Table 1.
First author (study year) |
Toxicant | N | Age at toxicant measure |
Toxicant measure |
Age at MRI |
MRI measure |
Exposure main effect |
---|---|---|---|---|---|---|---|
Alemany et al. (2018) | PAH, EC, and NO2 | 163 | 7-11 years | High volume sampler | 7-11 years | Basal ganglia vol. (caudate, putamen, globus pallidus) | Greater exposure to PAH and NO2 associated with smaller caudate vol. only. |
Beckwith et al. (2020) | ECAT | 135 | First year of life | Land use regression | 11 – 14.71 years | Whole brain CT, Whole brain VBM | High ECAT group had reduced GMV in bilateral cerebellum and left parietal lobe, and thinner parietal and frontal cortex. No other associations. |
Brunst et al. (2019) | ECAT | 127 | At birth, average from birth to MRI, average past year | Land use regression | At age 12 MRI visit | MRS voxel in bilateral ACC (metabolites : mI, NAA, Cr, Cho, Glu, GLX, GSH). | Elevated past year ECAT associated with elevated mI in bilateral ACC. No associations with other time periods or metabolites detected. |
Burnor et al. (2021) | PM2.5 | 7602 | 9-10 years | Hybrid spatiotempor al model | 9-10 years | rND, hD, rNO, MD, FA of all white matter fibers in each hemisphere and of ATR, CGC, CGH, CC, CST, FX, UF, IFO, ILF, and SLF in each hemisphere. | Hemisphere-stratified models revealed positive associations between PM2.5 and rNO in L hemisphere tracts (CGH, UF, FX, SLF) and R hemisphere tracts (UF, FX). Negative associations between PM2.5 and MD globally, in L hemisphere tracts (ATR, CGH, FX, SLF, UF, IFO, ILF), and R hemisphere tracts (ILF, UF, CGH, FX). No associations with FA, rND, or hD. |
Calderon-Garciduenas et al. (2008) | Air pollution (general) | 36 | N/A | Lifetime residency | M=10.71 years | WMH | 7.6% of Polotitlan youth had WMH, vs. 56.5% from Mexico City. |
Calderon-Garciduenas et al. (2011) | Air pollution (general) | 30 | N/A | Lifetime residency | M= 6.95 years | WMH, cortical GMV and cortical WMV of lobes, CSF, vol. of hippocampus, caudate, putamen, globus pallidus, amygdala | WMH+ children (vs. WMH−) had greater WMV in R parietal lobe. Polotitlan children had greater WMV in bilateral temporal and R parietal, lobes (compared to Mexico City youth). No associations with any other ROI. |
Calderon-Garciduenas et al. (2012) | Air pollution (general) | 30 | N/A | Lifetime residency | M=7.13 years | WMH, combined GMV and WMV of lobes, vol. of frontal cingulate, parietal cingulate, cerebellum, CC, PFC, insula, hippocampus, caudate, putamen, globus pallidus, amygdala | Between baseline and follow-up, WMH+ children had greater volumetric brain growth (GMV and WMV) in temporal, parietal, and frontal regions, compared to WMH-children. WMH+ and Polotitlan children did not differ. No associations with other ROIs. |
Calderon-Garciduenas et al. (2015) | Air pollution (general) | 57 | N/A | Lifetime residency | M = 12.45 years | MRS voxels in R and L hippocampus (metabolites : NAA, Cho, Cr, mI) | Children with APOE e4 genotype from Mexico City, compared to children from Polotitlan, had reduced NAA/Cr ratio in R hippocampus. |
Cserbik et al. (2020) | PM2.5 | 9697 | 9-10 years | Hybrid spatiotemporal model | 9-10 years | 31 SA regions, 27 CT regions, 8 subcortical vols, total SA, total CT, TBV, cortical GMV, subcortical GMV, cortical WMV, CSF, ICV, ventricle vols. | Greater PM2.5 exposure associated with: (1) thinner L frontal, R temporal lobes; (2) thicker R frontal, L temporal lobes, (3) thicker and thinner bilateral cingulate, (4) reduced SA in R frontal pole, L cuneus, (5) greater SA in R lateral OFC, (6) greater R thalamus, R pallidum, L accumbens vol, (7) reduced L putamen, L pallidum vol. No other associations detected. |
Guxens et al. (2018) | NO2, particulate matter (coarse and fine particles), and absorbance of fine particles | 783 | Prenatal | Land use regression | 6-10 years | Whole brain CT, TBV, cortical GMV, cortical WMV, subcortical GMV, vol. of caudate, putamen, pallidum, accumbens, hippocampu s, amygdala, thalamus, ventricles | Higher fine particle exposure associated with thinner R frontal, R parietal, and L occipital cortex. Higher coarse particle exposure associated with thinner R lateral OFC. Absorbance of fine particles associated with thinner L fusiform. No associations with any other measure. |
Lubczynska et al. (2021) | NO2, NOx, PM10, PM2.5, PMcoarse, PM2.5 absorbance, PAH, BAP, OC, Cu, Fe, K, Si, Zn, OP, UFP | 3133 | Prenatal, average from birth to MRI | Land use regression | 9-12 years | TBV, cortical GMV, subcortical GMV, cortical WMV, vol. of CC, cerebellum, thalamus, caudate, putamen, pallidum, hippocampus, amygdala, accumbens. Whole brain CT and SA. | Both thinner and thicker cortex associated with exposure, prenatally and across childhood, depending on region. Across childhood exposure associated with less PFC SA, but greater SA in other regions. No associations between pregnancy exposure and SA reported. Both pregnancy and across childhood exposure associated with smaller CC, smaller hippocampus , larger amygdala, larger cerebellum. No associations with other measures. |
