Evolution of efficient methods to sample lead sources, such as house dust and hand dust, in the homes of children.

Efficient sampling methods to recover lead-containing house dust and hand dust have been evolved so that sufficient lead is collected for analysis, and to ensure that correlational analyses linking these two parameters to blood lead are not dependent on the efficiency of sampling. Precise collection of loose house dust from a 1-unit area (484 cm2) with a Tygon or stainless steel sampling tube connected to a portable sampling pump (1.2 to 2.5 liters/min) required repetitive sampling (three times). The Tygon tube sampling technique for loose house dust less than 177 microns in diameter was around 72% efficient with respect to dust weight and lead collection. A representative house dust contained 81% of its total weight in this fraction. A single handwipe for applied loose hand dust was not acceptably efficient or precise, and at least three wipes were necessary to achieve recoveries of greater than 80% of the lead applied. House dusts of different particle sizes less than 246 microns adhered equally well to hands. Analysis of lead-containing material usually required at least three digestions/decantations using hot plate or microwave techniques to allow at least 90% of the lead to be recovered. It was recommended that other investigators validate their handwiping, house dust sampling, and digestion techniques to facilitate comparison of results across studies. The final methodology for the Cincinnati longitudinal study was three sampling passes for surface dust using a stainless steel sampling tube; three microwave digestions/decantations for analysis of dust and paint; and three wipes with handwipes with one digestion/decantation for the analysis of six handwipes together.

[1]  P S Gartside,et al.  Fecal lead excretion in young children as related to sources of lead in their environments , 1980, International archives of occupational and environmental health.

[2]  A Lafontaine,et al.  Exposure to lead by the oral and the pulmonary routes of children living in the vicinity of a primary lead smelter. , 1980, Environmental research.

[3]  Gary Ter Haar,et al.  New Information on Lead in Dirt and Dust as Related to the Childhood Lead Problem , 1974, Environmental health perspectives.

[4]  L. Levin,et al.  Study and models of total lead exposures of battery workers. , 1984, American Industrial Hygiene Association journal.

[5]  C Chavalitnitikul,et al.  A laboratory evaluation of wipe testing based on lead oxide surface contamination. , 1984, American Industrial Hygiene Association journal.

[6]  H. Roels,et al.  Repeated surveillance of exposure to cadmium, manganese, and arsenic in school-age children living in rural, urban, and nonferrous smelter areas in Belgium. , 1980, Environmental research.

[7]  R. A. Rubino,et al.  Role of Airborne Lead in Increased Body Burden of Lead in Hartford Children* , 1974, Environmental health perspectives.

[8]  Evan Charney,et al.  Lead Analysis of the House Dust: A Method for the Detection of Another Source of Lead Exposure in Inner City Children* , 1974, Environmental Health Perspectives.

[9]  Fairey Fs,et al.  Soil lead and pediatric lead poisoning in Charleston, S. C. , 1970 .

[10]  L Bruckman,et al.  Investigations into sources of lead in the environment of urban children. , 1975, Environmental research.

[11]  I. B. Millar,et al.  Urban lead—A study of environmental lead and its significance to school children in the vicinity of a major trunk road , 1982 .

[12]  J S Boleij,et al.  The Arnhem Lead Study. II. Indoor pollution, and indoor/outdoor relationships. , 1981, Environmental research.

[13]  M. J. Duggan,et al.  Lead in urban dust: An assessment , 1980 .

[14]  I B Pless,et al.  House and hand dust as a potential source of childhood lead exposure. , 1974, American journal of diseases of children.

[15]  E. Charney,et al.  Increased lead absorption in inner city children: where does the lead come from? , 1980, Pediatrics.

[16]  I. von Lindern,et al.  The Silver Valley lead study: the relationship between childhood blood lead levels and environmental exposure. , 1977, Journal of the Air Pollution Control Association.

[17]  B. Brunekreef,et al.  The Arnhem Lead Study. I. Lead uptake by 1- to 3-year-old children living in the vicinity of a secondary lead smelter in Arnhem, The Netherlands. , 1981, Environmental research.

[18]  J. Webb,et al.  Significance of High Soil Lead Concentrations for Childhood Lead Burdens , 1974, Environmental health perspectives.

[19]  R. Jervis,et al.  Lead Contamination around Secondary Smelters: Estimation of Dispersal and Accumulation by Humans , 1974, Science.