1
|
Furst L, Cipoli Y, Galindo N, Yubero E, Viegas C, Pena P, Nunes T, Feliciano M, Alves C. Comprehensive analysis of particulate matter, gaseous pollutants, and microbiological contamination in an international chain supermarket. ENVIRONMENTAL POLLUTION (BARKING, ESSEX : 1987) 2024; 363:125236. [PMID: 39505100 DOI: 10.1016/j.envpol.2024.125236] [Citation(s) in RCA: 0] [Impact Index Per Article: 0] [Reference Citation Analysis] [Abstract] [Key Words] [Track Full Text] [Subscribe] [Scholar Register] [Received: 09/11/2024] [Revised: 10/24/2024] [Accepted: 11/01/2024] [Indexed: 11/08/2024]
Abstract
Indoor environmental quality is of utmost importance since urban populations spend a large proportion of their life in confined spaces. Supermarkets offer a wide range of products and services that are prone to emitting several air pollutants. This study aimed to perform a comprehensive characterisation of the indoor and outdoor air quality in a multinational supermarket, encompassing not only criteria parameters but also unregulated pollutants of concern. Monitoring included measurements of comfort parameters, CO2, multiple gaseous pollutants, particulate matter (PM10) and bioburden. PM10, volatile organic compounds (VOCs) and carbonyls were subject to chemical speciation. Globally, the supermarket presented CO2, VOCs, and PM10 values below the limits imposed by international regulations. The PM10 concentration in the supermarket was 33.5 ± 23.2 μg/m3, and the indoor-to-outdoor PM10 ratio was 1.76. Carbonaceous constituents represented PM10 mass fractions of 21.6% indoors and 15.3% outdoors. Due to the use of stainless-steel utensils, flour and fermentation processes, the bakery proved to be a pollution hotspot, presenting the highest concentrations of PM10 (73.1 ± 9.16 μg/m3), PM10-bound elements (S, Cl, K, Ca, Ti, and Cr) and acetaldehyde (42.7 μg/m3). The maximum tetrachloroethylene level (130 μg/m3) was obtained in the cleaning products section. The highest values of colony-forming units of bacteria and fungi were recorded in the bakery, and fruit and vegetable section. The most prevalent fungal species was Penicillium sp., corresponding to 56.9% of the total colonies. In addition, other fungal species/sections with toxicological or pathogenic potential were detected (Aspergillus sections Aspergilli, Circumdati, Flavi, Mucor and Fusarium sp.).
Collapse
Affiliation(s)
- Leonardo Furst
- Department of Environment and Planning, Centre for Environmental and Marine Studies (CESAM), University of Aveiro, 3810-193 Aveiro, Portugal.
| | - Yago Cipoli
- Department of Environment and Planning, Centre for Environmental and Marine Studies (CESAM), University of Aveiro, 3810-193 Aveiro, Portugal
| | - Nuria Galindo
- Department of Applied Physics, Miguel Hernández University, Elche, Spain
| | - Eduardo Yubero
- Department of Applied Physics, Miguel Hernández University, Elche, Spain
| | - Carla Viegas
- H&TRC-Health & Technology Research Center, ESTeSL-Escola Superior de Tecnologia e Saúde, Instituto Politécnico de Lisboa, 1990-096 Lisbon, Portugal; Public Health Research Centre, Comprehensive Health Research Center, CHRC, REAL, CCAL, NOVA National School of Public Health, NOVA University Lisbon, 1099-085 Lisbon, Portugal
| | - Pedro Pena
- H&TRC-Health & Technology Research Center, ESTeSL-Escola Superior de Tecnologia e Saúde, Instituto Politécnico de Lisboa, 1990-096 Lisbon, Portugal; Public Health Research Centre, Comprehensive Health Research Center, CHRC, REAL, CCAL, NOVA National School of Public Health, NOVA University Lisbon, 1099-085 Lisbon, Portugal
| | - Teresa Nunes
- Department of Environment and Planning, Centre for Environmental and Marine Studies (CESAM), University of Aveiro, 3810-193 Aveiro, Portugal
