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Assessment of Blood Lead Levels Among Children Aged ≤5 Years — Zamfara State, Nigeria, June–July 2012

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Assessment of Blood Lead Levels Among Children Aged ≤5 Years — Zamfara State, Nigeria, June–July 2012

MMWR Weekly
Vol. 63, No. 15
April 18, 2014
PDF of this issue

Assessment of Blood Lead Levels Among Children Aged ≤5 Years — Zamfara State, Nigeria, June–July 2012


April 18, 2014 / 63(15);325-327

Muhammed Bashir, MD1, Nasir Umar-Tsafe, MSc1, Kabiru Getso, MBBS1, Ibrahim M. Kaita, MSc1, Abdulsalami Nasidi, PhD2; Nasir Sani-Gwarzo MD2; Patrick Nguku, MD3, Lora Davis, DVM3, Mary Jean Brown ScD4 (Author affiliations at end of text)
Since 2010, Nigerian state and federal governments and the international community have been responding to an outbreak of lead poisoning caused by the processing of lead-containing gold ore in Zamfara State, Nigeria, that resulted in the deaths of approximately 400 children aged ≤5 years (1). Widespread education, surveys of high-risk villages, testing of blood lead levels (BLLs), medical treatment, and environmental cleanup all have been implemented. To evaluate the success of these remediation efforts in reducing the prevalence of lead poisoning and dangerous work practices, a population-based assessment of children's BLLs and ore processing techniques was conducted during June–July 2012. The assessment found few children in need of medical treatment, significantly lower BLLs, and substantially less exposure of children to dangerous work practices. Public health strategies designed to identify and treat children with lead poisoning, clean up existing environmental hazards, and prevent children from being exposed to dangerous ore processing techniques can produce a sustained reduction in BLLs.
The 2010 outbreak of lead poisoning in Zamfara State caused by unsafe processing of lead-containing gold ore resulted in severe neurologic illness and death in children. When processed dry with low technology methods, the gold ore produced fine particles that contaminated water and food crops and were easily inhaled or ingested during normal hand-to-mouth activities common among toddlers (2).
When inhaled or ingested, lead can cause damage to the brain, kidneys, bone marrow, and other body systems in young children. In infants and children, BLLs as low as 5 µg/dL have been associated with developmental problems, including impaired cognitive function, behavioral difficulties, impaired hearing, and reduced stature (3). BLLs ≥75µg/dL can cause coma, convulsions, and death. No safe BLL has been identified for children (4).
During June–July 2012, the Zamfara State Ministry of Health, Nigerian Field Epidemiology and Laboratory Training Program, and CDC collaborated to conduct a representative, cross-sectional, population-based, multistage stratified cluster design survey to estimate the geometric mean (GM) BLLs of children living in Zamfara State aged ≤5 years. Investigators also examined the extent of exposure to ore processing methods that generate dust (i.e., crushing ore, dry grinding ore using power flour grinders, and open air drying of ore), and they examined the ore processing practices among the children's mothers, an important factor because ore processing inside the family compound is a female role in this population. Because mothers also are responsible for child care, ore processing among mothers is a risk factor for young children who eat, sleep, and play within the compound.
To create systematic samples for village-level and family-level surveys, a total of 112 villages initially were selected from among the 14 local government areas in Zamfara State, proportionate to the population of the areas, using ambient population distribution software (5). An additional 10 villages were selected as potential replacements should some selected villages be inaccessible or unsafe, bringing the total to 122. To obtain population-based estimates of children's blood and environmental lead levels, one child in each of seven systematically selected families was surveyed in more detail from each of 56 villages systematically selected from among the 122 villages, for a total of 392 children in the study sample.*
Venous blood samples were collected from children aged ≤5 years. BLLs were analyzed using inductively coupled plasma mass spectroscopy, with a lower limit of detection of 0.25 µg/dL. The precision and quality assurance measures used have been described previously (6). GM BLLs were analyzed for correlation with exposure to different ore processing methods, with statistical significance determined at p<0.05. The study protocol was approved by the National Health Research Ethics Committee of Nigeria and the CDC Institutional Review Board.
Among the 392 children aged ≤5 years, the mean age was 35 months. The mothers of 69 (17.6%) children were involved in ore processing activities. Sixty-one (15.6%) mothers used processing techniques that generated large amounts of dust, and 17 (4.3%) mothers processed ore using dust-generating techniques within the family compound.
A history of convulsions was reported in 90 (23.0%) children. Thirty-four of the children lived in villages that used dust-generating ore processing methods, 40 lived in villages that used non–dust-generating methods, and 16 lived in villages that did not do ore processing (Table).
Venous blood samples were collected from 383 (97.7%) of the 392 children. The GM BLL for the 383 children was 6.9 µg/dL (range = 1.6–61.0 µg/dL). A total of 88 children (23.0%) had BLLs ≥10 µg/dL, and four (1.0%) had BLLs ≥45 µg/dL, the threshold for treatment with chelation therapy recommended by CDC (7).
The GM BLL of the children whose mothers were involved in dust-generating ore processing activities was 8.5 µg/dL (standard deviation [SD] = 11.1), compared with 6.4 µg/dL (SD = 5.3; p<0.001) among those whose mothers used non–dust-generating ore processing methods (Table). When dust-generating activities were conducted within the family compound, the GM BLL in children was 8.9 µg/dL (SD = 9.8). All four children with BLLs ≥45 µg/dL had mothers involved in dust-generating activities within the family compound.
Although the use of mercury for gold extraction to amalgamate gold was not defined as a dust-generating activity, children living in villages where mercury was used had BLLs significantly higher than children where gold ore was not processed (GM 11.2 µg/dL [SD = 5.1] compared with 3.4 µg/dL [SD = 5.1], p<0.05). Additionally, for children living in villages where excess mercury was burned off the ore, the GM BLL tended to be significantly higher (GM 13.1 µg/dL [SD = 16.6]), compared with children living in villages in which mercury was not used to amalgamate gold.


