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Table 1 Study characteristics of studies with non-occupational populations

From: Respiratory health effects of exposure to low levels of airborne endotoxin – a systematic review

Non-occupational populations

Author (Year) Country

Study designa

Population

Ageb

Endotoxin assessment methods

Exposure variables measured

Spirometry

Questionnaire

Confounders accounted for

Asthma/COPD patient populations

Rabinovitch et al. (2005) US [45]

CS

24 asthmatic school-children

8.8–9.0 (SD 1.0–1.1)

-Personal and stationary sampling

-37 mm Teflon filter

- 2 L/min

-LAL assay

Airborne endotoxin, PM

FEV1

Questionnaire on asthma severity

Delfino et al. (2015) US [46]

L: follow up 10 days

43 asthmatic school-children

14.3 (range 9–18)

-Personal sampling (10 days)

- 2.5 μm cyclone filter

-4 L/min

-LAL assay

PM2.5, endotoxin

FEV1 and FeNO

Reporting the use of asthma medication and symptoms every two waking hours

Temperature, humidity

Lai et al. (2015) US [47]

L: follow up 12 months

248 asthmatic school-children

8 (range 4–13)

-Area air sampling with charged particle samplers (Quadra)

-LAL assay

Airborne endotoxin, settled dust and settled endotoxin

FEV1 and FVC

Questionnaire on respiratory symptoms and follow-up phone calls

Age, sex, race, annual income, controller medication, home and school settled dust endotoxin and mouse allergen, season

Bose et al. (2016) US [62]

L: follow up 6 months

84 COPD patients

68.9 (SD 7.4)

-Area air sampling

-37-mm Teflon filters

-4 L/min

-LAL assay

Airborne and dust endotoxin, PM, second hand smoke, NO2

FEV1

Combination of MRC dyspnoea scale, modified ATS-DLD, and St. George’s Respiratory Questionnaire

Age, gender, education, season of sampling, baseline pre-bronchodilator percent predicted FEV1

Other non-occupational populations

Schiffman et al. (2005) US [35]

E: 1 h expo-sure

48 healthy subjects

26 (±9.46)

- Air sampling

-Fiberglass filters

-46 L/min

-LAL assay

H2S, ammonia, total suspended particles, endotoxin and odour

FVC, FEV1and FEF25–75%

Environmental Exposures and Health Questionnaire

Subjects were their own controls.

Hoopmann et al. (2006) Germany [37]

CS

3867 children

Range: 5–6

Individual exposure estimated with Lagrange dispersion model based on the emission of neighbouring livestock facilitiesc

Airborne endotoxin, fungi, bacteria, total dust

Questionnaire of the ISAAC studies for respiratory and allergic symptoms

Atopic status parents

Horick et al. (2006) US [38]

L: follow up 12 months

360 children

range 2–3 months

Airborne endotoxin levels were calculated from dust endotoxin levelsd

Endotoxin, dust

Monthly telephone calls during the first year of the child’s life

Race, pets, total mass of dust collected, concrete floor, water damage and respiratory illness

Ramagopal et al. (2014) US [61]

CS

75 children

Range: 3–59 months

Method 1: Stationary Indoor Monitors (SIM)

Method 2: PIPER (pre-toddler inhalable particulate environmental robotic)

PM, endotoxin

ISAAC questionnaire

Age, gender, family history of asthma, floor covering, pets

  1. aCS cross-sectional, L longitudinal, E experimental
  2. bAge (years): mean, presented as range if mean age is presented for subgroups only
  3. cEmissions used in the dispersion model were measured in the surroundings of stables. Meteorological data and data on the amount and type of animals were included in the model and exposures were assigned to participants’ address coordinates
  4. dA measurement error correction analysis was performed according to the regression calibration method. Initial measurements were endotoxin levels derived from living-room floor dust. Regression calibration was performed using 93 living-room airborne endotoxin measurements (polycarbonate filters, 2 L/min)