| Literature DB >> 30815700 |
David M Evans1,2,3, Gunn-Helen Moen4,5, Liang-Dar Hwang1, Debbie A Lawlor2,3,6, Nicole M Warrington1.
Abstract
BACKGROUND: There is considerable interest in estimating the causal effect of a range of maternal environmental exposures on offspring health-related outcomes. Previous attempts to do this using Mendelian randomization methodologies have been hampered by the paucity of epidemiological cohorts with large numbers of genotyped mother-offspring pairs.Entities:
Keywords: DOHaD; Developmental Origins of Health and Disease; Fetal Insulin Hypothesis; Maternal effects; Mendelian randomization; birthweight; fetal effects; offspring genetic effects; type 2 diabetes
Mesh:
Year: 2019 PMID: 30815700 PMCID: PMC6659380 DOI: 10.1093/ije/dyz019
Source DB: PubMed Journal: Int J Epidemiol ISSN: 0300-5771 Impact factor: 7.196
Figure 1.Structural equation model (SEM) used to estimate maternal and offspring genetic effects on birthweight. The three observed variables (in squares) denote the birthweight of a UK Biobank individual (BW), the birthweight of their offspring (BWO) and their own genotype (SNP). The latent unobserved variables (in circles) represent the genotypes of the individual’s mother (their offspring’s grandmother; GG) and the genotype of the individual’s first offspring (GO). The total variance of the latent genotypes for the individual’s mother (GG) and offspring (GO) and for the observed SNP variable are set to Φ and are estimated from the data. The causal path between the individual’s own genotype and both their mother and offspring’s latent genotype is set to 0.5. The β and βo path coefficients refer to maternal and offspring genetic effects on birthweight, respectively. The residual error terms for the birthweight of the individual and their offspring are represented by ɛ and ɛ, respectively, and the variance of both these terms is estimated in the structural equation model. The covariance between the error terms is denoted by ρ. The model can be modified easily to include observed genotypes and/or the absence of one of the birthweight phenotypes.
Figure 2.Power to detect maternal effects on birthweight as a function of variance explained. We assume a residual correlation of 0.2 between own birthweight and offspring birthweight and that the same locus exerts a maternal effect only. We compare power for N = 50 000 genotyped mother–offspring pairs (i.e. which is an estimate of the current number of available genotyped mother–offspring pairs worldwide that could be conceivably used for these analyses) with the current number of individuals contributing to the UK Biobank and Early Growth Genetics Consortium Analysis of birthweight (i.e. number of genotyped individuals who have data on their own birthweight and their offspring’s birthweight N = 85 518; number of genotyped individuals who have data on their own birthweight only N = 178 980; number of genotyped individuals who have data on their offspring’s birthweight only N = 93 842) at genome-wide significance (α = 5 × 10–8). Asymptotic power calculations were performed using the ‘Maternal and Offspring Genetic Effects Power Calculator’ (Moen et al., 2019).
Figure 3.Estimated maternal and offspring genetic effects on birthweight for 58 autosomal SNPs robustly associated with birthweight. Squares highlight the subset of SNPs that exert their effects predominantly through the mother’s genome (Pmaternal < 0.001 and Poffspring > 0.5). Triangles highlight the subset of SNPs with both maternal and offspring genetic effects operating in opposite directions (Pmaternal < 0.05 and Poffspring < 0.05); the SNPs with their gene names are those previously associated with type 2 diabetes. The figure is based on data presented in Warrington et al. (2018).
Figure 4.Effect sizes and standard errors for 51 autosomal birthweight-associated SNPs, which have a minor allele frequency greater than 1%, estimated from a structural equation model using covariance matrices derived from GWAS summary results of own birthweight and offspring birthweight from the UK Biobank Study. Both GWASs used z-scores of birthweight in a subset of unrelated Europeans, after adjusting for ancestry informative principal components and sex for the individual’s own birthweight (sex was not available for the birthweight of the first child in the UK Biobank Study). The x-axis presents results when the sample overlap is known and the y-axis presents results when the sample overlap is estimated using bivariate LD score regression. The phenotypic correlation between own birthweight and offspring birthweight was assumed to be 0.23 (misspecifying this correlation by small amounts i.e. ρ = 0.1–0.3 did not appear to influence estimates nor their standard errors for these data—results not shown).
