Children's environmental health. Lessons from the past and prospects for the future.

Environmental pediatrics is an area of pediatric medicine that has come a long way in the past 50 years. It has risen to importance in parallel with two developments: (1) the conquest in the industrialized nations of the major infectious diseases and their replacement by chronic conditions, such as asthma, cancer, developmental disabilities, and birth defects as the primary causes of illness and death in children and (2) the growing recognition that chemicals in the environment are responsible, at least in part, for these changes in patterns of disease. The challenge now to environmental pediatrics is to better understand the impact of chemical substances on the patterns of health and disease in children and to design evidence-based approaches to the treatment and prevention of childhood disease of environmental origin.

Pesticides and inner-city children: exposures, risks, and prevention.

Six million children live in poverty in America's inner cities. These children are at high risk of exposure to pesticides that are used extensively in urban schools, homes, and day-care centers for control of roaches, rats, and other vermin. The organophosphate insecticide chlorpyrifos and certain pyrethroids are the registered pesticides most heavily applied in cities. Illegal street pesticides are also in use, including tres pasitos (a carbamate), tiza china, and methyl parathion. In New York State in 1997, the heaviest use of pesticides in all counties statewide was in the urban boroughs of Manhattan and Brooklyn. Children are highly vulnerable to pesticides. Because of their play close to the ground, their hand-to-mouth behavior, and their unique dietary patterns, children absorb more pesticides from their environment than adults. The long persistence of semivolatile pesticides such as chlorpyrifos on rugs, furniture, stuffed toys, and other absorbent surfaces within closed apartments further enhances urban children's exposures. Compounding these risks of heavy exposures are children's decreased ability to detoxify and excrete pesticides and the rapid growth, development, and differentiation of their vital organ systems. These developmental immaturities create early windows of great vulnerability. Recent experimental data suggest, for example, that chlorpyrifos may be a developmental neurotoxicant and that exposure in utero may cause biochemical and functional aberrations in fetal neurons as well as deficits in the number of neurons. Certain pyrethroids exert hormonal activity that may alter early neurologic and reproductive development. Assays currently used for assessment of the toxicity of pesticides are insensitive and cannot accurately predict effects to children exposed in utero or in early postnatal life. Protection of American children, and particularly of inner-city children, against the developmental hazards of pesticides requires a comprehensive strategy that monitors patterns of pesticide use on a continuing basis, assesses children's actual exposures to pesticides, uses state-of-the-art developmental toxicity testing, and establishes societal targets for reduction of pesticide use.

Unraveling the chronic toxicity of lead: an essential priority for environmental health.

Although population exposure to lead has declined, chronic lead toxicity remains a major public health problem in the United States affecting millions of children and adults. Important gaps exist in knowledge of the pathophysiology of chronic lead intoxication. These gaps have impeded development of control strategies. To close current gaps in knowledge of chronic lead toxicity, we propose an integrated, multidisciplinary, marker-based research program. This program combines a) direct measurement of individual lead burden by 109Cd X-ray fluorescence analysis of lead in bone, b) determination of ALA-D phenotype, an index of individual susceptibility to lead, and c) assessments of subclinical injury produced by lead in the kidneys, nervous system and, reproductive organs. Data from this research will provide answers to questions of great public health importance: a) Are current environmental and occupational standards adequate to prevent chronic lead intoxication? b) is lead mobilized from the skeleton during pregnancy or lactation to cause fetal toxicity? c) Is lead mobilized from bone during menopause to cause neurotoxicity? d) What is the significance of genetic variation in determining susceptibility to lead? e) What is the contribution of lead to hypertension, renal disease, chronic neurodegenerative disease or declining sperm counts? f) Is chelation therapy effective in reducing body lead burden in persons with chronic overexposure to lead?

Lead poisoning due to hai ge fen. The porphyrin content of individual erythrocytes.

A 45-year-old Korean man developed abdominal colic, muscle pain, and fatigue. Following a 3-week hospitalization, acute intermittent porphyria was diagnosed based on the symptoms and a high level of urinary delta-aminolevulinic acid (378 mumol/L [4.95 mg/dL]). However, discovery of an elevated blood lead level (3.7 mumol/L [76 micrograms/dL]) subsequently led to the correct diagnosis. No occupational source of lead exposure was identified. The patient reported ingesting a Chinese herbal preparation for 4 weeks prior to becoming ill. A public health investigation revealed that the source of lead exposure was hai ge fen (clamshell powder), one of the 36 ingredients of the Chinese herbal medicine. We used fluorescence image-based cytometry to determine the frequency distribution of the zinc protoporphyrin content in circulating red blood cells and found that 70% of the patient's cells contained elevated levels of zinc protoporphyrin, consistent with the duration of lead exposure and effect of lead on heme synthesis. Analysis of zinc protoporphyrin content in circulating red blood cell distributions may be useful in the diagnosis, therapy, and kinetic modeling of lead poisoning. Environmental lead poisoning is best addressed through the close collaboration of clinicians, public health specialists, and laboratory scientists.

Strategies for the prevention of environmental neurotoxic illness.

