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Randomized Controlled Trial
. 2023 May;131(5):57002.
doi: 10.1289/EHP11139. Epub 2023 May 4.

Respiratory Effects of Traffic-Related Air Pollution: A Randomized, Crossover Analysis of Lung Function, Airway Metabolome, and Biomarkers of Airway Injury

Affiliations
Randomized Controlled Trial

Respiratory Effects of Traffic-Related Air Pollution: A Randomized, Crossover Analysis of Lung Function, Airway Metabolome, and Biomarkers of Airway Injury

Xinlei Zhu et al. Environ Health Perspect. 2023 May.

Abstract

Background: Exposure to traffic-related air pollution (TRAP) has been associated with increased risks of respiratory diseases, but the biological mechanisms are not yet fully elucidated.

Objectives: Our aim was to evaluate the respiratory responses and explore potential biological mechanisms of TRAP exposure in a randomized crossover trial.

Methods: We conducted a randomized crossover trial in 56 healthy adults. Each participant was exposed to high- and low-TRAP exposure sessions by walking in a park and down a road with high traffic volume for 4 h in random order. Respiratory symptoms and lung function, including forced expiratory volume in the first second (FEV1), forced vital capacity (FVC), the ratio of FEV1 to FVC, and maximal mid-expiratory flow (MMEF), were measured before and after each exposure session. Markers of 8-isoprostane, tumor necrosis factor-α (TNF-α), and ezrin in exhaled breath condensate (EBC), and surfactant proteins D (SP-D) in serum were also measured. We used linear mixed-effects models to estimate the associations, adjusted for age, sex, body mass index, meteorological condition, and batch (only for biomarkers). Liquid chromatography-mass spectrometry was used to profile the EBC metabolome. Untargeted metabolome-wide association study (MWAS) analysis and pathway enrichment analysis using mummichog were performed to identify critical metabolomic features and pathways associated with TRAP exposure.

Results: Participants had two to three times higher exposure to traffic-related air pollutants except for fine particulate matter while walking along the road compared with in the park. Compared with the low-TRAP exposure at the park, high-TRAP exposure at the road was associated with a higher score of respiratory symptoms [2.615 (95% CI: 0.605, 4.626), p=1.2×10-2] and relatively lower lung function indicators [-0.075L (95% CI: -0.138, -0.012), p=2.1×10-2] for FEV1 and -0.190L/s (95% CI: -0.351, -0.029; p=2.4×10-2) for MMEF]. Exposure to TRAP was significantly associated with changes in some, but not all, biomarkers, particularly with a 0.494-ng/mL (95% CI: 0.297, 0.691; p=9.5×10-6) increase for serum SP-D and a 0.123-ng/mL (95% CI: -0.208, -0.037; p=7.2×10-3) decrease for EBC ezrin. Untargeted MWAS analysis revealed that elevated TRAP exposure was significantly associated with perturbations in 23 and 32 metabolic pathways under positive- and negative-ion modes, respectively. These pathways were most related to inflammatory response, oxidative stress, and energy use metabolism.

Conclusions: This study suggests that TRAP exposure might lead to lung function impairment and respiratory symptoms. Possible underlying mechanisms include lung epithelial injury, inflammation, oxidative stress, and energy metabolism disorders. https://doi.org/10.1289/EHP11139.

