Children's Health Volume 121 | Issue 10 | October 2013
Bulky DNA Adducts in Cord Blood, Maternal Fruit-and-Vegetable Consumption, and Birth Weight in a European Mother–Child Study (NewGeneris)
Marie Pedersen,1,2,3 Bernadette Schoket,4 Roger W. Godschalk,5 John Wright,6 Hans von Stedingk,7 Margareta Törnqvist,7 Jordi Sunyer,1,2,8,9 Jeanette K. Nielsen,10 Domenico F. Merlo,11 Michelle A. Mendez,1,12 Helle M. Meltzer,13 Viktória Lukács,4 Anette Landström,14 Soterios A. Kyrtopoulos,15 Katalin Kovács,4 Lisbeth E. Knudsen,10 Margaretha Haugen,13 Laura J. Hardie,16 Kristine B. Gützkow,17 Sarah Fleming,16 Eleni Fthenou,18 Peter B. Farmer,19 Aina Espinosa,1,2,8 Leda Chatzi,18 Gunnar Brunborg,17 Nigel J. Brady,19 Maria Botsivali,15 Khelifa Arab,20 Lívia Anna,4 Jan Alexander,21 Silvia Agramunt,8 Jos C. Kleinjans,22 Dan Segerbäck,14 and Manolis Kogevinas1,2,8,23
Background: Tobacco-smoke, airborne, and dietary exposures to polycyclic aromatic hydrocarbons (PAHs) have been associated with reduced prenatal growth. Evidence from biomarker-based studies of low-exposed populations is limited. Bulky DNA adducts in cord blood reflect the prenatal effective dose to several genotoxic agents including PAHs.
Objectives: We estimated the association between bulky DNA adduct levels and birth weight in a multicenter study and examined modification of this association by maternal intake of fruits and vegetables during pregnancy.
Methods: Pregnant women from Denmark, England, Greece, Norway, and Spain were recruited in 2006–2010. Adduct levels were measured by the 32P-postlabeling technique in white blood cells from 229 mothers and 612 newborns. Maternal diet was examined through questionnaires.
Results: Adduct levels in maternal and cord blood samples were similar and positively correlated (median, 12.1 vs. 11.4 adducts in 108 nucleotides; Spearman rank correlation coefficient = 0.66, p < 0.001). Cord blood adduct levels were negatively associated with birth weight, with an estimated difference in mean birth weight of –129 g (95% CI: –233, –25 g) for infants in the highest versus lowest tertile of adducts. The negative association with birth weight was limited to births in Norway, Denmark, and England, the countries with the lowest adduct levels, and was more pronounced in births to mothers with low intake of fruits and vegetables (–248 g; 95% CI: –405, –92 g) compared with those with high intake (–58 g; 95% CI: –206, 90 g).
Conclusions: Maternal exposure to genotoxic agents that induce the formation of bulky DNA adducts may affect intrauterine growth. Maternal fruit and vegetable consumption may be protective.
Citation: Pedersen M, Schoket B, Godschalk RW, Wright J, von Stedingk H, Törnqvist M, Sunyer J, Nielsen JK, Merlo DF, Mendez MA, Meltzer HM, Lukács V, Landström A, Kyrtopoulos SA, Kovács K, Knudsen LE, Haugen M, Hardie LJ, Gützkow KB, Fleming S, Fthenou E, Farmer PB, Espinosa A, Chatzi L, Brunborg G, Brady NJ, Botsivali M, Arab K, Anna L, Alexander J, Agramunt S, Kleinjans JC, Segerbäck D, Kogevinas M. 2013. Bulky DNA adducts in cord blood, maternal fruit-and-vegetable consumption, and birth weight in a European mother–child study (NewGeneris). Environ Health Perspect 121:1200–1206; http://dx.doi.org/10.1289/ehp.1206333
Address correspondence to M. Pedersen, Centre for Research in Environmental Epidemiology (CREAL), 88 Doctor Aiguader Rd., Barcelona 08003 Spain. Telephone: 34 932147318. E-mail: firstname.lastname@example.org
We thank participants in the study and the collaborators from the hospitals.
The NewGeneris (Newborns and Genotoxic exposure risks) study was funded by the European Union (EU contract FOOD-CT-2005-016320). The study was also supported by the National Institute for Health Research, United Kingdom (programme grant RP-PG-0407-10044), the Norwegian Ministry of Health, the Norwegian Ministry of Education and Research, the Norwegian Research Council/FUGE (grant 151918/S10), the EU funded HiWATE (contract Food-CT-2006-036224), the U.S. National Institutes of Health (NIH)/National Institute of Environmental Health Sciences (contract NO-ES-75558), and the U.S. NIH/National Institute of Neurological Disorders and Stroke (grant 1 UO1 NS 047537-01). M.P. holds a Juan de la Cierva postdoctoral fellowship awarded from the Spanish Ministry of Science and Innovation (JCI-2011-09479).
