6. Erythrocyte Protoporphyrin (EP) by Extrac-
tion: Risk Classification of Asymptomatic Children for -
Priority Medical Evaluation®
Blood Lead EP (ug/dL)
(ug/dL) <B% 35-109 110-248 >250
Not done 1 t t +
<24 1 Ia Ia 1
25-48 Ih II II III
50-69 § 111 I IV
=70 § 4 IV IV
* Diagnostic evaluation is more urgent than the classifi-
cation indicates for (1) children with any symptoms
compatible with lead toxicity, (2) children younger than
86 months of age, (8) children whoae blood lead and EP
lavels place them in the upper part of & particular class,
(4) children whose siblings are in a higher class, These
guidelines refer to the interpretation of screening results,
but the final disgnosis and disposition rest on a more
complete medical and laboratory examination of the
child. Screening tests are not diagnostic. Therefore, every
child with a positive screening test result should be
referred to a physician for evaluation, with the degree of
urgency indicated by the risk classification. At the first
diagnostic evaluation, if the screening test was done on
capillary blood, & venous blood léad level should be de-
tarmined in a laboratory that participates in the Centers
for Disease Control's blood lead proficiency-tasting pro-
gram. Even when tests are done by experienced person-
nel, blood lsad levels may vary 10% to 15%, depending
on the level being testad. Tests for the same child may
vary a8 much 8s £5 ug/dL in a 24-hour period. Thus,
direction should not necessarily be Interpreted as indie-
ative of actual changss in the child's lead absorption or
excretion.
t Blood lead test needed to estimate risk.
1 Erythropoistic protoporphyria. Iron deficiency may
cause elevated EP levels up to 300 pg/dL, but thie i rare,
§ In practice, this combination of results is not generally
shaeed; if it is observed, immediately retest with whole
blo
termination if the erythrocyte protoporphyrin level
is elevated. Filter paper sampling provides ease of
collection and transport, but the accuracy of anal
yaes based on filter paper samples is not yet estab-
lished. Determination of the blood lead level by
fingerstick sampling is subject to contamination by
lead on the skin, whether collection is by capillary
tube or filter paper. Such contemination does not
affect the determination of the erythrocyte proto-
porphyrin level, 5 :
Two analytical techniques are available for de-
termination of erythrocyte protoporphyrin: (1) ex-
traction of protoporphyrin from erythrocytes and
subsequent measurement in a fluorimeter and (2)
direct fluorimetry of a thin layer of RBCs (heme-
tofluorometer). Because values derived from these
two methods may differ (Tables 4 and §), a pedia-
trician should be aware of which is in use. When in
doubt, the extraction method is preferred, because:
of its greater reprodudibility, particularly at lower
concentrations of erythrocyte protoporphyrin.
5
SENT BY:NHeLP
PA 5-10-91 5 12:13
It is most important to note that screening tests
are not diagnostic. Every child with a positive
screening test result should be referred to & pedia-
trician for further evaluation, with the urgency of
referral indicated by the risk classification (Tables
4 and b). At the first diagnostic evaluation, if the
seresxing 18st. was performed on capillary blood, &
venous blood lead level should be determined in 8
~lahgratory that participates in an eceredited blood
lead proficiency-testing program. To reduce the
likelihood of false-positive results, lead-free sy-
ringes, needles, and tubes must be used in obtaining
venous blood samples for lead analysis,
The developmentally disabled who reside in
“halfway houses” or community residences or who
attend school in older buildings deserve special
attention in lead-screening programs. Because this
population may be older than preschool age, pro-
tective statutes may not recognize their high-risk
status, particularly with respect to pica behaviors.
Physicians caring for developmentally disabled pa-
tients should be aware that their risk of lead inges-
tion may continue long beyond the age of 6 years.
INTERVENTION
Once a diagnosis of increased lead absorption has
been confirmed by venous blood lead determina-
tion, the sine qua non of intervention is the prompt
and complete termination of any further exposure
to lead.*® This intervention requires accurate iden-
tification of the source of lead and either its removal
or removal of the child from the unsafe environ-
ment, Some states (eg, Massachusetts) have passed
stringent legislation requiring prompt removal of
lead hazards in cases of lead poisoning, and there
are strong penalties for failure to comply. At all
costs, a child should not be permitted to enter or to
be present in o leaded environment during deleading
until the deleading, subsequent cleanup, and rein.
spection have been satisfactorily completed, Al-
though some regulations call only for removal of
leaded paint from “chewable” surfaces (eg, window
sills and door frames) or up to & height of 1.2 m (4
ft), all chipping and peeling paint should be re-
moved from all surfaces, particularly from ceilings.
