Acute effects of urban air pollution on respiratory emergency hospital admissions in the Canary Islands
In: Air quality, atmosphere and health: an international journal, Volume 9, Issue 7, p. 713-722
ISSN: 1873-9326
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In: Air quality, atmosphere and health: an international journal, Volume 9, Issue 7, p. 713-722
ISSN: 1873-9326
Our aim was to investigate the relation between PBDEs and fetal growth or newborn anthropometry in a Spanish cohort (2003-2008). PBDE congeners (BDE-47, -99, -153, -154, and -209) were determined in serum of 670 mothers at gestational week 12 and in 534 umbilical cord samples. Abdominal circumference (AC), estimated fetal weight (EFW), femur length (FL), and biparietal diameter (BPD) during gestation were measured by ultrasounds. At birth, weight (BW), head circumference (HC), and length (BL) were also measured. We assessed growth in the intervals between 12-20 and 20-34 weeks of gestation and size at birth by standard deviation (SD)-scores adjusted for constitutional characteristics. We conducted multivariate linear regression analyses between PBDE congeners and their sum (ΣPBDEs) and outcomes. We found statistically significant inverse associations between ΣPBDEs and AC, EFW, and BPD at weeks 20-34 and HC at birth. Regarding congeners, the association was clearer with BDE-99, with inverse associations being found with AC, EFW, and BPD at weeks 20-34, and with BW and HC at delivery. These outcomes decreased between 1.3% and 3.5% for each 2-fold PBDE increase. Concerning matrices, we found statistically significant inverse associations with BPD, HC, and BW when using maternal serum, and for AC and EFW with cord serum. In conclusion, PBDEs may impair fetal growth in late pregnancy and reduce birth size. © 2015 American Chemical Society. ; The authors are grateful to mothers who participated in the study and to San Agustin Hospital in Aviles and La Fe Hospital in Valencia. This work was supported by grants from the European Union (FP7-ENV-2011 cod 282957 and HEALTH.2010.2.4.5-1), and grants from the Instituto de Salud Carlos III in Spain (Red INMA G03/176, CB06/02/0041, and FIS-FEDER PI03/1615, PI04/1509, PI04/1112, PI04/1931, PI04/2018, PI05/1079, PI05/1052, PI06/1213, PI07/0314, PI09/02647, PI09/02311, PI11/01007, PI11/02591, PI11/02038, MS11/0178, PI13/1944, PI13/02429, PI14/00891, and PI14/01687), Conselleria de Sanitat of the Generalitat Valenciana, Obra Social Cajastur and University of Oviedo. ; Peer reviewed
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BACKGROUND: Prenatal perfluorooctanoate (PFOA) exposure has been associated with reduced birth weight but maternal glomerular filtration rate (GFR) may attenuate this association. Further, this association remains unclear for other perfluoroalkyl substances (PFAS), such as perfluorooctane sulfonate (PFOS), perfluorohexane sulfonate (PFHxS), and perfluorononanoate (PFNA). We estimated associations between prenatal PFAS exposure and birth outcomes, and the influence of GFR, in a Spanish birth cohort. METHODS: We measured PFHxS, PFOS, PFOA, and PFNA in 1st-trimester maternal plasma (years: 2003-2008) in 1202 mother-child pairs. Continuous birth outcomes included standardized weight, length, head circumference, and gestational age. Binary outcomes included low birth weight (LBW), small-for-gestational-age, and preterm birth. We calculated maternal GFR from plasma-creatinine measurements in the 1st-trimester of pregnancy (n=765) using the Cockcroft-Gault formula. We used mixed-effects linear and logistic models with region of residence as random effect and adjustment for maternal age, parity, pre-pregnancy BMI, and fish intake during pregnancy. RESULTS: Newborns in this study weighted on average 3263g and had a median gestational age of 39.8weeks. The most abundant PFAS were PFOS and PFOA (median: 6.05 and 2.35ng/mL, respectively). Overall, PFAS concentrations were not significantly associated to birth outcomes. PFOA, PFHxS, and PFNA showed weak, non-statistically significant associations with reduced birth weights