SUPPLEMENTARY FILES Air pollutants of the indoor environment … · 2013. 11. 21. · Litonjua et...

28
SUPPLEMENTARY FILES Air pollutants of the indoor environment and respiratory health. Marion Hulin a,b , Marzia Simoni c , Giovanni Viegi c,d , Isabella Annesi-Maesano a,b a INSERM, UMR 707, EPAR, Paris, F-75012 France b UPMC Univ Paris 06, UMR_S 707, EPAR, Paris, F-75012 France c Pulmonary Environmental Epidemiology Unit, CNR Institute of Clinical Physiology, Pisa, Italy d CNR Institute of Biomedicine and Molecular Immunology “A. Monroy”, Palermo, Italy

Transcript of SUPPLEMENTARY FILES Air pollutants of the indoor environment … · 2013. 11. 21. · Litonjua et...

  • SUPPLEMENTARY FILES

    Air pollutants of the indoor environment and respiratory health. Marion Hulina,b, Marzia Simonic, Giovanni Viegic,d, Isabella Annesi-Maesanoa,b

    a INSERM, UMR 707, EPAR, Paris, F-75012 France b UPMC Univ Paris 06, UMR_S 707, EPAR, Paris, F-75012 France c Pulmonary Environmental Epidemiology Unit, CNR Institute of Clinical Physiology, Pisa, Italy d CNR Institute of Biomedicine and Molecular Immunology “A. Monroy”, Palermo, Italy

  • Table S1. Epidemiological evidence on the relationship between respiratory health and exposure to indoor moulds objectively assessed

    Population Pollution assessment Main results

    Strachan et al. 1990 [1]

    Case-control on wheezing, Great-Britain

    88 children (6-7 years old)

    Total and specific mould levels: four air sampling (winter) in

    living room and bedroom and in a third room (where visible moulds

    was detected or in kitchen)

    - Higher concentration of mycelia sterilia counts in the homes of wheezy children compared to the one of non-wheezy children

    - No significant differences for all combined other mould species (Penicillium spp, Cladosporium spp, Sistotrema brinkmanii or white rot basidiomycetes)

    Smedje et al. 1996 [2] Cross-sectional study at school (40

    schools, Sweden 1,410 employees (16-64 years old)

    MVOC concentration: one air sampling in classrooms, by pumps

    - Positive associations between MVOC concentration (2-methyl-iso-borneol, 3-methyl furan, 2-heptatone, 1-octen-3-ol) and the risk of asthma

    Smedje et al. 1997 [3] Cross-sectional study at school (11

    schools), Sweden. 627 children (13-14 years old)

    Total and specific mould levels: one dust sample from desks,

    chairs and floor

    - Positive associations between viable mould counts (increase of 1000 organism/m3) and the risk of current asthma

    Garett et al., 1998 [4] Cross-sectional study at home,

    Australia 148 children (7-14 years old)

    Total airborne and specific fungal spore levels: one air sampling in

    living room, bedroom and kitchen during 10h

    - Positive association between Aspergillus concentration (increase of 10 CFU/m3) and the risk of atopy

    - Positive associations between Aspergillus, Cladosporium and Penicillium concentrations (increase of 100 CFU/m3) and the risk allergic sensibilization to moulds

    - Positive association between Penicillium concentration in winter (increase of 100 CFU/m3) and the risk of asthma

    Elke et al., 1999 [5] Cross-sectional study at home,

    Germany 132 children (5-7 years old)

    MVOC concentration : one sampling period, in bedroom, by passive diffusion, during 4 weeks

    - No association between MVOC concentration (high vs. low) and the risk of self-reported asthma, wheezing or allergies

    Douwes et al. 2000 [6]

    Case-control study on chronic respiratory symptoms (recent

    wheezing, shortness of breath with wheezing, dry cough, and/or doctor-

    diagnosed asthma ever in life), Netherlands

    159 children (7-11 years old)

    (1→3)-β-D-glucan concentration: one dust sample on living room,

    bedroom floor and child’s mattress

    - No differences of (1→3)-β-D-glucans concentration between children with or without respiratory symptoms

    - Positive association between (1→3)-β-D-glucans concentrations and PEF variability among asthmatic and/or atopic children

    Dharmage et al. 2001 [7]

    Cross-sectional study at home, Australia

    485 adults (20-44 years old)

    Ergosterol concentration and total and specific moulds levels: one air sampling and dust sample in

    - Positive association between ergosterol concentration (high vs. low, high= >7.6 µg/g) and the risk of allergic sensitization to moulds

  • bedroom - Negative association between the number of total moulds or specific to Penicillium or Cladosporium (high vs. low, high= >842, >146, >366 CFU/m3 respectively) and allergic sensitization to moulds

    - Positive association between ergosterol concentration (high vs. low, high= >7.6 µg/g) and the risk of having “wheezing only”

    - Positive between the number of total moulds or specific to Penicillium or Cladosporium (high vs. low, high= >842, >146, >366 CFU/m3 respectively) and the risk of having “BHR only”

    - No association with current asthma

    Jacob et al. 2002 [8] 2 case-control studies on asthma and/or

    atopy, Germany 272 children (5-7 and 8-10 years old)

    Total and specific fungal spore levels: one dust sample (winter) in

    living room floor

    - Positive associations between Cladosporium spore levels in winter (high vs. low, high= >35000 CFU/g), and Aspergillus (medium vs. low, medium= between LOD and >25000 CFU/g) with the risk of allergic sensitization

    - No association with asthma or persistent wheezing

    Smedje et al. 2001 [9]

    Longitudinal study at school (39 schools), Sweden.

    Cohort of 1,347 children (7-13 years old) followed during 4 years

    Two sampling periods in classrooms, by active sampling,

    during 4 hours, at start and end of the study

    - No association between mould spore counts and the incidence of self-reported allergy and doctor-diagnosed asthma

    - Among non atopic, positive association between total mould spore counts (increase of 10 units) and the incidence of doctor-diagnosed asthma

    Gent et al. 2002 [10] Longitudinal study, United-States

    Birth cohort of 819 children followed during 1 year

    Total and specific mould counts: one air sampling in living room, during 1 mn, 2 to 4 months after

    birth

    - Positive associations between the number of Penicillium counts (high vs. low, high= >1000 CFU/m3) and the rate of wheezing and persistent cough

    - No association with total or other specific mould levels

    Belanger et al. 2003 [11]

    Longitudinal study, United-States Birth cohort of 819 children followed

    during 1 year

    Total mould counts: one air sampling in living room and bedroom, during 1 mn, 2 to 4

    months after birth

    - Positive association between total mould counts (increase of 20 units) and the risk of wheezing among children of mothers with asthma

    - No association with persistent cough

    Jovanic et al. 2004 [12]

    Case-control study on allergic diseases (lifetime: asthma, asthmatic-spastic or

    obstructive bronchitis, hay fever, atopic eczema), Germany

    397 children (9-11 years old)

    Total mould counts: 4 air sampling and 1 dust sample in bedroom floor and the child’s

    mattress

    - No differences between cases and controls

  • Blanc et al. 2005 [13] Cross-sectional study, United-States 226 asthmatic or rhinitic adults

    (1→3)-β-D-glucan concentration : dust samples from mattress,

    kitchen and living room floors - No association with FEV1 (%) levels

    Matheson et al. 2005 [14]

    Longitudinal study, Australia Cohort of 360 adults (20-45 years old)

    followed during 2 years

    Ergosterol concentration: two air sampling in bedroom and dust samples in bedroom floor and

    bed, at start and end of the study Total mould counts:

    one dust sample in bedroom floor and bed, at start and end of the

    study

    - Positive associations between Cladosporium spore counts (double) and the risk of developing new asthma crises

    - Positive association between total spore counts (double) and the risk of developing atopy

    - Negative association between an increase in ergosterol concentration (double) and the remission of wheezing

    - No association with self-reported asthma or wheezing

    Douwes et al., 2006 [15]

    Longitudinal study, Netherlands Birth cohort of 696 children followed

    during 4 years

    EPS-Pen/Asp et (1→3)-β-glucan concentrations: one dust sample on living room floor and

    mattress, 3 months after birth

    - Negative association between EPS-Pen/Asp concentration in living room (high vs. low, high= >8802.3 units/m2) and the risk of doctor-diagnosed asthma, persistent wheezing and atopy at 4 years. No modifying effect by atopy.