| | - Manuel Feliciano
- Centro de Investigação de Montanha (CIMO), Instituto Politécnico de Bragança, Campus de Santa Apolónia, 5300-253 Bragança, Portugal; Laboratório Associado para a Sustentabilidade e Tecnologia em Regiões de Montanha (SusTEC), Instituto Politécnico de Bragança, Campus de Santa Apolónia, 5300-253 Bragança, Portugal
| | - Célia Alves
- Department of Environment and Planning, Centre for Environmental and Marine Studies (CESAM), University of Aveiro, 3810-193 Aveiro, Portugal
| |
Collapse
|
2
|
Ge L, Liu J, Kang X, Wang W, Zhang D. Association of serum individual and mixed aldehydes with depressive symptoms in the general population: A machine learning study. J Affect Disord 2024; 345:8-17. [PMID: 37865348 DOI: 10.1016/j.jad.2023.10.123] [Citation(s) in RCA: 0] [Impact Index Per Article: 0] [Reference Citation Analysis] [Abstract] [Key Words] [MESH Headings] [Track Full Text] [Journal Information] [Submit a Manuscript] [Subscribe] [Scholar Register] [Received: 08/10/2023] [Revised: 10/16/2023] [Accepted: 10/18/2023] [Indexed: 10/23/2023]
Abstract
BACKGROUND Humans have many opportunities to be exposed to aldehydes which have potential mechanisms for causing depression. We aimed to explore the relationships between serum individual and mixed aldehydes with depressive symptoms in general population. METHODS The data was extracted from the National Health and Nutrition Examination Survey 2013-2014. Depressive symptoms were assessed by Patient Health Questionnaire-9. Weighted binomial logistic regression and Bayesian kernel machine regression (BKMR) model were used to explore the association of six individual aldehyde and mixed aldehydes with depressive symptoms, respectively. Sex stratification analysis and sensitivity analysis were conducted. RESULTS A total of 701 participants were included. We found a positive association between the highest (Q4) versus lowest quartile (Q1) of butyraldehyde with depressive symptoms (OR: 2.86, 95 % CI: 1.22-6.68), and a negative association between the Q3 versus Q1 of benzaldehyde (0.21, 0.07-0.60) and isopentanaldehyde (0.28, 0.08-0.90) with depressive symptoms in multivariate-adjusted model. The mixed aldehydes were positively associated with depressive symptoms using BKMR model, and butyraldehyde and heptanaldehyde were the dominant aldehydes. Several aldehydes, such as butyraldehyde and benzaldehyde, interacted with each other in their effects on depressive symptoms. The results of gender stratification analysis showed that butyraldehyde was the major contributor to the total effect of aldehydes on depressive symptoms in males, while heptanaldehyde was the dominant aldehyde in females. LIMITATIONS Causality cannot be inferred in this cross-sectional study. CONCLUSIONS Our study indicated that mixed aldehydes can increase the risk of depressive symptoms, of which butyraldehyde and heptanaldehyde were the major contributing aldehydes.
Collapse
Affiliation(s)
- Lin Ge
- Department of Epidemiology and Health Statistics, the School of Public Health of Qingdao University, No. 308 Ningxia Road, Qingdao 266071, China
| | - Jin Liu
- Department of Epidemiology and Health Statistics, the School of Public Health of Qingdao University, No. 308 Ningxia Road, Qingdao 266071, China
| | - Xiao Kang
- Department of Epidemiology and Health Statistics, the School of Public Health of Qingdao University, No. 308 Ningxia Road, Qingdao 266071, China
| | - Weijing Wang
- Department of Epidemiology and Health Statistics, the School of Public Health of Qingdao University, No. 308 Ningxia Road, Qingdao 266071, China.
| | - Dongfeng Zhang
- Department of Epidemiology and Health Statistics, the School of Public Health of Qingdao University, No. 308 Ningxia Road, Qingdao 266071, China.
