ABSTRACT
There is a great concern in the Basque Country regarding emissions from waste incineration, in particular that of organochlorines (OCs), including dioxins, furans and polychlorinated biphenyls (PCBs), and their potential effect on human health. In 2005, a municipal solid waste plant (MSWP) started to operate in Bilbao, representing an opportunity to assess the exposure to the aforementioned pollutants among people living at various distances from the plant. In 2006 and 2008, we carried out two cross-sectional studies to quantify and assess changes in levels of these pollutants. The objective of this study was to describe the levels of OCs in the blood serum in 2013 of 127 adults of this prospective cohort, in four centres of population, near to and further away from the MSWP, and to study trends over time since it started to operate. This study shows the levels of OCs have decreased significantly, from 37.2% to 80.1%. Further, levels of OCs in areas near to the MSWP were not found to be higher than those in areas further afield.
Subject(s)
Air Pollutants/blood , Dibenzofurans, Polychlorinated/blood , Hydrocarbons, Chlorinated/blood , Incineration , Polychlorinated Dibenzodioxins/blood , Adult , Aged , Cross-Sectional Studies , Environmental Monitoring , Female , Humans , Male , Middle Aged , Prospective Studies , Spain , Young AdultABSTRACT
The aim of this work was to determine and study the concentration of different groups of disinfection by-products (DBPs): trihalomethanes, haloacetic acids, haloacetonitriles, haloacetones and combined chlorine (as an indicator of chloramine levels), in the water of 175 public swimming pools in Gipuzkoa (Basque Country, Spain). The study included chlorinated and brominated pools, indoor and outdoor, used for recreational and sports purposes, and filled with water from calcareous and siliceous soils. The most abundant were haloacetic acids, followed by trihalomethanes, with chlorinated or brominated forms predominating depending on whether the pools were disinfected by chlorination or bromination, respectively. All the 75th percentiles of DBPs were below the limits established by the European Chemical Agency (ECHA), although the maximum values of trihalomethanes exceeded them. The same was true for dichloroacetonitrile in chlorinated pools and dibromoacetonitrile in brominated pools. All families of DBPs showed positive associations with each other, all being significant except for combined chlorine. Their mean levels were higher in outdoor pools than in indoor pools, significantly so in all except combined chlorine. Recreational pools showed higher levels of haloacetic acids and combined chlorine than sports pools. The concentrations of the different groups of DBPs were higher in the pools than in the mains water that fed them. This increase, especially that of the haloacetonitriles, as well as the high concentrations of brominated forms in the pools disinfected by bromination, make it necessary to focus on their toxicological implication. The differences in the DBP profiles of the filling network water were not transferred to the pool water.
ABSTRACT
BACKGROUND: Findings and limitations of previous studies on persistent organic pollutants (POPs) and pancreatic cancer risk support conducting further research in prospective cohorts. METHODS: We conducted a prospective case-control study nested within the European Prospective Investigation into Cancer and Nutrition (EPIC) cohort. Participants were 513 pancreatic cancer cases and 1020 matched controls. Concentrations of 22 POPs were measured in plasma collected at baseline. RESULTS: Some associations were observed at higher concentrations of p, p'-DDT, trans-nonachlor, ß-hexachlorocyclohexane and the sum of six organochlorine pesticides and of 16 POPs. The odds ratio (OR) for the upper quartile of trans-nonachlor was 1.55 (95% confidence interval 1.06-2.26; P for trend = 0.025). Associations were stronger in the groups predefined as most valid (participants having fasted >6 h, with microscopic diagnostic confirmation, normal weight, and never smokers), and as most relevant (follow-up ≥10 years). Among participants having fasted >6 h, the ORs were relevant for 10 of 11 exposures. Higher ORs were also observed among cases with microscopic confirmation than in cases with a clinical diagnosis, and among normal-weight participants than in the rest of participants. Among participants with a follow-up ≥10 years, estimates were higher than in participants with a shorter follow-up (for trans-nonachlor: OR = 2.14, 1.01 to 4.53, P for trend = 0.035). Overall, trans-nonachlor, three PCBs and the two sums of POPs were the exposures most clearly associated with pancreatic cancer risk. CONCLUSIONS: Individually or in combination, most of the 22 POPs analysed did not or only moderately increased the risk of pancreatic cancer.