ranging from 8.6g to 10.3g per doubling of exposure. Higher PFOS exposure was associated with an OR of 1.90 (95% CI: 0.98, 3.68) for LBW (similar in births-at-term) in boys. Maternal GFR did not confound the associations. CONCLUSIONS: In this study, PFAS showed little association with birth outcomes. Higher PFHxS, PFOA, and PFNA concentrations were non-significantly associated with reduced birth weight. The association between PFOS and LBW seemed to be sex-specific. Finally, maternal GFR measured early during pregnancy had little influence on the estimated associations. ; This study was funded by grants from the European Union (FP7-ENV-2011 cod 282957 and HEALTH.2010.2.4.5-1), and from Spain: Instituto de Salud Carlos III, Ministry of Health CIBERESP, the Conselleria de Sanitat, Generalitat Valenciana, (Red INMA G03/176; CB06/02/0041; PI041436, PI081151, PI06/0867, PS09/00090, PI13/02187; FIS-FEDER: PI03/1615, PI04/1509, PI04/1112, PI04/1931, PI05/1079, PI05/1052, PI06/1213, PI07/0314, PI09/02647, PI11/01007, PI11/02591, PI11/ 02038, PI12/01890, PI13/1944, PI13/2032, PI14/00891, and PI14/1687; pre-doctoral grant PFIS - FI14/00099 and; Miguel Servet-FEDER: CP11/0178 and CPII16/00051), Department of Health of the Basque Government (2005111093 and 2009111069); the Provincial Government of Gipuzkoa (DFG06/004 and DFG08/001); and the Generalitat de Catalunya-CIRIT (1999SGR 00241)
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Background: Several studies have investigated the possible association between prenatal exposure to perfluoroalkyl substances (PFASs) and birth anthropometry. However, none has assessed fetal size longitudinally. We studied the possible association between PFASs and fetal biometry. Methods: In 1230 mother-child pairs of three cohorts from the Spanish INMA-Project, we analyzed perfluorohexanesulfonic acid (PFHxS), perfluorooctanesulfonic acid (PFOS), perfluorooctanoic acid (PFOA), and perfluorononanoic acid (PFNA) in first-trimester maternal plasma (collection: 2003-2008). We measured abdominal circumference (AC), femur length (FL), biparietal diameter (BPD), and estimated fetal weight (EFW) by ultrasounds at 12, 20, and 34 gestational weeks. We conducted multivariable linear regression analyses between log2-transformed (PFASs) and SD-scores of fetal parameters in each cohort and subsequent meta-analysis. We also assessed effect modification by sex and maternal smoking. Results: PFHxS, PFOA, PFOS, and PFNA medians were: 0.58, 2.35, 6.05, and 0.65 ng/mL, respectively. There were no associations for the whole population in any trimester of pregnancy. However, we found an indication that maternal smoking modified the effect in different directions depending on the PFAS. Among smokers (31%), we found negative associations between both PFOA and PFNA and FL or EFW at week 20 (% change ranging between -6.8% and -5.7% per twofold PFAS increase) and positive associations between PFHxS or PFOS and BPD at week 34 (6.8% and 6.3%, respectively). Conclusions: Results did not suggest an overall association between prenatal PFASs and fetal growth. The results among smokers should be taken with caution and further studies are warranted to elucidate the possible role of smoking in this association. ; This work was supported by grants from the European Union [FP7-ENV-2011 cod 282957 and HEALTH.2010.2.4.5-1] and from Spain: Instituto de Salud Carlos III [Red INMA G03/176, CB06/02/0041, FIS-FEDER: PI03/1615, PI041436, PI04/1509, PI04/1112, PI04/1931, PI05/1079, PI05/1052, PI06/0867, PI06/1213, PI07/0314, PI081151, PI09/02647, PI09/00090, PI11/01007, PI11/02591, PI11/02038, PI12/01890, PI13/1944, PI13/2032, PI14/00891, PI14/01687, PI16/1288, and PI17/00663; Miguel Servet-FEDER CP11/0178, Miguel Servet-FSE: MS16/00128, and MSII16/00051; and PFIS-FI14/00099]; Alicia Koplowitz Foundation 2017; Generalitat Valenciana [FISABIO-UGP 15-230, 15-244, and 15-249]; Department of Health of the Basque Government [2005111093 and 2009111069]; the Provincial Government of Gipuzkoa [DFG06/004 and DFG08/001]; and the Generalitat de Catalunya-CIRIT [1999SGR 00241].
