by Chan Tung. / Thesis (M.Phil.)--Chinese University of Hong Kong, 1998. / Includes bibliographical references (leaves 85-102). / Abstract and questionnaire also in Chinese. / Abstract --- p.i / Chinese abstract --- p.ii / Table of contents --- p.iii / Acknowledgment --- p.v / List of tables --- p.vi / List of figures --- p.vii / Glossary of terms and abbreviations --- p.viii / Chapter Chapter 1 --- Introduction --- p.1 / Chapter 1.1 --- Asthma epidemiology --- p.1 / Chapter 1.2 --- Aim of study --- p.3 / Chapter Chapter 2 --- Literature review --- p.4 / Chapter 2.1 --- Definitions of asthma --- p.4 / Chapter 2.2 --- Questionnaire in asthma epidemiological surveys --- p.7 / Chapter 2.3 --- Asthma prevalence studies in Western populations --- p.9 / Chapter 2.4 --- Asthma prevalence studies in Hong Kong --- p.13 / Chapter 2.4.1 --- Adult asthma --- p.14 / Chapter 2.4.2 --- Childhood asthma --- p.15 / Chapter 2.4.3 --- Asthma mortality --- p.17 / Chapter 2.5 --- Environmental risk factors of asthma --- p.17 / Chapter 2.5.1 --- Allergens --- p.19 / Chapter 2.5.2 --- Air pollution --- p.23 / Chapter 2.5.3 --- Environmental tobacco smoke --- p.27 / Chapter 2.5.4 --- Viral infections --- p.29 / Chapter 2.5.5 --- Dietary factors --- p.30 / Chapter 2.5.6 --- Allergen avoidance --- p.32 / Chapter Chapter 3 --- Epidemiological survey --- p.34 / Chapter 3.1 --- Subjects and methods --- p.34 / Chapter 3.1.1 --- Subjects --- p.34 / Chapter 3.1.2 --- Written questionnaire --- p.35 / Chapter 3.1.3 --- Video questionnaire --- p.36 / Chapter 3.1.4 --- Bronchial hyperresponsiveness testing --- p.38 / Chapter 3.2 --- Results --- p.42 / Chapter 3.3 --- Discussion --- p.55 / Chapter Chapter 4 --- Environmental survey --- p.63 / Chapter 4.1 --- Subjects and methods --- p.63 / Chapter 4.1.1 --- Subjects --- p.63 / Chapter 4.1.2 --- Questionnaire survey --- p.63 / Chapter 4.1.3 --- Allergen sampling --- p.64 / Chapter 4.2 --- Results --- p.68 / Chapter 4.3 --- Discussion --- p.73 / Chapter Chapter 5 --- Overall discussion and conclusions --- p.81 / References --- p.85 / Appendix

Os efeitos tóxicos decorrentes da exposição ambiental e ocupacional ao benzeno são amplamente descritos na literatura. Seus produtos de biotransformação fenólicos, entre os quais os compostos hidroxilados como FE e hidroquinona HQ, são indutores importantes de efeitos citotóxicos e genotóxicos responsáveis pela toxicidade ao sistema imune. No entanto, a contribuição de cada metabólito e os mecanismos envolvidos não estão completamente esclarecidos. Desta forma, o presente trabalho teve por objetivo estudar a capacidade da resposta inflamatória em ratos expostos à HQ, ao FE, ou a ambos simultaneamente (HQ+FE). Para tanto, ratos Wistar machos foram expostos aos agentes químicos por período de tempo prolongado (doses diárias de 5 ou 10mg/kg; i.p.; com 5 doses/semana no período de 17 ou 23 dias). Animais controles receberam o veículo pela mesma via. As respostas inflamatórias foram induzidas 24 horas após a última dose administrada. Foram avaliadas a resposta inflamatória inespecífica, decorrente da instilação intranasal de LPS de Salmonella abortus e a resposta inflamatória específica em animais previamente sensibilizados e desafiados pela OVA. Na resposta inflamatória inespecífica, as exposições à HQ e à HQ+FE provocaram redução acentuada no influxo de leucócitos para o pulmão inflamado, pelo menor número de leucócitos no LBA e pela atividade