Abstract
Background
ATP-binding cassette (ABC) transporters have been associated with methylmercury (MeHg) toxicity in experimental animal models.
Aims
To evaluate the association of single nucleotide polymorphisms (SNPs) in maternal ABC transporter genes with 1) maternal hair MeHg concentrations during pregnancy and 2) child neurodevelopmental outcomes.
Materials and methods
Nutrition Cohort 2 (NC2) is an observational mother-child cohort recruited in the Republic of Seychelles from 2008–2011. Total mercury (Hg) was measured in maternal hair growing during pregnancy as a biomarker for prenatal MeHg exposure (N=1313) (mean 3.9 ppm). Infants completed developmental assessments by Bayley Scales of Infant Development II (BSID-II) at 20 months of age (N=1331). Genotyping for fifteen SNPs in ABCC1, ABCC2 and ABCB1 was performed for the mothers.
Results
Seven of fifteen ABC SNPs (ABCC1 rs11075290, rs212093, and rs215088; ABCC2 rs717620; ABCB1 rs10276499, rs1202169, and rs2032582) were associated with concentrations of maternal hair Hg (p<0.001 to 0.013). One SNP (ABCC1 rs11075290) was also significantly associated with neurodevelopment; children born to mothers with rs11075290 CC genotype (mean hair Hg 3.6 ppm) scored on average 2 points lower on the Mental Development Index (MDI) and 3 points lower on the Psychomotor Development Index (PDI) than children born to mothers with TT genotype (mean hair Hg 4.7 ppm) while children with the CT genotype (mean hair Hg 4.0 ppm) had intermediate BSID scores.
Discussion
Genetic variation in ABC transporter genes was associated with maternal hair Hg concentrations. The implications for MeHg dose in the developing child and neurodevelopmental outcomes need to be further investigated.
Keywords: ABC transporter, MRP1, MRP2, MDR1, p-glycoprotein, neurodevelopment
1. Introduction
Fish is a primary source of protein for more than four billion people worldwide (FAO/WHO 2011). Methylmercury (MeHg) is a well-documented neurotoxicant that is present in all fish to a varying extent. At adequate dosages, MeHg poses a risk for the developing fetus, as it is known to readily cross the placenta and the blood-brain barrier (WHO 2007). However, the results concerning consequences of methylmercury exposure naturally found in fish on child neurodevelopment has been contradictory. While studies in New Zealand, Faroe Islands, and the United States have reported adverse developmental influences associated with prenatal MeHg exposure (Crump et al. 1998; Grandjean et al. 1997; Oken et al. 2005; Sagiv et al. 2012), no overall association between prenatal MeHg exposure and developmental outcomes were observed in large studies in the Seychelles, United Kingdom and Spain (Daniels et al. 2004, Davidson et al. 1998; Llop et al. 2012, Myers et al. 2003, Strain et al. 2015). These results reveal that the association between prenatal MeHg exposure from maternal fish consumption and child developmental outcomes is far more complex than previously thought and inconsistencies among study findings may be due to variability in concomitant dietary exposures or genetic factors influencing MeHg toxicity. Several factors influence the concentration of MeHg experienced by the fetus, such as the type and the amount of fish consumed; however, the contribution of the genetic background has rarely been studied. Sequence variation in maternal genes responsible for the toxicokinetics of MeHg is likely to result in differences in MeHg concentrations, and in turn differences in neurotoxicity, between infants of mothers with a similar fish intake. Yet, very little is known about gene – MeHg interactions on child neurodevelopment (Llop et al. 2015).
Animal studies provide evidence that transporter proteins can affect MeHg toxicokinetics. The ATP-binding cassette (ABC) transporters Multidrug resistance-associated protein 1 (MRP1, gene name ATP-Binding Cassette, Sub-Family C (CFTR/MRP), Member 1 (ABCC1)), Multidrug resistance-associated protein 1 (MRP2, gene name ATP-Binding Cassette, Sub-Family C (CFTR/MRP), Member 2 (ABCC2)) and Multidrug resistance protein 1 (MDR1, gene name ATP-Binding Cassette, Sub-Family B (MDR/TAP), Member MDR1 (ABCB1) are the best-characterized ABC transporters. ABCC1 and ABCC2 have been associated with MeHg accumulation and toxicity in fruit flies and mice () (Bridges and Zalups 2005; Prince et al. 2014; Toyama et al. 2011). The role of ABCB1 in MeHg transport and toxicity is not yet known. These three ABC transporter genes are highly conserved across species and are abundant in tissues where MeHg transport is most critical (e.g. blood-brain-barrier, liver, gut and the placenta). The role of ABC transporters in MeHg transport suggests that single nucleotide polymorphisms (SNPs) in ABC transporters may influence MeHg body burden in both mother and fetus during pregnancy. Indeed, in a study based on two European birth cohorts, it was found that child SNPs in ABCC1, ABCC2, and ABCB1 modified the relationship between maternal fish consumption and cord blood Hg concentrations (Llop et al. 2014). However, it is not known whether ABC SNPs influence the concentration of maternal hair Hg, a biomarker often used as a proxy for prenatal exposure to MeHg (Davidson et al. 2008). The potential influence of ABC genotype on MeHg body burden in pregnant mothers or their children may mediate adverse associations with developmental outcomes; however, few studies have investigated the association between ABC SNPs and child neurodevelopment directly. The current study comprises a mother-child cohort from the Seychelles Child Development Study (SCDS), characterized by high fish intake and hair Hg concentrations which are substantially higher than in many other populations. Here, we characterize the associations of maternal SNPs in ABC transporters with hair Hg concentrations during pregnancy and with child neurodevelopmental outcomes.