After deleading, the house must be thoroughly
cleaned and reinspected to assure compliance with
safety regulations. Indeed, repeated thorough clean- __1s unproven: but, in children who have blood lead
ing 1s advisable, especially in the case of deterio-
rated or dilapidated housing, High-phosphate de-
tergents are particularly useful in removing lead
dust. Children should not return home until ¢lean-
ing is completed.
Medical intervention should begin with thro-
rough clinicel evaluation in®4ding diagnostic stud-
ies of lead toxicity and, when indicated, & lead
mobilization test.*® Diagnostic studies should in-
-482 LEAD POUSARNING
ol ak
clude a blood cell count with RBC indices, a retic-
uloeyte count, and, if indicated and available, tests
of serum iron and iron-binding capacity, and a
serum ferritin assay. Routine urinalysis might be
considered. Because chelating agents are poten-
tially nephrotoxic, BUN and/or serum creatinine
velues should be determined before chelation to
rule out occult renal disease either secondary to
plumbism or preexisting.“ Roentgenographic stud-
ies to be considered include a film of the abdomen
to detect radiopaque paint chips or other leaded
materials in the gastrointestinal tract and s film of
the metaphyseal plate of a growing “long” bone,
usually the proximal fibula, to detect interference
with calcium deposition, the so-called “Jead line.”
Because this phenomenon is usually seen only after
several weeks of increased lead absorption in chil-
dren whose blood lead levels may exceed 50 ug/dL,
its presence or absence may help to determine the
duration of increased lead exposure.
Once a diagnosis of plumbism has been made, a
child's condition and the effect of intervention
should be monitored by serial venous determina-
tions of the blood lead and, if available, erythrocyte
protoporphyrin levels. If iron deficiency is present,
iron studies should also be repeated periodically to
monitor compliance with iron replacernent therapy.
The lead mobilization test may be used to assess
the “mobilizable” pool of lead in a child for whom
chelation therapy is contemplated. Lead mobiliza-
tion is determined by measuring lead diuresis in =
timed urine collection following a single dose of
chelating agent.®# This test is most helpful in
determining which children with blood lead concen-
trations in the range of 25 to 55 ug/dL will require
a full course of chelation therapy and also in deter-
mining the advisability of further chelation in a
child already receiving therapy. It should be noted
that the erythrocyte protoporphyrin level is not a
useful predictor of the amount of chelatable lead
and may, in fact, be misleading in this regard.
Therapeutic modalities include removing the -..
child from lead exposure, improving nutrition,
administration of iron supplements, and chelation
therapy. *#~4" In children with mild increased lead
gbsorption, the efficacy of chelation therapy to _ :
modify neurobehayioral outcomes of-lead. toxicity
levels between 25 and 65 pg/dL and & positive lead
mobilization test, it is highly desirable to rapidly
decrease the readily mobile, potentially most toxic
fraction of body lead stores by three to five days of =
CaNas-ethylenediaminetetraacetic acid (calcium
disodium EDTA) therapy.
Long-term follow-up is indicated in all cases of .
lead exposure. Children near or at school age who
have a history of plumbism should have a neuro. ¥
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ing handicaps, and school authorities should be
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x. RECOMMENDATIONS
Qur recommendations rest on three premises: (1)
that exposure to lead is widespread; (2) that lead
causes neuropsychologic and other serious impair-
ments in children at relatively low levels of expo-
(3) that the neuropsychologic effects of
Pediatricians must play a central role in this
prevention. Although our recommendations are di-
vided into two categories—those directed princi-
pally to practitioners and those directed to govern-
ment agencies—the distinction is somewhat artifi-
cial. Throughout the past five decades, pediatri-
cians, acting individually, as well as collectively
through the Academy, have been prime movers in
stimulating the agencies of government to protect
the children of the United States against exposure
to lead. It is important that this tradition of public
involvement continue and that pediatricians con-
tinue to act publicly as advocates for the health of
children.
Recommendations for Practitioners
1. The Academy recommends that the erythro-
cyte protoporphyrin test be used for screening chil-
dren for lead toxicity, when that test is available.