Figure 5.Directed acyclic graphs illustrating the core assumptions underlying Mendelian randomization. Assumption (i) requires robust association between the genetic variants and the maternal exposure. Assumption (ii) requires that the genetic variants are uncorrelated with confounders. Assumption (iii) assumes that the genetic variants are only potentially associated with the offspring outcome through the maternal exposure of interest. Offspring genetic variants violate assumption (iii), as they allow a path to offspring outcome that is not through the maternal exposure (iv). However, conditioning on offspring variants (indicated by a box around offspring SNPs) blocks path (iv) and assumption (iii) holds.
Potential limitations of MR studies of maternal exposures and offspring outcomes and suggestions of how to deal with them. We do not list limitations that are endemic to all types of MR studies, but rather focus on issues that are specific to MR studies of maternal exposures and offspring outcomes
| Potential limitation | Description | Solution |
|---|---|---|
| Suitability of genetic variants to proxy maternal environmental exposure of interest | A key question is whether genetic variants identified in GWAS of men and (non-pregnant) women are appropriate instruments for the research question, e.g. if the interest is on the effect of maternal environmental exposures during pregnancy on offspring outcomes, is it appropriate to use SNP effects from a GWAS of the environmental exposure in another population? | Where possible utilize estimates of the association of SNPs with maternal exposures in population of interest during time period of interest |
| Timing of maternal exposure | Since an individual’s genetic variants are present from conception, causal estimates derived from MR studies are often thought to represent life-long effects of the environmental exposure. Interpretation of these estimates may be difficult if the investigator is interested in the effect of the maternal exposure during a particular time period (e.g. prenatal exposures) | See above. |
| Examining the causal effect of paternal exposures on offspring outcomes may be informative. Evidence for similar maternal and paternal effects on offspring outcomes is consistent with post-natal effects of the environmental exposure, whereas evidence for maternal-specific effects on offspring outcomes in the absence of (or considerably weaker) paternal effects is more consistent with prenatal effects of the environmental exposure, although maternal-specific effects for some exposures may reflect a stronger postnatal maternal effect | ||
| Paternal genetic effects | Paternal genotypes at the same (or correlated) SNPs may have effects on the study exposure/outcome. Failure to take these effects into account may result in biased estimates of the causal effect of the maternal exposure on the offspring outcome | Include paternal genotypes in the statistical model where possible |
| Low power | MR studies may have low power because individual SNPs explain small portions of variance in the exposure and the outcome. This potential limitation may be exacerbated in MR studies of maternal exposures because the causal effect of the maternal exposure on the offspring outcome may be smaller than the effect of the maternal exposure on maternal outcomes (as is examined in typical MR studies) | Utilize multiple instruments that explain more variance in the maternal exposure |
| Utilize two-sample MR methods described in this manuscript to increase sample size and statistical power | ||
| Violation of exclusion restriction criteria via offspring genetic effects on offspring outcome | Maternal SNPs may be associated with offspring outcome via their association with offspring genotype violating the exclusion restriction assumption of MR and biasing causal estimates | Perform MR analyses conditioning on offspring genotype |
| Utilize two-sample MR methods described in this manuscript | ||
| Paucity of genotyped mother–offspring pairs | There is a dearth of cohorts worldwide that contain large numbers of genotyped mother–offspring pairs for MR analyses of maternal exposures meaning that these sorts of analyses may lack power | Utilize two-sample MR methods described in this manuscript to combine summary-results information across many different cohorts |
Figure 6.This figure illustrates the four possible ways in which maternal SNPs that are associated with offspring birthweight (conditional on offspring genotype at the same locus) can also be (unconditionally) associated with offspring cardiometabolic disease risk. The ‘X’ represents the effect of conditioning the association analysis on either the offspring or maternal genotype and therefore blocking the path between the conditioned genotype and the other variables of interest. The dashed path with the question mark indicates the potential pleiotropic effects of the offspring’s SNPs on their own cardiometabolic disease risk.