2. Methods
2.1 Study population
The SCDS is a longitudinal observational study conducted in the Republic of Seychelles, an archipelago in the Indian Ocean. The population resides mainly on the island of Mahé and is of mixed African, European, and East Asian origin. The overall aim of the SCDS is to investigate the effects of MeHg exposure during pregnancy on child developmental outcomes. Healthy mothers were recruited to Nutrition Cohort 2 (NC2) during their first antenatal visit (from 14 weeks of gestation) at eight health centres across Mahé. Mothers were enrolled from 2008 until 2011 when the target number of 1500 mothers had consented (Strain et al. 2015). Mothers with double pregnancies were only counted once in analyses of developmental outcomes (one of each sibling pair was removed randomly). One hair Hg value was an outlier (194.3 ppm, the next highest observed was 31.66 ppm); the Hg was found to be primarily inorganic and this value was therefore excluded from the Hg analyses. After exclusions owing to missing data (Strain et al. 2015), there were 1313 mothers who were included in the analyses of MeHg toxicokinetics and 1331 mother-child pairs were included in analyses of developmental outcomes. Further information on inclusion criteria and power calculations has previously been described (Strain et al. 2015). The study was reviewed and approved by the Seychelles Ethics Board, the Research Subjects Review Board at the University of Rochester, and the Regional Ethics Committee at Lund University, Sweden.
2.2 Hair Hg analyses
Hair samples were cut at delivery and the longest available segment of maternal hair growing during gestation was analysed assuming a hair growth rate of 1.1 cm/month. Total mercury in maternal hair during gestation is a known biomarker for prenatal MeHg exposure and was measured by cold-vapor Atomic-Absorption-Spectrometry as previously described (Cernichiari et al. 1995) and reported in parts per million (ppm).
2.3 Developmental assessment
When infants were aged approximately 20 months, they completed developmental testing with a Creole version of the Bayley Scales of Infant Development (BSID-II), which has been successfully used in a previous Seychellois cohort (Davidson et al. 2008) as well as in the current NC2 cohort (Strain et al. 2015). Testing was conducted by specially trained nurses at the Child Development Centre, Victoria, Mahé. All study forms were shipped to the University of Rochester, where data were double-entered and the Mental Development Index (MDI) and Psychomotor Development Index (PDI) endpoints were scaled according to the child’s age at testing. Test reliability for the BSID-II was determined as previously described (Strain et al. 2015).
2.4 DNA extraction and genotyping
DNA was extracted from maternal blood using the Qiagen DNA Blood Mini kit (Qiagen, Hilden, Germany). SNPs were genotyped by the iPLEX® Gold assay on the MassARRAY platform (SequenomTM, San Diego, USA) and by TaqMan allelic discrimination assay on an ABI 7900 instrument (Applied Biosystems, Foster City, CA, USA), according to the manufacturer’s instructions. We characterized the variation in the ABC genes by choosing TagSNPs that capture as much of the genetic variation within a gene as possible due to linkage disequilibrium with other (not genotyped) SNPs. TagSNPs were selected according to HapMap data (Thorisson et al. 2005) for YRI (Yoruba in Ibadan, Nigeria) as a proxy for African populations, since earlier screenings of this population have shown that the allele frequencies are more similar to YRI than the other Hapmap populations (Yeates et al. 2015). In total, we genotyped 15 SNPs (description of all SNPs is found in Table 1) including the three SNPs that previously had been linked to cord blood Hg in Mediterranean cohorts: ABCC1 rs11075290, ABCC2 rs2273697, and ABCB1 rs2032582 (Llop et al. 2014). ABCB1 rs2032582 is tri-allelic and was genotyped by two different TaqMan assays to capture all three alleles. Five percent of the samples were re-analyzed for quality control purposes with perfect agreement between original and repeat genotyping runs for all SNPs.
Table 1.
Single nucleotide polymorphisms (SNPs) included in the NC2 study. All genotyped individuals included in either the association analyses with hair Hg or with BSID analyses are included (n=1410–1416 depending on the SNP).