| |
Collapse
|
3
|
Miligi L, Piro S, Airoldi C, Di Rico R, Ricci R, Paredes Alpaca RI, De Pasquale F, Veraldi A, Ranucci A, Massari S, Marinaccio A, Stoppa G, Cenni A, Trane C, Peruzzi A, Aprea MC. Formaldehyde and Acetaldehyde Exposure in "Non-Traditional" Occupational Sectors: Bakeries and Pastry Producers. INTERNATIONAL JOURNAL OF ENVIRONMENTAL RESEARCH AND PUBLIC HEALTH 2023; 20:1983. [PMID: 36767350 PMCID: PMC9916260 DOI: 10.3390/ijerph20031983] [Citation(s) in RCA: 0] [Impact Index Per Article: 0] [Reference Citation Analysis] [Abstract] [Key Words] [MESH Headings] [Track Full Text] [Figures] [Subscribe] [Scholar Register] [Received: 10/24/2022] [Revised: 01/12/2023] [Accepted: 01/17/2023] [Indexed: 06/18/2023]
Abstract
INTRODUCTION Formaldehyde, a colorless and highly irritating substance, causes cancer of the nasopharynx and leukemia. Furthermore, it is one of the environmental mutagens to which humans are most abundantly exposed. Acetaldehyde was recently classified as carcinogen class 1B and mutagen class 2 in Annex VI EC regulation. Occupational exposure to the two aldehydes occurs in a wide variety of occupations and industries. The aim of this study is to deepen exposure to the two aldehydes in the non-traditional productive sectors of bakeries and pastry producers. METHODS The evaluation of exposure to formaldehyde and acetaldehyde was conducted in Italy in 2019, in specific tasks and positions of 11 bakeries and pastry producers (115 measures, of which 57.4% were in fixed positions and the rest were personal air sampling). The measurements were performed using Radiello© radial diffusion samplers. A logarithmic transformation of the data was performed, and the correlation between the two substances was calculated. Moreover, linear models considering the log-formaldehyde as the outcome and adjusting for log-acetaldehyde values were used. RESULTS The study identified high levels of acetaldehyde and formaldehyde exposure in the monitored workplaces. Higher mean values were observed in the leavening phase (8.39 µg/m3 and 3.39 µg/m3 for log-transformed data acetaldehyde and formaldehyde, respectively). The adjusted univariate analyses show statistically significant factors for formaldehyde as the presence of yeast, the presence of type 1 flour, the use of barley, the use of fats, the type of production, the use of spelt, and the presence of type 0 flour. CONCLUSIONS The measurements confirmed the release of formaldehyde and acetaldehyde in bakeries and pastry industries, especially in some phases of the work process, such as leavening.
Collapse
Affiliation(s)
- Lucia Miligi
- Occupational and Environmental Epidemiology Branch, Cancer Risk Factors and Lifestyle Epidemiology Unit, Institute for Cancer Research, Prevention and Clinical Network (ISPRO), 50139 Florence, Italy
| | - Sara Piro
- Occupational and Environmental Epidemiology Branch, Cancer Risk Factors and Lifestyle Epidemiology Unit, Institute for Cancer Research, Prevention and Clinical Network (ISPRO), 50139 Florence, Italy
| | - Chiara Airoldi
- Occupational and Environmental Epidemiology Branch, Cancer Risk Factors and Lifestyle Epidemiology Unit, Institute for Cancer Research, Prevention and Clinical Network (ISPRO), 50139 Florence, Italy
| | - Renato Di Rico
- Local Health Unit AUSL Modena, SPSAL-Department of Public Health, 41121 Modena, Italy
| | - Raffaella Ricci
- Local Health Unit AUSL Modena, SPSAL-Department of Public Health, 41121 Modena, Italy
| | | | - Fabrizio De Pasquale
- Local Health Unit AUSL Modena, SPSAL-Department of Public Health, 41121 Modena, Italy
| | - Angela Veraldi
- Occupational and Environmental Epidemiology Branch, Cancer Risk Factors and Lifestyle Epidemiology Unit, Institute for Cancer Research, Prevention and Clinical Network (ISPRO), 50139 Florence, Italy