enzimática da MPO reduzida no tecido pulmonar. O efeito não é dependente de modificações no número de leucócitos circulantes nem de alterações nas expressões de moléculas de adesão nos leucócitos circulantes (L-selectina e β2 integrina) e no endotélio pulmonar (ICAM-1 , VCAM-1 e PECAM-1) envolvidas na interação leucócito-endotélio. Na vigência de resposta inflamatória específica, as exposições à HQ, FE ou HQ+FE reduziram significativamente a migração de leucócitos para o LBA e para o tecido pulmonar. Da mesma forma que a RI induzida pelo LPS, não foram detectados alterações nos número de leucócitos circulantes e na expressão de moléculas de adesão. No entanto, os resultados obtidos em ensaios de anafilaxia passiva cutânea e reação anafilática in vitro mostraram que o efeito é dependente, pelo menos em parte, da menor concentração de imunoglobulinas anafiláticas circulantes e, consequentemente, da menor habilidade de desgranulação mastocitária. Em conjunto, os dados obtidos demonstram que as exposições à HQ, ao FE ou à HQ+FE prejudicam a migração de leucócitos para o foco de lesão na vigência de respostas inflamatórias de origem inata ou adquirida. / The toxic effects of the ambiental and occupational exposures to benzene is widely described in the literature. Phenolic hydroxylated compounds obtainded from its biotransformation, such as phenol (PHE) and hydroquinone (HQ), induce important of cytotoxic and genotoxic effects responsible for the immunotoxicity. However, the role of each metabolite and mechanisms of toxicity are unknown. Then, the present work aimed to study the inflammatory response in rats exposed to HQ, PHE, ar both simultaneously (HQ+PHE). Male Wistar rats were exposed to they chemical agents for extended period of time (5 or 10mg/kg/day; ip.; during 17 or 23 days; 2 days intervals each 5 doses). Control animais received the vehicle. Inflammatory reactions were induced 24 hours after the last dose by they intranasal instillation of lipopolysaccharide of Salmonella aborlus (non-specific response) or by inhalation of ovalbumin in animals previously sensitized to the same antigen (specific response, produced by anaphylactic immunoglobulins). Animais exposed to HQ or HQ/PHE presented reduced n,3umbers of PMN and MN cells in the bronchoalveolar lavage fluid (BALF) and lesser myeloperoxidase (MPO) activity in the pulmonary tissue. The reduced influx of leukocytes is not dependent oh alterations on the numbers of circulating leukocytes either adhesion molecules expressions on leukocytes (L-selectin or β2 integrin) and on lung microvascular endothelium (ICAM-1, V CAM-1 or PECAM-1) responsible for leukocyte-endothelial interactions. On the other hand, rats exposed to ali schedules of exposures presented reduced numbers of leukocytes in the BALF and lesser MPO activity in the pulmonary tissue after an antigenic stimulus. As shown to inflammation induced by LPS, no alterations on circulating leukocyte numbers and adhesion molecules expressions were detected. However, the impaired leukocyte migration to the inflamed lung may be dependent, at last in part, on reduced levels of circulating anaphylactic antibodies, as detected by passive cutaneous anaphylaxis test, and by consequent reduced ability of mast cell desgranulation, evidenced by in vitro trachea contraction. Together, our data show that HQ and PHE exposure differently affect the specific and non-specific ínflammatory reactions.