The authors declare they have no actual or potential competing financial interests.
Received: 30 November 2012
Accepted: 19 July 2013
Advance Publication: 23 July 2013
Final Publication: 1 October 2013
Environmental exposures in utero may have adverse effects on health both immediately and in later life. Measurement of biomarkers in cord blood improves exposure assessment and may improve our understanding of biological mechanisms during this critical window of exposure and vulnerability (Wild and Kleinjans 2003).
Bulky DNA adducts are a widely accepted and sensitive biomarker of the biologically effective dose of genotoxic agents in complex environmental exposures, including those in ambient air, tobacco smoke, and diet (Godschalk et al. 2005; Karttunen et al. 2010; Kovács et al. 2011). They reflect individual exposure, absorption, and metabolic activation of heterogeneous adduct-forming compounds, in combination with the ability to repair induced DNA damage (Farmer 1994), and may be predictive of cancer risk (Veglia et al. 2008).
Bulky DNA adducts are commonly detected in human DNA by 32P-postlabeling combined with multidimensional thin-layer chromatography. Among common environmental genotoxic agents, polycyclic aromatic hydrocarbons (PAHs) [International Agency for Research on Cancer (IARC) 2010] cause DNA damage that is readily detectable as bulky DNA adducts, although the chemical nature of the DNA damage that leads to adduct formation is not known with certainty. A positive correlation between DNA adducts in blood and PAH exposure has been reported in adult populations exposed to high levels of PAHs in ambient air or food (Nielsen et al. 1996; van Maanen et al. 1994), which suggests that bulky DNA adducts reflect DNA damage caused by genotoxic PAHs. Bulky DNA adducts and more specific PAH-related DNA adducts have been detected in human umbilical cord white blood cells (Godschalk et al. 2005; Hansen et al. 1993; Pedersen et al. 2009; Perera et al. 1998, 2005; Topinka et al. 2009), in human placenta (Everson et al. 1988; Hansen et al. 1993; Sram et al. 2006) and in ex vivo human placental perfusions (Karttunen et al. 2010), which suggests that PAHs and other environmental genotoxic agents are capable of forming DNA adducts in utero.
Food is an important source of PAHs (IARC 2010; Kazerouni et al. 2001). Intake of meat with a blackened surface (Pedersen et al. 2012a), exposure to traffic-related air pollution during pregnancy (Pedersen et al. 2009), and smoking during pregnancy (Godschalk et al. 2005; Hansen et al. 1993; Pedersen et al. 2009) have been associated with higher levels of bulky DNA adducts in human cord blood. However, evidence regarding associations between bulky DNA adducts and birth outcomes is conflicting. Smoking-related DNA adducts measured by the 32P-postlabeling method in placental tissue from 30 women in the United States were associated with reduced birth weight (Everson et al. 1988), but in a study of 199 women in the Czech Republic, there were no associations between bulky DNA adducts in placenta tissue and birth weight, the risk of low birth weight (< 2,500 g), gestational duration, or preterm delivery (Sram et al. 2006).
Consumption of fruits and vegetables is considered beneficial for health (Slavin and Lloyd 2012) and may protect against cancer (World Cancer Research Fund/American Institute for Cancer Research 2007) through antioxidative effects and other properties related to dietary intake of fiber, folate, and other beneficial nutrients. In the European Prospective Investigation into Cancer and Nutrition (EPIC) cohort study, higher intake of fibers was negatively associated with bulky DNA adduct levels in white blood cells from 1,085 adults (Peluso et al. 2008). In addition, a diet rich in vitamin C has been associated with lower levels of DNA damage [reviewed by Sram et al. (2012)], and high maternal vitamin C intake during pregnancy appeared to reduce the association between estimated maternal dietary benzo[a]pyrene (BaP) intake and size at birth of 586 newborns from Spain (Duarte-Salles et al. 2012).
In the present study, we investigated the association between bulky DNA adduct levels and birth weight in 612 newborns and further assessed whether maternal consumption of fruits and vegetables during pregnancy modified this association.
Study population. The study was conducted as a part of the NewGeneris (Newborns and Genotoxic exposure risks) study of the impact of diet during pregnancy on child health (Merlo et al. 2009). Pregnant women were enrolled during 2006–2010 from 11 maternity units located in Copenhagen, Denmark; Bradford, England; Heraklion, Greece; Oslo, Norway; and Barcelona and Sabadell, Spain (Pedersen et al. 2012b). Births were included in the present analysis if they occurred during the periods of cord blood collection and processing, if there was a sufficient volume of cord blood, and if blood processing and biomarker analysis was successful. Precise participation rates for the present analysis cannot be estimated because the number of births that might have been eligible cannot be determined.
