Printer Friendly

Fatal pediatric poisoning from leaded paint - Wisconsin, 1990.

Although fatal lead poisoning among children occurs rarely in the United States, it represents a medical and public health emergency. This report summarizes the investigation of a child who died from poisoning associated with ingestion of lead-based paint.

On September 12, 1990, a 28-month-old Wisconsin boy was admitted to a hospital with a 4-day history of lethargy and reduced appetite. Although the child had no known past medical problems, his parents reported that he had eaten flaking paint. On initial neurologic examination, the child had extreme lethargy with facial palsy and gasping respirations, consistent with lead encephalopathy; laboratory results revealed severe lead toxicity and hematologic abnormalities blood lead level [BLL] 144 [micro]g/dL; erythrocyte protoporphyrin level 593 [micro]g/dL; hemoglobin 8.1; and basophilic stippling). Despite chelation therapy with British antilewisite and calcium disodium edetate (CaNa[sub.2]-EDTA), the child developed seizures, became comatose, and died 26 hours after admission. An autopsy showed massive cerebral edema with uncal herniation. The intestines contained multiple roundworms (Ascaris lumbricoides) and flake-like material consistent with paint chips. Radiographs revealed prominent epiphyseal lines in the lower extremities, consistent with chronic lead exposure.

On September 20, staff from the Wisconsin Division of Health and the Waukesha County Health Department inspected the child's residence. The child and his parents had lived for at least 4 months on the second floor of a two-story, nonresidential structure built in 1923. The interior paint was badly deteriorated with paint chips visibly flaking from the walls and accumulating on floors, windowsills, and stairs. Eleven paint chip samples from the apartment ranged from 0.2% to 33.1% lead by weight (average: 9.1%); the U.S. Consumer Product Safety Commission (CPSC) permits a maximum of 0.06% lead in new residential paint.(*) House dust from the child's bedroom floor contained 3900 [micro]g lead/ft[sup. 2], and dust from a windowsill above the child's bed contained 31,128 Kg lead/ft[sup. 2] . These levels are more than 10 times (*)16 Code of Federal Regulations, part 1303. Ban of lead-containing paint and certain consumer products bearing lead-containing paint. higher than those proposed in recent guidelines issued by the U.S. Department of Housing and Urban Development (1 ), which recommend the maximum dust lead levels permissible before reoccupancy of a unit following lead paint abatement. After the child's death, the parents moved and were unavailable for follow-up. The landlord has blocked access to the second floor and plans to eliminate the lead paint hazards in the building. Reported by: J Schirmer, MS, HA Anderson, MD, State Environmental Epidemiologist, Div of Health, Wisconsin Dept of Health and Social Svcs; LA Saryan, PhD, Industrial Toxicology Laboratory, West Allis Memorial Hospital, West Allis, Wisconsin. Lead Poisoning Prevention Br, Center for Environmental Health and injury Control, CDC. Editorial Note: Lead encephalopathy usually is associated with a BLL [is greater than]100 [micro]g/dL, although it has been reported at BLLs as low as 70 [micro]g/dL (2). As in this report, children with acute lead encephalopathy often have a recent history of prodromal symptoms, including anorexia, apathy, decreased play activity, hyperirritability, aggressiveness, poor coordination, and sporadic vomiting. Because lead encephalopathy in a child can rapidly progress to death, either a BLL [equal to or greater than]70 [micro]g/dL in a child or the onset of encephalopathy constitutes an acute medical emergency.

At least four factors may account for the dramatic decline in the incidence of acute lead encephalopathy and childhood deaths from lead poisoning since the 1960s (3), including 1) increased screening of children at risk, 2) recognition of toxicity before the onset of life-threatening symptoms, 3) improvements in the treatment for lead poisoning, and 4) reduction of lead exposure from certain environmental sources. Although childhood deaths from poisoning associated with exposure to lead-based paint are now rare in the United States (4 ) (the most recently reported lead-based paint-associated death occurred in the mid-1970s [5]), subclinical toxicity is a widespread and persistent public health problem (6). BLLs as low as 10 [micro]g/dL, once considered safe, are now known to adversely affect cognitive development and behavior in children (7), with potentially long-term sequelae (8). In 1984, an estimated 3-4 million U.S. children had BLLs [equal to or greater than]15 [micro]g/dL (6).