    - No association with (1→3)-β-D-glucan concentration

    Iossifova et al. 2006 [16]

    Longitudinal study, United-States Birth cohort of 574 children followed

    during 13 months in means

    (1→3)-β-D-glucan concentration : one dust sample

    from baby’s primary activity room floor, around 8 months after

    birth

    - Negative associations between (1→3)-β-D-glucan concentration (medium vs. low, medium= >134-900 µg/g) and the risk of recurrent wheezing, among both atopic and non atopic

    - When considering high exposure (>900 µg/g), positive association between (1→3)-β-glucan and the risk of recurrent wheezing, among both atopic and non atopic concentration

    - No association with atopy

    Turyk et al. 2006 [17] Panel study, United-States 61 asthmatic children (6-13 year old)

    Allergens : one dust sample from child’ mattress, living room and

    bedroom floor

    - Positive association between Penicillium concentration (high vs. low) in bedroom and asthma symptoms

    - No association with total fungi concentration

    Kim et al. 2007 [18] Cross-sectional study at school (8

    schools), Sweden 1,014 children (5-14 years old)

    Total mould counts: one air sampling in classrooms of 23

    schools. MVOC concentration: one

    sampling period (summer), by active sampling, during 4 hours

    - Positive association between total mould counts (increase of 1 103/m3) and the risk of current wheezing

    - Positive associations between MVOC concentration (high vs. low) and the risk of current wheezing (for 3-octanone), doctor-diagnosed asthma (MVOC, 2-heptanone, 2-Methyl-1-butanol) and nocturnal attacks of breathlessness

  • Zhao et al. 2008 [19] Cross-sectional study at school (10

    schools), China 1,993 children (11-15 years old)

    Ergosterol concentration: two dust samples in classrooms floor and

    desks

    - Negative association between ergosterol concentration (increase of 10 µg/g) and the risk of daytime attacks of breathlessness and history of atopy

    - No association with cumulative incidence of asthma (ever and doctor-diagnosed), medication use, wheezing and nocturnal attacks of breathlessness

    Bertelsen et al. 2010 [20]

    Longitudinal study, Norway Birth cohort of 260 children, followed

    during 10 years

    (1→3)-β-D-glucan concentration : one dust sample on living room

    floor, at the age of 2 years

    - No association with the risk of asthma or atopy

    MVOC = microbial volatile organic compounds; EPS-Asp/Pen = extracellular polysaccharides from Aspergillus and Penicillium, CFU = Colony Fungal Unit FEV1 = Forced expiratory volume in one second, AHR=airway hyperresponsiveness

  • Table S2. Epidemiological evidence on the relationship between respiratory health and exposure to indoor endotoxins objectively assessed

    Population Pollution assessment Main results

    Smedje et al. 1997 [3]

    Cross-sectional study at school (11 schools), Sweden.

    627 children (13-14 years old)

    One dust sample from desks, chairs and floor

    - No association between endotoxins concentration and current asthma

    Douwes et al. 2000 [6]

    Case-control study on chronic respiratory symptoms (recent

    wheezing, shortness of breath with wheezing, dry cough, and/or doctor-

    diagnosed asthma ever in life), Netherlands

    159 children (7-11 years old)

    One dust sample on living room and bedroom floors and child’s

    mattress

    - Higher concentration in the mattress of children with cough then in the one of controls

    - No association with PEF variability

    Gereda et al. 2000 [21]

    Cross-sectional study, United-States 61 wheezing children (9-24 months)

    One dust sample from living-room floor and couch, kitchen

    floor and participant’s bed

    - Lower house-dust endotoxins concentrations in the homes of allergen-sensitized infants than in those of non-sensitized infants

    Ghering et al. 2001 [22]

    Longitudinal study, Germany Birth cohort of 1,884 children,

    followed during 1 year

    One dust sample from mother’s and children’s mattresses, 3

    months after birth

    - Positive association between endotoxins concentration in mother’s or children’s mattresses (High vs. low, high= >1973 EU/g) and the risk of cough with respiratory infection, bronchitis, or both in the first 6 months.

    - Positive association between a high endotoxin concentration in mother’s mattresses (High vs. low: high= >4365 EU/g) and the risk of wheezing

    Ghering et al. 2002 [23]

    Two cross-sectional studies, Germany

    454 children (5-10 years)

    One dust sample from living room floor

    - Negative association between endotxins concentration and the risk of multiple sensitization and sensitization to Cladosporium herbarum.

    - No association with the risk of asthma and wheezing

    Litonjua et al. 2002 [24]

    Longitudinal study, United-States Cohort of 226 siblings (81.3 EU/mg) and the risk of wheezing, especially in the year following samples, and the risk of repeated wheezing

    Böttcher et al. 2003 [25]

    Longitudinal study, Estonia and Sweden

    Birth cohort of 219 children followed during 2 years

    One dust sample, from a carpet and child’s mattress, between 3

    and 12 months of age

    - Negative association between endotoxin concentration in the carpet (increase of 10 EU/mg) and the development of atopy in Swedish children

    Bolte et al. 2003 [26]

    Longitudinal study, Germany Birth cohort of 1,942 children

    One dust sample from mother’s and children’s mattresses, 3

    - Positive association between endotoxin concentration in children’ mattress (high vs. low, high= >7752 EU/g) and the risk of

  • followed during 2 years months after birth repeated wheezing, independent of atopic status. - Positive association between endotoxin concentration and the risk

    of repeated wheezing or allergic sensitization to inhalant allergens in infants with parental atopy

    - No association with the incidence of physician-diagnosed asthma

    Blanc et al. 2005 [13]

    Cross-sectional study, United-States 226 asthmatic or rhinitic adults

    Dust samples from mattress, kitchen and living room floors

    - Association between endotoxin concentration (Medium vs. low, medium= >23 and 19.6 EU/mg) and the risk of wheezing (ever, past year and past month)

    - Positive associations between a high concentration of endotoxin in the bedroom floor (>16.6 EU/mg) and the risk of asthma symptoms (past year) and wheezing (ever and past month)

    - No significant association among children only - No significant interaction between endotoxin and respiratory

    outcomes, but a higher risk among allergic subjects.

    Tavernier et al. 2006 et 2005[29, 30]

    Case-control study on asthma, Great-Britain

    200 children (4-17 years old)

    One dust sample, from living room carpet, child’s bedroom

    floor or mattress

    - Higher endotoxin concentration in the carpet of cases than the one of controls

    - Positive association between endotoxin concentration in living-room carpet and asthma

    Dales et al. 2006 [31]

    Longitudinal study, Canada Birth cohort of 332 children

    followed during 2 years

    One air sampling, in bedroom and living room, during 5 to 7

    days, before one year old

    - Positive association between endotoxin concentration and the risk of illness episodes or the number of illness days (stuffy nose, cough, wheezing, and shortness of breath)

    Douwes et al. 2006 [15]

    Longitudinal study, Netherlands Birth cohort of 696 children,

    followed during 4 years

    One dust sample from living room floor and child’s mattress, 3

    months after birth

    - Negative associations between endotoxin concentration (High vs. low, high= >142.2 EU/m2) and the risk of doctor-diagnosed asthma. No modifying effect by atopy.

    - No association with wheezing or atopy

    Iossifova et al. 2006 [16]

    Longitudinal study, Unites-States Birth cohort of 574 children followed during 13 months

    One dust sample from baby’s primary activity room floor, around 8 months after birth

    - No association with the risk of recurrent wheezing or atopy

    Perzanowski et al. 2006 [32]

    Longitudinal study, Unites-States Birth cohort of 301 children

    One dust sample, from bedroom floor, at the age of 12 or 36

    - Positive association between an increase in endotoxin concentration and the risk of wheezing between 13 and 24 months

  • followed during 3 years months - No association with the risk of wheezing between 0 to 12 or 25 to 36 months

    Celedon et al. 2007 [33]

    Longitudinal study, United-States Birth cohort of 440 children,

    followed during 7 years

    One dust sample, from parents’ and child’s bed, child’bedroom,

    living-room and kitchen floors, 2 to 3 months after birth

    - Negative association between endotoxin concentration in living-room (medium vs. low, medium= 52.49 et 125.59 EU/mg) and the risk of atopy

    - Positive associations between endotoxin concentration (high vs. low, high=>125.59 EU/mg) and the risk of persistent wheezing. No modifying effect by atopy.

    - No association with the risk of asthma

    Ghering et al. 2008 [34]

    Case-control study on wheezing, International

    840 children (9-12 years old)

    One dust sample on mattress or living-room floor

    - Negative associations between endotoxin concentration (increase of one IQR=5.4) and the risk of ever asthma, in both atopic and non atopic subjects

    - Negative associations between endotoxin load (increase of one IQR=4.2) and the risk of asthma ever, current wheezing and atopy

    - Negative associations between endotoxin load and the risk of current wheezing only in atopic subjects

    Rennie et al. 2008 [35]

    Case-control study on asthma, Canada

    196 children (6-13 years old)

    One sample of dust, from activity room floor and child’s mattress - No association with the risk of asthma

    Zhao et al. 2008 [19]

    Cross-sectional study at school (10 schools)

    1,993 children (11-15 years old)

    LPS measurement: one dust sample on classroom floor and

    desks

    - Negative association between LPS levels (increase of 10nmol/sample) and daytime attacks of breathlessness but positive when adjustment on ergosterol and muramic acid concentrations

    - Negative associations between LPS C10 concentration and wheezing, and LPS C10, C12, C14 and the risk of daytime attacks of breathlessness

    - No association with wheezing, incidence of asthma and doctor-diagnosed asthma or history of atopy

    Ryan et al. 2009 [36]

    Longitudinal study, United-States Birth cohort of 624 children,

    followed during 3 years

    One dust sample from baby’s primary activity room floor, around 8 months after birth

    - Positive associations between endotoxin concentration associated with high exposure to traffic-related particles and the risk of persistent wheezing and predictive index of asthma, in the whole and non atopic population

    Bertelsen et al. 2010 [20]

    Longitudinal study, Norway Birth cohort of 260 children,

    followed during 10 years

    One dust sample on living room floor, at the age of 2 years

    - No association between endotoxin and the risk of atopy or asthma

    LPS = lipopolysaccharides, EU = Endotoxin unit, IQR = Interquartile range, FEV1 = Forced expiratory volume in one second, PEF = peak expiratory flow

  • Table S3. Epidemiological evidence on the relationship between respiratory health and exposure to indoor nitrogen dioxide objectively assessed

    Population Pollution assessment Main results

    Melia et al. 1982 [37]

    Cross-sectional study, England 179 children (5-6 years old)

    One sampling period (winter) in bedroom and the living room, by passive diffusion, during

    14 weeks

    - Positive association (p45 µg/m3) and the risk of having one or more asthmatic or bronchitic symptoms

    Berwick et al. 1989 [38]

    Longitudinal study, United-States Cohort of 121 children (30 µg/m3) and the risk of having lower respiratory symptoms among children under the age of 7.