Detailed information on personal characteristics was obtained from the mothers by using extensive questionnaires collected before or around the time of delivery (Table 1). The questionnaires were self-administered (Denmark-2009, Norway), partly supported (Denmark-2007, Spain, and England), and administered by an interviewer (Greece) (Pedersen et al. 2012b). Dietary information concerning diet during pregnancy was obtained from country-specific food frequency questionnaires. Information on birth weight, birth head circumference, gestational age, infant sex, and mode of delivery was obtained from maternity records. Gestational age at birth was based on last menstrual period and/or ultrasound-based estimated date of conception and corrected by ultrasound measurements if there was a discordance of ≥ 7 days between both estimates.
Cord blood DNA adduct measurements were available from 630 newborns born to women with singleton deliveries. We excluded 18 newborns with missing information on maternal smoking, gestational age, birth weight, and/or sex, and included 612 newborns.
Ethical approval was obtained from the ethics committee in each country. Written informed consent was obtained from all participating women.
Blood collection and bulky DNA adduct analysis (32P-postlabeling). Umbilical cord blood (~ 50 mL) was collected immediately after delivery. Peripheral blood (~ 45 mL) was also drawn from 229 mothers.
DNA was isolated centrally from ~ 0.5-mL aliquots of buffy-coat samples using Qiagen Midi Kit catalog no.13343 (Qiagen, Hilden, Germany) with some modifications (Arab et al. 2009). Levels of bulky DNA adducts were determined by using the 32P-postlabeling method with the nuclease P1 adduct enrichment version according to standardized protocols (Godschalk et al. 2005; Karttunen et al. 2010; Kovács et al. 2011). The protocols were harmonized and adjusted in an interlaboratory comparison study among the three 32P-postlabeling investigator laboratories, including the use of the same external benzo[a]pyrene-7,8-diol-9,10-epoxide (BPDE)–DNA standard [111 adducts in 108 normal nucleotides (nt), which was a kind gift from F.F. Beland (National Center for Toxicological Research, Little Rock, AR, USA)]. All samples from Greece, Spain, and Norway and the Danish samples collected in 2006–2007 were analyzed in Budapest, Hungary (61% of the samples); the Danish samples from 2009 were analyzed in Stockholm, Sweden (21%); and the samples from England were analyzed in Maastricht, the Netherlands (18%). The interlaboratory comparison study showed a very high repeatability between two of the three laboratories, whereas the adduct levels measured in the third laboratory were consistently 3.7 times lower than the mean levels determined by the two other laboratories. Differences in DNA adduct determinations between laboratories normally occur because of the complicated multistep and sensitive procedures used for the detection of the adducts, and interlaboratory studies are therefore necessary. A correction for the laboratory factor of 3.7 was thus applied to the samples analyzed in Stockholm (Denmark-2009, 21% of the total). A sensitivity analysis that included or subsequently excluded these samples gave similar results, so all analyses were based on the total study population including the corrected data.
The individual level of DNA adducts was obtained as the average of at least two independent measurements. The detection limit of the assay was approximately 0.1–0.3 adducts per 108 unmodified nucleotides (n/108 nt).
Statistical analysis. We performed linear regression models with a random effect for country to estimate the difference in mean birth weight (grams) associated with bulky DNA adduct levels in cord blood. Furthermore, we estimated associations with head circumference (centimeters) and gestational age (completed weeks) at birth. Low birth weight (< 2,500 g, n = 7) and preterm (< 37 completed weeks of gestation, n = 26) were too uncommon to estimate associations with bulky DNA adduct levels.
DNA adduct levels measured in cord blood were modeled as categorized according to tertiles: low (n = 205), middle (n = 203), or high (n = 204) (< 5.9, ≥ 5.9–12.4, and ≥ 12.5 adducts/108 nt, respectively).
We examined the effect of different degrees of adjustment for potential confounders on the association of bulky DNA adduct levels on birth weight. Potential confounders selected a priori for the adjusted model were gestational age (completed weeks, continuous), infant sex, maternal prepregnancy body mass index (BMI; kilograms per meter squared), parity (0, ≥ 1), maternal age (years), maternal ethnicity (white, nonwhite), self-reported maternal active smoking at the end of pregnancy (no, yes), self-reported maternal exposure to secondhand smoke (SHS) during pregnancy (no, yes), ethylene oxide–hemoglobin (Hb) adduct levels in cord blood (picomoles per gram Hb; to assess exposure to tobacco smoke during pregnancy), mode of delivery (vaginal, cesarean section), dietary supplements (none, any), maternal consumption of fruits and vegetables during pregnancy (low, high), season of delivery (March–May, June–August, September–November, December–February), country of delivery, and maternal education (low, middle, high) as a marker of socioeconomic position. In addition, we estimated basic adjusted associations using models that included country, maternal smoking at the end of pregnancy, sex, and gestational age only.