| | - Alessandra Ranucci
- Occupational and Environmental Epidemiology Branch, Cancer Risk Factors and Lifestyle Epidemiology Unit, Institute for Cancer Research, Prevention and Clinical Network (ISPRO), 50139 Florence, Italy
| | - Stefania Massari
- Department of Occupational and Environmental Medicine, Epidemiology and Hygiene, Italian Workers’ Compensation Authority (INAIL), 00143 Rome, Italy
| | - Alessandro Marinaccio
- Department of Occupational and Environmental Medicine, Epidemiology and Hygiene, Italian Workers’ Compensation Authority (INAIL), 00143 Rome, Italy
| | - Giorgia Stoppa
- Occupational and Environmental Epidemiology Branch, Cancer Risk Factors and Lifestyle Epidemiology Unit, Institute for Cancer Research, Prevention and Clinical Network (ISPRO), 50139 Florence, Italy
| | - Anna Cenni
- Unit of Occupational Hygiene and Toxicology, Public Health Laboratory, Department of Prevention, AUSL South-East Tuscany, 53100 Siena, Italy
| | - Cinzia Trane
- Unit of Occupational Hygiene and Toxicology, Public Health Laboratory, Department of Prevention, AUSL South-East Tuscany, 53100 Siena, Italy
| | - Antonio Peruzzi
- Unit of Occupational Hygiene and Toxicology, Public Health Laboratory, Department of Prevention, AUSL South-East Tuscany, 53100 Siena, Italy
| | - Maria Cristina Aprea
- Unit of Occupational Hygiene and Toxicology, Public Health Laboratory, Department of Prevention, AUSL South-East Tuscany, 53100 Siena, Italy
| |
Collapse
|
4
|
Binazzi A, Mensi C, Miligi L, Di Marzio D, Zajacova J, Galli P, Camagni A, Calisti R, Balestri A, Murano S, Piro S, d’Errico A, Bonzini M, Massacesi S, Sorasio D, Marinaccio A. Exposures to IARC Carcinogenic Agents in Work Settings Not Traditionally Associated with Sinonasal Cancer Risk: The Experience of the Italian National Sinonasal Cancer Registry. INTERNATIONAL JOURNAL OF ENVIRONMENTAL RESEARCH AND PUBLIC HEALTH 2021; 18:12593. [PMID: 34886319 PMCID: PMC8656996 DOI: 10.3390/ijerph182312593] [Citation(s) in RCA: 4] [Impact Index Per Article: 1.3] [Reference Citation Analysis] [Abstract] [Key Words] [MESH Headings] [Track Full Text] [Download PDF] [Figures] [Subscribe] [Scholar Register] [Received: 10/04/2021] [Revised: 11/23/2021] [Accepted: 11/24/2021] [Indexed: 11/16/2022]
Abstract
The aim of this study is to highlight tasks and jobs not commonly considered at high risk for sinonasal cancer (SNC) identified by Regional Operating Centers currently active in the Italian National Sinonasal Cancer Registry (ReNaTuNS), which retrieve occupational histories through a standardized questionnaire. Data on exposures to IARC carcinogenic agents in work settings unknown to be associated with SNC risk were collected and analyzed. Out of 2,208 SNC cases recorded in the ReNaTuNS database, 216 cases and their worked exposure periods were analyzed. Unsuspected jobs with exposure to wood dust include construction-related tasks, production of resins, agriculture and livestock jobs (straw and sawdust), and heel factory work (cork dust). Other examples are hairdressers, bakers (formaldehyde), dressmakers, technical assistants, wool and artificial fiber spinners, and upholsterers (textile dusts). Moreover, settings with coexposure to different agents (e.g., wood with leather dusts and chromium-nickel compounds) were recognized. The study describes jobs where the existence of carcinogenic agents associated with SNC risk is unexpected or not resulting among primary materials employed. The systematic epidemiological surveillance of all epithelial SNC cases with a detailed collection of their work history, as performed by a dedicated population registry, is essential for detecting all potential occupational cases and should be considered in the context of forensic medicine and the compensation process.