Toxic chemicals in the environment can cause a wide range of neurological disease. High-dose exposures to environmental neurotoxicants have produced encephalopathy in children ingesting chips of lead-based paint, blindness in persons who ingested methanol, blindness and ataxia in persons who consumed organic mercury, spinal cord degeneration and peripheral neuropathy in persons exposed to tri-ortho-cresyl phosphate (TOCP), and Parkinsonism in persons exposed to MPTP or to manganese. Environmental neurotoxicants have also been shown to produce a wide range of subclinical neurotoxic effects, including reduction in intelligence, impairment in reasoning ability, shortening of attention span, and alternation of behavior. The first step in the prevention of environmental neurotoxicity is to test chemicals for their toxic potential. More than 70,000 chemicals are currently in commerce. However, except for pharmaceuticals, fewer than 10% of these chemicals have been tested for neurotoxicity. A logical approach to neurotoxicologic assessment of chemical substances will build on and extend currently available test systems. It will have a tiered structure. The first or screening tier will consist of tests to measure obvious structural and functional changes, often a functional observational battery. Subsequent levels of testing will be guided by the results of initial screening. Toxicologic testing must be supplemented by epidemiologic surveillance of populations exposed to known and suspect neurotoxicants. Screening programs in these populations designed to detect excessive absorption of a neurotoxic agent or subclinical neurological dysfunction can be useful in identifying affected individuals before severe disability occurs.

Strategies for epidemiologic studies of lead in bone in occupationally exposed populations.

Lead exposure is widespread among industrial populations in the United States. X-ray fluorescence (XRF) analysis of the lead content of bone offers a promising approach to acquisition of individualized data on chronic lead absorption in occupationally exposed populations. Dosimetric data obtained by XRF will permit accurate definition of dose-response relationships for such chronic consequences of lead exposure as central and peripheral neurologic impairment, renal disease. hypertension, and possibility reproductive dysfunction. Additionally, data on bone lead content obtained by XRF will permit validation of models describing the body lead burden and will allow direct assessment of the efficacy of therapeutic chelation. XRF data may also permit assessment of the possible role of genetic polymorphism of the enzyme delta-aminolevulinic dehydrase as a determinant of the pharmacokinetics and toxicity of lead. In both cross-sectional and prospective epidemiologic studies of body lead burden in occupationally exposed populations, the K-XRF instrument appears to be the technology of choice.

A case report of lead paint poisoning during renovation of a Victorian farmhouse.

We describe a series of four cases of childhood lead poisoning and two cases of adult lead toxicity in a professional family exposed to lead dust and fume during renovation of a rural farmhouse. Initial blood lead levels in the children ranged from 2.70 to 4.20 microM/L (56 to 87 microns/dl) and all four required chelation therapy. Lead-based paint poisoning, a well recognized entity among young children in poor, urban neighborhoods, is not confined exclusively to such areas.

Acute lead poisoning in construction workers: the failure of current protective standards.

Construction workers who use oxyacetylene torches to cut lead-painted metal are at high risk of acute and subacute lead poisoning. Poisoning results from inhalation of submicron-diameter particles of lead fume generated in paint burning. We describe a series of 14 cases of lead poisoning in ironworkers cutting a lead-painted bridge in New York City. Peak blood lead levels ranged from 2.32 to 5.80 mumol/l (48-120 micrograms/dl). Median duration of employment was 4 wk. Two workers required chelation therapy. Personal (breathing zone) exposures to airborne lead ranged from 600 to 4,000 micrograms/m3. Construction workers are specifically exempted from the provisions of the U.S. Occupational Safety and Health Administration (OSHA) lead standard. The data from this study indicate that such exemption is not warranted. A need exists for improved protection of construction workers against occupational exposure to lead.

Effects of elevated lead and cadmium burdens on renal function and calcium metabolism.

To assess the pathophysiologic significance of increased body burdens of lead and cadmium, detailed renal function studies and evaluation of calcium, phosphorus, and vitamin D metabolism were carried out in 38 industrial workers exposed to lead and cadmium for 11 to 37 yr. Body burden of lead, as assessed by x-ray fluorescence measurement of tibia lead content, was elevated in 58% of the men and, when assessed by excretion of lead after Ca-EDTA infusion, was elevated in 36%. Liver or kidney cadmium burden, as assessed by neutron activation analysis, was elevated in 31%. Creatinine clearance was normal in all workers. One worker was hyperuricemic and two were proteinuric; three had increased beta 2 microglobulin excretion and one had diminished urinary acidifying ability. Maximal urinary concentrating ability was abnormal in a significant fraction, i.e., 52% of the men. Individuals with a high lead burden had a slight decrease in mean serum phosphorus but no accompanying phosphaturia. There was no abnormality of serum calcium. Twenty-two percent of subjects were hypercalciuric and two had low vitamin D levels, but these abnormalities bore no relation to heavy metal burden. In this carefully characterized group of men with chronic lead and calcium exposure, definite, if subclinical, effects on renal function and serum phosphorus but not calcium or vitamin D metabolism were demonstrable.