Given that bulky DNA adduct levels in cord blood reflect a steady state between DNA damage and repair during the previous few months (Godschalk et al. 2005), we classified women who smoked during the last four months of pregnancy as smokers, whereas those who never smoked or who quit before the last 4 months of pregnancy were classified as nonsmokers. Women exposed to SHS in the home and/or elsewhere during pregnancy were categorized as exposed. In addition, to further assess exposure to dietary acrylamide and tobacco smoke during pregnancy, we adjusted for acrylamide and ethylene oxide Hb adduct levels (picomoles per gram Hb), respectively, in cord blood samples (von Stedingk et al. 2011).
Maternal intake of fruits and vegetables during pregnancy (grams/day, based on 20–61 questionnaire items depending on country) was categorized as high or low according to overall and country-specific median levels as a proxy measure of the consumption of nutrients that might be protective against genotoxic activation processes. We also classified mothers according to their intake of fruits high in vitamin C and other antioxidants (i.e., all types of citrus fruits, both in terms of whole fruits and juice, kiwi fruit, and berries, ranging from three to seven questionnaire items). Women (n = 54) with a total energy estimate of < 500 or > 6,000 kcal/day were excluded from adjusted analyses and analyses of effect modification by diet (Butte and King 2005; Willett 1998).
In addition, we performed a meta-analysis by country to derive country-specific effect estimates of associations between cord blood DNA adduct levels and birth weight. Pregnancy outcomes in Northern European countries (England, Denmark, and Norway, n = 367), which had low average levels of adducts, were compared with outcomes in Southern European countries (Greece and Spain, n = 245), which had higher average adduct levels.
To estimate the association between bulky DNA adduct levels and term birth weight, we repeated the main analysis after excluding preterm deliveries (n = 26). We used an alpha level of 5% for statistical significance. All statistical analyses were performed using Stata S.E. version 12.1 (StataCorp, College Station, TX, USA).
Study population. The study population was composed of neonates from Denmark (33%), Spain (29%), England (18%), Greece (11%), and Norway (10%). Mothers were predominantly white Europeans, multiparous, and nonsmoking (Table 1). Most children were born at term (96%) and weighed > 2,500 g at birth (97%). Some study population characteristics differed significantly between the Northern and Southern European populations (e.g., maternal smoking; 8% vs. 18%, respectively), whereas characteristics such as maternal prepregnancy BMI and dietary supplement use were similar. The daily median fruit and vegetable intake of the Southern European mothers was 58 g higher than that of Northern European mothers, but the difference was not statically significant (p = 0.13). The difference in fruit and vegetable intake between Southern and Northern European mothers was also not statically significant after adjustment for individual total energy intake. Differences were smaller for fruits high in vitamin C (Table 1).
Adduct levels in maternal and cord blood samples. All maternal (n = 229) and cord blood (n = 612) samples had detectable levels of adducts. Median levels of adducts in paired maternal and cord blood samples were similar (12.1 vs. 11.4 adducts/108 nt, p = 0.23). Cord blood adduct levels ranged from 0.6 to 87.5 (adducts/108 nt) and were significantly positively correlated with maternal levels (Spearman’s rank correlation coefficient = 0.66, p = 0.001, n = 229).
Bulky DNA adduct levels were higher in children from Southern Europe (median, 12.8 adducts/108 nt; range, 0.8–87.5) than from Northern Europe (median, 7.0/108 nt; range, 0.6–52.7; p < 0.001), although an opposite pattern was observed for birth weight (medians of 3,325 g and 3,544 g, respectively, p < 0.001) (Table 1, Figure 1). The difference in DNA adduct levels was also observed when the analysis was restricted to children born to mothers who did not smoke during the last 4 months of pregnancy (median, 13.0/108 nt; range, 0.8–87.5 for Southern Europe vs. median, 6.8/108 nt; range, 0.6–52.7 for Northern Europe; p < 0.001). Median adduct levels in the children of nonsmokers also differed significantly (p < 0.001) among the individual countries (Greece: 13.4/108 nt, range 0.8–43.9, n = 54; Spain: 12.9/108 nt, range 1.1–87.5, n = 148; England: 9.5/108 nt, range 0.6–52.7, n = 57; Denmark: 6.4/108 nt, range 1.3–42.7, n = 192; Norway: 5.4/108 nt, range 1.2–22.3, n = 57). The same pattern of higher adduct levels in children from Southern Europe than those from Northern Europe was found for children born to nonsmokers without exposure to SHS.
The median bulky DNA adduct level in the 71 children born to mothers who actively smoked at the end of their pregnancy (10.9 adducts/108 nt; range, 0.6–73.9) was higher than the median level in the 541 children of mothers who never smoked or who quit before the last 4 months of pregnancy (8.2 adducts/108 nt; range, 0.6–87.5, p = 0.07). Adduct levels were lowest in the 505 children born to mothers who never smoked during their pregnancy (8.0 adducts/108 nt; range, 0.6–87.5, p = 0.10).
