Detecting lead toxicity with capillary collections
|Test Id||Reporting Name||Available Separately||Always Performed|
|PBBC||Lead, Capillary, B||No||Yes|
Inductively Coupled Plasma-Mass Spectrometry (ICP-MS)
The CDC recommends venous collection of samples for lead testing. Capillary lead testing is acceptable for pediatrics and patients with phlebotomy considerations, but capillary blood collection may be more susceptible to contamination. Elevated capillary blood levels must be confirmed with a venous lead blood test (PBDV / Lead, Venous, with Demographics, Blood).
|PTAD7||Patient Street Address|
|PTZI7||Patient Zip Code|
|PTPH7||Patient Home Phone|
|GDFN7||Guardian First Name|
|GDLN7||Guardian Last Name|
|MDOR7||Health Care Provider Name|
|MDAD7||Health Care Provider Street Address|
|MDCI7||Health Care Provider City|
|MDST7||Health Care Provider State|
|MDZI7||Health Care Provider Zip Code|
|MDPH7||Health Care Provider Phone|
|LABP7||Submitting Laboratory Phone|
Patient Preparation: High concentrations of gadolinium and iodine are known to interfere with most metals tests. If either gadolinium- or iodine-containing contrast media has been administered, a specimen should not be collected for 96 hours.
Supplies: Microtainer (EDTA) Tube, 0.5 mL (T174)
Collection Container/Tube: BD Microtainer with EDTA
Specimen Volume: 0.4 mL
1. See Trace Metals Analysis Specimen Collection and Transport for complete instructions.
2. Send specimen in original tube.
1. Lead and Heavy Metals Reporting (T491)
2. If not ordering electronically, complete, print, and send a General Request (T239) with the specimen.
|Specimen Type||Temperature||Time||Special Container|
|Whole blood||Refrigerated (preferred)||28 days|
Detecting lead toxicity with capillary collections
Lead is a heavy metal naturally found in the environment that can be an acute and chronic toxin. Lead can enter the environment through releases from mining lead and other metals, and from factories that make or use lead, lead alloys, or lead compounds. Lead is released into the air during burning coal, oil, or waste. Before the use of leaded gasoline in motor vehicles was banned (January 1, 1996), most of the lead released into the United States environment came from vehicle exhaust.
Lead was banned from household paints in 1978 but is still found in paint produced for nondomestic use and in artistic pigments. Ceramic products available from noncommercial suppliers (such as local artists) often contain significant amounts of lead that can be leached from the ceramic by weak acids such as vinegar and fruit juices. Lead is commonly found in soil especially near roadways, older houses, old orchards, mining areas, industrial sites, near power plants, incinerators, landfills, and hazardous waste sites. Recent data has also shown that inexpensive cosmetic jewelry pieces sold to the general public may contain high levels of lead, which can be transferred to the skin through routine handling. However, not much lead can get into your body through your skin.
People may be exposed to lead by eating food or drinking water that contains lead. Drinking (tap) water in houses containing lead pipes may contain lead, especially if the water is acidic or "soft". Foods may contain small amounts of lead. Leafy fresh vegetables grown in lead-containing soils may have lead-containing dust on them. Lead may also enter foods if they are put into improperly glazed pottery or ceramic dishes and from leaded-crystal glassware. However, since lead solder is no longer used in cans, very little lead is typically found in food.
The typical diet in the United States contributes 1 to 3 mcg of lead per day, of which 1% to 10% is absorbed; children may absorb as much as 50% of the dietary intake, and the fraction of lead absorbed is enhanced by nutritional deficiency. The majority of the daily intake is excreted in the stool after direct passage through the gastrointestinal tract. While a significant fraction of the absorbed lead is incorporated into bone (approximately 94% adults; approximately 73% children) and erythrocytes, lead ultimately distributes among all tissues, with lipid-dense tissues such as the central nervous system being particularly sensitive to organic forms of lead. All absorbed lead is ultimately excreted in the bile or urine. Soft-tissue turnover of lead occurs within approximately 120 days.
Other alternative sources of lead include moonshine distilled in lead pipes, some traditional home medicines, non-Western cosmetics (eg, surma and kohl), and some types of hair colorants, cosmetics, and dyes.
Lead expresses its toxicity by several mechanisms:
1) It avidly inhibits aminolevulinic acid dehydratase and ferrochelatase, 2 of the enzymes involved in the synthesis of heme. In the end, this inhibition causes decreased hemoglobin synthesis resulting in anemia.
2) Lead is also an electrophile that avidly forms covalent bonds with the sulfhydryl group of cysteine in proteins. Thus, proteins in all tissues exposed to lead will have lead bound to them. The most common sites affected are epithelial cells of the gastrointestinal tract and epithelial cells of the proximal tubule of the kidney.