| Gene | SNPa | SNP typeb | Functional effectc | Allele freq. NC2 |
Allele freq. YRI d |
Allele freq. CEU e |
|---|---|---|---|---|---|---|
| ABCC1 | rs215088 | Intronic A/G | regulatory variant - enhancer | 0.41 (A) | 0.59 | 0.29 |
| ABCC1 | rs1292798 | Intronic G/T | regulatory variant - promotor flanking | 0.05 (T) | 0.10 | 0.08 |
| ABCC1 | rs1107529 | Intronic C/T | regulatory variant - promotor flanking | 0.37 (T) | 0.30 | 0.55 |
| ABCC1 | rs246241 | Intronic G/T | regulatory variant - promotor flanking | 0.24 (T) | 0.26 | 0.11 |
| ABCC1 | rs212093 | 5’ near gene G/A | no predicted change of function | 0.41 (A) | 0.38 | 0.57 |
| ABCC2 | rs717620 | 5’ untranslated region C/T | regulatory variant – promotor | 0.10 (T) | 0.03 | 0.21 |
| ABCC2 | rs2756103 | Intronic A/C | regulatory variant - promotor flanking | 0.29 (C) | 0.23 | 0.42 |
| ABCC2 | rs7393105 | Intronic A/C | no predicted change of function | 0.36 (C) | 0.40 | 0.42 |
| ABCC2 | rs2273697 | Non-synonymous, | predicted tolerated | 0.20 (A) | 0.25 | 0.20 |
| ABCB1 | rs2032582 | Non-synonymous, Ala(G)/Ser(T) /Thr(A) |
Ser ->Ala predicted tolerated Ser ->Thr predicted deleterious |
0.79(G)/ 0.18(T)/ 0.02(A) |
100 (G) |
0.56/0.43/ 0.01 |
| ABCB1 | rs2235035 | Intronic G/A | no predicted change of function | 0.21 (A) | 0.21 | 0.31 |
| ABCB1 | rs1027458 | Intronic G/A | no predicted change of function | 0.16 (A) | 0.20 | 0.13 |
| ABCB1 | rs1202169 | Intronic T/C | no predicted change of function | 0.34 (C) | 0.19 | 0.42 |
| ABCB1 | rs1202171 | Intronic T/A | no predicted change of function | 0.25 (T) | 0.36 | 0.37 |
| ABCB1 | rs1027649 | Intronic C/T | no predicted change of function | 0.38 (C) | 0.35 | 0.06 |
SNPs are ordered according to their position in the gene at 5’ to 3’ direction, according to Human genome assembly 38 (GRCh38). ABCB1 is situated on chromosome 7, ABCC1 on chromosome 16, and ABCC2 on chromosome 10.
Ancestral allele is denoted first.
According to www.ensembl.org. Amino acid exchange predictions are from “Sorting Intolerant from tolerant” (SIFT) and from PolyPhen-2 (Polymorphism Phenotyping v2) at Ensembl.
Data from Hapmap (www.hapmap.org) for an African population (YRI, Yoruba in Ibadan, Nigeria).
Data from Hapmap (www.hapmap.org) for a European population (CEU, Utah Residents with Northern and Western European ancestry).
2.5 Statistical analyses
Deviations from Hardy-Weinberg equilibrium were tested using chi-square analysis. Linkage disequilibrium was evaluated using Haploview (Barrett et al. 2005). Tests for associations between outcomes and SNPs were carried out from a priori analysis plans and all associations were evaluated using two-sided tests of significance at the α=0.05 level. For the tri-allelic ABCB1 rs2032582 we excluded genotypes with the A-allele due to allele frequency <5% (there were 60 subjects with GA, AT and AA genotype removed from the analysis of genetic association with maternal hair Hg concentrations and 61 from the analysis of genetic associations with child BSID-II); after this removal there were three SNP levels. All statistical analyses were undertaken using R (version 3.0.2; The R Foundation for Statistical Computing).
Simple linear regression with no covariate adjustment (assuming that fish consumption patterns and other determinants of MeHg exposure are similar for mothers with different SNPs) was used to estimate the association of each of the ABC SNPs with maternal hair Hg concentrations. We used a 2 degree of freedom test to evaluate differences in hair Hg across the three levels of each SNP. Multiple linear regression was also used to estimate the association of ABC SNPs with BSID-II scores and these were adjusted for covariates previously chosen to cover the most important determinants of neurocognitive development in children (Strain et al. 2015).
The covariates included child sex, maternal age at delivery, presence of two parents in the household, Hollingshead socioeconomic score, and child age at testing. The models for the BSID MDI and PDI did not include maternal hair Hg because as a potential mediator it would affect our ability to estimate the direct association between SNPs and BSID scores. Because there were many missing values for maternal hair Hg, our sample sizes for these analyses were considerably larger than those reported in Strain et al. (2015).
3. Results
Summary statistics for the cohort are shown in Table 2. All SNPs were in Hardy-Weinberg equilibrium. ABCC2 (rs7393105 and rs2756103) were in linkage disequilibrium (R2 = 0.72), while all other pairwise combinations of SNPs had a R2 lower than 0.3.
Table 2.
Summary statistics for the Nutrition Cohort 2 in the Seychelles Child Development Study.
| Variable | N | Mean | SD |
|---|---|---|---|
| Maternal hair Hg (ppm) | 1313 | 3.94 | 3.47 |
| Fish meals per week | 1243 | 8.58 | 4.63 |
| Birthweight (g) | 1305 | 3172 | 498 |
| Gestational age (weeks) | 1262 | 38.96 | 1.61 |
| BSID score MDI | 1327 | 87.63 | 10.74 |
| BSID score PDI | 1325 | 96.69 | 10.59 |
| % Girls | 1331 | 48% | |
| % Two parents in the household |
1331 | 73% | |
| Maternal age (years) | 1331 | 27.06 | 6.29 |
| Hollingshead SES | 1331 | 32.04 | 10.35 |
Abbreviations: N= Number of individuals, SD = Standard deviation, Hg = mercury,
SNPs in all three ABC genes were significantly associated (p<0.050) with maternal hair Hg (Table 3). None of these SNPs were in linkage disequilibrium. Three SNPs in ABCC1 (rs11075290, rs212093, and rs215088), one SNP in ABCC2 (rs717620), and three SNPs in ABCB1 (rs10276499, rs1202169, and rs2032582) were associated with hair Hg concentrations, and all but two (ABCC1 rs212093 and rs215088) showed an alleleconcentration effect. For example, the mean hair Hg among CC carriers of rs11075290 was 1 ppm (~20%) lower than the mean hair Hg among TT carriers. Using Hapmap data, we compared this population with those of African and European ancestry. The alleles associated with higher concentrations of Hg in hair in this study (Table 3) showed in general a higher allele frequency in Hapmap individuals with European ancestry, but a lower allele frequency in Hapmap individuals with African ancestry, compared with in NC2 (Table 1).