Adduct levels in cord blood and birth outcomes. Higher levels of bulky DNA adducts in cord blood were associated with lower birth weight (Table 2). For the full study population (n = 612), the estimated difference in mean birth weight for infants in the highest tertile versus the lowest tertile of adduct levels was –110 g (95% CI: –192, –28 g), based on basic adjusted models that included country, maternal smoking at the end of pregnancy, sex, and gestational age only. The corresponding association was similar when restricted to the 541 mothers who did not smoke during the last 4 months of pregnancy (–108 g; 95% CI: –202, –14 g), but was slightly stronger when restricted to the 505 mothers who did not smoke at any time during the pregnancy (–124 g; 95% CI: –216, –32 g).
After further adjusting for maternal age, prepregnancy BMI, exposure to SHS, maternal education, ethnicity, intake of fruits and vegetables, delivery type, and season of delivery (n = 409), the estimated difference in mean birth weight associated with the highest versus lowest tertile of DNA adduct levels was –129 g (95% CI: –233, –25 g) (Table 2). After additional adjustment for ethylene oxide–cord blood Hb adduct levels (picomoles per gram Hb, n = 390), the estimated mean difference was –139 g (95% CI: –245, –32 g). When we further adjusted for acrylamide Hb adduct levels in cord blood (picomoles per gram Hb, n = 390) the associations remained practically unchanged (–140 g (95% CI: –247, –34 g).
When 26 preterm births (< 37 weeks) were excluded, the estimated difference in birth weight for infants in the highest versus lowest tertile of adduct levels was –139 g (95% CI: –245, –33 g).
Bulky DNA adduct levels were negatively associated with head circumference based on the basic adjusted model (–0.28 cm for the highest vs. lowest tertile; 95% CI: –0.59, 0.03 cm, p = 0.08, n = 530) and after further adjustment for maternal age, prepregnancy BMI, exposure to SHS, maternal education, ethnicity, intake of fruits and vegetables, delivery type, and season of delivery (–0.33 cm; 95% CI: –0.72, 0.06 cm, p = 0.10, n = 388).
The estimated difference in mean gestational age at birth for infants in the highest versus lowest tertile of adduct levels was –0.29 weeks (95% CI, –0.63, 0.04 weeks; p = 0.08) based on the further adjusted model. When restricted to vaginal deliveries (n = 243, further adjusted model), the estimated difference in gestational age was –0.54 weeks (95% CI: –1.06, –0.03 weeks), compared with a difference of 0.15 weeks (95% CI: –0.23, 0.53 weeks; p = 0.43) for deliveries by cesarean section (n = 166).
Differences between countries. Consistent with associations estimated for the full study population, mean birth weight was significantly lower for Northern European infants in the highest versus lowest tertile of adduct levels (–119 g; 95% CI: –234, –4 g) based on the basic adjusted model. However, there was a nonsignificant positive association among the 245 Southern Europeans (71 g; 95% CI: –59, 202 g; p = 0.28). Estimates based on adjusted models also indicated negative associations for the Northern European countries, but not for the Southern European countries (Figure 2; p-value for heterogeneity = 0.03), and when imputed data were used to include individuals with missing information on covariates (results not shown). Therefore, although birth weight was lowest and adduct levels were highest in Greece and Spain (Figure 1), the negative association between adduct levels and birth weight estimated for the full study population appears to be driven by the Northern countries.
Differences by intake of fruits and vegetables. The association of bulky DNA adduct levels with birth weight differed according to maternal intake of fruits and vegetables and intake of fruits high in vitamin C, although interactions were only marginally significant (Table 3). The estimated difference in birth weight between the highest and lowest tertiles of adduct levels was greater among births to mothers with low intakes of fruits and vegetables (–248 g; 95% CI: –405, –92 g) than among births to mothers with high intakes (–58 g; 95% CI: –206, 90 g; p = 0.44). Consumption of dietary supplements during pregnancy was common in both Northern and Southern Europeans (85% and 90%, respectively) and did not appear to modify or confound associations between adduct levels and birth weight (data not shown).
We measured levels of bulky DNA adducts in white blood cells from cord blood in a large multicenter European prospective general population study and found that higher adduct levels in cord blood were significantly negatively associated with birth weight. The negative association was observed among newborns from England, Denmark, and Norway, who had the lowest average adduct levels, but was not evident among Southern Europeans, who had the highest mean adduct levels. The negative association with birth weight was stronger among the children of mothers with low versus high intakes of fruits and vegetables.
Tobacco smoke contains PAHs and other DNA adduct–forming compounds in addition to other potentially harmful compounds, and active maternal smoking is a recognized risk factor for reduced fetal growth (Li et al. 1993). Furthermore, ambient airborne PAHs (Wilhelm et al. 2011) and intake of barbecued meat during pregnancy has also been associated with reduced birth weight (Jedrychowski et al. 2012).
