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. Author manuscript; available in PMC: 2021 Apr 12.
Published in final edited form as: Inhal Toxicol. 2020 Feb 26;32(1):1–13. doi: 10.1080/08958378.2020.1725187

Table 5.

Significant effects on the immune system resulting from exposure to particle filtered diesel exhaust (fDE) or whole diesel exhaust (wDE) relative to filtered air exposure (arrows indicate direction of effect and statistical significance at α < 0.05; dashes indicate no statistically significant effect observed). NR = not reported; IgG = immunoglobulin G; IgE = immunoglobulin E.

Immune System
PM μg/m3 NO2 (ppm) Species Sex Duration Allergen co-exposure Effect fDE wDE Author Year
fDE wDE fDE wDE
18.9 292.2 0.15 0.052 Human Male and female 2 hr House dust mite; grass; birch White blood cell count (24 h) Wooding et al. 2019
Neutrophil count (24 h) -
Eosinophil count (48 h) -
40 1010 2.93 1.99 BABL/c mice Male 12 hr/day for 5 weeks Sugi basic protein (allergen of Japanese cedar pollen) Chemokine production Fujimaki et al. 2004
40 1010 NR NR C57BL/6 mice Male 12 hr/day for 5 weeks Sugi basic protein (allergen of Japanese cedar pollen) T lymphocytes - Fujimaki et al. 2005
Chemokine production -
IgG1 titers
IgG2a titers
0 36 (low), 169 (high) 0.51 0.15 (low), 0.51 (high) ICR mice Female 5 hr day, 5 day/wk for 8 weeks Ovalbumin Ovalbumin-induced eosinophilic airway inflammation Tanaka et al. 2013
Cytokine and chemokine production
Production/release of myeloperoxidase into alveolar space
NR 1730 NR 0.79 Fischer rats Male (in utero exposure) 6 hr/day for 19 days during gestation Crude Japanese cedar pollen Serum testosterone Watanabe & Ohsawa 2002
IgE titers