It is now generally acknowledged that particulate air pollution can cause respiratory symptoms and that indoor dust particles may be associated with mucous membrane irritation and odour annoyance. One reason for this may be that dust particles adsorb large quantities of gases and other volatile compounds. It is therefore important to be able to determine the chemical compounds adsorbed onto indoor dust particles. In this thesis, a new technique was developed that can analyse chemical compounds in indoor dust particles in a simple yet accurate way. In its basic configuration, it comprises a one stage thermal desorption oven, a gas flow cell with a miniaturized GC column, and a nitrogen-flushed photo diode array (PDA) detector for fast UV spectra recording. The dust sample is thermally desorbed in the oven and the released compounds are flushed onto the GC column by means of a carrier gas stream; the separated compounds are then registered by the PDA detector and identified by their characteristic gas-phase UV spectra. Using this set-up, a number of volatile organic as well as inorganic compounds were identified in indoor dust particles, e.g. nitric oxide, ammonia, hydrogen sulphide, pyridine, 2-furaldehyde, 2-methylfuran, and isoprene. Moreover, acrylate monomers were identified in dust samples from a secondary school with problems due to powdering floor polish. An instrumental set-up with higher performance was achieved by interfacing the gas flow cell to a capillary GC column. When airborne indoor dust samples were analysed by this system and by GC-MS under similar conditions of thermal desorption (150 °C) and GC separation, the two analytical systems were found to be complementary. GC-UV together with GC-MS was thus demonstrated to be considerably more powerful than GC-MS alone for the analysis of volatile organic compounds (VOC) in indoor dust. When airborne dust samples from damp (n=9) and control (n=9) residences were analysed for VOC and microorganisms, identifications made by culture and microscopy of the major moulds found, i.e. Aspergillus, Cladosporium and Penicillum, coincided with the identification of VOC known to be produced by these species. A number of additional VOC were also found, some of which may be irritating to the skin, eyes or respiratory tract if present at higher concentrations. Quantitative GC-UV analysis of indoor dust from 389 residences in Sweden showed that the VOC found at the highest concentrations were saturated aldehydes (C5-C10), furfuryl alcohol, 2,6-di-tert-butyl-4-methylphenol, 2-furaldehyde, and benzaldehyde. Alkenals were also found, notably 2-butenal (crotonaldehyde), 2-methyl-propenal (methacrolein), hexenal, heptenal, octenal, and nonenal. GC-UV was also applied (together with GC-MS) to determine VOC in dust from residences of 198 children with symptoms of asthma and/or allergy (cases) and from residences of 202 children without symptoms (controls). The mean concentration of nicotine was found to be significantly higher in dust from case residences, while the mean concentrations of hexane, nonanal, octane, 2-pentylfuran and tridecanol were significantly higher in dust from control residences. In a stepwise logistic regression model, nicotine, hexanal, furfuryl alcohol, nonane, butanol, and octenal showed increased relative risks, expressed as odds ratios comparing cases with controls. By contrast, benzaldehyde, nonanal, butenal, hexane, tridecanol, and pentylfuran showed decreased relative risks. These findings point to the possibility that not only environmental tobacco smoke but also other emissions in the indoor environment may be linked to the increased prevalence of asthma and/or allergy in children. It is concluded that GC-UV may be used as an alternative or complement to GC-MS for measuring chemicals in indoor dust, thus improving the survey and control of human exposure to particle-bound toxicants and other chemicals. / Copyright Agreement: Figure 3 included in the PDF file abowe is the exclusive property of SAGE Publications (http://www.sagepublications.com/), or its licensors and is protected by copyright and other intellectual property laws. The download of the file(s) is intended for the User's personal and noncommercial use. Any other use of the download of the Work is strictly prohibited. User may not modify, publish, transmit, participate in the transfer or sale of, reproduce, create derivative works (including coursepacks) from, distribute, perform, display, or in any way exploit any of the content of the file(s) in whole or in part. Permission may be sought for further use from Sage Publications Ltd, Rights and Permissions Department, 1 Oliver's Yard, 55 City Road, London EC1Y 1SP Fax: +44 (020) 7324-8600. By downloading the file(s), the User acknowledges and agrees to these terms.