Subject(s)
Environmental Pollutants , Pancreatic Neoplasms , Pesticides , Polychlorinated Biphenyls , Case-Control Studies , Humans , Pancreatic Neoplasms/epidemiology , Persistent Organic Pollutants , Pancreatic NeoplasmsABSTRACT
The lack of knowledge about the onset and progression of Parkinson's disease (PD) hampers its early diagnosis and treatment. Metabolomics might shed light on the PD imprint seeking a broader view of the biochemical remodeling induced by this disease in an early and pre-symptomatic stage and unveiling potential biomarkers. To achieve this goal, we took advantage of the great potential of the European Prospective Study on Nutrition and Cancer (EPIC) cohort to apply metabolomics searching for early diagnostic PD markers. This cohort consisted of healthy volunteers that were followed for around 15 years until June 2011 to ascertain incident PD. For this untargeted metabolomics-based study, baseline preclinical plasma samples of 39 randomly selected individuals that developed PD (Pre-PD group) and the corresponding control group were analyzed using a multiplatform approach. Data were statistically analyzed and exposed alterations in 33 metabolites levels, including significantly lower levels of free fatty acids (FFAs) in the preclinical samples from PD subjects. These results were then validated by adopting a targeted HPLC-QqQ-MS approach. After integrating all the metabolites affected, our finding revealed alterations in FFAs metabolism, mitochondrial dysfunction, oxidative stress, and gut-brain axis dysregulation long before the development of PD hallmarks. Although the biological purpose of these events is still unknown, the remodeled metabolic pathways highlighted in this work might be considered worthy prognostic biomarkers of early prodromal PD. The findings revealed by this work are of inestimable value since this is the first study conducted with samples collected many years before the disease development.
ABSTRACT
BACKGROUND: The chemical quality of drinking water is widely unknown in low-income countries. OBJECTIVE: We conducted an exploratory study in Manhiça district (Mozambique) to evaluate drinking water quality using chemical analyses and cell-based assays. METHODS: We measured nitrate, fluoride, metals, pesticides, disinfection by-products, and industrial organochlorinated chemicals, and conducted the bioassays Ames test for mutagenicity, micronuclei assay (MN-FACS), ER-CALUX, and antiAR-CALUX in 20 water samples from protected and unprotected sources. RESULTS: Nitrate was present in all samples (median 7.5 mg/L). Manganese, cobalt, chromium, aluminium, and barium were present in 90-100% of the samples, with median values of 32, 0.6, 2.0, 61, 250 µg/l, respectively. Manganese was above 50 µg/l (EU guideline) in eight samples. Arsenic, lead, nickel, iron, and selenium median values were below the quantification limit. Antimony, cadmium, copper, mercury, zinc and silver were not present. Trihalomethanes, haloacetic acids, haloacetonitriles and haloketones were present in 5-28% samples at levels ≤4.6 µg/l. DDT, dieldrin, diuron, and pirimiphos-methyl were quantified in 2, 3, 3, and 1 sample, respectively (range 12-60 ng/L). Fluoride was present in one sample (0.11 mg/l). Trichloroethene and tetrachloroethene were not present. Samples were negative in the in vitro assays. SIGNIFICANCE: Results suggest low exposure to chemicals, mutagenicity, genotoxicity and endocrine disruption through drinking water in Manhiça population. High concentration of manganese in some samples warrants confirmatory studies, given the potential link to impaired neurodevelopment.