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Figures

Figure 1 is a set of two heatmaps titled positive ionization mode and negative ionization mode, plotting Arginine and Proline Metabolism, Aspartate and asparagine metabolism, Beta-Alanine metabolism, Butanoate metabolism, Carnitine shuttle, Di-unsaturated fatty acid beta-oxidation, Fatty acid activation, Fatty Acid Metabolism, Glycine, serine, alanine and threonine metabolism, Glycosphingolipid metabolism, Linoleate metabolism, Lysine metabolism, Nitrogen metabolism, Omega-3 fatty acid metabolism, Pentose and Glucuronate Interconversions, Saturated fatty acids beta-oxidation, Squalene and cholesterol biosynthesis, Tyrosine metabolism, Urea cycle or amino group metabolism, Vitamin B3 (nicotinate and nicotinamide) metabolism, Vitamin B6 (pyridoxine) metabolism, Vitamin B9 (folate) metabolism, Vitamin E metabolism; and Alanine and Aspartate Metabolism, Arginine and Proline Metabolism, Ascorbate (Vitamin C) and Aldarate Metabolism, Beta-Alanine metabolism, Butanoate metabolism, Chondroitin sulfate degradation, De novo fatty acid biosynthesis, Fatty acid activation, Fatty Acid Metabolism, Fructose and mannose metabolism, Glutamate metabolism, Glycerophospholipid metabolism, Glycolysis and Gluconeogenesis, Glycosphingolipid metabolism, Glyoxylate and Dicarboxylate Metabolism, Heparan sulfate degradation, Hexose phosphorylation, Leukotriene metabolism, Lysine metabolism, Methionine and cysteine metabolism, Pentose phosphate pathway, Phosphatidylinositol phosphate metabolism, Propanoate metabolism, Purine metabolism, Pyrimidine metabolism, Pyruvate Metabolism, Sialic acid metabolism, TCA cycle, Tryptophan metabolism, Tyrosine metabolism, Urea cycle or amino group metabolism, Vitamin B9 (folate) metabolism (y-axis) across T R A P, U F P, B C, N O 2, C O, and particulate matter begin subscript 2.5 end subscript (x-axis), respectively. A scale depicting lowercase p values ranges from 0.00 to 1.00 in increments of 0.05.
Figure 1.
The identified metabolic pathways associated with TRAP and individual air pollutants in positive-ionization mode (POS) and negative-ionization mode (NEG) based on the untargeted metabolome-wide association study (MWAS) conducted for exhaled breath condensate (EBC) metabolomics in a randomized crossover trial in China (n=56 adults). TRAP exposure was fitted as a binary indicator of exposure (low/high); individual pollutants were modeled as continuous variables. The linear mixed-effect models and the mummichog pathway analysis (version 1.0.10; Python) were applied for pathway enrichment analysis. Fisher’s exact test (FET) as an enrichment test of metabolic features on pathways was applied, and an adjusted p<0.05 from FET was considered statistically significant. p-Values are shown in Table S4. Note: BC, black carbon; CO, carbon monoxide; NO2, nitrogen dioxide; PM2.5, fine particulate matter; TCA, tricarboxylic acid; TRAP, traffic-related air pollution; UFP, ultrafine particles.
Figure 2 is an illustration flowchart with six steps. Step 1: traffic-related air pollution leads to airway epithelial cells. Step 2: Epithelial cells lead to energy metabolic rewiring, pro-inflammation tumor necrosis factor lowercase a, and oxidative stress (8-isoprostane). Step 3: Under energy metabolic rewiring, Glycolysis and Gluconeogenesis, including glucose, glucose-6-phosphate, pyruvate, and lactate, are combined with the Tricarboxylic Acid Cycle, including malate, fumarate, and succinate. Under pro-inflammation, tumor necrosis factor lowercase a, arginine, and proline metabolism are involved, including L-arginine with inducible nitric oxide synthase, citrulline, nitric oxide, and leukotrienes, including leukotriene B-4 and 10,11-dihydro-leukotriene B 4. Under Oxidative stress 8-isoprostane, linoleate, 13- hydroperxyoctadecadienoic acid, 13-hydroxyoctadecadienoic acid, 13-oxooctadecadienoic acid; Purine metabolism, including hypoxanthine with Xanthine Oxidoreductase, xanthine with Xanthine Oxidoreductase, uric acid; Methionine and cysteine metabolism, including methionine; and Vitamin E metabolism, including alpha-tocotrienol and 11 prime carboxy-alpha-tocotrienol. Purine metabolism with methionine and cysteine metabolism leads to reactive oxygen species. The reactive oxygen species lead to cell membrane phospholipid. The cell membrane phospholipid and phospholipase A2 lead to free fatty acids. The free fatty acids lead to leukotriene. Step 4: Lung epithelial injury, including ezrin and surfactant proteins D. Step 5: Lung function reductions, including forced vital capacity, forced expiratory volume in the first second, ratio of forced expiratory volume in the first second to forced vital capacity, and maximal mid-expiratory flow. Step 6: Respiratory symptoms, including symptom scores.
Figure 2.
Possible mechanisms underlying the respiratory effects of TRAP exposure identified in this randomized crossover study in China (n=56 adults). Note: 13-HODE, 13-hydroxyoctadecadienoic acid; 13-HPODE, 13-hydroperxyoctadecadienoic acid; 13-OxoODE, 13-oxooctadecadienoic acid; EBC, exhaled breath condensate; FADH2, reduced form of flavin adenine dinucleotide; FEV1, forced expiratory volume in the first second; FVC, forced vital capacity; iNOS, inducible nitric oxide synthase; MMEF, maximal mid-expiratory flow; NADPH, reduced form of nicotinamide adenine dinucleotide phosphate; p, phosphate; PLA2, phospholipase A2; ROS, reactive oxygen species; SP-D, surfactant proteins D; TCA, tricarboxylic acid; TNF-α, tumor necrosis factor-α; TRAP, traffic-related air pollution; XOR, xanthine oxidoreductase.

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