Additionally, the erythrocyte protoporphyrin test
is a sensitive indicator of subclinical iron deficiency
and may add complementary information to the
determination of hematocrit values. It will not,
however, identify children with anemia due to acute
blood loss or hemoglobin C, 88, 8C, or E disease,
The Academy encourages clinical and hospital lab-
oratories to make the erythrocyte protoporphyrin
test widely and economically available,
_2. Upon consideration of recent CDC recommen-
dations, the Academy recommends that, iaeally, all
preschool children should be screened for ead ab-
80 sarption. by. mean. of the srvihroeyta profeodt
er. it is. recognized that the in-
cidence of oh exposure may be so low ip certain
areas that pediatricians may prudently consider
their patients. to. be at little risk of TJead “toxicity;
therefore, the, following priority y guidelines I ranked
from highest to lowest are offered to assist t pedia-
tricians in 1 deciding which children _ to. ‘screen. (a)
children, 19 121 to, 38 ‘months of age, who | live ir in or are
phy Te
(highest); (b)_children,.8 8 “months to 6 years c of “age,
and play- who are ‘siblings, housemates, . visitors,
d toxicity; (c)
der housing where
i der, dilapidate 9
he rah sana be me]
lead smelters and processin & par-
«ents or.other honseho isle ey ate in &
lead-related occupation or hobby. Frequency of
screening should be flexible but should be guided
by consideration of a child's age, nutrition and iron
status, and housing age, housing condition, and
population density. The first erythrocyte protopor-
phyrin test should generally occur at the same time
as the determination of the hematocrit, which typ-
ically is performed between 9 and 15 months of age.
Because the prevalence of lead poisoning increases
sharply at 18 to 24 months of age, any child judged
to be at elevated risk of plumbism should have a
second erythrocyte protoporphyrin test performed
at or about 18 months of age and at frequent
intervals (3 to 6 months) thereafter appropriate to
the degree of risk. Surveillance should continue
routinely up to age 6 years and, if appropriate,
longer.
3. The Academy sitommends that any child, in
whom increased lead absorption or lead poisoning
has been confirmed by venous blood lead determi.
nation, be followed closely by means of repeat ve-
nous tests. For such children, ‘abatement of envi-
ronmental sources of lead is essential.
4. The Academy notes that some predisposing
factors for lead poisoning, iron deficiency in partic-
ular, are preventable. Pediatricians should make
vigorous efforts to identify and correct iron defi.
ciency, calcium deficiency, and other nutritional
deficiencies, particularly in children from areas of
high lead exposure.
5. The Academy recommends that pediatricians
attempt vigorously to educate parents, particularly
parents of children in high-risk populations, about
the hazards of lead, its sources and routes of ab-
sorption, and safe approaches to the prevention of
exposure.
Recommendations for Public Agencles
1. The Academy recommends that reporting of
cases of lead poisoning to state health departments
be mandatory in all states.
2. The Academy notes that, in the present ap-
proach to screening for lead, inspection of a child's
environment is generally undertaken only when an
elevated blood lead level is found. In effect, children
are used as biologic monitors for environmental
lead. The Academy recommends that this sequence
be reversed. A national program for systematic
screening of lead hazards in housing is overdue.
The enormity of the task favors a stepwise ap-
{
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SENT BY: NHeLP
proach, Suggested approaches might include:
screening of oldest housing, followed by newer
housing; screening of housing in inner cities, then
in less densely populated areas; and targeted
screening of housing with small children.
8. The Academy supports the prompt, vigorous,
and safe abatement of all environmental lead haz-
ards. The US Department of Housing and Urban
Development, state health departments, and local
health departments should require that all hazard.
ous lead-based paint (exterior and interior) be re-
moved from all housing. Development of methods
of abatement, which are safer and more effective
than those currently in use (torches, heat guns, and
sanders) must be given high priority to prevent the
further endangering of lead-poisoning victims. The
US Environmental Protection Agency is urged to
persist in its laudable plan to promptly and finally
remove all lead from gasoline.
4. The Academy urges the US Congress and the
US Department of Health and Human Services to
become fully cognizant of the high prevalence of
childhood lead poisoning in the United States, its
irreversible consequences, and its great human and
fiscal costs. Restoration of funding is urgently
needed for screening, hazard identification, and
hazard abatement.