Os efeitos tóxicos decorrentes da exposição ambiental e ocupacional ao benzeno são amplamente descritos na literatura. Seus produtos de biotransformação fenólicos, entre os quais os compostos hidroxilados como FE e hidroquinona HQ, são indutores importantes de efeitos citotóxicos e genotóxicos responsáveis pela toxicidade ao sistema imune. No entanto, a contribuição de cada metabólito e os mecanismos envolvidos não estão completamente esclarecidos. Desta forma, o presente trabalho teve por objetivo estudar a capacidade da resposta inflamatória em ratos expostos à HQ, ao FE, ou a ambos simultaneamente (HQ+FE). Para tanto, ratos Wistar machos foram expostos aos agentes químicos por período de tempo prolongado (doses diárias de 5 ou 10mg/kg; i.p.; com 5 doses/semana no período de 17 ou 23 dias). Animais controles receberam o veículo pela mesma via. As respostas inflamatórias foram induzidas 24 horas após a última dose administrada. Foram avaliadas a resposta inflamatória inespecífica, decorrente da instilação intranasal de LPS de Salmonella abortus e a resposta inflamatória específica em animais previamente sensibilizados e desafiados pela OVA. Na resposta inflamatória inespecífica, as exposições à HQ e à HQ+FE provocaram redução acentuada no influxo de leucócitos para o pulmão inflamado, pelo menor número de leucócitos no LBA e pela atividade enzimática da MPO reduzida no tecido pulmonar. O efeito não é dependente de modificações no número de leucócitos circulantes nem de alterações nas expressões de moléculas de adesão nos leucócitos circulantes (L-selectina e β2 integrina) e no endotélio pulmonar (ICAM-1 , VCAM-1 e PECAM-1) envolvidas na interação leucócito-endotélio. Na vigência de resposta inflamatória específica, as exposições à HQ, FE ou HQ+FE reduziram significativamente a migração de leucócitos para o LBA e para o tecido pulmonar. Da mesma forma que a RI induzida pelo LPS, não foram detectados alterações nos número de leucócitos circulantes e na expressão de moléculas de adesão. No entanto, os resultados obtidos em ensaios de anafilaxia passiva cutânea e reação anafilática in vitro mostraram que o efeito é dependente, pelo menos em parte, da menor concentração de imunoglobulinas anafiláticas circulantes e, consequentemente, da menor habilidade de desgranulação mastocitária. Em conjunto, os dados obtidos demonstram que as exposições à HQ, ao FE ou à HQ+FE prejudicam a migração de leucócitos para o foco de lesão na vigência de respostas inflamatórias de origem inata ou adquirida. / The toxic effects of the ambiental and occupational exposures to benzene is widely described in the literature. Phenolic hydroxylated compounds obtainded from its biotransformation, such as phenol (PHE) and hydroquinone (HQ), induce important of cytotoxic and genotoxic effects responsible for the immunotoxicity. However, the role of each metabolite and mechanisms of toxicity are unknown. Then, the present work aimed to study the inflammatory response in rats exposed to HQ, PHE, ar both simultaneously (HQ+PHE). Male Wistar rats were exposed to they chemical agents for extended period of time (5 or 10mg/kg/day; ip.; during 17 or 23 days; 2 days intervals each 5 doses). Control animais received the vehicle. Inflammatory reactions were induced 24 hours after the last dose by they intranasal instillation of lipopolysaccharide of Salmonella aborlus (non-specific response) or by inhalation of ovalbumin in animals previously sensitized to the same antigen (specific response, produced by anaphylactic immunoglobulins). Animais exposed to HQ or HQ/PHE presented reduced n,3umbers of PMN and MN cells in the bronchoalveolar lavage fluid (BALF) and lesser myeloperoxidase (MPO) activity in the pulmonary tissue. The reduced influx of leukocytes is not dependent oh alterations on the numbers of circulating leukocytes either adhesion molecules expressions on leukocytes (L-selectin or β2 integrin) and on lung microvascular endothelium (ICAM-1, V CAM-1 or PECAM-1) responsible for leukocyte-endothelial interactions. On the other hand, rats exposed to ali schedules of exposures presented reduced numbers of leukocytes in the BALF and lesser MPO activity in the pulmonary tissue after an antigenic stimulus. As shown to inflammation induced by LPS, no alterations on circulating leukocyte numbers and adhesion molecules expressions were detected. However, the impaired leukocyte migration to the inflamed lung may be dependent, at last in part, on reduced levels of circulating anaphylactic antibodies, as detected by passive cutaneous anaphylaxis test, and by consequent reduced ability of mast cell desgranulation, evidenced by in vitro trachea contraction. Together, our data show that HQ and PHE exposure differently affect the specific and non-specific ínflammatory reactions.