    Neas et al. 1991 [39]

    Longitudinal study, United-States Cohort of 1,567 children (7-11 years old)

    followed during 18 months

    Two sampling periods (summer, winter), in kitchen, the activity room and the bedroom, by passive diffusion, during one week

    - Positive association between NO2 concentration (increase of 27 µg/m3) and the incidence of lower respiratory symptoms. - No association with asthma and lower respiratory symptoms taken independently (shortness of breath, chronic wheezing, chronic cough, chronic phlegm and bronchitis) - Positive association between NO2 concentration (increase of 27 µg/m3) and FEV1/FVC levels

    Samet et al. 1993 [40]

    Longitudinal study, United-States Birth cohort study of 1,205 children followed

    during 18 months

    Several sampling periods in bedroom, by passive diffusion

    - No association between NO2 concentration and the incidence of lower respiraotry symptoms

    Pilotto et al. 1997 [41]

    Longitudinal study at school (8 schools), Australia

    388 children (6-11 years old)

    At school : 9 sampling periods (every two weeks) in classrooms, by passive diffusion, 6h, and sampling every hours during 2 weeks At home: 4 sampling periods during evenings for children exposed to gas appliances

    - Positive dose-reponse trends between mean NO2 concentration and mean rates for cough with phlegm - No association with dry cough or wheezing

    Smedje et al. 1997 [3]

    Cross-sectional study at school (11 schools), Sweden

    627 children (13-14 years old)

    One sampling period (spring) by passive diffusion, during 6 to 7 days

    - No association with current asthma

    Garrett et al. 1998 [42]

    Cross-sectional study at home, Australia 148 children (7-14 years old).

    4 sampling periods (summer, winter) in bedroom, the living room and the kitchen, by

    passive diffusion, during 4 days

    - Positive association between NO2 concentration in the bedroom (high vs. low, high= >20 µg/m3) in summer and respiratory symptom score (cough, shortness of breath,

  • waking due to shortness of breath, wheezing, asthma attacks, chest tightness, cough in the morning, and chest tightness in the morning.) - No association with atopy, asthma ou respiratory symptoms taken independently or lung function change

    Shima et al. 2000 [43]

    Longitudinal study, Japan Cohort of 842 children (9-10 years old)

    Two sampling period (summer, winter) in living room, by passive diffusion, during 24 hours

    - Positive associations between NO2 concentration (increase of 18 µg/m3) and the risk of doctor-diagnosed of asthma, bronchitis or self-reported wheezing among girls - No association with history of allergic diseases or incidence of wheezing or asthma.

    Smith et al., 2000 [44]

    Panel study, Australia 125 asthmatics (all ages)

    3 sampling periods, by passive badges, at home, during one week

    - Positive association between daily NO2 concentration and the report of chest tightness, breathlessness on exertion and night and daytime asthma attacks the same day or the day after. - No association with wheezing, cough or breathlessness

    Emenius et al. 2003 [45]

    Nested case-control study on recurrent wheezing, Sweden

    540 children (1-2 years old)

    One sampling period (winter), in living room, by passive diffusion, during 4 weeks

    - No association between NO2 concentration and the risk of recurrent wheezing in the first two years - Positive association between NO2 concentration (high vs. low) and exposure to tobacco smoke and the risk of recurrent wheezing (significant interaction)

    Venn et al., 2003 [46]

    Case-control study on wheezing, Great-Britain 416 children (9 à 11 years old)

    One sampling period (winter) in kitchen, by passive diffusion, during 4 weeks

    - No association between NO2 concentration and wheezing, or with respiratory symptoms among cases

    Simoni et al. 2004 [47]

    Two cross-sectional studies, Italy 1,090 adults (>15 years old)

    Two sampling periods (summer, winter) in living room, by passive diffusion, during one week. Evaluation of exposure (exposure time*concentration)

    - No association between NO2 exposure and bronchitic and/or asthmatic symptoms (sputum from the chest, shortness of breath, attack of shortness of breath, wheezings) without fever and without acute respiratory illnesses

    Sunyer et al. 2004 [48]

    Longitudinal study, Spain. Birth cohort of 1,611 children followed

    during 1 year

    One sampling period, in living room, by passive diffusion, during 2 weeks, 3 months after birth

    - No association with cumulative rates of lower respiratory tract infections

    Van Strien et al. 2004 [49]

    Longitudinal study, United-States Birth cohort of 768 children with asthmatic

    siblings, followed during one year

    One sampling period, in living room, by passive diffusion, during 2 weeks, 2 to 4 months after birth

    - Positive associations between NO2 concentration (high vs. low, high= >31.3 µg/m3) and the number of days of wheezing or shortness of breath - No association with cough

    Blanc et al. 2005 [13]

    Cross-sectional study, United-States 226 asthmatic or rhinitic adults

    One sampling period, in kitchen, by passive diffusion, during 1 week - No association with FEV1 levels

  • Belanger et al. 2006 [50]

    Longitudinal study, United-States Cohort of 768 asthmatic siblings (100 µg/m3) and the risk of frequent respiratory symptoms (cough, wheezing, or shortness of breath) in non atopic children - No association with the risk of PEF40 years)

    Three air sampling in three sites in kitchen, by active sampling, during 5 minutes - No association with COPD

  • Osman et al. 2007 [56]

    Cross-sectional study, Scotland 148 adults with COPD

    One sampling period (winter), in living room, by passive diffusion, during 1 week

    - No association with respiratory symptom score

    Hansel et al. 2008 [57]

    Longitudinal study, United-States 150 asthmatic children (2-6 years old)

    3 sampling period every 3 months, in bedroom, by passive diffusion, during 72h.

    - Positive association between NO2 concentration (increase of 36 µg/m3) and frequency of limited speech due to wheezing, coughing without a cold, and nocturnal awakenings due to cough, wheezing, and shortness of breath or chest tightness and while running. - No association with wheezing, and shortness of breath or chest tightness during the daytime, and having to slow activity due to asthma, wheezing, chest tightness or cough - Higher association between NO2 concentration and nocturnal symptoms in atopic children than among non atopic ones (significant interaction)

    Zhao et al. 2008 [58]

    Cross-sectional study at school (10 schools), China

    1,993 children (11-15 years old)

    One sampling period,in classrooms, by passive diffusion, during one week

    - Positive association between NO2 concentration (increase of 10 µg/m3) and the risk of nocturnal attacks of breathlessness - No association with cumulative asthma, wheezing or whistling in the chest, daytime attacks of breathlessness or furry pet or pollen allergy

    Raaschou-Nielsen et al. 2010 [59]

    Longitudinal study, Denmark. Birth cohort of 378 children from asthmatic

    mothers followed during 18 months

    Up to 3 measurement in bedroom during the first 18 months of life, by passive diffusion,

    during 10 weeks

    - No association with the risk of symptom-day or the number of symptom-days of wheezing

    NO2= nitrogen dioxide, FEV1=Forced expiratory volume in one second, FVC=Force vital capacity, COPD= chronic obstructive pulmonary disease

  • Table S4. Epidemiological evidence on the relationship between respiratory health and exposure to indoor particles objectively assessed

    Population Pollution assessment Main results

    Neas et al. 1994 [60]

    Longitudinal study, United-States

    Cohort of 1,237 children (7-11 years) followed during 3 years

    2 consecutive 1-week sampling periods (winter, summer) in the activity room, by impactor.

    - Positive association between PM2.5 concentration (increase of 30 µg/m3) and the cumulative incidence of respiratory symptoms (shortness of breath, persistent wheezing, chronic cough, chronic phlegm or bronchitis) among the 9-10 years old children - Positive associations between an increase of PM2.5 concentration (increase of 30 µg/m3) and the cumulative incidence of bronchitis and lower respiratory symptoms among boys - No association with asthma, shortness of breath, persistent wheezing, chronic cough or chronic phlegm

    Smedje et al. 2001 [9]

    Longitudinal study at school (39 schools), Sweden.