Table 3.
Associations between maternal ABC genotypes, maternal hair Hg, and the BSID MDI and PDI a.
| Gene/SNP | Hair Hg | MDI | PDI | |||||||||
|---|---|---|---|---|---|---|---|---|---|---|---|---|
| N | Mean | P | N | Mean | β | P | N | Mean | β | P | ||
| ABCC1 (MRP1) | ||||||||||||
| rs215088 | G | 47 | 4.3 |
0.01 3 |
480 | 87.6 | - | 0.3 4 |
479 | 96.8 | - | 0.42 |
| G | 0 | 3.7 | 621 | 88.0 | 0.4 | 621 | 96.3 | −0.39 | ||||
| G | 62 | 3.8 | 226 | 86.8 | 2 | 225 | 97.4 | 0.67 | ||||
| A | 2 | - | ||||||||||
| A | 22 | 0.7 | ||||||||||
| A | 1 | 5 | ||||||||||
| rs1292798 0 |
G | 11 | 3.9 | 0.09 | 119 | 87.6 | - | 0.7 0 |
119 | 96.5 | - | 0.08 0 |
| G | 84 | 4.4 | 7 | 88.4 | 0.8 | 6 | 98.7 | 2.47 | ||||
| GT | 12 | 6.5 | 127 | 87.3 | 5 | 126 | 95.7 | −1.26 | ||||
| TT | 5 | 3 | 0.2 | 3 | ||||||||
| 4 | 7 | |||||||||||
| rs1107529 0 |
CC | 54 | 3.6 |
<0.0 01 |
545 | 87.2 | - |
0.0 42 |
547 | 95.7 | - |
0.00 2 |
| CT | 3 | 4.0 | 560 | 87.4 | 0.2 | 556 | 97.0 | 1.23 | ||||
| TT | 55 | 4.7 | 216 | 89.2 | 7 | 216 | 98.6 | 2.95 | ||||
| 3 | 1.9 | |||||||||||
| 21 | 2 | |||||||||||
| 1 | ||||||||||||
| rs246241 | G | 74 | 4.0 | 0.22 | 756 | 87.8 | - | 0.5 2 |
754 | 96.9 | - | 0.60 |
| G | 6 | 4.0 | 493 | 87.5 | - | 493 | 96.3 | −0.52 | ||||
| GT | 49 | 3.3 | 78 | 86.4 | 0.1 | 78 | 97.1 | 0.38 | ||||
| TT | 2 | 7 | ||||||||||
| 75 | - | |||||||||||
| 1.0 | ||||||||||||
| 9 | ||||||||||||
| rs212093 | G | 46 | 3.6 |
0.00 7 |
468 | 88.2 | - | 0.3 6 |
467 | 96.7 | - | 0.78 |
| G | 0 | 4.2 | 638 | 87.3 | - | 638 | 96.9 | 0.14 | ||||
| G | 63 | 3.8 | 219 | 87.5 | 0.9 | 218 | 96.3 | −0.45 | ||||
| A | 8 | 4 | ||||||||||
| A | 21 | - | ||||||||||
| A | 3 | 0.8 | ||||||||||
| 5 | ||||||||||||
| ABCC2 (MRP2 | ||||||||||||
| rs717620 | CC | 10 | 3.8 |
<0.0 01 |
106 | 87.8 | - | 0.5 2 |
106 | 96.8 | - | 0.41 |
| CT | 56 | 4.4 | 6 | 87.2 | - | 5 | 96.0 | −0.72 | ||||
| TT | 24 | 7.6 | 249 | 85.1 | 0.2 | 248 | 98.7 | 1.92 | ||||
| 4 | 12 | 3 | 12 | |||||||||
| 13 | - | |||||||||||
| 2.0 | ||||||||||||
| 9 | ||||||||||||
| rs2756103 | A | 67 | 3.8 | 0.25 | 689 | 87.8 | - | 0.6 3 |
685 | 96.9 | - | 0.60 |
| A | 9 | 4.0 | 528 | 87.5 | - | 529 | 96.3 | −0.51 | ||||
| A | 52 | 4.4 | 110 | 86.9 | 0.3 | 111 | 97.0 | 0.07 | ||||
| C | 3 | 4 | ||||||||||
| CC | 11 | - | ||||||||||
| 1 | 0.8 | |||||||||||
| 7 | ||||||||||||
| rs7393105 | A | 54 | 3.9 | 0.52 | 554 | 87.8 | - | 0.8 8 |
551 | 97.0 | - | 0.47 |
| A | 5 | 3.9 | 608 | 87.5 | - | 608 | 96.3 | −0.73 | ||||
| A | 60 | 4.2 | 165 | 87.4 | 0.2 | 166 | 96.9 | −0.11 | ||||
| C | 5 | 8 | ||||||||||
| CC | 16 | - | ||||||||||
| 3 | 0.2 | |||||||||||
| 2 | ||||||||||||
| rs2273697 | G | 84 | 3.9 | 0.94 | 849 | 87.8 | - | 0.6 | 849 | 96.6 | - | 0.89 |
| G | 3 | 3.9 | 428 | 87.3 | - | 4 | 427 | 96.9 | 0.37 | |||
| G | 42 | 4.1 | 50 | 87.3 | 0.3 | 49 | 96.2 | −0.45 | ||||
| A | 1 | 1 | ||||||||||
| A | 49 | - | ||||||||||
| A | 0.5 | |||||||||||
| 2 | ||||||||||||
| ABCB1 (MDR1) | ||||||||||||
| rs2032582 | G | 84 | 3.6 |
<0.0 01 |
848 | 87.5 | - | 0.0 77 |
848 | 96.9 | - | 0.11 |
| G | 0 | 4.4 | 364 | 87.7 | 0.0 | 364 | 96.1 | −0.86 | ||||
| GT | 35 | 5.6 | 54 | 90.8 | 9 | 54 | 99.1 | 1.75 | ||||
| TT | 7 | 1.7 | ||||||||||
| 56 | 3 | |||||||||||
| rs2235035 | G | 82 | 3.9 | 0.69 | 832 | 87.7 | - | 0.9 6 |
832 | 96.3 | - | 0.30 |