The 2010 outbreak of lead poisoning in Zamfara State was unprecedented in recent decades. In two investigations in 2010 conducted to identify villages where risk for lead poisoning was extremely high, one found that 97% of children had BLLs ≥45 µg/dL, and the second found that, among ore processing villages, 30% of children had BLLs ≥45 µg/dL, but no children in villages that did not process ore had BLLs this high. (8)
Since 2010, a team of international, Nigerian federal, and Nigerian state public health agencies, environmental remediation specialists, health-care providers, and educators has worked to reduce BLLs in young children. These efforts have resulted in identification of lead contamination in approximately 50 villages, cleanup of environmental lead contamination in 11 villages, chelation therapy for children with BLLs ≥45 µg/dL, widespread public education campaigns, and training for local workers responsible for testing and remediation activities (9).
In the assessment described in this report, 74% of the 56 villages were involved in the gold trade, and the GM BLL was significantly higher among children whose mothers processed ore using dust-generating methods. Few families (20 [5%] compared with 84 [71%] in 2010) (1) were processing ore within the family compound, where children aged ≤5 years spend most of their time, and three of the 20 families used non–dust-generating ore processing methods. However, the highest GM BLLs were found among children who lived in villages where mothers used certain non–dust-generating methods, such as amalgamating ore using mercury or burning excess mercury off the ore; the high GM BLLs might have resulted from toxic lead fumes released during burning.
Although work remains, much has been done to address the problem of lead exposure in Zamfara State. New and safer processing techniques that control dust and residual ore wastes, a better understanding of potential exposure to lead-contaminated foodstuffs, continued BLL surveillance, chelation therapy when warranted, and environmental cleanup of hazardous sites remain critical (9). When such strategies are successfully implemented, a sustained reduction of BLLs in children can be achieved.
1Zamfara State Ministry of Health and Nigeria Field Epidemiology and Laboratory Training Program; 2Nigeria CDC; 3US CDC Country Office Nigeria,4Division of Emergency and Environmental Health Services, National Center for Environmental Health, CDC (Corresponding author: Mary Jean Brown,, 770-488-3300)


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* A sample size of 46 villages had been determined large enough to estimate the prevalence of elevated BLLs ≥10 µg/dL (then defined as the CDC BLLs of concern). An additional 10 villages were added to the sample in the event some of the 46 selected villages were inaccessible or unsafe, bringing the total to 56 villages, each with seven children, for a total of 392 children in the sample.

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