Skip to main page content
U.S. flag

An official website of the United States government

Dot gov

The .gov means it’s official.
Federal government websites often end in .gov or .mil. Before sharing sensitive information, make sure you’re on a federal government site.

Https

The site is secure.
The https:// ensures that you are connecting to the official website and that any information you provide is encrypted and transmitted securely.

Access keys NCBI Homepage MyNCBI Homepage Main Content Main Navigation
. 2009 Nov;30(6):1207-13.
doi: 10.1016/j.neuro.2009.04.005. Epub 2009 Apr 23.

High levels of hair manganese in children living in the vicinity of a ferro-manganese alloy production plant

Affiliations

High levels of hair manganese in children living in the vicinity of a ferro-manganese alloy production plant

José A Menezes-Filho et al. Neurotoxicology. 2009 Nov.

Abstract

Manganese (Mn) is an essential element, but an effective toxic at high concentrations. While there is an extensive literature on occupational exposure, few studies have examined adults and children living near important sources of airborne Mn. The objective of this study was to analyze hair Mn of children living in the vicinity of a ferro-manganese alloy production plant in the Great Salvador region, State of Bahia, Brazil and examine factors that influence this bioindicator of exposure. We examined 109 children in the age range of 1-10 years, living near the plant. Four separate housing areas were identified a priori on the bases of proximity to the emission sources and downwind location. A non-exposed group (n=43) of similar socio-economic status was also evaluated. Mn hair (MnH) concentration was measured by graphite atomic absorption spectrometry (GFAAS). Possible confounding hematological parameters were also assessed. Mean MnH concentration was 15.20 microg/g (1.10-95.50 microg/g) for the exposed children and 1.37 microg/g (0.39-5.58 microg/g) for the non-exposed. For the former, MnH concentrations were 7.95+/-1.40 microg/g (farthest from the plant), 11.81+/-1.11 microg/g (mid-region), 34.43+/-8.66 microg/g (closest to the plant) and 34.22+/-9.15 microg/g (directly downwind). Multiple regression analysis on log transformed MnH concentrations for the exposed children derived a model that explained 36.8% of the variability. In order of importance, area of children's residence, gender (girls>boys) and time of mother's residence in the area at the birth of the child, were significantly associated with MnH. Post hoc analyses indicated two groupings for exposure areas, with those living closest to and downwind of the plant displaying higher MnH concentrations compared to the others. The contribution of the time the mother lived in the community prior to the child's birth to the children's current MnH suggests that in utero exposure may play a role. A study of neurobehavioral performance with respect to Mn exposure in these children is currently underway.

PubMed Disclaimer

Figures

Figure 1
Figure 1
Schematic map of the Cotegipe Village (exposed community) in Simões Filho town and reference community (Capiarara, Lauro de Freitas), in the Metropolitan Area of Salvador, Bahia, Brazil (top); showing the four residential areas with radial distances from the plant (bottom).
Figure 2
Figure 2
Box plot of MnH data according to area of residence, clustered by gender. R is for referents and A thru D the four residential areas in the exposed community.
Figure 3
Figure 3
Residual plot of log transformed Mn concentration in hair versus years of maternal exposure time previous to child birth.

References

    1. Agusa T, Kunito T, Fujihara J, Kubota R, Minh TB, Kim Trang PT, Iwata H, et al. Contamination by arsenic and other trace elements in tube-well water and its risk assessment to humans in Hanoi, Vietnam. Environmental Pollution. 2006;139(1):95–106. - PubMed
    1. ATSDR (Agency for Toxic Substances and Disease Registry) Summary Report Hair Analysis Panel Discussion Exploring The State Of The Science . 2001. [Accessed Nov. 3, 2008]. http://www.atsdr.cdc.gov/HAC/hair_analysis/index.html)
    1. Baldwin M, Mergler D, Larribe F, Bélanger S, Tardif R, Bilodeau l, Hudnell K. Bioindicator and exposure data for population based study of manganese. Neurotoxicology. 1999;20(2):30, 343–354. - PubMed
    1. Bouchard M, Laforest F, Vandelac L, Bellinger D, Mergler D. Hair Manganese and Hyperactive Behaviors: Pilot Study of School-Age Children Exposed through Tap Water. Environ Health Perspect. 2007;15(1):122–127. - PMC - PubMed
    1. Brenneman KA, Wong BA, Bucellato MA, Costa ER, Gross EA, Dorman DC. Direct olfactory transport of inhaled manganese (54MnCl2)to the rat brain: Toxikinetic investigations in a unilateral nasal occlusion model. Toxicol Appl Pharmacol. 2000;169:238–248. - PubMed

Publication types

MeSH terms