Collapse
Affiliation(s)
- Alessandra Binazzi
- Department of Occupational and Environmental Medicine, Epidemiology and Hygiene, Istituto Nazionale per l’Assicurazione Contro gli Infortuni sul Lavoro, 00100 Roma, Italy; (D.D.M.); (A.M.)
| | - Carolina Mensi
- Sinonasal Cancer Registry of Lombardy, Epidemiology Unit, Fondazione IRCCS Ca’ Granda Ospedale Maggiore Policlinico, 20100 Milano, Italy; (C.M.); (M.B.)
| | - Lucia Miligi
- Sinonasal Cancer Registry of Tuscany, Occupational and Environmental Epidemiology Unit, Institute for Cancer Research, Prevention and Clinical Network (ISPRO), 50139 Firenze, Italy; (L.M.); (S.P.)
| | - Davide Di Marzio
- Department of Occupational and Environmental Medicine, Epidemiology and Hygiene, Istituto Nazionale per l’Assicurazione Contro gli Infortuni sul Lavoro, 00100 Roma, Italy; (D.D.M.); (A.M.)
| | - Jana Zajacova
- Sinonasal Cancer Registry of Piedmont, Occupational Health and Safety Department, CN1 Local Health Authority, 12037 Saluzzo, Italy; (J.Z.); (D.S.)
| | - Paolo Galli
- Sinonasal Cancer Registry of Emilia Romagna, Occupational Safety and Prevention Unit, Public Health Department, Bologna Local Health Authority, 40121 Bologna, Italy; (P.G.); (A.C.)
| | - Angela Camagni
- Sinonasal Cancer Registry of Emilia Romagna, Occupational Safety and Prevention Unit, Public Health Department, Bologna Local Health Authority, 40121 Bologna, Italy; (P.G.); (A.C.)
| | - Roberto Calisti
- Sinonasal Cancer Registry of Marche, Department of Prevention, Unit of Workplace Prevention and Safety and of Occupational Epidemiology (SPreSAL Epi Occ), Regional Health Authority Marche, 62012 Civitanova Marche, Italy; (R.C.); (S.M.)
| | - Anna Balestri
- Sinonasal Cancer Registry of Lazio, Department of Epidemiology, Servizio Sanitario Regionale del Lazio, 00100 Roma, Italy;
| | - Stefano Murano
- Sinonasal Cancer Registry of Autonomous Province of Bolzano, Alto Adige Health Authority, Occupational Medicine Unit, 39100 Bolzano, Italy;
| | - Sara Piro
- Sinonasal Cancer Registry of Tuscany, Occupational and Environmental Epidemiology Unit, Institute for Cancer Research, Prevention and Clinical Network (ISPRO), 50139 Firenze, Italy; (L.M.); (S.P.)
| | - Angelo d’Errico
- Epidemiology, Local Health Unit ASL TO3, Piedmont Region, 10095 Grugliasco, Italy;
| | - Matteo Bonzini
- Sinonasal Cancer Registry of Lombardy, Epidemiology Unit, Fondazione IRCCS Ca’ Granda Ospedale Maggiore Policlinico, 20100 Milano, Italy; (C.M.); (M.B.)
- Department of Clinical Science and Community Health, University of Milano, 20100 Milano, Italy
| | - Stefania Massacesi
- Sinonasal Cancer Registry of Marche, Department of Prevention, Unit of Workplace Prevention and Safety and of Occupational Epidemiology (SPreSAL Epi Occ), Regional Health Authority Marche, 62012 Civitanova Marche, Italy; (R.C.); (S.M.)
| | - Denise Sorasio
- Sinonasal Cancer Registry of Piedmont, Occupational Health and Safety Department, CN1 Local Health Authority, 12037 Saluzzo, Italy; (J.Z.); (D.S.)
| | - Alessandro Marinaccio
- Department of Occupational and Environmental Medicine, Epidemiology and Hygiene, Istituto Nazionale per l’Assicurazione Contro gli Infortuni sul Lavoro, 00100 Roma, Italy; (D.D.M.); (A.M.)