Subject(s)
Arsenic , Drinking Water , Water Pollutants, Chemical , Arsenic/analysis , Environmental Monitoring , Mozambique , Water Pollutants, Chemical/analysis , Water QualityABSTRACT
BACKGROUND AND AIMS: There is evidence that endocrine disrupting chemicals (EDCs) have developmental effects at environmental concentrations. We investigated whether some EDCs are associated with the adverse birth outcome Small for Gestational Age (SGA). METHODS: We used PCB 153, p,p'-DDE, HCB, PFOS and PFOA measured in maternal, cord blood or breast milk samples of 5446 mother-child pairs (subset of 693 for the perfluorinated compounds) from seven European birth cohorts (1997-2012). SGA infants were those with birth weight below the 10th percentile for the norms defined by gestational age, country and infant's sex. We modelled the association between measured or estimated cord serum EDC concentrations and SGA using multiple logistic regression analyses. We explored effect modification by child's sex and maternal smoking during pregnancy. RESULTS: Among the 5446 newborns, 570 (10.5%) were SGA. An interquartile range (IQR) increase in PCB 153 was associated with a modestly increased risk of SGA (odds ratio (OR) of 1.05 [95% CI: 1.04-1.07]) that was stronger in girls (OR of 1.09 [95% CI: 1.04-1.14]) than in boys (OR of 1.03 [95% CI: 1.03-1.04]) (p-interactionâ¯=â¯0.025). For HCB, we found a modestly increased odds of SGA in girls (OR of 1.04 [95% CI: 1.01-1.07] per IQR increase), and an inverse association in boys (OR of 0.90 [95% CI: 0.85-0.95]) (p-interactionâ¯=â¯0.0003). Assessment of the HCB-sex-smoking interaction suggested that the increased odds of SGA associated with HCB exposure was only in girls of smoking mothers (OR of 1.18 [95% CI: 1.11-1.25]) (p-interactionâ¯=â¯0.055). Higher concentrations of PFOA were associated with greater risk of SGA (OR of 1.64 [95% CI: 0.97-2.76]). Elevated PFOS levels were associated with increased odds of SGA in newborns of mothers who smoked during pregnancy (OR of 1.63 [95% CI: 1.02-2.59]), while an inverse association was found in those of non-smoking mothers (OR of 0.66 [95% CI: 0.61-0.72]) (p-interactionâ¯=â¯0.0004). No significant associations were found for p,p'-DDE. CONCLUSIONS: Prenatal environmental exposure to organochlorine and perfluorinated compounds with endocrine disrupting properties may contribute to the prevalence of SGA. We found indication of effect modification by child's sex and smoking during pregnancy. The direction of the associations differed by chemical and these effect modifiers, suggesting diverse mechanisms of action and biological pathways.
Subject(s)
Endocrine Disruptors/adverse effects , Infant, Low Birth Weight , Maternal Exposure , Prenatal Exposure Delayed Effects , Female , Fetal Blood/chemistry , Humans , Infant, Newborn , Male , Milk, Human/chemistry , Pregnancy , Smoking/epidemiologyABSTRACT
Chronic consumption of water, which contains contaminants, may give rise to adverse health effects. The Madrid region, covered by the population-based multicase-control (MCC-Spain) study, includes two drinking water supply areas. The different sources of the water, coupled together with the possible differences in water management, mean that there may be differences in drinking water quality. In the context of the MCC study, our aims were to describe contaminant concentrations in tap water drawn from various sampling points distributed around the region, assess these concentrations by reference to guideline values and study possible differences between the two supply areas. Tap water samples were collected from 34 sampling points in 7 towns in the Madrid region (19-29 April 2010), and 23 contaminants (metals, nitrates, disinfection by-product and Mutagen X levels) were quantified. We undertook a descriptive analysis of the contaminant concentrations in the water and compared them between the two water supply areas (Wilcoxon test). We created maps representing the distribution of the concentrations observed at water sampling points and assessed the correlations (Spearman's coefficient) between the different parameters measured. The concentrations of the contaminants were below guideline values. There were differences between the two supply areas in concentration of nitrates (p value = 0.0051) and certain disinfection by-products. While there were positive correlations (rho >0.70) among some disinfection by-products, no correlations were found in metals or nitrates. The differences in nitrate levels could be linked to differences in farming/industrial activities in the catchment areas and in disinfection by-products might be related to the existence of different treatment systems or bromine content in source waters.
Subject(s)
Neoplasms/epidemiology , Water Pollutants, Chemical/analysis , Disinfection , Humans , Spain/epidemiology , Water/chemistry , Water SupplyABSTRACT
INTRODUCTION: Exposure to organochlorine compounds (OCs) may interfere with thyroid hormone (TH) homeostasis. The disruption of the deiodinase (DIO) enzymes has been proposed as a mechanism of action. AIM: To evaluate the association between exposure to OCs and TH status in pregnant women, as well as to explore the role of genetic variations in the DIO1 and DIO2 genes. METHODS: The study population (n=1128) was composed of pregnant women who participated in the INMA Project (Spain, 2003-2006). Hexachlorobenzene (HCB), 1,1-dichloro-2,2-bis(4-chlorophenyl)ethylene (4,4´-DDE), b-hexachlorocyclohexane (b-HCH), polychlorobiphenyl (PCB) congeners 138, 153 and 180, thyroid stimulating hormone (TSH), total triiodothyronine (TT3) and free thyroxine (FT4) were measured in serum samples taken during the first trimester of pregnancy (mean [standard deviation (SD)]: 13.5 [2] weeks of gestation). Polymorphisms in DIO1 (rs2235544) and DIO2 (rs12885300) were genotyped in maternal DNA. Sociodemographic and dietary characteristics were obtained by questionnaire. RESULTS: A 2-fold increase in HCB was associated with lower TT3 (% change=-1.48; 95%CI: -2.36, -0.60). Women in the third tertile for b-HCH had lower TT3 (% change=-3.19; 95%CI: -5.64, -0.67). The interactions between DIO1 rs2235544 and PCB153 and b-HCH were statistically significant. The inverse association between PCB153 and TT3 was the strongest among women with AA genotype. Women with CC genotype presented the strongest inverse association between b-HCH and FT4. CONCLUSION: Exposure to HCB and b-HCH was associated to a disruption in maternal TT3. The DIO1 rs2235544 SNP modified the association between exposure to some of the OCs (specifically b-HCH and PCB153) and maternal thyroid hormone levels. These results strengthen the hypothesis that DIO enzymes play a role in explaining the disruption of thyroid hormones in relation to exposure to OCs.