Lubczynska et al. (2020) | NO2, NOx, PM10, PM2.5, PMcoarse, PM2.5 absorbance, PAH, BAP, OC, Cu, Fe, K, Si, Zn, OP, UFP | 2,954 | Prenatal, average from birth to MRI | Land use regression | 9-12 years | Global FA, global MD, follow-up analyses on individual white matter tracts | In single pollutant analyses, prenatal and average childhood exposure predicted lower FA and higher MD for many air pollutants assessed. |
Mortamais et al. (2017) | Total sum of PAH levels, BAP | 242 | 8-12 years | High volume sampler | 8-12 years | Basal ganglia vol. (caudate, putamen, globus pallidus), brain parenchyma l fraction | Outdoor and indoor BAP predicted smaller caudate vol. Effect of total outdoor PAH on caudate vol. was similar but smaller than the effect of outdoor BAP. No other associations found. |
Mortamais et al. (2019) | PM2.5 | 186 | Prenatal, average across first 2 years of life, time of MRI | Land use regression | 8-11.7 years | Cortical GMV, cortical WMV, vol. of lateral ventricles and CC sub-regions | Greater 3rd trimester exposure linked to decreased vol. of anterior and body of CC. Associations did not survive correction for multiple comparisons. No associations with other ROIs or time periods. |
Perez-Crespo et al. (2022) | NOx, NO2, PM2.5, PM2.5 absorbance, PM10 | 2197 | Prenatal, 0-3, 3 – 6, 6 to time of MRI | Land use regression | 9-12 years | Resting state functional connectivity of 6 brain networks | NO2 from 0-3 and NOx from 3-6 both associated with higher visual - task positive network connectivity. PM2.5 absorbance from 0-3 associated with higher connectivity between visual and auditory, task positive, and task negative networks as well as between auditory and task positive and task negative networks, and between task positive and task negative networks. PM2.5 absorbance from 0-3 also associated with greater connectivity within the visual, motor, task positive, and task negative networks. No other associations with other air pollutants or time periods. |
Peterson et al. (2015) | PAH | 40 | Prenatal, at age 5 | Personal backpack monitor for 48 hours; spot urine sample from child | 7-9 years | Whole brain CT, surface morphology | Prenatal exposure to PAH correlated with reduced vol. in bilateral frontal, superior temporal, and parietal lobes and in L rostro-caudal extent of mesial surface—associations driven by changes in white matter. PAH at age 5 correlated with reduced WMV in bilateral dorsal PFC, especially SFG. No association with CT. |
Peterson et al. (2022) | PM2.5, PAH | 332 | Prenatal | Personal backpack monitor for 48 hours; spatiotempor al model | 6-14 years | Whole brain CT, FA, ADC, MRS (metabolites: NAA, Cr, Cho, GLX), rCBF, surface morphology | PAH & PM2.5 associated with (1) thicker lateral temporal, posterior inferior, and mesial wall cortices, (2) thinner dorsal parietal cortices, (3) smaller white matter vols in the inferior parietal lobes and cingulate gyrus, (4) larger white matter vols in dorsal convexity, SFG, and posterior inferior brain surface, (5) higher FA in basal ganglia and ACC, (6) lower rCBF in frontal gray matter, (7) higher NAA and Cho in cingulate. ADC alterations different for PM2.5 vs. PAH. |
Pujol, Fenoll et al. (2016) | Copper | 263 | 8-12 years | High volume sampler | 8-12 years | Whole brain CT,Whole brain VBM, FA, resting state functional connectivity with seeds in PFC and caudate | Greater Cu associated with higher gray matter concentratio n in the caudate, greater FA in white matter in and around the caudate, diffusion changes in the caudate, reduced resting state functional connectivity between the caudate and frontal lobe operculum, and increased CT in L SMA. |
Pujol, Martinez-Vilavella et al. 2016 | Average of EC, NO2 | 239 | 8-12 years | High volume sampler (EC), passive dosimeter (NO2) | 8-12 years | Whole brain CT, Whole brain VBM, FA, brain activation during sensory task, resting state functional connectivity with seeds in medial frontal, dorsal frontal, PCC, and SMA, MRS voxel in L frontal lobe (metabolite:Cho/Cr ratio) | In the resting state analysis, higher exposure to air pollution was associated with weaker connectivity within DMN and stronger connectivity between the DMN and the lateral boundary of the DMN. In the task analysis, greater exposure to air pollution was associated with lower deactivations in the SMA and somatosenso ry cortex. No association with sMRI, FA, or MRS measures. |
Note. See notes following Table 9 for table notes and a comprehensive list of abbreviations.