| G | 1 | 4.0 | 434 | 87.5 | - | 434 | 97.3 | 0.88 | ||||
| G | 43 | 4.3 | 61 | 87.7 | 0.1 | 59 | 97.4 | 0.94 | ||||
| A | 0 | 5 | ||||||||||
| A | 62 | 0.0 | ||||||||||
| A | 2 | |||||||||||
| rs1027458 7 |
G | 92 | 4.0 | 0.58 | 942 | 87.5 | - | 0.5 4 |
939 | 96.8 | - | 0.74 |
| G | 9 | 3.8 | 340 | 87.6 | 0.0 | 341 | 96.3 | −0.56 | ||||
| G | 34 | 3.6 | 44 | 89.3 | 7 | 44 | 97.2 | 0.45 | ||||
| A | 1 | 1.8 | ||||||||||
| A | 42 | 5 | ||||||||||
| A | ||||||||||||
| rs1202169 | TT | 56 | 3.7 |
0.00 6 |
572 | 87.5 | - | 0.9 2 |
570 | 97.2 | - | 0.32 |
| TC | 4 | 4.0 | 606 | 87.7 | - | 606 | 96.3 | −0.95 | ||||
| CC | 59 | 4.7 | 147 | 87.9 | 0.1 | 147 | 96.4 | −0.87 | ||||
| 9 | 1 | |||||||||||
| 14 | - | |||||||||||
| 8 | 0.1 | |||||||||||
| 8 | ||||||||||||
| rs1202171 | A | 74 | 4.1 | 0.25 | 753 | 87.6 | - | 0.6 3 |
749 | 96.7 | - | 0.99 |
| A | 5 | 3.7 | 498 | 87.4 | - | 500 | 96.7 | −0.05 | ||||
| AT | 49 | 4.0 | 76 | 88.7 | 0.1 | 76 | 96.6 | 0.09 | ||||
| TT | 9 | 7 | ||||||||||
| 69 | 1.0 | |||||||||||
| 3 | ||||||||||||
| rs1027649 9 |
TT | 50 | 4.4 |
<0.0 01 |
510 | 87.9 | - | 0.0 65 |
509 | 96.3 | - | 0.27 |
| TC | 7 | 3.8 | 610 | 87.9 | 0.2 | 609 | 97.2 | 0.86 | ||||
| CC | 60 | 3.2 | 206 | 86.1 | 3 | 206 | 96.1 | −0.13 | ||||
| 2 | - | |||||||||||
| 20 | 1.3 | |||||||||||
| 3 | 7 | |||||||||||
The hair Hg model is unadjusted, so the p-values test for differences between the three means.
The homozygote for the most common allele is used as reference. The beta coefficients (β) for the MDI and PDI models are adjusted for child sex, maternal age at delivery, presence of two parents in the household, Hollingshead socioeconomic score, and child age at testing. The p-values from the sequential sum of squares test for differences in the effect of SNP and are unadjusted for the other covariates.
SNP: single nucleotide polymorphism.
In our analysis of maternal ABC genotypes in relation to the neurodevelopment of their children we found that only ABCC1 rs11075290 was significantly associated with MDI and PDI (Table 3). Mothers with the CC variant had the lowest hair Hg concentrations, but the children born to them showed poorer performance. Their children averaged 2 points lower for the MDI and 3 points lower for the PDI than children born to mothers with TT variant who had higher hair Hg. No other clear patterns of associations were found between the BSID-II outcomes and ABC SNPs.
4. Discussion
This study suggests that genetic differences in ABC transporters influence human MeHg body burden; seven out of 15 ABC SNPs genotyped were significantly associated with concentrations of Hg in hair among mothers in a cohort with high fish consumption and a mean hair Hg concentration of 3.9 ppm. Among the various maternal ABC transporter genotypes that were associated with Hg in hair, only one SNP, in ABCC1 (rs11075290), was associated with child BSID scores. No other clear pattern of association with developmental outcomes was observed. Based on the strong association of ABC genotype with maternal hair Hg concentrations we predict that the ABC transporter genotype of the child may also play a role in the child’s MeHg body burden. Importantly, these transporters are intrinsic components of the placenta and the blood-brain barrier and thus could influence brain exposure to MeHg in the developing child.