    Cohort of 1,347 children (7-13 years old) followed during 4

    years

    Two sampling periods (at start and end of the follow-up) in classrooms, by direct

    reading, twice in each classroom during 15 mn

    - Positive association between respirable particles concentration (increase of 10 µg/m3) and the incidence of self-reported allergy to pet - No association with the incidence of self-reported allergy to pollen or asthma diagnosis, even after stratification for a history of allergy.

    Delfino et al. 2004 [61]

    Panel study, United-States 19 asthmatic children (9-17

    years)

    One sampling period in the living room, by pumps, during 24h

    - Negative association between PM2.5 concentration (increase of one IQR) and a change in FEV1 levels (%)

    Simoni et al. 2004 [47]

    Two cross-sectional studies, Italy

    1,090 adults (>15 years)

    Two sampling periods (summer, winter) in the living room, by pumps, during 2 consecutive 48-h. Evaluation of exposure (exposure time*concentration)

    - Positive association between PM2.5 concentration (high vs. low) and bronchitic and/or asthmatic symptoms (sputum from the chest, shortness of breath, attack of shortness of breath, wheezings) without fever and without acute respiratory illnesses - Positive associations between a PM2.5 concentration (high vs. low) and PEF maximum amplitude (%) and diurnal variation (%).

    Koenig et al. 2005 [62]

    Panel study, United-States 19 asthmatic children (6-13

    years)

    Estimation of exposure based on particles

    measurement at home, by impactor

    - Negative association between indoor-generated PM2.5 concentration (increase of 10 µg/m3) and FEV1 and FVC levels among children not using inhaled corticosteroid

    Tavernier et al, 2006 [29]

    Case-control study on asthma, Great-Britain 200 children (4-

    17 years old)

    Two sampling periods in the bedroom and the living

    room, by impactor

    - No differences between cases and controls

    Trenga et al. 2006 [63]

    Panel study, United-States 57 adults (56-89 years) , 17

    children with asthma

    5 to 10 sampling periods in home over a period of 3 years, by impactor, during

    - Negative association between PM2.5 concentration (increase of 10 µg/m3) and a change in FEV1 levels in adults. No association with a change in PEF levels. - Negative association between PM2.5 concentration (increase of 10 µg/m3)

  • 24h and a change in FEV1 and PEF, and MMEF levels in children not taking inflammatory medication.

    Diette et al. 2007 [53]

    Nested case-control study on asthma, United-States

    300 children (2-6 years)

    One sampling period of 72 h, in the bedroom, by impactor + PM gravimetric analysis

    - No differences between cases and controls

    Liu et al. 2007 [55] 2 cross-sectional studies, China 194 women (>40 years)

    Three air sampling in three sites in the kitchen, by

    active sampling, during 5 minutes

    - No association with the risk of COPD

    Osman et al. 2007 [56]

    Cross-sectional study, Scotland 148 adults with COPD

    One sampling period (winter), in the living room, by direct reading, during 12

    to 18 hours

    - Positive associations between PM2.5 concentration and respiratory symptom score

    Ma et al. 2008 [64] Panel study at hospital, Japan 19 severe asthmatic children

    (8-15 years)

    Seven sampling periods, at hospital, by direct

    measurement, during 24h

    - Negative associations between PM2.5 concentration (increase of 10 µg/m3) and change in PEF levels in the morning and the evening. - Positive association between PM2.5 concentration (increase of 10 µg/m3) and the prevalence of wheezing in the morning or the evening

    McCormack et al. 2009 [65]

    Longitudinal study, United-States

    Cohort of 150 asthmatic children (2-6 years)

    Three sampling periods every 3 months, in the bedroom, by impactor,

    during 3 days

    - Positive associations between PM2.5-10 concentration (increase of 10 µg/m3) and the incidence rate of cough, wheezing or chest tightness, nocturnal symptoms, wheezing that limited speaking ability and rescue medication use. - Positive associations between PM2.5 concentration (increase of 10 µg/m3) and the incidence rate of asthma symptoms that need to slow down or stop activities, symptoms with exercise, nocturnal symptoms, wheezing that limited speaking ability and rescue medication use.

    De Hartog et al. 2010 [66]

    Cross-sectional study, Europe 135 subjects with asthma or

    COPD (>35 years)

    One sampling period, by impactor and direct

    measurement, during 24h - No association between PM2.5 concentration and change in lung function

    Raaschou-Nielsen et al. 2010 [59]

    Longitudinal study, Denmark. Birth cohort of 378 children

    from asthmatic mothers followed during 18 months

    Up to 3 measurement in the bedroom during the first 18 months of life, by cyclone

    and pumps, for 1 week

    - No association between PM2.5 concentration and the risk of symptom-day or number of symptom-days of wheezing

    Simoni et al. 2010 [67]

    Cross-sectional study at school (21 schools), Europe

    654 children (10 years)

    One sampling period in classrooms, by direct

    measurement, for 1 to 2 h

    - No association between PM2.5 concentration (high vs. low, high:>50 µg/m3 or an increase of 10 µg/m3) and the prevalence of wheezing or dry cough at night.

    PM2.5=particulate matter with an aerodynamic diameter

  • Table S5. Epidemiological evidence on the relationship between respiratory health and exposure to indoor formaldehyde objectively assessed

    Population Pollution assessment Main results

    Krzyzanowski et al. 1990 [68]

    Cross-sectional study, United States

    298 children (5 - 15 years) + 613 adults (>15 years)

    Two sampling periods, in kitchen, living room and each subject’s bedroom, by passive diffusion,

    during one week

    - Higher prevalence of doctor-diagnosed asthma and bronchitis in children living in homes with high level of pollution (>75µg/m3)

    - Decreased in the levels of PEF as formaldehyde concentration increased

    - No association with respiratory symptoms (chronic cough, wheezing, chronic phlegm, attacks of shortness of breath) or in adults

    Norbäck et al. 1995 [69]

    Case-control study on respiratory symptoms (asthma

    attacks, nocturnal breathlessness, current use of asthma medication), Sweden.

    88 adults (20-45 years)

    One sampling period in bedroom and living room, by active sampling, during 2 hours

    - Positive association between formaldehyde concentration (increase of 10 µg/m3) and the risk of nocturnal breathlessness

    - No significant association between formaldehyde concentration and bronchial hyperresponsiveness, variability in PEF and change in FEV1

    Smedje et al. 1997 [3] Cross-sectional study at school

    (11 schools) , Sweden 627 children (13-14 years)

    One sampling period (summer) in classrooms, by active sampling,

    during 4 hours

    - Positive association between formaldehyde concentration (increase of 10 µg/m3) and the risk of current asthma

    Garett et al. 1999 [70] Cross-sectional study, Australia 148 children (7-14 years).

    4 sampling periods (summer, winter) in bedroom, living room

    and kitchen, by passive diffusion, during 4 days

    - Higher number of positive skin prick test in relation with higher formaldehyde concentration ( >50 µg/m3)

    - No association with current asthma - Positive association between formaldehyde concentration

    (High vs. low, high=>50 µg/m3) and respiratory symptom score (cough, cough in the morning, waking due to shortness of breath, wheezing/whistling, asthma attacks, chest tightness, chest tightness in the morning) in children suffering from respiratory symptoms

    Smedje et al. 2001 [9]

    Longitudinal study at school (39 schools), Sweden

    Cohort of 1,347 children (7-13 years) followed during 4 years

    2 sampling periods (at start and end of the follow-up) in

    classrooms, by active sampling, during 4 hours

    - No association with the incidence of self-reported allergy - In non allergic children, positive association between

    formaldehyde concentration (increase of 10 µg/m3) and the incidence of doctor-diagnosed asthma

  • Rumchev et al. 2002 [71]

    Case-control study on asthma, Australia

    192 children (6 months-3 years).

    2 sampling periods (summer, winter) in living room and

    bedroom, by passive diffusion, during 8 hours

    - Positive association between formaldehyde concentration (increase of 10 µg/m3, and high vs. low, high= >60 µg/m3) and the risk of doctor-diagnosed asthma

    Venn et al., 2003 [46] Case-control study on current

    wheezing, Great-Britain 416 children (9- 11 years)

    Onse sampling period (winter) in bedroom, by passive diffusion,

    during 3 days

    - No association with current wheezing - Among cases, positive association between formaldehyde

    concentration (high vs. low, high=>32 µg/m3) and the risk of nocturnal symptoms

    Blanc et al. 2005 [13]

    Cross-sectional study, United-States

    226 asthmatic or rhinitic adults

    One sampling period, in kitchen, by passive diffusion, during 1

    week - No association with change in FEV1

    Mi et al. 2006 [51] Cross-sectional study at school

    (10 schools), China 1,414 children (13-14 years).