5. The Academy recommends that state health
departments and Academy chapters exert their
maximum influence to assure that state licensing
agencies permit laboratories to perforz blood lead
and erythrocyte protoporphyrin tests only if those
laboratories consistently meet criteria for accuracy
and repeatability as determined by their perform-
ance in interlaboratory proficiency-testing pro-
grams.
SUMMARY
Patterns of childhood lead poisoning have
changed substantially in the United States. The
mean blood lead level has declined, and acute in-
toxication with encephalopathy has become uncom-
mon. Nonetheless, between 1976 and 1880, 780,000
children, 1 to 6 years of age, had blood lead concen-
trations of 30 ug/L or above. These levels of ab-
sorption, previously thought to be safe, are now
known to cause loss of neurologic and intellectual
function, even in asymptomatic children. Because
this loss is largely irreversible and cannot fully be
restored by medical treatment, pediatricians’ ef-
forts must be directed toward prevention. Preven-
tion js achieved by reducing children’s exposure to
lead and by early detection of increased absorption,
Childhoa# lead poisoning is now defined by the
Academy as a whole blood lead concentration of 25
£g/L or more, together with an erythrocyte proto-
484 1 FAD DAIQARIIR IS
porphyrin level of 85 ug/dL or above. This defini-
tion does not require the presence of symptoms. Jt
is identical with the new definition of the US Public
Health Service. Lead poisoning in children previ-
ously was defined by a blood lead concentration of ©
30 pg/dL with an erythrocyte protoporphyrin level
of 50 ug/dL.
To prevent lead exposure in children, the Acad.
emy urges public agencies to develop safe and effec-
tive methods for the removal and proper disposal
of all lead-based paint from public and private
housing, Also, the Academy urges the rapid and
complete removal of all lead from gasoline.
To achieve early detection of lead poisoning, the
Academy ends hildren in the
United States at risk of exposure to lead be screened
for ead abaotpiion at approximately 12 months of
ry dl
age by means of the erythroc nn
uh when that test is available, Furthermore, the
Academy recommends follow-up erythrocyte pro-
toporphyrin testing of children judged to be at high
risk of lead absorption. Repor+ing of lead poisoning
should be mandatory in all states,
- ACKNOWLEDGMENT
We are grateful for the assistance of J, Julian Chisolm,
Jr, MD, Jane L. Lin-Fu, MD, Vernon Houk, MD, John ib
Stevenson, MD, and John F. Rosen, MD.
COMMITTEE ON ENVIRONMENTAL
HAZARDS, 1984-1986
Philip J. Landrigan, MD, Chairman
John H. DiLiberti, MD
Stephen H. Gehlbach, MD
John W. Graef, MD
James W. Hanson, MD
Richard J, Jackson, MD
Gerald Nathenson, MD
Liaison Representatives
Henry Falk, MD
Robert W, Miller, MD
Walter Rogan, MD
Diane Rowley, MD
COMMITTEE ON ACCIDENT AND POISON i
PREVENTION, 1984-1988
Joseph Greensher, MD, Chairman
Regine Aronow, MD
Joel L., Bass, MD
William E. Boyle, Jr, MD
Leonard Krassner, MD
Ronald B, Mack, MD
Sylvia Mieik, MD
Mark David Widome, MD
Liaison Representatives
Andre I'Archeveque, MD
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Gerald M. Breitzer, DO
Chuck Williams, MD
AAP Section Liaison
Jerry Foster, MD
Joyce A. Schild, MD
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1. Centers for Disease Control: Surveillance of childhood lead
poisoning— United States, MMWR 1882;31:132-134
E _ 2. Mahaffey KR, Annest JL, Roberta J, et al: National esti.
mates of blood lead levels: United States 1978-1980: Asso-
ciated with selectsd demographic and socioeconomic factors.