The results of the previous similar biomarker-based studies on fetal growth are inconsistent; studies based on 1-hydroxypyrene in maternal urine (n = 449 samples, Poland) (Polańska et al. 2010), bulky DNA adducts (n = 30, newborns of smokers, United States) (Everson et al. 1988), and structurally related PAH–DNA adducts in cord blood (n = 135, newborns of women living in coal-burning areas, Poland) (Perera et al. 1998) support an association between higher prenatal exposure to PAHs and reduced birth weight opposite to the findings from cord blood–based studies on bulky DNA adducts (Sram et al. 2006), BPDE–DNA adducts (n = 181, newborns of women who lived near the World Trade Center fires on 11 September 2001 while they were pregnant) (Perera et al. 2005) and on BPDE–DNA adducts (n = 150, newborns of women living near a coal-fired power plant, China) (Tang et al. 2006). Results from these studies are, however, inconsistent, and evidence from European populations exposed to contemporary lifestyle and environment is limited.
Mechanisms by which environmental genotoxicants that cause bulky DNA adduct formation might affect fetal growth are not known; but along with direct modification of DNA (measurable as bulky DNA adducts), possible mechanisms may include binding to aryl hydrocarbon receptor (AhR) and/or other receptors causing endocrine disruption, altered placental growth, decreased placental exchange of nutrients and gases in utero possibly related to induction of P450 enzymes, global DNA methylation changes, induction of apoptosis, altered gene expression, cellular mutations, or oxidative stress (Baird et al. 2005; IARC 2010; Kannan et al. 2006; Sram et al. 2006; Tang et al. 2012). Developmental and reproductive toxicity due to prenatal exposure to PAHs and similar AhR ligands has been observed in various animal species (Pocar et al. 2005; Sanyal and Li 2007).
Our findings suggest that maternal intake of fruits and vegetables may modify the association between bulky DNA adduct levels and birth weight. This finding is consistent with the findings of a questionnaire-based study evaluating dietary BaP (Duarte-Salles et al. 2012).
Children from Southern Europe had, on average, higher bulky DNA adduct levels and lower birth weight than Northern European children. However a negative association between adducts and birth weight was found only in the Northern Europeans. The same pattern of higher bulky DNA adduct levels in Southern Europe than in Northern Europe has been found in adults (Ricceri et al. 2010), and this may reflect differences in ambient air quality (Table 4), but also wider geographical differences in diet, food preparations, and other factors, or perhaps different susceptibility toward environmental genotoxic agents. It is possible that exposures that cause adducts in children from Northern Europe also cause reduced birth weight, whereas exposures responsible for adducts among Southern European children might differ and may not affect birth weight. A complementary explanation could involve a saturation effect of the toxicity of these adducts on birth weight, although other studies in populations exposed to very high air pollution levels and corresponding high adduct levels have reported negative associations with birth weight (Perera et al. 1998, 2005).
A key strength of the present study is the measurement of bulky DNA adducts in cord blood, which enabled a more accurate evaluation of the biologically effective dose of genotoxic agents resulting from complex environmental exposures than estimates based solely on external exposure assessment. Large biomarker-based studies are rare because of their costs and complexity. Standardized protocols were developed (Merlo et al. 2009) and applied to the collection of cord blood from multiple study centers. Detailed information on maternal characteristics and diet was collected in a manner that allowed pooling of data from five different countries (Pedersen et al. 2012b). In addition to increasing the sample size, enrolling participants from different countries allows us to test hypotheses in different settings.
32P-Postlabeling is considered to be the most suitable and sensitive method for assessing total DNA damage resulting from exposures to unknown, complex mixtures of genotoxic compounds. We used the validated in vitro BPDE–DNA standard in each 32P-postlabeling session in duplicate for normalization of the DNA adduct levels. Each DNA sample was analyzed at least twice. The interlaboratory comparison study, the use of common protocols, and use of a validated BPDE–DNA standard minimized the potential for measurement error. Thus, we believe that measurement error of the method was properly handled and is not a special concern in our study.
Low birth weight is an important outcome because it is associated with greater risk of neonatal mortality, hypertension and cardiovascular disease, diabetes, certain cancers, reduced and/or delayed postnatal growth, and cognitive development (Gluckman et al. 2008). Our findings suggest that environmental exposures that result in the in utero formation of bulky DNA adducts also may affect prenatal growth, and that this potential effect may be reduced by high maternal fruit and vegetable consumption.
Arab K, Pedersen M, Nair J, Meerang M, Knudsen LE, Bartsch H. 2009. Typical signature of DNA damage in white blood cells: a pilot study on etheno adducts in Danish mother–newborn child pairs. Carcinogenesis 30:282–285.
CBMDC (City of Bradford Metropolitan District Council). 2009. 2009 Air Quality Updating and Screening Assessment for Bradford. Available: http://www.bradford.gov.uk/NR/rdonlyres/947BD14D-DADF-42F3-A876-D91EB5966C2D/0/BradfordUpdatingandScreeningAssessmentofAirQuality2009.pdf [accessed 25 March 2013].