Subject(s)
Hydrocarbons, Chlorinated/blood , Iodide Peroxidase/genetics , Pregnancy Trimester, First/blood , Pregnancy/blood , Thyroxine/blood , Triiodothyronine/blood , Adult , Diet , Female , Humans , Spain , Thyrotropin/bloodABSTRACT
BACKGROUND: Several studies have reported decreases in birth size associated with exposure to organochlorine compounds (OCs), but uncertainties remain regarding the critical windows of prenatal exposure and the effects on fetal body segments. OBJECTIVE: We examined the relationship between prenatal OC concentrations and fetal anthropometry. METHODS: We measured 4,4´-dichlorodiphenyldichloroethylene (4,4´-DDE), hexachlorobenzene (HCB), and polychlorinated biphenyl (PCB) congeners (138, 153, and 180) in 2,369 maternal and 1,140 cord serum samples in four Spanish cohorts (2003-2008). We used linear mixed models to obtain longitudinal growth curves for estimated fetal weight (EFW), abdominal circumference (AC), biparietal diameter (BPD), and femur length (FL) adjusted by parental and fetal characteristics. We calculated standard deviation (SD) scores of growth at 0-12, 12-20, and 20-34 weeks of gestation as well as size at gestational week 34 for the four parameters. We studied the association between OCs and the fetal outcomes by cohort-specific linear models and subsequent meta-analyses. RESULTS: PCBs were associated with a reduction in AC up to mid-pregnancy, and BPD and FL from gestational week 20 onward. An inverse association was also found between HCB and AC growth in early pregnancy. The reduction of these parameters ranged from -4% to -2% for a doubling in the OC concentrations. No association between 4,4´-DDE and fetal growth was observed. CONCLUSIONS: To our knowledge, this is the first study to report an association between prenatal exposure to some PCBs and HCB and fetal growth: AC during the first two trimesters of pregnancy, and BPD and FL later in pregnancy. CITATION: Lopez-Espinosa MJ, Murcia M, Iñiguez C, Vizcaino E, Costa O, Fernández-Somoano A, Basterrechea M, Lertxundi A, Guxens M, Gascon M, Goñi-Irigoyen F, Grimalt JO, Tardón A, Ballester F. 2016. Organochlorine compounds and ultrasound measurements of fetal growth in the INMA cohort (Spain). Environ Health Perspect 124:157-163; http://dx.doi.org/10.1289/ehp.1408907.
Subject(s)
Fetal Development/drug effects , Hydrocarbons, Chlorinated/toxicity , Maternal Exposure/adverse effects , Adult , Female , Humans , Pregnancy , Spain , Ultrasonography, PrenatalABSTRACT
BACKGROUND: A plant of lindane in Barakaldo produced discharges of hexachlorocyclohexane (HCH). Closed in 1987 leaving inside 4500Tm; the problem was not solved until 2002. A judicial process required an epidemiological assessment of the possible contamination The aim of this study is to measure the degree of impregnation of the POPs in the nearby population. METHODS: Cross-sectional study conducted in 2008, 154 volunteers from three health centres in Barakaldo and 270 controls from Bilbao, Alonsotegi and Balmaseda. We measured serum levels of eight organochlorine pesticides, and seven polychlorinated biphenyls (PCBs). We used the χ² test to study the association between categorical variables and t test of Student to compare geometric means. Confounding factors were adjusted using a linear regression model. RESULTS: There was a detectable compound average of 6.3 per person. PCBs 52 and 101, α -HCH, ß-endosulfan and heptachlor epoxide could not be quantified; PCB 28, γ-HCH and p, p'-DDT were detected in 6.6, 0.9 and 8.05 % of subjects respectively and the ß-HCH, HCB, p, p'-DDE, and PCBs 118, 138, 153 and 180 in the 73.8, 87.3, 98.6, 59.2, 97.6, 98.6 y 98.6 % respectively. After adjusting for age, there were no higher levels of ß-HCH in Barakaldo than in controls, (beta = 0.02, SE = 0.07), or HCB, p, p'-DDE, PCB 118, PCB 138, PCB 153 and PCB 180. CONCLUSION: Six years after having solved the problem near to the factory and storage of HCH, there was no significantly higher levels of HCH, after adjustment for age.