The primary source of high-dose lead exposure among children in U.S. urban areas is lead-based paint (6). Although CPSC banned lead-based paint for residential use in 1978, an estimated 12 million children [is not greater than]7 years of age reside in homes containing previously applied lead-based paint (6). Interior paints used before 1940 contained as much as 50% lead (9). Although children can ingest lead directly by eating paint chips, ingestion of lead-contaminated house dust and soil during normal mouthing and exploratory behaviors contributes substantially to elevating BLLs (10). The child reported in Wisconsin appeared to have been ingesting paint chips and was exposed to highly contaminated house dust.

All cases of lead poisoning are preventable. A national health objective for the year 2000 is to reduce the prevalence of children aged 6 months through 5 years with BLLs [is greater than]15 [micro]g/dL to less than 500,000 and the prevalence of those with BLLs [is greater than]25 [micro]g/dL to zero (11 ). Recently, several federal agencies responsible for housing, health, and the environment have focused attention on this problem and have set goals to abate lead-based paint in privately owned housing (12), reduce the number of children with elevated BLLs (13), and promote national efforts to eliminate childhood lead poisoning (14). References 1. Office of Public and indian Housing. Lead-based paint: interim guidelines for hazard

identification and abatement in public and Indian housing. Washington, DC: US Department

of Housing and Urban Development, Office of Public and indian Housing, 1990. 2. Piomelli S, Rosen JF, Chisolm JJ, Graef JW. Management of childhood lead poisoning.

J Pediatr 1984;105:523-32. 3. Lin-Fu JS. The evolution of childhood lead poisoning as a public health problem. In:

Chisolm JJ, O'Hara DM, eds. Lead absorption in children: management, clinical and environmental

aspects. Baltimore: Urban and Schwarzenberg, Inc, 1982:1-10. 4. NCHS. Vital statistics mortality data, multiple cause-of-death detail [machine-readable

public-use data tape]. Hyattsville, Maryland: US Department of Health and Human Services,

Public Health Service, CDC, 1970-1987. 5. Klein R. Lead poisoning. in: Barness LA, ed. Advances in pediatrics. Vol 24. Chicago: Year

Book Medical Publishers, 1977:103-32. 6. Agency for Toxic Substances and Disease Registry. The nature and extent of lead poisoning

in children in the United States: a report to Congress. Atlanta: US Department of Health and

Human Services, Agency for Toxic Substances and Disease Registry, 1988. 7. Mushak P, Davis JM, Crocetti AF, Grant LD. Prenatal and postnatal effects of low-level lead

exposure: integrated summary of a report to the US Congress on childhood lead poisoning.

Environ Res 1989;50:11-36. 8. Needleman HL, Schell A, Bellinger D, Leviton A, Allred EN. The long-term effects of exposure

to low doses of lead in childhood, an 11 -year follow-up report. N Engl J Med 1990;322:83-8. 9. National Academy of Sciences. Report of the Ad Hoc Committee to Evaluate the Hazard of

Lead in Paint. Washington, DC: US Consumer Product Safety Commission, 1973:3. 10. Charney E, Sayre J, Coulter M. increased lead absorption in inner city children: where does

the lead come from. Pediatrics 1980;65:226-31. 11. Public Health Service. Healthy people 2000: national health promotion and disease prevention

objectives. Washington, DC: US Department of Health and Human Services, Public

Health Service, 1990; DHHS publication no. (PHS)90-50212. 12. Office of Policy Development and Research. Comprehensive and workable plan for the

abatement of lead-based paint in privately owned housing: a report to Congress. Washington,

DC: US Department of Housing and Urban Development, Office of Policy Development

and Research, 1990. 13. Environmental Protection Agency. Strategy for reducing lead exposures. Washington, DC:

US Environmental Protection Agency, 1991. 14. CDC. Strategic plan for the elimination of childhood lead poisoning. Atlanta: US Department

of Health and Human Services, Public Health Service, 1991.
COPYRIGHT 1991 U.S. Government Printing Office
No portion of this article can be reproduced without the express written permission from the copyright holder.
Copyright 1991 Gale, Cengage Learning. All rights reserved.

Article Details
Printer friendly Cite/link Email Feedback
Publication:Morbidity and Mortality Weekly Report
Date:Mar 29, 1991
Words:1353
Previous Article:Infant mortality among racial/ethnic minority groups, 1983-1984.
Next Article:Characteristics of, and HIV infection among, women served by publicly funded HIV counseling and testing services - United States, 1989-1990.
Topics:

Terms of use | Privacy policy | Copyright © 2018 Farlex, Inc. | Feedback | For webmasters