It should however be stressed that ABC transporters transports a number of different molecules and are thus not specific for MeHg transport. Consequently, the associations between ABC transporters and neurodevelopment may be blurred by the transport of other compounds that may influence neurodevelopmental outcomes. The involvement of ABCC1/MRP1 in human MeHg distribution and elimination was suggested by findings from experimental studies. Knocking down ABCC1 in fruit flies resulted in accumulation of MeHg and greater developmental toxicity measured as eclosion (Prince et al. 2014) and overexpression of the ABCC1/MRP1 protein in mice resulted in decreased accumulation of MeHg in brain and liver (Toyama et al. 2011). However, we do not presently know the role of ABCC1/MRP1 in altering MeHg body burden in humans, and particularly during pregnancy. The ABCC1/MRP1 protein is expressed in several tissues that are critical in absorption, distribution and excretion of MeHg, both in the mother and the fetus. ABCC1/MRP1 expression occurs in many tissues (www.proteinatlas.org), including the placenta (Aye et al. 2007), the blood-brain barrier (Leslie et al. 2005), the intestine (Berggren et al 2007) and the hair follicle (Haslam et al. 2013). Its expression in the hair follicle is of particular relevance when considering hair as the biomarker of exposure as used in this study. During hair synthesis MeHg from the bloodstream is transported to keratinocytes in the follicle that, subsequent to differentiation and death, are incorporated in the matrix of the growing hair shaft (Kempson and Lombi 2011; Zareba et al. 2008). Nonetheless, information about the apical/basal orientation of ABCC1/MRP1 within the hair follicle, and other tissues, is limited and it is therefore difficult to predict how the genotype ultimately influences the kinetics of MeHg transport and distribution in various compartments of the body.
Among the 15 SNPs investigated, just one SNP, rs11075290 in ABCC1, was associated with both maternal hair Hg concentrations and child BSID scores. It is positioned in the first intron of the ABCC1 gene in a promoter flanking region. The C allele creates a CpG site, which can be methylated and potentially result in lower expression of ABCC1. Nevertheless, the function of this SNP has not been tested in vitro and is uncertain. Its impact on MeHg transport and distribution at the level of the placental/fetal circulation remains unclear. Thus, in contrast to the strong association between maternal ABC genotype and a maternal mercury disposition phenotype, the impact at the level of developmental phenotype in the offspring is less certain. The association with developmental phenotype is likely to be determined also by the child’s ABC genotype. Future analyses incorporating the children’s ABC SNPs are needed to determine if there are susceptible sub-populations that can be identified. It is also possible that our findings reflect linkage disequilibrium of this SNP with other functional SNPs not yet characterized.
We did not include Hg in hair in the model for the association between ABC genotype and neurodevelopment. If ABC genotype would have been clearly associated with neurodevelopmental outcomes then it would have been appropriate to conduct a mediation model including Hg in hair. However, in the absence of clear associations of ABC genotype with neurodevelopmental outcomes as well as Hg in hair and neurodevelopmental outcomes (Davidson et al. 1998; Myers et al. 2003; Strain et al. 2015), and recognizing the broad functions of ABC transporters, we did not conduct a mediation analysis that included Hg in hair as a covariate in the model.
We found that additional SNPs in ABCC1, ABCC2, and ABCB1 were also associated with hair Hg, and are thus candidates to explore for a role in MeHg transport, distribution and elimination. The ABC SNPs varied in allele frequency when comparing NC2 with individuals from Hapmap with European and African ancestry: alleles associated with elevated Hg in hair were in general higher in frequency in Hapmap individuals with European ancestry. Further studies on the role of ABC SNPs for MeHg concentrations in different tissues, such as blood and brain, will facilitate understanding of individual differences in Hg distribution and elimination. Such studies will potentially help us to identify susceptible groups. An earlier study found that the promoter-associated rs717620 (http://www.ensembl.org) was correlated with urinary Hg concentrations (a marker of inorganic Hg) among gold miners (Engstrom et al. 2013). The rs717620 A-allele carriers had higher Hg concentrations in urine than individuals with the GG genotype. A parallel pattern was seen for hair Hg in this study, where the A-allele was associated with higher hair Hg concentrations, suggesting that this SNP may act to influence overall transport and elimination of mercury.
Strengths of this study include the large well-characterized cohort and extensive information about sequence variation in some genes encoding potential transporters for MeHg. The lack of genetic data for the children is a limitation, but further studies aim to characterize more fully the contribution of child genotype on MeHg body burden and cognitive outcomes.
5. Conclusions
We found that SNPs in genes coding for three ABC transporter genes are associated with maternal hair Hg concentrations in a population consuming large quantities of ocean fish. These findings suggest that genetics may play a role in determining maternal, and thus prenatal, MeHg exposure. While consistent associations with BSID outcomes were not observed, we cannot exclude the possibility that ABC transporter genes play a role in influencing child MeHg body burden and possibly neurodevelopmental outcomes. Further studies are needed to explore the functional consequences of these polymorphisms, importantly, extending the study to the child’s ABC transporters, to fully understand effects on MeHg toxicokinetics and MeHg-related effects on neurodevelopment.
Highlights.
SNPs in three ABC transporter genes were associated with hair mercury in mothers
Maternal ABCC1 SNP rs11075290 was associated with child neurodevelopment
Genetics of ABC may determine prenatal methylmercury concentrations.