    One sampling period in 30 classroom, by active sampling,

    during 4hours

    - No association with respiratory symptoms (wheezing, attack of breathlessness, asthma attacks, asthma medication), current asthma and self-reported allergy to furry pet or pollen

    Tavernier et al, 2006 [29] Case-control study on asthma,

    Great-Britain 200 children (4-17 years)

    Two sampling period one week apart, in bedroom and living

    room, by active sampling - No differences between cases and controls

    Kim et al. 2007 [18] Cross-sectional study at school

    (8 schools), Sweden 1,014 children (5-14 years)

    One sampling period (summer) in 3 classrooms of each school, by active sampling, during 6 hours

    - No association with current wheezing, doctor-diagnosed asthma or attacks of breathlessness

    Zhao et al. 2008 [58] Cross-sectional study at school

    (10 schools), China 1,993 children (11-15 years)

    One sampling period in classrooms, by passive diffusion,

    during 7 days

    - Positive association between formaldehyde concentration (increase of 10 µg/m3) and the risk nocturnal attacks of breathlessness and current wheezing

    - No association with ever asthma, daytime attacks of breathlessness or self-reported allergy to furry pets or pollens

    Raaschou-Nielsen et al. 2010 [59]

    Longitudinal study, Danemark. Birth cohort of 378 children

    from asthmatic mothers followed during 18 months

    Up to 3 measurement in bedroom during the first 18 months of life, by passive diffusion, during 10

    weeks

    - No association with the risk of symptom-day or the number of symptom-days of wheezing

    FEV1=Forced expiratory volume in one second, PEF= peak expiratory flow

  • Table S6. Epidemiological evidence on the relationship between respiratory health and exposure to indoor VOCs objectively assessed

    Population Pollution assessment Main results

    Norbäck et al. 1995 [69]

    Case-control study on respiratory symptoms (asthma attacks, nocturnal breathlessness, current use of asthma

    medication), Sweden. 88 adults (20-45 years)

    One sampling period in bedroom and living room, by active sampling, during 2 hours

    - Positive associations between toluene, C8-aromatics, terpene and TVOC concentrations (10 fold increase) and nocturnal attacks of breathlessness

    - No association with wheezing, daytime attacks of breathlessness or tightness in the chest

    - Positive association between limonene concentration (10 fold increase) and bronchial hyper-reactivity

    - Positive association between α-pinene and δ-karen concentration (10 fold increase) and PEF variability

    Smedje et al. 1997 [3]

    Cross-sectional study at school (11 schools), Sweden

    627 children (13-14 years)

    One sampling period (summer) in classrooms, by active sampling, during 7

    days

    - Positive association between TVOC concentration (increase of 10 µg/m3) and current asthma

    Diez et al. 2000 [72]

    Longitudinal study, Germany Birth cohort of 266 children with risk of allergy, followed during one year

    One sampling period, in bedroom, by passive diffusion, 4 weeks after birth - No association with the risk of wheezing

    Smedje et al. 2001 [9]

    Longitudinal study at school (39 schools), Sweden

    Cohort of 1,347 children (7-13 years) followed during 4 years

    2 sampling periods (at start and end of the follow-up) in classrooms, by active

    sampling, during 4 hours

    - No association with the incidence of self-reported allergy or doctor-diagnosed asthma

    Venn et al., 2003 [46]

    Case-control study on current wheezing, Great-Britain

    416 children (9 to 11 years old)

    One sampling period (winter) in bedroom, by passive diffusion, during 4 weeks

    - No association with the risk of wheezing or respiratory symptoms among cases

    Lehmann et al. 2001 [73]

    Cross-sectional study, Germany 120 children (3 years)

    One sampling period, in bedroom, by passive diffusion, during 4 weeks - No association with allergic sensitization to aeroallergens

    Rumchev et al. 2004 [74]

    Case-control study on asthma, Australia

    192 children (6 months- 3 years).

    2 sampling periods (summer/winter) in living room and bedroom, by passive

    diffusion, during 8 hours

    - Positive association between benzene, toluene, ethylbenzene, m,p-xylene, 1.2-dichlorobenzene, 1.4-dichlorobenzene and TVOC concentrations (increase of 10µg/m3) and the risk of doctor-diagnosed asthma

    Tavernier et al, 2006 [29]

    Case-control study on asthma, Great-Britain

    200 children (4- 17 years)

    Two sampling period one week apart, in bedroom and living room, by active

    sampling - No differences between cases and controls

    TVOC= Total volatile organic compounds, PEF= peak expiratory flow

  • Table S7. Epidemiological evidence on the relationship between respiratory health and exposure to indoor pollutants objectively assessed in rural areas: farming environment in children

    Population Pollution assessment Main results

    Braun-Fahrländer et al. 2002 [75]

    Cross-sectional study, Austria, Germany and Switzerland 812 children (6-13 years)

    Endotoxin concentration: one dust sample in mattress

    - Negative associations between endotoxin load (high vs. low) and atopic sensitization, atopic asthma and atopic wheezing

    Van Strien et al. 2004 [76]

    Cross-sectional study, Austria, Germany and Switzerland 553 children (6-13 years)

    Muramic acid concentration: one dust sample in mattress

    - Negative association between muramic acid concentration (increase of 108 ng/mg) and the risk of wheezing

    - No association with atopy or asthma

    Schram-Bijkerk et al. 2005 [77]

    Case-control study on atopic wheezing, Europe

    711 children (5-13 years)

    Endotoxin, fungal β(1,3)-glucans and fungal EPS concentrations: One dust

    sample form living room floor and mattress

    - Negative association between endotoxin and EPS concentrations (increase f a factor 4 and 3 respectively) and the risk of atopic wheezing

    - No association with glucan concentration - No association when mutually adjusted for all pollutant

    Schram-Bijkerk et al. 2006 [78]

    Cross-sectional study, Europe 402 children (5-13 years)

    Mite allergens concentration: one dust sample in mattress

    - Positive association between mite allergen concentration (medium vs. low) and the risk of allergic sensitization

    EPS= extracellular polysaccharides

  • Table S8. Epidemiological evidence on the relationship between respiratory health and exposure to indoor pollutants objectively assessed in rural areas: farming environment in adults

    Population Pollution assessment Main results

    Preller et al. 1995 [79]

    Cross-sectional study, the Netherlands

    194 pig farmers selected toward chronic respiratory symptoms

    Endotoxin concentration and dust quantity: 2 personal inhalable dust sampling

    (winter/summer), during one work shift, during 8 hours in mean. Evaluation of exposure

    - In asymptomatic farmers (without chronic respiratory symptoms), negative association between endotoxin exposure and FVC and FEV1 levels.

    - No association with dust concentration

    Post et al. 1998 [80]

    Cross-sectional study, the Netherlands

    140 workers of grain processing and animal feed industry

    Endotoxin concentration and dust quantity: 2 personal dust sampling during specific

    task, in 8 facilities, during 8 hours. Evaluation of exposure

    - Negative association between dust exposure (high vs. low) and FEV1 and MMEF levels.

    - Negative association with endotoxin concentration (high vs. low) and FEV1 levels

    - No association with FVC and MMEF values.

    Volgezang et al. 1998 [81]

    Longitudinal study, The Netherlands

    171 pig farmers selected toward chronic respiratory symptoms

    Endotoxin concentration and dust quantity: 2 personal inhalable dust sampling

    (winter/summer), during one work shift, during 8 hours in mean. Evaluation of exposure

    - Association between long-term average endotoxin exposure and FEV1 and FVC decline

    - Association between long-term average exposure to dust and FVC decline

    Eduard et al. 2001 [82]

    Cross-sectional study, Norway 290 farmers

    Fungal spores, Endotoxins, β(1->3) glucans, EPS Pen/Asp concentrations: three

    personal dust sampling during specific tasks, with an upper limit of 1 hour.

    Evaluation of exposure

    - Positive associations between fungal spores concentration (high vs. low, high= 0.5-17*106/m3) and the risk of cough.

    - No associations with chest tightness or wheezing. - No association with dust quantity

    Monso et al. 2004 [83]

    Cross-sectional study, Europe 105 animal farmers

    Endotoxin concentration and dust quantity: personal dust sampling during daily work in

    buildings

    - Positive association between total dust concentration (high vs. low, high= >17ppm) and the risk of COPD

    - No association with endotoxin concentration

    Kirychuk et al. 2006 [84]

    Cross-sectional study, Canada 111 poultry farmers Endotoxin: personal dust sampling

    - Positive association between endotoxin concentration (high vs. low, high= >6.38 ln[EU/mg]) and the risk of chronic phlegm

    - No association with lung function or other respiratory symptoms (cough, wheezing or shortness of breath)

    Eduard et al. 2004 [85]

    Cross-sectional study, Norway 1,614 farmers

    Fungal spores, endotoxin concentrations and dust quantity: personal dust sampling,

    in a random sample of farms, during 12 specific tasks.

    Evaluation of exposure for all farms.