DCE (Danish Center for Environment and Energy). 2013. Database: Retrieve air quality data. Available: http://www2.dmu.dk/1_Viden/2_miljoe-tilstand/3_luft/4_maalinger/5_database/hentdata_en.asp [accessed 25 March 2013].
Duarte-Salles T, Mendez MA, Morales E, Bustamante M, Rodríguez-Vicente A, Kogevinas M, et al. 2012. Dietary benzo(a)pyrene and fetal growth: effect modification by vitamin C intake and glutathione S-transferase P1 polymorphism. Environ Int 45:1–8.
Everson RB, Randerath E, Santella RM, Avitts TA, Weinstein IB, Randerath K. 1988. Quantitative associations between DNA damage in human placenta and maternal smoking and birth weight. J Natl Cancer Inst 80:567–576.
Gencat (Generalitat de Catalunya). 2013a. Diòxid de nitrogen (NO2): 01/01/07–31/12/07 [in Catalan]. Available: http://www20.gencat.cat/docs/dmah/Home/Ambits%20dactuacio/Atmosfera/Qualitat%20de%20laire/Avaluacio/Balancos%20i%20informes/documentos/no.pdf [accessed 28 August 2013].
Gencat (Generalitat de Catalunya). 2013b. Diòxid de nitrogen (NO2): 01/01/09–31/12/09 [in Catalan]. Available: http://www20.gencat.cat/docs/dmah/Home/Ambits%20dactuacio/Atmosfera/Qualitat%20de%20laire/Avaluacio/Balancos%20i%20informes/documentos/no2%282%29.pdf [accessed 28 August 2013].
Gencat (Generalitat de Catalunya). 2013c. Partícules en suspensió (PM10): 01/01/07–31/12/07 [in Catalan]. Available: http://www20.gencat.cat/docs/dmah/Home/Ambits%20dactuacio/Atmosfera/Qualitat%20de%20laire/Avaluacio/Balancos%20i%20informes/documentos/pm10%281%29.pdf [accessed 28 August 2013].
Gencat (Generalitat de Catalunya). 2013d. Partícules en suspensió (PM10) manual: 01/01/09–31/12/09 [in Catalan]. Available: http://www20.gencat.cat/docs/dmah/Home/Ambits%20dactuacio/Atmosfera/Qualitat%20de%20laire/Avaluacio/Balancos%20i%20informes/documentos/pm10%283%29.pdf [accessed 28 August 2013].
Gencat (Generalitat de Catalunya). 2013e. Partícules en suspensió (PM2.5): 01/01/07–31/12/07 [in Catalan]. Available: http://www20.gencat.cat/docs/dmah/Home/Ambits%20dactuacio/Atmosfera/Qualitat%20de%20laire/Avaluacio/Balancos%20i%20informes/documentos/pm25%281%29.pdf [accessed 28 August 2013].
Gencat (Generalitat de Catalunya). 2013f. Partícules en suspensió (PM2.5) manual: 01/01/09–31/12/09 [in Catalan]. Available: http://www20.gencat.cat/docs/dmah/Home/Ambits%20dactuacio/Atmosfera/Qualitat%20de%20laire/Avaluacio/Balancos%20i%20informes/documentos/pm25%283%29.pdf [accessed 28 August 2013].
Godschalk R, Hogervorst J, Albering H, Mercelina-Roumans P, van Schooten FJ, de Haaen J, et al. 2005. Interaction between cadmium and aromatic DNA adducts in hprt mutagenesis during foetal development. Mutagenesis 20:181–185.
Jedrychowski W, Perera FP, Tang D, Stigter L, Mroz E, Flak E, et al. 2012. Impact of barbecued meat consumed in pregnancy on birth outcomes accounting for personal prenatal exposure to airborne polycyclic aromatic hydrocarbons: birth cohort study in Poland. Nutrition 28:372–377.
Kannan S, Misra DP, Dvonch JT, Krishnakumar A. 2006. Exposures to airborne particulate matter and adverse perinatal outcomes: a biologically plausible mechanistic framework for exploring potential effect modification by nutrition. Environ Health Perspect 114:1636–1642; doi:10.1289/ehp.9081.
Nielsen PS, De Pater N, Okkels H, Autrup H. 1996. Environmental air pollution and DNA adducts in Copenhagen bus drivers. Effect of GSTM1 and NAT2 genotypes on adduct levels. Carcinogenesis 17:1021–1027.
NILU (Norsk institutt for luftforskning). 2013. Luftkvaliteten i Norge [in Norwegian]. Available: http://www.luftkvalitet.info/home.aspx [accessed 25 March 2013].
Pedersen M, von Stedingk H, Botsivali M, Agramunt S, Alexander J, Brunborg G, et al. 2012b. Birth weight, head circumference, and prenatal exposure to acrylamide from maternal diet: the European Prospective Mother–Child Study (NewGeneris). Environ Health Perspect 120:1739–1745; doi:10.1289/ehp.1205327.