N Engl J Med 1082;807:673-678
8 Klein R: Lead poisoning, Adv Pediatr 1877;24:108-132
® 4. Annest JL, Pitkle JL, Makue D, et al Chronological trend
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5. Plomelli 8, Corash L, Corash MB, et zl: Blood jead concen-
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8. Grandjean P, Fjerdingetad E, Nielsen OV: Lead concentra-
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7. Hernbarg 8: Biochemical and clinieal effects and TESpOnEES
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8. Berlin A, Schaller KH, Grimes H, ot al: Environmental
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EO 10. Mahaffey XR, Rosen JF, Chesney RW, at al: Association
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11, Ross JF, Chesney RW, Hamstru A, et al; Reduction in
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12. Needleman H, Gunnoe C, Leviton A, st al: Deficits in
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18. Winneke G, Kramer G, Brockhaus A, et al: Neuropsycho-
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15, Rutter M: Low levsl lead exposure: Sources, effects, and
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12._Centers for Nissese Control: Preventing lead poisoning in
_young children. MMWR 1885,84:67-68
18. Landrigan PJ, Gehlbach SI Resmi BF, et al: Epidemic
lead absorption near an ore smelter: The role of particulata
lead N Engl J Med 1875; 1282:128-123
18. Assessment of the Safety of Lead and Lead Salts in Food: A
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Es #29
) ee HY ay it
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Department of Commerce, 1979
22. Fischbein A, Anderson KE, Sassa 8, et al: Lead poisoning
from “do-it-yourself” heat guns for removing lead.based
paint: Report of two cases, Environ Res 1981;24:425431
23. Landrigan PJ, Baker EL, Himmelstein JS, ot al: Exposure
to lsad from the Mystic Hver bridge: The dilemma of de-
leading, N Engl J Med 1882;306:873.876
24. Bose A, Vashistha K, O'Loughlin BJ: Azareén por Evie.
cho—Another cause of lead toxicity, Pediatrics 1883,72:106~
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25. Centers for Disease Control: Folk ramedy-aasociated dad
poisoning in Hmong ¢hildren—Minnesota. MMWR 1088;
32:656-666
26. Ali AR, Smalls ORC, Aslam M: Surma and lead poisoning,
Br Med J 1978;3:815-816
27. Shaltout A, Yaish 8A, Fernando N: Lead encephalopathy in
infants in Kuwait. Ann Trop Poediatr 1981:1:208-215
28. Miller C: The pottery and plumbiam puzzle, Med J Austr
1682:30:442-443
28, Ostarud HT, Tufts E, Holmes M8: Plumbism at the Green
Parrot goat farm. Clin Toxicol 1978:6:1-7
30, Baker EL Jr, Folland DE, Taylor TA, et al: Lead poisoning
in lead workers and their children: Home contamination
with industrial dust. N Engl J Med 1877:296:260-261
81. Chisolm JJ Jr: Fouling one's own nest. Pediatrics
1878;62:614-617
32. Ziegler EE, Edwards BB, Jansen RL, ot al: Absorption and
retention of lead by infants. Pediatr Res 1878;12:26-34
33. Roels HA, Buchet JP, Lauwerys RR, ot al: Exposure to lead
+ by the oral and the pulmonary routes of children living in
the vicinity of a primary lead amelter. Environ Res
1980;22:81-94
8. Rayre JW, Charney E, Vostal J, ot al: House and hand dust
as a potential source of childhood lead exposure. Am J Dis
Child 1974;127:1687-171
35. Charney E, Kessler B, Farfel M, ot al: Childhood I "i
poisoning: A controlied trial of the effect of dust-con
atau on blood lead levels, N Engl J Med 1883;308: J085-
109
36. Baritrop D: The prevalence of pica. Am J Dis Chiid
1966;112:116-123
37. Mahaffey KR: Nutritional factors in lead poisoning. Nutr
Rev 1981:39:353-362
38. Nathen D, Oski F: Hematology of Infancy and Childhood, ed
2. Philadelphia, WE Saundars Co, 1881
38. Yip R, Schwartz §, Deinard AS: Screening for iron defl-
clency with the erythrocyte protoporphyrin test. Pediatrics
1983;72:214-219
40. Piomelli 8, Rosen JF, Chisolm JJ Jr, et al: Management of
childhood lead poisoning. J Padiatr 1884;108:525-582
41. Preventing Lead Poisoning in Young Children, publication
No. 00-2629. Atlante, Centers for Disease Control, April
1678
42. Blickman JH, Wilinson R, Graef J: The lead line revisited
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43. Markowitz ME, Rosen JF; Assessment of lead sons; in
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J Pediatr 1984;104:337-341
44. Teisinger J, 8rbova J: The value of mobilization of lead by
calcium sthylene diaminetetrancetate in the diagnosis of
lead poisoning. Br J Ind Med 1858;16:148-153
45. Chisolm JJ Jz, Barltrop D: Recognition and management of
childesn with increased lead absorption. Arch Dis Child
1879:54:249-262
46. Graef JW: Clinical outpetiont management of childhood
lead poisoning, in Chisolm JJ Jr, O'Hara D (eds): Lead
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1882, pp 153-164
47. Chisolm JJ Jr: Management of increased lead absorphiod®
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SENT BY :NHeLP ® y 12217 2 a 6240075,830
aliN-PG—-'91 THU 11:4F TTORNEY BEN: WHF ICE EL NUL? Va els roe ———
DANIEL E. LUNGREN, Attorney General
of the State of California
CHARLTON G. HOLLAND, II
Assistant BEL et General
Ee Depry Attorney Cored
Deputy A General
2101 Webster Street, 12th Floor
Oakland, California 94612-3049
Telephone: (415) 464-1173
Attorneys for Defendant
UNITED STATES DISTRICT COURT
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DECLARATION OF RUTH 8S. 12 | Matthews, and PROPLE UNITED FOR A
RANGE, MPH. PHN, BETTER OAKLAND, On Behalf of
13 || Themselves and All Others Similarly Stinated,
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16 | MOLLY Cav pe w Director, California
Department of Ith Services,
Defendant.