Introdução: Os dados epidemiológicos e experimentais têm mostrado efeitos adversos da exposição pré e pós natal ao material particulado (MP2,5) sobre a saúde fetal e adulto. Entretanto, poucos estudos abordaram a toxicidade fetal da exposição gestacional à poluição do ar ambiental, bem como efeitos a longo prazo de adversos da exposição pré-natal sobre o desenvolvimento pós-natal e maturação de vários sistemas de órgãos. Objetivos: O objetivo deste estudo foi determinar se a exposição pré-natal e / ou pós-natal ao material particulado, influencia o desenvolvimento pulmonar e resposta vascular pulmonar em um modelo de camundongo suscetível a aterosclerose (LDLr-/- camundongos knockout). Métodos: Camundongos LDLr-/- foram expostos durante a gestação ao ar filtrado (AF) ou ar poluído (AC). Após o período de desmame, os filhotes foram subdivididos e novos quatro grupos foram formados de acordo com a exposição gestacional ou a exposição pós natal contínua no ar poluído. Atingindo a idade de 3 meses, esses grupos foram novamente subdivididos, formando um total de 8 grupos e uma dieta hipercolesterolêmica foi introduzida. Os seguintes parâmetros foram analisados: desfechos gestacionais, dosagem de colesterol total (CT) e triglicerídeos (TG) do fígado, avaliação de citocinas no LBA, e avaliação imunohistoquímica da resposta vascular pulmonar . Resultados: Nos grupos que receberam dieta hipercolesterolêmica (DH) os níveis de colesterol apresentaram-se aumentados (p=0,002); A expressão da IL6 no LBA mostrou-se elevada (p=0,01) somente no grupo que não foi exposto a poluição em nunhum período da vida e recebeu dieta postnatalmente. Diferenças significativas também foram observadas na expressão pulmonar vascular dos seguintes imunomarcadores: endotelina (p=0,05); ENOS (p=0,04); IL1? (p=0,005); INOS (p=0,002); ISOP (p=0,001); NOX2 (0,01) e ICAM (0,04) quando comparados ao grupo controle. O volume pulmonar total também se mostra alterado em decorrência do tratamento. Assim, conclui-se que a resposta do desenvolvimento pulmonar à exposição gestacional à poluição particulada do ar pode ser evidenciada mais tarde durante a vida adulta e agir como um fator modulador de insultos pós-natal devido à exposição a poluição do ar e a uma dieta hipercolesterolemica em individuos predispostos aterosclerose / Epidemiological and experimental data have shown adverse effects of gestational and post natal exposure to ambient particulate matter (PM) on the fetal and adult health. However, few studies addressed the fetal toxicity of gestational exposure to environmental air pollution as well as long-term adverse consequences of prenatal exposure on postnatal development and maturation of several organ systems. The aim of this study was to determine if prenatal and/or postnatal exposure to concentrated ambient particles influences lung development and pulmonary vascular response in an atherosclerosis susceptible mouse model (LDLr-/- knockout mice). LDLr-/- mice were exposed during the pregnancy to either filter (AF) or polluted air (CAP). After weaning period, pups were subdivided and new 4 groups formed according to gestational and continuous or not post natal exposure to air pollution. Reaching the age of 3 months these groups were again subdivided and a hypercholesterolemic (HC) diet introduced and a total of 8 groups were formed. Then the following parameters were analyzed: evaluation of the offspring outcomes, assessment of airway responsiveness, evaluation of cytokines in BALF, dosage of total cholesterol (TC) and triglycerides (TG) in the liver and pulmonary vascular response by immunohistochemistry. Results: Animals that received HC diet presented higher levels of cholesterol (p=0.002) when compared to those animals that received normal diet. Expression of IL-6 was only increased in the groups of mice exposed not exposed to particulate air pollution and that received the HC diet (p=0.01). Significant differences were also observed in vascular expression of immunomarkers in the lung endothelin (p=0.05); ENOS (p=0.04); IL1? (p=0.005); INOS (p=0.002); ISOP (p=0.001); NOX2 (0.01) e ICAM (0.04). Total lung volume was also different, there was an increase in those animals receiving a HC diet. In conclusion, the response of the lung development to gestational exposure to particulate air pollution can be evidenced later in life and act as a modulator factor for postnatal insults due to exposures to particulate air pollution and hypercholesterolemic diet in individual predisposed to atherosclerosis