Acknowledgments
We gratefully acknowledge the participation of all women and children who took part in the study and the nursing staff from the Child Development Centre, Seychelles for their assistance with data collection.
Supported by the US National Institute of Health (grants R01-ES010219 and P30-ES01247), The Swedish Research Council for Health, Working Life and Welfare (FORTE), Swedish Research Council for Environment, Agricultural Sciences and Spatial Planning (FORMAS), and in-kind support from the Government of Seychelles. The study sponsors had no role in the design, collection, analysis, or interpretation of data, in the writing of this article, or in the decision to submit the article for publication.
Glossary
- ABC
ATP-binding cassette
- ABCB1
ATP-Binding Cassette, Sub-Family B (MDR/TAP), Member 1
- ABCC1
ATP-Binding Cassette, Sub-Family C (CFTR/MRP), Member 1
- ABCC2
ATP-Binding Cassette, Sub-Family C (CFTR/MRP), Member 2
- BSID-II
Bayley scales of infant development II
- MDI
mental development index
- MDR1
multidrug resistance protein 1
- MeHg
methylmercury
- MRP1
Multidrug resistance-associated protein 1
- MRP2
Multidrug resistance-associated protein 2
- NC2
nutrition cohort 2
- PDI
psychomotor development index
- SCDS
Seychelles child development study
- SNP
single nucleotide polymorphism
Footnotes
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References
- Aye IL, Paxton JW, Evseenko DA, Keelan JA. Expression, localisation and activity of ATP binding cassette (ABC) family of drug transporters in human amnion membranes. Placenta. 2007;28:868–877. doi: 10.1016/j.placenta.2007.03.001. [DOI] [PubMed] [Google Scholar]
- Barrett JC, Fry B, Maller J, Daly MJ. Haploview: Analysis and visualization of ld and haplotype maps. Bioinformatics. 2005;21:263–265. doi: 10.1093/bioinformatics/bth457. [DOI] [PubMed] [Google Scholar]
- Berggren S, Gall C, Wollnitz N, Ekelund M, Karlbom U, Hoogstraate J, Schrenk D, Lennernäs H. Gene and protein expression of P-glycoprotein, MRP1, MRP2, and CYP3A4 in the small and large human intestine. Mol Pharm. 2007;4:252–257. doi: 10.1021/mp0600687. 2007. [DOI] [PubMed] [Google Scholar]
- Bridges CC, Zalups RK. Molecular and ionic mimicry and the transport of toxic metals. Toxicol Appl Pharmacol. 2005;204:274–308. doi: 10.1016/j.taap.2004.09.007. [DOI] [PMC free article] [PubMed] [Google Scholar]
- Cernichiari E, Toribara TY, Liang L, Marsh DO, Berlin MW, Myers GJ, et al. The biological monitoring of mercury in the seychelles study. Neurotoxicology. 1995;16:613–628. [PubMed] [Google Scholar]
- Crump KS, Kjellström T, Shipp AM, Silvers A, Stewart A. Influence of prenatal mercury exposure upon scholastic and psychological test performance: benchmark analysis of a New Zealand cohort. Risk Anal. 1998;18:701–713. doi: 10.1023/b:rian.0000005917.52151.e6. [DOI] [PubMed] [Google Scholar]
- Daniels JL, Longnecker MP, Rowland AS, Golding J The ALSPAC Study Team–University of Bristol Institute of Child Health. Fish intake during pregnancy and early cognitive development of offspring. Epidemiology. 2004;15:394–402. doi: 10.1097/01.ede.0000129514.46451.ce. [DOI] [PubMed] [Google Scholar]
- Davidson PW, Myers GJ, Cox C, Axtell C, Shamlaye C, Sloane-Reeves J, et al. Effects of prenatal and postnatal methylmercury exposure from fish consumption on neurodevelopment: outcomes at 66 months of age in the Seychelles Child Development Study. JAMA. 1998;280:701–707. doi: 10.1001/jama.280.8.701. [DOI] [PubMed] [Google Scholar]
- Davidson PW, Strain JJ, Myers GJ, Thurston SW, Bonham MP, Shamlaye CF, et al. Neurodevelopmental effects of maternal nutritional status and exposure to methylmercury from eating fish during pregnancy. Neurotoxicology. 2008;29:767–775. doi: 10.1016/j.neuro.2008.06.001. [DOI] [PMC free article] [PubMed] [Google Scholar]
- Engstrom K, Ameer S, Bernaudat L, Drasch G, Baeuml J, Skerfving S, et al. Polymorphisms in genes encoding potential mercury transporters and urine mercury concentrations in populations exposed to mercury vapor from gold mining. Environ Health Perspect. 2013;121:85–91. doi: 10.1289/ehp.1204951. [DOI] [PMC free article] [PubMed] [Google Scholar]
- Food and Agriculture Organization of the United Nations/World Health Organization (FAO/WHO) Joint fao/who expert consultation on the risks and benefits of fish consumption. 2011 Report. http://www.fao.org/docrep/014/ba0136e/ba0136e00.pdf.
