Table 1.
Study | Study Design | Inhalation Exposure | Results |
---|---|---|---|
Haynes et al., 2018 | Expansion of Communities Actively Researching Exposure (CARES) cohort (n = 106; East Liverpool Ohio, US) | Mn | Exposure negatively associated with Full Scale IQ measurements among children |
Haynes et al., 2015 | Expansion of CARES cohort (n = 404; East Liverpool Ohio, US) | Mn | Exposure negatively associated with Full Scale IQ measurements among children |
Menezes-Filho et al., 2018 | Cross-sectional study (n = 225; Simões Filho, Bahia, Brazil) | Mn and Pb | Exposure associated with intellectual deficiencies (IQ) |
Pesch et al., 2017 | Second follow up survey of Heinz Nixdorf Recall Study (HNRS) cohort (n = 1232; Germany) | Mn | Exposure associated with impaired dexterity |
Palzes et al., 2019 | Cross-sectional (n = 48; Zarcero County, Costa Rica) | Mn-associated fungicide | Exposure not associated with changes in working memory |
Pujol et al., 2016 | BREATHE Project cohort (n = 2836; Barcelona, Spain) | Cu | Exposure associated with impaired motor performance and altered basal ganglia in children |
Lubczyńska et al., 2020 | Generation R cohort (n = 2954; Rotterdam, Netherlands) | Various sizes of PM (including PM2.5) and metal constituents (including Si and Zn) | PM2.5 exposure associated with decrease in children’s fractional anisotropy Si exposure associated with increase in mean diffusivity Zn exposure associated with increase in mean diffusivity |
Liu et al., 2018 | Single-blind randomized cross-over trial (n = 53; Toronto, Canada) | Urban coarse ambient PM (>PM10); Concentrated ambient PM (PM0.1); Related metals (Al, Ba) |
Ba exposure associated with increase in ubiquitin C-terminal hydrolase L1 Al exposure associated with increased urinary neural marker vanillylmandelic acid |