Introdução: Os dados epidemiológicos e experimentais têm mostrado efeitos adversos da exposição pré e pós natal ao material particulado (MP2,5) sobre a saúde fetal e adulto. Entretanto, poucos estudos abordaram a toxicidade fetal da exposição gestacional à poluição do ar ambiental, bem como efeitos a longo prazo de adversos da exposição pré-natal sobre o desenvolvimento pós-natal e maturação de vários sistemas de órgãos. Objetivos: O objetivo deste estudo foi determinar se a exposição pré-natal e / ou pós-natal ao material particulado, influencia o desenvolvimento pulmonar e resposta vascular pulmonar em um modelo de camundongo suscetível a aterosclerose (LDLr-/- camundongos knockout). Métodos: Camundongos LDLr-/- foram expostos durante a gestação ao ar filtrado (AF) ou ar poluído (AC). Após o período de desmame, os filhotes foram subdivididos e novos quatro grupos foram formados de acordo com a exposição gestacional ou a exposição pós natal contínua no ar poluído. Atingindo a idade de 3 meses, esses grupos foram novamente subdivididos, formando um total de 8 grupos e uma dieta hipercolesterolêmica foi introduzida. Os seguintes parâmetros foram analisados: desfechos gestacionais, dosagem de colesterol total (CT) e triglicerídeos (TG) do fígado, avaliação de citocinas no LBA, e avaliação imunohistoquímica da resposta vascular pulmonar . Resultados: Nos grupos que receberam dieta hipercolesterolêmica (DH) os níveis de colesterol apresentaram-se aumentados (p=0,002); A expressão da IL6 no LBA mostrou-se elevada (p=0,01) somente no grupo que não foi exposto a poluição em nunhum período da vida e recebeu dieta postnatalmente. Diferenças significativas também foram observadas na expressão pulmonar vascular dos seguintes imunomarcadores: endotelina (p=0,05); ENOS (p=0,04); IL1? (p=0,005); INOS (p=0,002); ISOP (p=0,001); NOX2 (0,01) e ICAM (0,04) quando comparados ao grupo controle. O volume pulmonar total também se mostra alterado em decorrência do tratamento. Assim, conclui-se que a resposta do desenvolvimento pulmonar à exposição gestacional à poluição particulada do ar pode ser evidenciada mais tarde durante a vida adulta e agir como um fator modulador de insultos pós-natal devido à exposição a poluição do ar e a uma dieta hipercolesterolemica em individuos predispostos aterosclerose / Epidemiological and experimental data have shown adverse effects of gestational and post natal exposure to ambient particulate matter (PM) on the fetal and adult health. However, few studies addressed the fetal toxicity of gestational exposure to environmental air pollution as well as long-term adverse consequences of prenatal exposure on postnatal development and maturation of several organ systems. The aim of this study was to determine if prenatal and/or postnatal exposure to concentrated ambient particles influences lung development and pulmonary vascular response in an atherosclerosis susceptible mouse model (LDLr-/- knockout mice). LDLr-/- mice were exposed during the pregnancy to either filter (AF) or polluted air (CAP). After weaning period, pups were subdivided and new 4 groups formed according to gestational and continuous or not post natal exposure to air pollution. Reaching the age of 3 months these groups were again subdivided and a hypercholesterolemic (HC) diet introduced and a total of 8 groups were formed. Then the following parameters were analyzed: evaluation of the offspring outcomes, assessment of airway responsiveness, evaluation of cytokines in BALF, dosage of total cholesterol (TC) and triglycerides (TG) in the liver and pulmonary vascular response by immunohistochemistry. Results: Animals that received HC diet presented higher levels of cholesterol (p=0.002) when compared to those animals that received normal diet. Expression of IL-6 was only increased in the groups of mice exposed not exposed to particulate air pollution and that received the HC diet (p=0.01). Significant differences were also observed in vascular expression of immunomarkers in the lung endothelin (p=0.05); ENOS (p=0.04); IL1? (p=0.005); INOS (p=0.002); ISOP (p=0.001); NOX2 (0.01) e ICAM (0.04). Total lung volume was also different, there was an increase in those animals receiving a HC diet. In conclusion, the response of the lung development to gestational exposure to particulate air pollution can be evidenced later in life and act as a modulator factor for postnatal insults due to exposures to particulate air pollution and hypercholesterolemic diet in individual predisposed to atherosclerosis