- Grandjean P, Weihe P, White RF, Debes F, Araki S, Yokoyama K, et al. Cognitive deficit in 7-year-old children with prenatal exposure to methylmercury. Neurotoxicol Teratol. 1997;19:417–428. doi: 10.1016/s0892-0362(97)00097-4. [DOI] [PubMed] [Google Scholar]
- Haslam IS, Pitre A, Schuetz JD, Paus R. Protection against chemotherapy-induced alopecia: Targeting atp-binding cassette transporters in the hair follicle? Trends Pharmacol Sci. 2013;34:599–604. doi: 10.1016/j.tips.2013.09.001. [DOI] [PubMed] [Google Scholar]
- Kempson IM, Lombi E. Hair analysis as a biomonitor for toxicology, disease and health status. Chemical Society reviews. 2011;40:3915–3940. doi: 10.1039/c1cs15021a. [DOI] [PubMed] [Google Scholar]
- Leslie EM, Deeley RG, Cole SP. Multidrug resistance proteins: Role of p-glycoprotein, mrp1, mrp2, and bcrp (abcg2) in tissue defense. Toxicol Appl Pharmacol. 2005;204:216–237. doi: 10.1016/j.taap.2004.10.012. [DOI] [PubMed] [Google Scholar]
- Llop S, Guxens M, Murcia M, Lertxundi A, Ramon R, Riaño I, et al. Prenatal exposure to mercury and infant neurodevelopment in a multicenter cohort in Spain: study of potential modifiers. Am J Epidemiol. 2012;175:451–465. doi: 10.1093/aje/kwr328. [DOI] [PubMed] [Google Scholar]
- Llop S, Engstrom K, Ballester F, Franforte E, Alhamdow A, Pisa F, et al. Polymorphisms in abc transporter genes and concentrations of mercury in newborns--evidence from two mediterranean birth cohorts. PloS one. 2014;9:e97172. doi: 10.1371/journal.pone.0097172. [DOI] [PMC free article] [PubMed] [Google Scholar]
- Llop S, Ballester F, Broberg K. Effect of gene-mercury interactions on mercury toxicokinetics and neurotoxicity. Curr Environ Health Rep. 2015;2:179–194. doi: 10.1007/s40572-015-0047-y. [DOI] [PubMed] [Google Scholar]
- Myers GJ, Davidson PW, Cox C, Shamlaye CF, Palumbo D, Cernichiari E, et al. Prenatal methylmercury exposure from ocean fish consumption in the Seychelles child development study. Lancet. 2003;361:1686–1692. doi: 10.1016/S0140-6736(03)13371-5. [DOI] [PubMed] [Google Scholar]
- Oken E, Wright RO, Kleinman KP, Bellinger D, Amarasiriwardena CJ, Hu H, et al. Maternal fish consumption, hair mercury, and infant cognition in a U.S. Cohort. Environ Health Perspect. 2005;113:1376–1380. doi: 10.1289/ehp.8041. [DOI] [PMC free article] [PubMed] [Google Scholar]
- Prince L, Korbas M, Davidson P, Broberg K, Rand MD. Target organ specific activity of drosophila mrp (abcc1) moderates developmental toxicity of methylmercury. Toxicol Sci. 2014;140:425–435. doi: 10.1093/toxsci/kfu095. [DOI] [PMC free article] [PubMed] [Google Scholar]
- Sagiv SK, Thurston SW, Bellinger DC, Amarasiriwardena C, Korrick SA. Prenatal exposure to mercury and fish consumption during pregnancy and attention-deficit/hyperactivity disorder-related behavior in children. Arch Pediatr Adolesc Med. 2012;166:1123–1131. doi: 10.1001/archpediatrics.2012.1286. [DOI] [PMC free article] [PubMed] [Google Scholar]
- Strain JJ, Yeates AJ, Van Wijngaarden E, Thurston SW, Mulhern MS, McSorley EM, et al. Prenatal exposure to methyl mercury and polyunsaturated fatty acids from fish consumption: Associations with children’s development at 20 months of age in the republic of seychelles. Am J Clin Nutr. 2015 doi: 10.3945/ajcn.114.100503. [DOI] [PMC free article] [PubMed] [Google Scholar]
- Thorisson GA, Smith AV, Krishnan L, Stein LD. The international hapmap project web site. Genome Res. 2005;15:1592–1593. doi: 10.1101/gr.4413105. [DOI] [PMC free article] [PubMed] [Google Scholar]
- Toyama T, Shinkai Y, Yasutake A, Uchida K, Yamamoto M, Kumagai Y. Isothiocyanates reduce mercury accumulation via an nrf2-dependent mechanism during exposure of mice to methylmercury. Environ Health Perspect. 2011;119:1117–1122. doi: 10.1289/ehp.1003123. [DOI] [PMC free article] [PubMed] [Google Scholar]
- Yeates AJ, Love TM, Engstrom K, Mulhern MS, McSorley EM, Grzesik K, et al. Genetic variation in fads genes is associated with maternal long-chain pufa status but not with cognitive development of infants in a high fish-eating observational study. Prostaglandins Leukot Essent Fatty Acids. 2015 doi: 10.1016/j.plefa.2015.08.004. [DOI] [PMC free article] [PubMed] [Google Scholar]
- World Health organization (WHO) Health risks of heavy metals from long-range transboundary air pollution. 2007 Available: Http://www.Euro.Who.Int/__data/assets/pdf_file/0007/78649/e91044.Pdf.
- Zareba G, Cernichiari E, Goldsmith LA, Clarkson TW. Validity of methyl mercury hair analysis: Mercury monitoring in human scalp/nude mouse model. J Appl Toxicol. 2008;28:535–542. doi: 10.1002/jat.1307. [DOI] [PubMed] [Google Scholar]
