From: Environmental exposure assessment in European birth cohorts: results from the ENRIECO project
Exposure topic | N * | Description |
---|---|---|
Outdoor air pollution | 27 | ·Many cohorts assessed outdoor air pollution exposure (27 cohorts). |
·Air pollution modeling is becoming increasingly the method of choice: land-use regression modeling (18 cohorts) and dispersion modeling (10 cohorts). | ||
·Sixteen cohorts are currently participating in the collaborative EU-funded ESCAPE project that adds land-use regression modeling of nitrogen oxides, particulate matter, soot and particle composition to existing cohort studies using a standardized protocol. | ||
 |  | ·Most cohorts currently have data on exposure during pregnancy and/or early life. |
Water contamination | 13 | ·Disinfection by-products were studied most. |
·Exposure assessment usually by means of a combination of questionnaires and individual measurements or routinely collected measurement data (8 cohorts). | ||
·Validation by means of biomonitoring in a small number of subjects (3 cohorts). | ||
 |  | ·Most studies assessed exposure during pregnancy. |
Allergens & microbial agents | 27 | ·Exposure to cat and dog allergen was assessed by means of questionnaires in all cohorts and by means of measurements in house dust samples in 9 and 4 cohorts, respectively. |
·Mite allergen levels were measured in settled house dust samples in 10 cohorts. | ||
·Mold exposure was mainly assessed by means of questionnaires. | ||
 |  | ·Exposure was assessed during infancy and/or early childhood in most studies. |
Metals | 20 | ·Most cohorts have analyzed the effects of low-level environmental exposure to mercury (Hg; 15 cohorts) and lead (Pb; 16 cohorts); little attention to other metals. |
·Exposure was mainly assessed by means of biomonitoring. Five cohorts used questionnaires, two of them in addition to biomonitoring, | ||
·There are well-standardized protocols for most of the metals. | ||
·Inductively coupled plasma mass spectrometry (ICP-MS) and atomic absorption spectroscopy (AAS) were used most. | ||
 |  | ·Most measurements were performed in cord blood; other non-invasive matrices such as hair and urine are gaining attention. |
Pesticides a | 18 | ·Many studies assessed household use (16 cohorts); and occupational exposure (13 cohorts), fewer cohorts assessed dietary exposure (6 cohorts) or residence proximity to crops (2 cohorts). |
 |  | ·Exposures via household use, occupational exposure and diet, were mainly assessed by means of questionnaires. |
Persistent organic pollutants | 19 | ·Exposure assessment by means of high performance liquid chromatography (HPLC) measurements in biological samples with adjustment for lipid content. |
·Variation between studies with regard to sampling medium, timing of sample collection and lipid adjustment. | ||
 |  | Most data available for polychlorinated biphenyl (PCB) and dichlorodiphenyltrichloroethane (DDT). |
Other chemical exposures b | 17 | ·Few cohorts have measured these contaminants (13 cohorts), but this is a rapidly developing field and more cohorts are planning to assess exposure to other chemicals (7 cohorts). |
·Exposure was mainly assessed by means of biomonitoring. | ||
 |  | There is heterogeneity with regard to the type of biological media used and the timing of the exposure measurement. |
Radiation | 12 | Ionizing radiation |
·Mainly assessed by questionnaire: maternal occupational exposures (3 cohorts), prenatal medical ionizing radiation exposures (6 cohorts); 2 cohorts currently plan to ask questions about medical radiation exposures in children. | ||
·1 cohort is planning to assess residential radon exposure using geographical methods. | ||
·No standardized questionnaires or protocols in this field. | ||
Ultraviolet (UV) | ||
·Only six cohorts are collecting UV-related data through questionnaire questions on sunburn in children, use of sun beds during pregnancy, and time spent outdoors. | ||
·None of the cohorts collect data on maternal and child skin type, sunscreen use, or clothing. | ||
·Standard questionnaires are not available. | ||
Non-ionizing radiation | ||
·Very few cohorts assess exposure to non-ionizing radiation: 2 cohorts include occupational electromagnetic field (EMF) exposure in their questionnaires, 2 cohorts assess extreme low frequency (ELF) exposure to overhead high-voltage power lines through geographical information from electricity companies, 2 cohorts include questions about mobile phone use of the mother during pregnancy and 4 on children’s mobile phone use. | ||
·A few cohorts have started using base-station maps combined with information from home appliances and personal radio frequency (RF) exposimeters, in order to estimate whole body RF/ELF-EMF exposure. | ||
 |  | ·There are no standardized or validated questionnaires, models or protocols in use at this moment. |
Smoking and second hand tobacco smoke | 37 | ·All cohorts have information about exposure during pregnancy and 29 cohorts in addition assessed exposure at different periods during infancy and childhood. |
 |  | Assessment mainly by questionnaire; cotinine measurements in biological samples (mainly urine) in 14 cohorts. |
Noise | 14 | ·All cohorts used questionnaire assessments, mainly about noise annoyance. |
·5 cohorts used noise propagation modeling or noise maps. | ||
·Traffic is the source of noise that has been studied most. | ||
 |  | ·Most cohorts assessed exposure during pregnancy. |
Occupational exposures | 33 | ·All cohorts have information on maternal occupation and most cohorts (n=26) have information on paternal occupation for at least one point in time. |
·Data mainly collected by means of questionnaires (most often job title; sometimes checklist occupation or occupational exposures). | ||
 |  | ·Coding of maternal job title (n=17) or use of Job Exposure Matrices (JEM) (n=8) planned/done in a number of studies. |