Subject(s)
Environmental Exposure/statistics & numerical data , Environmental Pollutants/blood , Hexachlorocyclohexane/blood , Hydrocarbons, Chlorinated/blood , Insecticides/blood , Polychlorinated Biphenyls/blood , Adult , Aged , Chi-Square Distribution , Cross-Sectional Studies , Environmental Exposure/analysis , Female , Humans , Industrial Waste/analysis , Linear Models , Male , Middle Aged , Population Surveillance , Spain , Urban PopulationABSTRACT
Fundamentos: Una fábrica de lindano de Barakaldo generó múltiples vertidos de hexaclorociclohexano (HCH). Cerró en 1987 dejando 4.500Tm en su interior, no solucionándose el problema hasta 2002. Un proceso judicial requirió una evaluación epidemiológica de la posible contaminación. Este trabajo pretende medir la impregnación de COPs en la población cercana a la planta. Métodos: Estudio transversal, realizado en 2008, de 154 personas voluntarias de tres centros de salud de Barakaldo y 270 personas controles de Bilbao, Alonsotegi y Balmaseda. Se cuantificaron en suero ocho plaguicidas organoclorados y siete PCBs. Se utilizó la X² para contrastar la asociación entre variables categóricas y la t de Student para comparar medias geométricas. Se ajustaron factores de confusión mediante regresión lineal. Resultados: Se detectaron 6,3 compuestos de media detectables por persona. No se cuantificaron PCB 52 y 101, alpha-HCH, Beta-Endosulfán y Hep-tacloro-Epóxido; el PCB 28, γ-HCH y p,p-DDT en un 6,6, 0,9 y 8,05%; y el Beta-HCH , HCB, p,p-DDE y PCB 118, 138, 153 y 180 en el 73,8, 87,3, 98,6, 59,2, 97,6, 98,6 y 98,6% de los individuos, respectivamente. Ajustando por la edad no se observaron niveles más elevados en Barakaldo que en la población control de Beta-HCH (beta= 0,02; EE= 0,07), ni de HCB, p,p-DDE, PCB 118, 138, 153 y 180. Conclusiones: Seis años después de resolverse el problema de los residuos en la población cercana a la fábrica de producción y de un almacenamiento masivo de HCH, no se observaron niveles significativamente mayores de HCH, tras su ajuste por edad(AU)
Bakcground: A plant of lindane in Barakaldo produced discharges of hexachlorocyclohexane (HCH). Closed in 1987 leaving inside 4500Tm; the problem was not solved until 2002. A judicial process required an epidemiological assessment of the possible contamination The aim of this study is to measure the degree of impregnation of the POPs in the nearby population. Methods: Cross-sectional study conducted in 2008, 154 volunteers from three health centres in Barakaldo and 270 controls from Bilbao, Alonsotegi and Balmaseda. We measured serum levels of eight organochlorine pesticides, and seven polychlorinated biphenyls (PCBs). We used the X² test to study the association between categorical variables and t test of Student to compare geometric means. Confounding factors were adjusted using a linear regression model. Results: There was a detectable compound average of 6.3 per person. PCBs 52 and 101, alpha-HCH, Beta-endosulfan and heptachlor epoxide could not be quantified; PCB 28, γ-HCH and p, p'-DDT were detected in 6.6, 0.9 and 8.05 % of subjects respectively and the Beta-HCH, HCB, p, p'-DDE, and PCBs 118, 138, 153 and 180 in the 73.8, 87.3, 98.6, 59.2, 97.6, 98.6 y 98.6 % respectively. After adjusting for age, there were no higher levels of BetaHCH in Barakaldo than in controls, (beta = 0.02, SE = 0.07), or HCB, p, p'DDE, PCB 118, PCB 138, PCB 153 and PCB 180. Conclusion: Six years after having solved the problem near to the factory and storage of HCH, there was no significantly higher levels of HCH, after adjustment for age(AU)