    - Positive association between fungal spores exposure (high vs. low, high= >3.5 106/m3) and the risk of asthma in non-atopic farmers

    - Negative association between fungal spores exposure (high vs low, high= >3.5 106/m3) and the risk of asthma in non-atopic farmers

    - Positive association between total dust exposure (high vs. low, high= >2.7 mg/m3) and the risk of asthma in non-atopic farmers

    - No association with exposure to endotoxin

  • Portengen et al. 2005 [86]

    Cross-sectional study, the Netherlands

    194 pig famers

    Endotoxin concentration: two dust samples (summer/winter)

    Evaluation of exposure

    - Positive association between endotoxin exposure and the risk of AHR in sensitized farmers

    - Negative association between endotoxin exposure and atopic sensitization to common allergens

    - No association with respiratory symptoms and FEV1 level

    Smit et al. 2008 [87]

    Cross-sectional study, the Netherlands

    877 famers and agricultural industry workers

    Endotoxin concentration: 249 full-shift personal airborne endotoxin, by pumps.

    Evaluation of exposure

    - Positive associations between endotoxin exposure (increase of one IQR) and cough symptoms (daily cough, daily cough with phlegm, woken due to cough), shortness of breath, wheezing.

    - Associations in allergic and non allergic farmers

    Eduard et al. 2009 [88]

    Cross-sectional study, Norway 4,735 farmers

    Fungal spores, Endotoxins, β(1->3) glucans, EPS Pen/Asp concentrations: three

    personal dust sampling during specific tasks, with an upper limit of 1 hour.

    Evaluation of exposure

    - Positive associations between exposure (10-fold increase) to fungal spores and actinomycete spores and the risk of chronic bronchitis and COPD

    - Positive associations between exposure to EPS Asp/Pen antigens (10-fold increase) and the risk of chronic bronchitis and FEV1 level

    - Positive association between dust exposure (10-fold increase) and the risk of COPD in atopic farmers

    - Positive association between dust exposure (10-fold increase) and the risk of chronic bronchitis in non atopic farmers

    Smit et al. 2010 [89]

    Cross-sectional study, the Netherlands

    427 farmers and agricultural industry workers

    Endotoxin concentration: 249 full-shift personal airborne endotoxin, by pumps.

    Evaluation of exposure

    - Positive associations between endotoxin exposure (increase of one IQR) and the risk of wheezing and BHR

    - Negative associations between endoxin exposure (increase of one IQR) and the risk of allergic sensitization, especially to grass pollen

    COPD= chronic obstructive pulmonary diseases, BHR= bronchial hyperresponsivness, AHR= airway hyperresponsivness, FEV1=Forced expiratory volume in one second, FVC=Force vital capacity, MMEF= maximum midexpiratory flow, EU= endotoxin unit, IQR= interquartile range

  • 1. Strachan DP, Flannigan B, McCabe EM, McGarry F. Quantification of airborne moulds in the homes of children with and without wheeze. Thorax 1990: 45(5): 382-387. 2. Smedje G, Norback D, Wessen B, Edling C. Asthma among school employees in relation to the school environment. In: Indoor Air '96: Proceedings of the 7th International Conference on Indoor Air Quality and Climate; 1996 July 21-26; Nagoya, Japan; 1996. p. 611-616. 3. Smedje G, Norback D, Edling C. Asthma among secondary schoolchildren in relation to the school environment. Clin Exp Allergy 1997: 27(11): 1270-1278. 4. Garrett MH, Rayment PR, Hooper MA, Abramson MJ, Hooper BM. Indoor airborne fungal spores, house dampness and associations with environmental factors and respiratory health in children. Clin Exp Allergy 1998: 28(4): 459-467. 5. Elke K, Begerow J, Oppermann H, Kramer U, Jermann E, Dunemann L. Determination of selected microbial volatile organic compounds by diffusive sampling and dual-column capillary GC-FID--a new feasible approach for the detection of an exposure to indoor mould fungi? J Environ Monit 1999: 1(5): 445-452. 6. Douwes J, Zuidhof A, Doekes G, van der Zee SC, Wouters I, Boezen MH, Brunekreef B. (1-->3)-beta-D-glucan and endotoxin in house dust and peak flow variability in children. Am J Respir Crit Care Med 2000: 162(4 Pt 1): 1348-1354. 7. Dharmage S, Bailey M, Raven J, Mitakakis T, Cheng A, Guest D, Rolland J, Forbes A, Thien F, Abramson M, Walters EH. Current indoor allergen levels of fungi and cats, but not house dust mites, influence allergy and asthma in adults with high dust mite exposure. Am J Respir Crit Care Med 2001: 164(1): 65-71. 8. Jacob B, Ritz B, Gehring U, Koch A, Bischof W, Wichmann HE, Heinrich J. Indoor exposure to molds and allergic sensitization. Environ Health Perspect 2002: 110(7): 647-653. 9. Smedje G, Norback D. Incidence of asthma diagnosis and self-reported allergy in relation to the school environment--a four-year follow-up study in schoolchildren. Int J Tuberc Lung Dis 2001: 5(11): 1059-1066. 10. Gent JF, Ren P, Belanger K, Triche E, Bracken MB, Holford TR, Leaderer BP. Levels of household mold associated with respiratory symptoms in the first year of life in a cohort at risk for asthma. Environ Health Perspect 2002: 110(12): A781-786. 11. Belanger K, Beckett W, Triche E, Bracken MB, Holford T, Ren P, McSharry JE, Gold DR, Platts-Mills TA, Leaderer BP. Symptoms of wheeze and persistent cough in the first year of life: associations with indoor allergens, air contaminants, and maternal history of asthma. Am J Epidemiol 2003: 158(3): 195-202. 12. Jovanovic S, Felder-Kennel A, Gabrio T, Kouros B, Link B, Maisner V, Piechotowski I, Schick KH, Schrimpf M, Weidner U, Zollner I, Schwenk M. Indoor fungi levels in homes of children with and without allergy history. Int J Hyg Environ Health 2004: 207(4): 369-378. 13. Blanc PD, Eisner MD, Katz PP, Yen IH, Archea C, Earnest G, Janson S, Masharani UB, Quinlan PJ, Hammond SK, Thorne PS, Balmes JR, Trupin L, Yelin EH. Impact of the home indoor environment on adult asthma and rhinitis. J Occup Environ Med 2005: 47(4): 362-372. 14. Matheson MC, Abramson MJ, Dharmage SC, Forbes AB, Raven JM, Thien FC, Walters EH. Changes in indoor allergen and fungal levels predict changes in asthma activity among young adults. Clin Exp Allergy 2005: 35(7): 907-913. 15. Douwes J, van Strien R, Doekes G, Smit J, Kerkhof M, Gerritsen J, Postma D, de Jongste J, Travier N, Brunekreef B. Does early indoor microbial exposure reduce the risk of asthma? The Prevention and Incidence of Asthma and Mite Allergy birth cohort study. J Allergy Clin Immunol 2006: 117(5): 1067-1073.

  • 16. Iossifova YY, Reponen T, Bernstein DI, Levin L, Kalra H, Campo P, Villareal M, Lockey J, Hershey GK, LeMasters G. House dust (1-3)-beta-D-glucan and wheezing in infants. Allergy 2007: 62(5): 504-513. 17. Turyk M, Curtis L, Scheff P, Contraras A, Coover L, Hernandez E, Freels S, Persky V. Environmental allergens and asthma morbidity in low-income children. J Asthma 2006: 43(6): 453-457. 18. Kim JL, Elfman L, Mi Y, Wieslander G, Smedje G, Norback D. Indoor molds, bacteria, microbial volatile organic compounds and plasticizers in schools--associations with asthma and respiratory symptoms in pupils. Indoor Air 2007: 17(2): 153-163. 19. Zhao Z, Sebastian A, Larsson L, Wang Z, Zhang Z, Norback D. Asthmatic symptoms among pupils in relation to microbial dust exposure in schools in Taiyuan, China. Pediatr Allergy Immunol 2008: 19(5): 455-465. 20. Bertelsen RJ, Carlsen KC, Carlsen KH, Granum B, Doekes G, Haland G, Mowinckel P, Lovik M. Childhood asthma and early life exposure to indoor allergens, endotoxin and beta(1,3)-glucans. Clin Exp Allergy 2010: 40(2): 307-316. 21. Gereda JE, Leung DY, Thatayatikom A, Streib JE, Price MR, Klinnert MD, Liu AH. Relation between house-dust endotoxin exposure, type 1 T-cell development, and allergen sensitisation in infants at high risk of asthma. Lancet 2000: 355(9216): 1680-1683. 22. Gehring U, Bolte G, Borte M, Bischof W, Fahlbusch B, Wichmann HE, Heinrich J. Exposure to endotoxin decreases the risk of atopic eczema in infancy: a cohort study. J Allergy Clin Immunol 2001: 108(5): 847-854. 23. Gehring U, Bischof W, Fahlbusch B, Wichmann HE, Heinrich J. House dust endotoxin and allergic sensitization in children. Am J Respir Crit Care Med 2002: 166(7): 939-944. 24. Litonjua AA, Milton DK, Celedon JC, Ryan L, Weiss ST, Gold DR. A longitudinal analysis of wheezing in young children: the independent effects of early life exposure to house dust endotoxin, allergens, and pets. J Allergy Clin Immunol 2002: 110(5): 736-742. 25. Bottcher MF, Bjorksten B, Gustafson S, Voor T, Jenmalm MC. Endotoxin levels in Estonian and Swedish house dust and atopy in infancy. Clin Exp Allergy 2003: 33(3): 295-300. 26. Bolte G, Bischof W, Borte M, Lehmann I, Wichmann HE, Heinrich J. Early endotoxin exposure and atopy development in infants: results of a birth cohort study. Clin Exp Allergy 2003: 33(6): 770-776. 27. Lau S, Illi S, Platts-Mills TA, Riposo D, Nickel R, Gruber C, Niggemann B, Wahn U. Longitudinal study on the relationship between cat allergen and endotoxin exposure, sensitization, cat-specific IgG and development of asthma in childhood--report of the German Multicentre Allergy Study (MAS 90). Allergy 2005: 60(6): 766-773. 28. Thorne PS, Kulhankova K, Yin M, Cohn R, Arbes SJ, Jr., Zeldin DC. Endotoxin exposure is a risk factor for asthma: the national survey of endotoxin in United States housing. Am J Respir Crit Care Med 2005: 172(11): 1371-1377. 29. Tavernier G, Fletcher G, Gee I, Watson A, Blacklock G, Francis H, Fletcher A, Frank T, Frank P, Pickering CA, Niven R. IPEADAM study: indoor endotoxin exposure, family status, and some housing characteristics in English children. J Allergy Clin Immunol 2006: 117(3): 656-662. 30. Tavernier GO, Fletcher GD, Francis HC, Oldham LA, Fletcher AM, Blacklock G, Stewart L, Gee I, Watson A, Frank TL, Frank P, Pickering CA, Niven RM. Endotoxin exposure in asthmatic children and matched healthy controls: results of IPEADAM study. Indoor Air 2005: 15 Suppl 10: 25-32. 31. Dales R, Miller D, Ruest K, Guay M, Judek S. Airborne endotoxin is associated with respiratory illness in the first 2 years of life. Environ Health Perspect 2006: 114(4): 610-614.