Causal estimates of maternal (and offspring) susceptibility to type 2 diabetes on offspring birthweight using two-sample Mendelian randomization. Results are presented using unadjusted estimates (i.e. estimates of the SNP–birthweight association used in the MR analysis were not corrected for the correlation between maternal and offspring genotypes) and adjusted estimates where the maternal and offspring genetic effects on birthweight were first obtained through the SEM (i.e. estimates of the SNP–birthweight association used in the MR analysis were first corrected for the correlation between maternal and offspring genotypes using the SEM). Causal estimates are presented (β), their standard errors (in parentheses) and P-values from the analysis. Causal estimates represent the estimated difference in mean birthweight in standard deviation units comparing infants whose mothers are susceptible to type 2 diabetes to those mothers who are not (Maternal effect) and the estimated difference in mean birthweight in standard deviation units comparing infants who are themselves susceptible to type 2 diabetes vs those who are not (Offspring effect)
| Adjusted estimates (using SEM) | Unadjusted estimates | |||
|---|---|---|---|---|
| Method | Maternal effect | Offspring effect | Maternal effect | Offspring effect |
| IVW MR | β = 0.036 (0.007), | β = –0.043 (0.007), | β = 0.015 (0.007), | β = –0.024 (0.007), |
| Egger regression | β = 0.030 (0.013), | β = –0.028 (0.014), | β = 0.016 (0.012), | β = –0.013 (0.013), |
IVW MR, inverse variance-weighted Mendelian randomization.
List of cohorts that have maternal genotype data and offspring phenotype data
| Cohort | Approximate number of genotyped mother–phenotyped child pairsa |
|---|---|
| 1958 British Birth Cohort (B85C-T1DGC) | 858 |
| 1958 British Birth Cohort (B85C-WTCCC) | 836 |
| Add Health—National Longitudinal Study of Adolescent to Adult Health | ∼1000 |
| Autism Genome Project (AGP) | 2594 |
| Avon Longitudinal Study of Parents and Children (ALSPAC) | 7304 |
| Berlin Birth Cohort (BBC) | 1357 |
| Born in Bradford Study (BiB) | ∼10 000 |
| Chicago Food Allergy Study | 541 |
| Children’s Hospital of Philadelphia (CHOP) | 312 |
| Copenhagen Prospective Study on Asthma in Childhood (COPSAC-2000) | 282 |
| Danish National Birth Cohort—Genomics of Young Adolescent (DNBC-GOYA) | 1805 |
| Danish National Birth Cohort—Preterm Birth Study (DNBC-PTB) | 1656 |
| deCODE (Genealogy Database) | 54 546 |
| Environmental Risk (E-Risk) Longitudinal Twin Study | 804 |
| Exeter Family Study of Childhood Health (EFSOCH) | 746 |
| Family Atherosclerosis Monitoring In earLY life (FAMILY) study | 406 |
| Finnish Twin Cohort | ∼4000 |
| Hispanic B-cell Acute Lymphoblastic Leukemia Study | 323 |
| HUNT Study | ∼18 000 |
| Hyperglycemia and Adverse Pregnancy Outcome Study (HAPO) | 4437 |
| Millennium Cohort | 12 000 |
| Minnesota Center for Twin and Family Research (MCTFR) | 1404 |
| Netherlands Twin Register (NTR) | 707 |
| Northern Finland 1966 Birth Cohort Study (NFBC1966) | 2035 |
| Norwegian Mother and Child Cohort Study (MoBa) | ∼46 000 |
| Prediction and Prevention of Preeclampsia and Intrauterine Growth Restriction Study (PREDO) | ∼1000 |
| Pune Maternal Nutrition Study (PMNS) | 533 |
| QIMR Berghofer Cohort | 892 |
| Simons Simplex Collection | 2576 |
| Sister Study | 715 |
| STORK Study | 529 |
| STORK Groruddalen | 634 |
| TwinsUK | 1603 |
| UK Biobank | 221 528 |
The number of genotyped mother–phenotyped child duos is based on information provided in peer-reviewed papers including on birthweight and gestational weight gain, on the cohort’s official website or from discussions with the study principal investigators. These numbers are liable to change as more individuals are recruited/genotyped, and should only be considered approximations.
Birthweight only.