Pedersen M, Wichmann J, Autrup H, Dang DA, Decordier I, Hvidberg M, et al. 2009. Increased micronuclei and bulky DNA adducts in cord blood after maternal exposures to traffic-related air pollution. Environ Res 109:1012–1020.
Peluso M, Airoldi L, Munnia A, Colombi A, Veglia F, Autrup H, et al. 2008. Bulky DNA adducts, 4-aminobiphenyl-haemoglobin adducts and diet in the European Prospective Investigation into Cancer and Nutrition (EPIC) prospective study. Br J Nutr 100:489–495.
Perera FP, Tang D, Rauh V, Lester K, Tsai WY, Tu YH, et al. 2005. Relationships among polycyclic aromatic hydrocarbon–DNA adducts, proximity to the World Trade Center, and effects on fetal growth. Environ Health Perspect 113:1062–1067; doi:10.1289/ehp.7908.
Perera FP, Whyatt RM, Jedrychowski W, Rauh V, Manchester D, Santella RM, et al. 1998. Recent developments in molecular epidemiology: a study of the effects of environmental polycyclic aromatic hydrocarbons on birth outcomes in Poland. Am J Epidemiol 147:309–314.
Pocar P, Fischer B, Klonisch T, Hombach-Klonisch S. 2005. Molecular interactions of the aryl hydrocarbon receptor and its biological and toxicological relevance for reproduction. Reproduction 129:379–389.
Ricceri F, Godschalk RW, Peluso M, Phillips DH, Agudo A, Georgiadis P, et al. 2010. Bulky DNA adducts in white blood cells: a pooled analysis of 3,600 subjects. Cancer Epidemiol Biomarkers Prev 19:3174–3181.
Tang D, Li TY, Liu JJ, Chen YH, Qu L, Perera F. 2006. PAH–DNA adducts in cord blood and fetal and child development in a Chinese cohort. Environ Health Perspect 114:1297–1300; doi:10.1289/ehp.8939.
Tang WY, Levin L, Talaska G, Cheung YY, Herbstman J, Tang D, et al. 2012. Maternal exposure to polycyclic aromatic hydrocarbons and 5´-CpG methylation of interferon-γ in cord white blood cells. Environ Health Perspect 120:1195–1200; doi:10.1289/ehp.1103744.
Topinka J, Milcova A, Libalova H, Novakova Z, Rossner P Jr, Balascak I, et al. 2009. Biomarkers of exposure to tobacco smoke and environmental pollutants in mothers and their transplacental transfer to the foetus. Part I: Bulky DNA adducts. Mutat Res 669:13–19.
van Maanen JM, Moonen EJ, Maas LM, Kleinjans JC, van Schooten FJ. 1994. Formation of aromatic DNA adducts in white blood cells in relation to urinary excretion of 1-hydroxypyrene during consumption of grilled meat. Carcinogenesis 15:2263–2268.
von Stedingk H, Vikström AC, Rydberg P, Pedersen M, Nielsen JKS, Segerbäck D, et al. 2011. Analysis of hemoglobin adducts from acrylamide, glycidamide and ethylene oxide in paired mother/cord blood samples from Denmark. Chem Res Toxicol 24:1957–1965.
Wilhelm M, Ghosh JK, Su J, Cockburn M, Jerrett M, Ritz B. 2011. Traffic-related air toxics and preterm birth: a population-based case-control study in Los Angeles County, California. Environ Health 10:89; doi:10.1186/1476-069X-10-89.
World Cancer Research Fund/American Institute for Cancer Research. 2007. Food, Nutrition, Physical Activity and Prevention of Cancer: a Global Perspective. Available: http://www.dietandcancerreport.org/cancer_resource_center/downloads/Second_Expert_Report_full.pdf [accessed 27 August 2013].
2015 Impact Factor
EHP is pleased to announce its new impact factor of 8.44, up from 7.98 last year. We thank our authors, associate editors, reviewers, and readers for their contributions and support.
CEHN June 2016 Article of the Month
“Intrauterine Inflammation and Maternal Exposure to Ambient PM2.5 during Preconception and Specific Periods of Pregnancy: The Boston Birth Cohort” (doi:10.1289/EHP243 ) has been selected by the Children’s Environmental Health Network (CEHN) as its June 2016 Article of the Month. These CEHN summaries discuss the potential policy implications of current children’s environmental health research.
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Recent Advance Publications
Prenatal Exposure to Perfluoroalkyl Substances and Adiposity in Early and Mid-Childhood
Association of Cardiometabolic Genes with Arsenic Metabolism Biomarkers in American Indian Communities: The Strong Heart Family Study (SHFS)
The Case for Environment in All Policies: Lessons from the Health in All Policies Approach in Public Health
Mediation of the Relationship between Maternal Phthalate Exposure and Preterm Birth by Oxidative Stress with Repeated Measurements across Pregnancy
Urban and Transport Planning Related Exposures and Mortality: A Health Impact Assessment for Cities