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BACKGROUND: Air pollution exposure during pregnancy has been associated with impaired fetal growth. However, few studies have measured fetal biometry longitudinally, remaining unclear as to whether there are windows of special vulnerability. OBJECTIVE: The aim was to investigate the impact of nitrogen dioxide (NO2) exposure on fetal and neonatal biometry in the Spanish INMA study. METHODS: Biparietal diameter (BPD), femur length (FL), abdominal circumference (AC), and estimated fetal weight (EFW) were evaluated for up to 2,478 fetuses in each trimester of pregnancy. Size at 12, 20, and 34 weeks of gestation and growth between these points, as well as anthropometry at birth, were assessed by SD scores derived using cohort-specific growth curves. Temporally adjusted land-use regression was used to estimate exposure to NO2 at home addresses for up to 2,415 fetuses. Associations were investigated by linear regression in each cohort and subsequent meta-analysis. RESULTS: A 10-μg/m3 increase in average exposure to NO2 during weeks 0-12 was associated with reduced growth at weeks 0-12 in AC (-2.1%; 95% CI: -3.7, -0.6) and EFW (-1.6%; 95% CI: -3.0, -0.3). The same exposure was inversely associated with reduced growth at weeks 20-34 in BPD (-2.6%; 95% CI: -3.9, -1.2), AC (-1.8%; 95% CI: -3.3, -0.2), and EFW (-2.1%; 95% CI: -3.7, -0.2). A less consistent pattern of association was observed for FL. The negative association of this exposure with BPD and EFW was significantly stronger in smoking versus nonsmoking mothers. CONCLUSIONS: Maternal exposure to NO2 in early pregnancy was associated with reduced fetal growth based on ultrasound measures of growth during pregnancy and measures of size at birth. ; This study was funded by grants from the European Union: NEWGENERIS FP6-2003-Food-3-A-016320, FP7-ENV-2011 cod 282957, HEALTH.2010.2.4.5-1; and by grants from Spain: Instituto de Salud Carlos III (Red INMA G03/176, CB06/02/0031, and FIS-FEDER PI03/1615, PI04/1509, PI04/1112, PI04/1931, PI04/2018, PI04/1436, PI05/1079, PI05/1052, PI06/1213, PI07/0314, PI08/1151, PI09/02647, PI09/02311, PI11/01007, PI11/02591, PI11/02038, PI13/1944, PI13/02429, PI14/0891, PI14/1687, and Miguel Servet CP11/00178 and MS13/00054), Conselleria de Sanitat Generalitat Valenciana, Generalitat de Catalunya (CIRIT 1999SGR 00241), Diputación Foral de Guipúzcoa (DFG/004), Departamento de Sanidad y Consumo Gobierno Vasco (2005111093), Obra Social Cajastur, and Oviedo University.