5
20 § I, RUTH S. RANGE, declare:
21 I hold an M.S. degree in Nursing. I have spent my endre professionai
23 | carcer since 1958 in the area of public health, I have been employed by the Stato
23 | Department of Health Services since 1977 as Chief of the Regional Operations Section
24 | of the Child Health and Disability Prevention Branch of the Departinent. As such I
25 { have been significantly involved in lead screening and testing matters within the last
26 | decade.
27 5 The matters stated below are personally known to me and if called as a
L DECLARATION OF AUTH 8. RANGE, M.S. PHN
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witness 1 could and would testify competently concerning the sare.
3. The Department of Health Services does not dispute the seriousness of
the problem of lead poisoning in children. In fact, as recently as March 12, 199], the
Department's former Director, Dr, Kenneth Kizer stated that: "Lead poisoning is the
most significant environmental health problem facing California children today, and
insufficient consideration is being given to this potential problem during routine child
health evaluations." What the Department docs dispute is whether either the law or
good medical practice requires the actual testing of children’s blood far the presence of
lead in all cases, and particularly very young children in the Early and Periodic
Screening, Diagnostic and Treatment ("EPSDT") Program of the Federal Medicaid
Program (known as the Medi-Cal program in California, and administered by the
Department of Health Services).
4, The Department belicves that neither applicable laws nor good medical
practice requires that all EPSDT children receive biood lead tests as a part of the
mandatory screening process. Rather, it is the Department's position that young (ic.
vnder 6 years old) EPSDT children should first be screensd by their treating physicians
for bath the presence of objective medical indications and/or environmental factors
which might indicate the possibility of lead toxicity. If cither or both are present then
it a blood test would be indicated. While the State Medicaid Manual (Plaintiffs' Exhibit
N) recommends the erythrocyte protoparphyrin ("EP") test as the "primary screening
test” (Ex. N, at p. 5-15), this test is falling into disfevar due to its relative wreliability
vis-a-vis a blood lead test. (The former is a "pinprick” test while the latter draws a
sample of venous blood.)
5. A blood test is an intrusive procedure which causes some degree of
discomfort, and in the vast majority of cases is simply unnecessary to determine
1. CDHP Provider Informadon Notice #91.6, inchudad as Exhibit C in the
Exhibits In Support Of Plaintiffs’ Motion For Partial Summary Judgment,
2.
DECLARATION OF RUTH 8 RANGE, M8, F.H.N.
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whether a child is at risk of lead poisoning, Further, there is a significant cost factor
invalved in completing a blood test which must be considered In an age Of lunited
resources. In Fiscal Year 1989-90 Department records indicate that therc were 539,576
children under the age of six in the Medi-Cal program. The cost of an EP test is
$7.50, so the total cost of providing each of these children with such & test would be
$4,046,820. The cost of the more reliable blood lead test is $22.50, so the total cost of
providing each of these children with such a test would be $12,140,460,
6. It ig the present belief of the Department that univarsal blood lead
testing of young EPSDT children is not medically indicated, legally required nor fiscally
prudent,
I declare under penalty of perjury that the foregoing is true and correct.
Executed at Sacramento, Cabiformda this 7th day of June, 1991
DECLARATION CF AUTH 9. RANGE, M.A, PHN,