  • 32. Perzanowski MS, Miller RL, Thorne PS, Barr RG, Divjan A, Sheares BJ, Garfinkel RS, Perera FP, Goldstein IF, Chew GL. Endotoxin in inner-city homes: associations with wheeze and eczema in early childhood. J Allergy Clin Immunol 2006: 117(5): 1082-1089. 33. Celedon JC, Milton DK, Ramsey CD, Litonjua AA, Ryan L, Platts-Mills TA, Gold DR. Exposure to dust mite allergen and endotoxin in early life and asthma and atopy in childhood. J Allergy Clin Immunol 2007: 120(1): 144-149. 34. Gehring U, Strikwold M, Schram-Bijkerk D, Weinmayr G, Genuneit J, Nagel G, Wickens K, Siebers R, Crane J, Doekes G, Di Domenicantonio R, Nilsson L, Priftanji A, Sandin A, El-Sharif N, Strachan D, van Hage M, von Mutius E, Brunekreef B. Asthma and allergic symptoms in relation to house dust endotoxin: Phase Two of the International Study on Asthma and Allergies in Childhood (ISAAC II). Clin Exp Allergy 2008: 38(12): 1911-1920. 35. Rennie DC, Lawson JA, Kirychuk SP, Paterson C, Willson PJ, Senthilselvan A, Cockcroft DW. Assessment of endotoxin levels in the home and current asthma and wheeze in school-age children. Indoor Air 2008: 18(6): 447-453. 36. Ryan PH, Bernstein DI, Lockey J, Reponen T, Levin L, Grinshpun S, Villareal M, Hershey GK, Burkle J, LeMasters G. Exposure to traffic-related particles and endotoxin during infancy is associated with wheezing at age 3 years. Am J Respir Crit Care Med 2009: 180(11): 1068-1075. 37. Melia RJ, Florey Cdu V, Morris RW, Goldstein BD, John HH, Clark D, Craighead IB, Mackinlay JC. Childhood respiratory illness and the home environment. II. Association between respiratory illness and nitrogen dioxide, temperature and relative humidity. Int J Epidemiol 1982: 11(2): 164-169. 38. Berwick M, Leaderer BP, Stolwijk JA. Lower respiratory symptoms in children exposed to nitrogen dioxide from unvented combustion sources. Environment International 1989: 15: 369-373. 39. Neas LM, Dockery DW, Ware JH, Spengler JD, Speizer FE, Ferris BG, Jr. Association of indoor nitrogen dioxide with respiratory symptoms and pulmonary function in children. Am J Epidemiol 1991: 134(2): 204-219. 40. Samet JM, Lambert WE, Skipper BJ, Cushing AH, Hunt WC, Young SA, McLaren LC, Schwab M, Spengler JD. Nitrogen dioxide and respiratory illnesses in infants. Am Rev Respir Dis 1993: 148(5): 1258-1265. 41. Pilotto LS, Douglas RM, Attewell RG, Wilson SR. Respiratory effects associated with indoor nitrogen dioxide exposure in children. Int J Epidemiol 1997: 26(4): 788-796. 42. Garrett MH, Hooper MA, Hooper BM, Abramson MJ. Respiratory symptoms in children and indoor exposure to nitrogen dioxide and gas stoves. Am J Respir Crit Care Med 1998: 158(3): 891-895. 43. Shima M, Adachi M. Effect of outdoor and indoor nitrogen dioxide on respiratory symptoms in schoolchildren. Int J Epidemiol 2000: 29(5): 862-870. 44. Smith BJ, Nitschke M, Pilotto LS, Ruffin RE, Pisaniello DL, Willson KJ. Health effects of daily indoor nitrogen dioxide exposure in people with asthma. Eur Respir J 2000: 16(5): 879-885. 45. Emenius G, Pershagen G, Berglind N, Kwon HJ, Lewne M, Nordvall SL, Wickman M. NO2, as a marker of air pollution, and recurrent wheezing in children: a nested case-control study within the BAMSE birth cohort. Occup Environ Med 2003: 60(11): 876-881. 46. Venn AJ, Cooper M, Antoniak M, Laughlin C, Britton J, Lewis SA. Effects of volatile organic compounds, damp, and other environmental exposures in the home on wheezing illness in children. Thorax 2003: 58(11): 955-960. 47. Simoni M, Scognamiglio A, Carrozzi L, Baldacci S, Angino A, Pistelli F, Di Pede F, Viegi G. Indoor exposures and acute respiratory effects in two general population samples

  • from a rural and an urban area in Italy. J Expo Anal Environ Epidemiol 2004: 14 Suppl 1: S144-152. 48. Sunyer J, Puig C, Torrent M, Garcia-Algar O, Calico I, Munoz-Ortiz L, Barnes M, Cullinan P. Nitrogen dioxide is not associated with respiratory infection during the first year of life. Int J Epidemiol 2004: 33(1): 116-120. 49. van Strien RT, Gent JF, Belanger K, Triche E, Bracken MB, Leaderer BP. Exposure to NO2 and nitrous acid and respiratory symptoms in the first year of life. Epidemiology 2004: 15(4): 471-478. 50. Belanger K, Gent JF, Triche EW, Bracken MB, Leaderer BP. Association of indoor nitrogen dioxide exposure with respiratory symptoms in children with asthma. Am J Respir Crit Care Med 2006: 173(3): 297-303. 51. Mi YH, Norback D, Tao J, Mi YL, Ferm M. Current asthma and respiratory symptoms among pupils in Shanghai, China: influence of building ventilation, nitrogen dioxide, ozone, and formaldehyde in classrooms. Indoor Air 2006: 16(6): 454-464. 52. Nitschke M, Pilotto LS, Attewell RG, Smith BJ, Pisaniello D, Martin J, Ruffin RE, Hiller JE. A cohort study of indoor nitrogen dioxide and house dust mite exposure in asthmatic children. J Occup Environ Med 2006: 48(5): 462-469. 53. Diette GB, Hansel NN, Buckley TJ, Curtin-Brosnan J, Eggleston PA, Matsui EC, McCormack MC, Williams DL, Breysse PN. Home indoor pollutant exposures among inner-city children with and without asthma. Environ Health Perspect 2007: 115(11): 1665-1669. 54. Kattan M, Gergen PJ, Eggleston P, Visness CM, Mitchell HE. Health effects of indoor nitrogen dioxide and passive smoking on urban asthmatic children. J Allergy Clin Immunol 2007: 120(3): 618-624. 55. Liu S, Zhou Y, Wang X, Wang D, Lu J, Zheng J, Zhong N, Ran P. Biomass fuels are the probable risk factor for chronic obstructive pulmonary disease in rural South China. Thorax 2007: 62(10): 889-897. 56. Osman LM, Douglas JG, Garden C, Reglitz K, Lyon J, Gordon S, Ayres JG. Indoor air quality in homes of patients with chronic obstructive pulmonary disease. Am J Respir Crit Care Med 2007: 176(5): 465-472. 57. Hansel NN, Breysse PN, McCormack MC, Matsui EC, Curtin-Brosnan J, Williams DL, Moore JL, Cuhran JL, Diette GB. A longitudinal study of indoor nitrogen dioxide levels and respiratory symptoms in inner-city children with asthma. Environ Health Perspect 2008: 116(10): 1428-1432. 58. Zhao Z, Zhang Z, Wang Z, Ferm M, Liang Y, Norback D. Asthmatic symptoms among pupils in relation to winter indoor and outdoor air pollution in schools in Taiyuan, China. Environ Health Perspect 2008: 116(1): 90-97. 59. Raaschou-Nielsen O, Hermansen MN, Loland L, Buchvald F, Pipper CB, Sorensen M, Loft S, Bisgaard H. Long-term exposure to indoor air pollution and wheezing symptoms in infants. Indoor Air 2010: 20: 159-167. 60. Neas LM, Dockery DW, Ware JH, Spengler JD, Ferris BG, Jr., Speizer FE. Concentration of indoor particulate matter as a determinant of respiratory health in children. Am J Epidemiol 1994: 139(11): 1088-1099. 61. Delfino RJ, Quintana PJ, Floro J, Gastanaga VM, Samimi BS, Kleinman MT, Liu LJ, Bufalino C, Wu CF, McLaren CE. Association of FEV1 in asthmatic children with personal and microenvironmental exposure to airborne particulate matter. Environ Health Perspect 2004: 112(8): 932-941. 62. Koenig JQ, Mar TF, Allen RW, Jansen K, Lumley T, Sullivan JH, Trenga CA, Larson T, Liu LJ. Pulmonary effects of indoor- and outdoor-generated particles in children with asthma. Environ Health Perspect 2005: 113(4): 499-503.