| | | |
Collapse
|
5
|
Delikhoon M, Fazlzadeh M, Sorooshian A, Baghani AN, Golaki M, Ashournejad Q, Barkhordari A. Characteristics and health effects of formaldehyde and acetaldehyde in an urban area in Iran. ENVIRONMENTAL POLLUTION (BARKING, ESSEX : 1987) 2018; 242:938-951. [PMID: 30373039 PMCID: PMC6221454 DOI: 10.1016/j.envpol.2018.07.037] [Citation(s) in RCA: 20] [Impact Index Per Article: 3.3] [Reference Citation Analysis] [Abstract] [Key Words] [MESH Headings] [Grants] [Track Full Text] [Subscribe] [Scholar Register] [Received: 03/15/2018] [Revised: 06/17/2018] [Accepted: 07/09/2018] [Indexed: 05/18/2023]
Abstract
This study reports a spatiotemporal characterization of formaldehyde and acetaldehyde in the summer and winter of 2017 in the urban area of Shiraz, Iran. Sampling was fulfilled according to EPA Method TO-11 A. The inverse distance weighting (IDW) procedure was used for spatial mapping. Monte Carlo simulations were conducted to evaluate carcinogenic and non-cancer risk owing to formaldehyde and acetaldehyde exposure in 11 age groups. The average concentrations of formaldehyde/acetaldehyde in the summer and winter were 15.07/8.40 μg m-3 and 8.57/3.52 μg m-3, respectively. The formaldehyde to acetaldehyde ratios in the summer and winter were 1.80 and 2.43, respectively. The main sources of formaldehyde and acetaldehyde were photochemical generation, vehicular traffic, and biogenic emissions (e.g., coniferous and deciduous trees). The mean inhalation lifetime cancer risk (LTCR) values according to the Integrated Risk Information System (IRIS) for formaldehyde and acetaldehyde in summer and winter ranged between 7.55 × 10-6 and 9.25 × 10-5, which exceed the recommended value by US EPA. The average LTCR according to the Office of Environmental Health Hazard Assessment (OEHHA) for formaldehyde and acetaldehyde in summer and winter were between 4.82 × 10-6 and 2.58 × 10-4, which exceeds recommended values for five different age groups (Birth to <1, 1 to <2, 2 to <3, 3 to <6, and 6 to <11 years). Hazard quotients (HQs) of formaldehyde ranged between 0.04 and 4.18 for both seasons, while the HQs for acetaldehyde were limited between 0.42 and 0.97.
Collapse
Affiliation(s)
- Mahdieh Delikhoon
- Department of Occupational Health Engineering, School of Public Health, Shiraz University of Medical Sciences, Shiraz, Iran
| | - Mehdi Fazlzadeh
- Social Determinants of Health Research Center, Ardabil University of Medical Sciences, Ardabil, Iran; Department of Environmental Health Engineering, School of Public Health, Tehran University of Medical Sciences, Tehran, Iran
| | - Armin Sorooshian
- Department of Chemical and Environmental Engineering, University of Arizona, Tucson, AZ, USA; Department of Hydrology and Atmospheric Sciences, University of Arizona, Tucson, AZ, USA
| | - Abbas Norouzian Baghani
- Department of Environmental Health Engineering, School of Public Health, Tehran University of Medical Sciences, Tehran, Iran; Department of Environmental Health Engineering, School of Health, Shiraz University of Medical Sciences, Shiraz, Iran.