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Introduction: To date, the evidence for an association between perfluoroalkyl substances (PFAS) exposure and attention deficit and hyperactivity disorder (ADHD) is inconclusive. Objective: We investigated the association between early life exposure to perfluorooctane sulfonate (PFOS) and perfluorooctanoic acid (PFOA), and ADHD in a collaborative study including nine European population-based studies, encompassing 4,826 mother-child pairs. Methods: Concentrations of PFOS and PFOA were measured in maternal serum/plasma during pregnancy, or in breast milk, with different timing of sample collection in each cohort. We used a validated pharmacokinetic model of pregnancy and lactation to estimate concentrations of PFOS and PFOA in children at birth and at 3, 6, 12, and 24 months of age. We classified ADHD using recommended cutoff points for each instrument used to derive symptoms scores. We used multiple imputation for missing covariates, logistic regression to model the association between PFAS exposure and ADHD in each study, and combined all adjusted study-specific effect estimates using random-effects meta-analysis. Results: A total of 399 children were classified as having ADHD, with a prevalence ranging from 2.3% to 7.3% in the studies. Early life exposure to PFOS or PFOA was not associated with ADHD during childhood [odds ratios (ORs) ranging from 0.96 (95% CI: 0.87, 1.06) to 1.02 (95% CI: 0.93, 1.11)]. Results from stratified models suggest potential differential effects of PFAS related to child sex and maternal education. Conclusion: We did not identify an increased prevalence of ADHD in association with early life exposure to PFOS and PFOA. However, stratified analyses suggest that there may be an increased prevalence of ADHD in association with PFAS exposure in girls, in children from nulliparous women, and in children from low-educated mothers, all of which warrant further exploration. https://doi.org/10.1289/EHP5444. ; This research was primarily supported by a grant from the European Community's Seventh Framework Program (FP7/2007–2013) under grant agreement Developmental Neurotoxicity Assessment of Mixtures in Children (DENAMIC) no. 282957. M.-A.V. is the recipient of a Research Scholars J1 Award from the Fonds de recherche du Québec–Santé. Norwegian Human Milk Study (HUMIS) research was funded by a grant from the Norwegian Research Council, under the NEVRINOR program grant agreement no. 226402; by PROTECTion against Endocrine Disruptors: Detection, mixtures, health effects, risk assessment and communication, and by European Union (EU) Horizon 2020 Marie Skłodowska-Curie Actions Innovative Training Networks–European Training Network no. 722634. We thank Anteneh Desalegn for his work in the HUMIS biobank. The study was approved by the Regional Ethics Committee for Medical Research in Norway (ref. S-02122) and the Norwegian Data Inspectorate (refs. 2002/1398), and participation did not occur until after informed consent was obtained. The Infancia y Medio Ambiente (INMA) study was funded by grants from the EU: NEWGENERIS FP6-2003-Food-3-A-016320, FP7-ENV-2011 cod 282957, HEALTH.2010.2.4.5-1; and by grants from Spain: Instituto de Salud Carlos III (Red INMA G03/176 and CB06/02/0041, FIS-FEDER:PI 03/1615, PI04/1509, PI04/1112, PI04/1436, PI04/1931, PI/04/2018, PI05/1079, PI05/1052, PI06/0867, PI06/1213, PI07/0314, PI/08/1151, PI09/02647, FIS-PI041436, FIS-PI081151, FISS-PI042018, FISS-PI09/02311, FISPI06/0867 FIS-PS09/00090, FIS-PI07/0252, PS09/00090, PI11/01007, PI11/02591, PI11/02038, PI13/1944, PI13/2032, PI14/00891, PI14/01687, PI16/1288, PI17/00663 and Miguel Servet-FEDER: CP11/00178, MS13/00054, and MSII16/00051), Generalitat de Catalunya-CIRIT 1999SGR 00241, La Fundació La Marató de TV3 (090430), Alicia Koplowitz Foundation 2017, Conselleria de Sanitat Generalitat Valenciana, Department of Health of the Basque Government (2005111093 and 2009111069), Provincial Government of Gipuzkoa (DFG06/004 and DFG08/001), Obra Social Cajastur, Universidad de Oviedo, Consejería de Salud de la Junta de Andalucía (grant no. 183/07), EU Commission (QLK4-1999-01422, QLK4-2002-00603, and CONTAMED FP7-ENV-212502), and Fundación Roger Torné. Global Health Institute Barcelona (ISGlobal) is a member of the CERCA Programme, Generalitat de Catalunya. A full roster of the INMA Project Investigators can be found at http://www.proyectoinma.org/presentacion-inma/listadoinvestigadores/en_listado-investigadores.html. The INUENDO study was funded by the European Commission's Seventh and Fifth Framework Programmes (FP7-ENV-2008-1-226217 and QLK4-CT-2001-00202). The polychorinated biphenyl (PCB) cohort was funded by the U.S. National Institutes of Health (grants R01 CA096525 and R03 TW007152), the EU Seventh Framework Programme FP7/2007-2023 (grant agreement OBELIX, no. 227391), Slovak Research and Development Agency (grants APVT-21-016804, APVV-0571-12, APVV-0444-11), and by the ITMS project (no. 26240120033) based on the supporting operational research and development program from the European Regional Development Fund. ; This research was primarily supported by a grant from the European Community's Seventh Framework Program (FP7/2007–2013) under grant agreement Developmental Neurotoxicity Assessment of Mixtures in Children (DENAMIC) no. 282957. M.-A.V. is the recipient of a Research Scholars J1 Award from the Fonds de recherche du Québec–Santé. Norwegian Human Milk Study (HUMIS) research was funded by a grant from the Norwegian Research Council, under the NEVRINOR program grant agreement no. 226402; by PROTECTion against Endocrine Disruptors: Detection, mixtures, health effects, risk assessment and communication, and by European Union (EU) Horizon 2020 Marie Skłodowska-Curie Actions Innovative Training Networks–European Training Network no. 722634. We thank Anteneh Desalegn for his work in the HUMIS biobank. The study was approved by the Regional Ethics Committee for Medical Research in Norway (ref. S-02122) and the Norwegian Data Inspectorate (refs. 2002/1398), and participation did not occur until after informed consent was obtained. The Infancia y Medio Ambiente (INMA) study was funded by grants from the EU: NEWGENERIS FP6-2003-Food-3-A-016320, FP7-ENV-2011 cod 282957, HEALTH.2010.2.4.5-1; and by grants from Spain: Instituto de Salud Carlos III (Red INMA G03/176 and CB06/02/0041, FIS-FEDER:PI 03/1615, PI04/1509, PI04/1112, PI04/1436, PI04/1931, PI/04/2018, PI05/1079, PI05/1052, PI06/0867, PI06/1213, PI07/0314, PI/08/1151, PI09/02647, FIS-PI041436, FIS-PI081151, FISS-PI042018, FISS-PI09/02311, FISPI06/0867 FIS-PS09/00090, FIS-PI07/0252, PS09/00090, PI11/01007, PI11/02591, PI11/02038, PI13/1944, PI13/2032, PI14/00891, PI14/01687, PI16/1288, PI17/00663 and Miguel Servet-FEDER: CP11/00178, MS13/00054, and MSII16/00051), Generalitat de Catalunya-CIRIT 1999SGR 00241, La Fundació La Marató de TV3 (090430), Alicia Koplowitz Foundation 2017, Conselleria de Sanitat Generalitat Valenciana, Department of Health of the Basque Government (2005111093 and 2009111069), Provincial Government of Gipuzkoa (DFG06/004 and DFG08/001), Obra Social Cajastur, Universidad de Oviedo, Consejería de Salud de la Junta de Andalucía (grant no. 183/07), EU Commission (QLK4-1999-01422, QLK4-2002-00603, and CONTAMED FP7-ENV-212502), and Fundación Roger Torné. Global Health Institute Barcelona (ISGlobal) is a member of the CERCA Programme, Generalitat de Catalunya. A full roster of the INMA Project Investigators can be found at http://www.proyectoinma.org/presentacion-inma/listadoinvestigadores/en_listado-investigadores.html. The INUENDO study was funded by the European Commission's Seventh and Fifth Framework Programmes (FP7-ENV-2008-1-226217 and QLK4-CT-2001-00202). The polychorinated biphenyl (PCB) cohort was funded by the U.S. National Institutes of Health (grants R01 CA096525 and R03 TW007152), the EU Seventh Framework Programme FP7/2007-2023 (grant agreement OBELIX, no. 227391), Slovak Research and Development Agency (grants APVT-21-016804, APVV-0571-12, APVV-0444-11), and by the ITMS project (no. 26240120033) based on the supporting operational research and development program from the European Regional Development Fund.
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