  • 63. Trenga CA, Sullivan JH, Schildcrout JS, Shepherd KP, Shapiro GG, Liu LJ, Kaufman JD, Koenig JQ. Effect of particulate air pollution on lung function in adult and pediatric subjects in a Seattle panel study. Chest 2006: 129(6): 1614-1622. 64. Ma L, Shima M, Yoda Y, Yamamoto H, Nakai S, Tamura K, Nitta H, Watanabe H, Nishimuta T. Effects of airborne particulate matter on respiratory morbidity in asthmatic children. J Epidemiol 2008: 18(3): 97-110. 65. McCormack MC, Breysse PN, Matsui EC, Hansel NN, Williams D, Curtin-Brosnan J, Eggleston P, Diette GB. In-home particle concentrations and childhood asthma morbidity. Environ Health Perspect 2009: 117(2): 294-298. 66. de Hartog JJ, Ayres JG, Karakatsani A, Analitis A, Brink HT, Hameri K, Harrison R, Katsouyanni K, Kotronarou A, Kavouras I, Meddings C, Pekkanen J, Hoek G. Lung function and indicators of exposure to indoor and outdoor particulate matter among asthma and COPD patients. Occup Environ Med 2010: 67(1): 2-10. 67. Simoni M, Annesi-Maesano I, Sigsgaard T, Norback D, Wieslander G, Nystad W, Canciani M, Sestini P, Viegi G. School air quality related to dry cough, rhinitis and nasal patency in children. Eur Respir J 2010: 35(4): 742-749. 68. Krzyzanowski M, Quackenboss JJ, Lebowitz MD. Chronic respiratory effects of indoor formaldehyde exposure. Environ Res 1990: 52(2): 117-125. 69. Norback D, Bjornsson E, Janson C, Widstrom J, Boman G. Asthmatic symptoms and volatile organic compounds, formaldehyde, and carbon dioxide in dwellings. Occup Environ Med 1995: 52(6): 388-395. 70. Garrett MH, Hooper MA, Hooper BM, Rayment PR, Abramson MJ. Increased risk of allergy in children due to formaldehyde exposure in homes. Allergy 1999: 54(4): 330-337. 71. Rumchev KB, Spickett JT, Bulsara MK, Phillips MR, Stick SM. Domestic exposure to formaldehyde significantly increases the risk of asthma in young children. Eur Respir J 2002: 20(2): 403-408. 72. Diez U, Kroessner T, Rehwagen M, Richter M, Wetzig H, Schulz R, Borte M, Metzner G, Krumbiegel P, Herbarth O. Effects of indoor painting and smoking on airway symptoms in atopy risk children in the first year of life results of the LARS-study. Leipzig Allergy High-Risk Children Study. Int J Hyg Environ Health 2000: 203(1): 23-28. 73. Lehmann I, Rehwagen M, Diez U, Seiffart A, Rolle-Kampczyk U, Richter M, Wetzig H, Borte M, Herbarth O. Enhanced in vivo IgE production and T cell polarization toward the type 2 phenotype in association with indoor exposure to VOC: results of the LARS study. Int J Hyg Environ Health 2001: 204(4): 211-221. 74. Rumchev K, Spickett J, Bulsara M, Phillips M, Stick S. Association of domestic exposure to volatile organic compounds with asthma in young children. Thorax 2004: 59(9): 746-751. 75. Braun-Fahrlander C, Riedler J, Herz U, Eder W, Waser M, Grize L, Maisch S, Carr D, Gerlach F, Bufe A, Lauener RP, Schierl R, Renz H, Nowak D, von Mutius E. Environmental exposure to endotoxin and its relation to asthma in school-age children. N Engl J Med 2002: 347(12): 869-877. 76. van Strien RT, Engel R, Holst O, Bufe A, Eder W, Waser M, Braun-Fahrlander C, Riedler J, Nowak D, von Mutius E. Microbial exposure of rural school children, as assessed by levels of N-acetyl-muramic acid in mattress dust, and its association with respiratory health. J Allergy Clin Immunol 2004: 113(5): 860-867. 77. Schram-Bijkerk D, Doekes G, Douwes J, Boeve M, Riedler J, Ublagger E, von Mutius E, Benz MR, Pershagen G, van Hage M, Scheynius A, Braun-Fahrlander C, Waser M, Brunekreef B. Bacterial and fungal agents in house dust and wheeze in children: the PARSIFAL study. Clin Exp Allergy 2005: 35(10): 1272-1278.

  • 78. Schram-Bijkerk D, Doekes G, Boeve M, Douwes J, Riedler J, Ublagger E, von Mutius E, Budde J, Pershagen G, van Hage M, Wickman M, Braun-Fahrlander C, Waser M, Brunekreef B. Nonlinear relations between house dust mite allergen levels and mite sensitization in farm and nonfarm children. Allergy 2006: 61(5): 640-647. 79. Preller L, Heederik D, Boleij JS, Vogelzang PF, Tielen MJ. Lung function and chronic respiratory symptoms of pig farmers: focus on exposure to endotoxins and ammonia and use of disinfectants. Occup Environ Med 1995: 52(10): 654-660. 80. Post W, Heederik D, Houba R. Decline in lung function related to exposure and selection processes among workers in the grain processing and animal feed industry. Occup Environ Med 1998: 55(5): 349-355. 81. Vogelzang PF, van der Gulden JW, Folgering H, Kolk JJ, Heederik D, Preller L, Tielen MJ, van Schayck CP. Endotoxin exposure as a major determinant of lung function decline in pig farmers. Am J Respir Crit Care Med 1998: 157(1): 15-18. 82. Eduard W, Douwes J, Mehl R, Heederik D, Melbostad E. Short term exposure to airborne microbial agents during farm work: exposure-response relations with eye and respiratory symptoms. Occup Environ Med 2001: 58(2): 113-118. 83. Monso E, Riu E, Radon K, Magarolas R, Danuser B, Iversen M, Morera J, Nowak D. Chronic obstructive pulmonary disease in never-smoking animal farmers working inside confinement buildings. Am J Ind Med 2004: 46(4): 357-362. 84. Kirychuk SP, Dosman JA, Reynolds SJ, Willson P, Senthilselvan A, Feddes JJ, Classen HL, Guenter W. Total dust and endotoxin in poultry operations: comparison between cage and floor housing and respiratory effects in workers. J Occup Environ Med 2006: 48(7): 741-748. 85. Eduard W, Douwes J, Omenaas E, Heederik D. Do farming exposures cause or prevent asthma? Results from a study of adult Norwegian farmers. Thorax 2004: 59(5): 381-386. 86. Portengen L, Preller L, Tielen M, Doekes G, Heederik D. Endotoxin exposure and atopic sensitization in adult pig farmers. J Allergy Clin Immunol 2005: 115(4): 797-802. 87. Smit LAM, Heederik D, Doekes G, Blom C, van Zweden I, Wouters I. Exposure-response analysis of allergy and respiratory symptomes in endotoxin-exposed adults. Eur Respir J 2008: 31: 1241-1248. 88. Eduard W, Pearce N, Douwes J. Chronic bronchitis, COPD, and lung function in farmers - The role of biological agents. Chest 2009: 136: 716-725. 89. Smit L, Heederik D, Doekes G, Lammers J-W, Wouters I. Occupational endotoxin exposure reduces the risk of atopic sensitization but increases the risk of bronchial hyperresponsiveness. Int Arch Allergy Immunol 2010: 152: 151-158.