| | - Mohammad Golaki
- Department of Environmental Health Engineering, School of Health, Shahid Beheshti University of Medical Sciences, Tehran, Iran
| | - Qadir Ashournejad
- Department of Remote Sensing & GIS, Faculty of Geography, University of Tehran, Tehran, Iran
| | - Abdullah Barkhordari
- Department of Occupational Health, School of Public Health, Shahroud University of Medical Sciences, Shahroud, Iran
| |
Collapse
|
6
|
Siqueira CYDS, Lemos MVP, Araujo BCDC, Oliveira RDRPED, San Gil RADS, Aquino Neto FRD. Atmospheric distribution of organic compounds from urban areas near Olympic games sites in Rio de Janeiro, Brazil. Microchem J 2017. [DOI: 10.1016/j.microc.2017.04.027] [Citation(s) in RCA: 8] [Impact Index Per Article: 1.1] [Reference Citation Analysis] [Track Full Text] [Journal Information] [Subscribe] [Scholar Register] [Indexed: 10/19/2022]
|
7
|
Ochs SDM, Furtado LDA, Cerqueira WV, Pereira Netto AD. Characterization of the variation of carbonyl compounds concentrations before, during, and after the renovation of an apartment at Niterói, Brazil. ENVIRONMENTAL SCIENCE AND POLLUTION RESEARCH INTERNATIONAL 2016; 23:15605-15615. [PMID: 27130339 DOI: 10.1007/s11356-016-6657-6] [Citation(s) in RCA: 1] [Impact Index Per Article: 0.1] [Reference Citation Analysis] [Abstract] [Key Words] [MESH Headings] [Track Full Text] [Subscribe] [Scholar Register] [Received: 10/23/2015] [Accepted: 04/06/2016] [Indexed: 06/05/2023]
Abstract
The present work reports the variation of 31 carbonyl compounds (CC) in an apartment located at Niterói City, Rio de Janeiro State, Brazil. Eight sampling campaigns were conducted through a 1-year period, and three areas (living room, kitchen, and bedroom) were evaluated before, during, and after the renovation activities and reoccupation of the apartment. Samples were collected using SEP-PAK cartridges impregnated with 2,4-dinitrophenylhydrazine, and the hydrazones were analyzed using rapid resolution liquid chromatography with UV detection. The lowest total concentration of CC (19.0 ± 1.5 μg m(-3)) was found before the renovation when the apartment was empty, but door varnishing resulted in highest contamination of the apartment (1386 ± 384 μg m(-3)); however, an important dispersion of CC was observed in the subsequent sampling (148 ± 1.8 μg m(-3)). After apartment reoccupation, the indoor contamination seemed to depend on the routine activities taken there, such as household product use and cooking activities, but apparently, local temperature increase favored the vaporization of the volatile CC from the building materials in the apartment. As far as we are concerned, this is the first study comparing the concentrations of 31 CC in residential areas before, during, and after renovation activities taken in Brazil.
Collapse
Affiliation(s)
- Soraya de Mendonça Ochs
- Programa de Pós-Graduação em Química-Instituto de Química, Universidade Federal Fluminense, Outeiro de São João Batista, s/n, 24020-141, Valonguinho, Centro, Niterói, RJ, Brazil
- Laboratório de Química Analítica Fundamental e Aplicada-Departamento de Química Analítica, Instituto de Química-Universidade Federal Fluminense, Outeiro de São João Batista, s/n, 24020-141, Valonguinho, Centro, Niterói, RJ, Brazil
| | - Leonardo de Almeida Furtado
- Programa de Pós-Graduação em Química-Instituto de Química, Universidade Federal Fluminense, Outeiro de São João Batista, s/n, 24020-141, Valonguinho, Centro, Niterói, RJ, Brazil
| | - Wildson Vieira Cerqueira
- Programa de Pós-Graduação em Química-Instituto de Química, Universidade Federal Fluminense, Outeiro de São João Batista, s/n, 24020-141, Valonguinho, Centro, Niterói, RJ, Brazil
- Laboratório de Química Analítica Fundamental e Aplicada-Departamento de Química Analítica, Instituto de Química-Universidade Federal Fluminense, Outeiro de São João Batista, s/n, 24020-141, Valonguinho, Centro, Niterói, RJ, Brazil
| | - Annibal Duarte Pereira Netto
- Programa de Pós-Graduação em Química-Instituto de Química, Universidade Federal Fluminense, Outeiro de São João Batista, s/n, 24020-141, Valonguinho, Centro, Niterói, RJ, Brazil.
- Laboratório de Química Analítica Fundamental e Aplicada-Departamento de Química Analítica, Instituto de Química-Universidade Federal Fluminense, Outeiro de São João Batista, s/n, 24020-141, Valonguinho, Centro, Niterói, RJ, Brazil.
| |
Collapse
|