Avoidance of exposure to lead is the treatment of choice. However, chelation therapy is available to treat severe disease and may be necessary especially in children if the blood lead is higher than 25 mcg/dL. The standard chelating agents currently in use are dimercaprol (British Anti-Lewisite: BAL), CaNa2-EDTA (or EDTA), penicillamine, and 2,3-dimercaptosuccinic acid (DMSA; Succimer).
0-5 years: <3.5 mcg/dL
> or =6 years: <5.0 mcg/dL
Pediatrics (< or =15 years): > or =20.0 mcg/dL
Adults (> or =16 years): > or =70.0 mcg/dL
No safe blood lead level in children has been identified. Lead exposure can affect nearly every system in the body. Because lead exposure often occurs with no obvious symptoms, it frequently goes unrecognized. The current reference level at which the CDC recommends public health actions be initiated is 3.5 mcg/dL in patients 0 to 5 years old and 5 mcg/dL for patients 6 years and older. Chelation therapy is generally indicated in children when whole blood lead concentrations are above 25 mcg/dL.
The Occupational Safety and Health Administration (OSHA) has published the following standards for employees working in industry. OSHA Standards for General Industry (CFR 1910.1025) and Construction (CFR 1926.62) apply to workers exposed to airborne lead levels 30 mcg/m(3) or greater time-weighted average and require the removal of workers if a periodic and follow-up blood lead level is 60 mcg/dL (2.9 mcmol/L) or greater, 50 mcg/dL (2.4 mcmol/L) or greater for construction, or the average blood lead level of all tests over a 6-month period (or if there are fewer than 3 tests over a 6-month period, the average of 3 consecutive tests) is 50 mcg/dL (2.4 mcmol/L) or greater. Workers with a single blood lead level meeting the numerical criteria for medical removal must have their blood lead level retested within 2 weeks. If a worker is medically removed, a new blood lead level must be measured monthly during the removal period. Workers are permitted to return to work when their blood lead level is 40 mcg/dL (1.9 mcmol/L) or less. According to OSHA Lead Standards, a zinc protoporphyrin is also required on each occasion a blood lead level measurement is made.
No significant cautionary statements
1. Centers for Disease Control and Prevention (CDC). National Report on Human Exposure to Environmental Chemicals. CDC; Updated March 2021. Accessed November 19, 2021. Available at www.cdc.gov/exposurereport
2. Agency for Toxic Substances and Disease Registry: Toxicological Profile for Lead. US Department of Health and Human Services; August 2020. Accessed September 8, 2021. Available at: www.atsdr.cdc.gov/ToxProfiles/tp13.pdf
3. de Burbure C, Buchet JP, Leroyer A, et al: Renal and neurologic effects of cadmium, lead, mercury, and arsenic in children: evidence of early effects and multiple interactions at environmental exposure levels. Environ Health Perspect. 2006 Apr;114(4):584-590
4. Kosnett MJ, Wedeen RP, Rothenberg SJ, et al: Recommendations for medical management of adult lead exposure. Environ Health Perspect. 2007 Mar;115(3):463-471
5. Jusko T, Henderson C, Lanphear B, et al: Blood lead concentrations <10 mcg/dL and child intelligence at 6 years of age. Environ Health Perspect. 2008 Feb;116(2):243-248
6. Strathmann FG, Blum LM: Toxic elements. In Rifai N, Horwath AR, Wittwer CT, eds. Tietz Textbook of Clinical Chemistry and Molecular Diagnostics. 6th ed. Elsevier; 2018: 907-910
Lead in whole blood is analyzed by inductively coupled plasma-mass spectrometry in standard mode using iridium as an internal standard and using a salt matrix calibration.(Unpublished Mayo method)
Monday through Saturday
This test was developed, and its performance characteristics determined by Mayo Clinic in a manner consistent with CLIA requirements. This test has not been cleared or approved by the US Food and Drug Administration.
|Test Id||Test Order Name||Order LOINC Value|
|PBDC||Lead, Capillary, w/Demographics, B||10368-9|
|Result Id||Test Result Name||
Result LOINC Value
Applies only to results expressed in units of measure originally reported by the performing laboratory. These values do not apply to results that are converted to other units of measure.
|65639||Lead, Capillary, B||10368-9|
|PTAD7||Patient Street Address||56799-0|
|PTZI7||Patient Zip Code||45401-7|
|PTPH7||Patient Home Phone||42077-8|
|GDFN7||Guardian First Name||79183-0|
|GDLN7||Guardian Last Name||79184-8|
|MDOR7||Health Care Provider Name||52526-1|
|MDAD7||Health Care Provider Street Address||74221-3|
|MDCI7||Health Care Provider City||52531-1|
|MDST7||Health Care Provider State||52532-9|
|MDZI7||Health Care Provider Zip Code||87720-9|
|MDPH7||Health Care Provider Phone||68340-9|
|LABP7||Submitting Laboratory Phone||65651-2|