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International Journal of Molecular Sciences logoLink to International Journal of Molecular Sciences
. 2020 Aug 24;21(17):6079. doi: 10.3390/ijms21176079

Air Pollution and Atopic Dermatitis (AD): The Impact of Particulate Matter (PM10) on an AD Mouse-Model

Yu Ri Woo 1,, Seo-Yeon Park 2,, Keonwoo Choi 2, Eun Sun Hong 1, Sungjoo Kim 2, Hei Sung Kim 1,2,*
PMCID: PMC7503766  PMID: 32846909

Abstract

Air pollution reportedly contributes to the development and exacerbation of atopic dermatitis (AD). However, the exact mechanism underlying this remains unclear. To examine the relationship between air pollution and AD, a clinical, histological, and genetic analysis was performed on particulate matter (PM)-exposed mice. Five-week-old BALB/c mice were randomly divided into four groups (control group, ovalbumin (OVA) group, PM group, OVA + PM group; n = 6) and treated with OVA or PM10, alone or together. Cutaneous exposure to OVA and PM10 alone resulted in a significant increase in skin severity scores, trans-epidermal water loss (TEWL) and epidermal thickness compared to the control group at Week 6. The findings were further accentuated in the OVA + PM group showing statistical significance over the OVA group. A total of 635, 501, and 2149 genes were found to be differentially expressed following OVA, PM10, and OVA + PM10 exposure, respectively. Strongly upregulated genes included RNASE2A, S100A9, SPRR2D, THRSP, SPRR2A1 (OVA vs. control), SPRR2D, S100A9, STFA3, CHIL1, DBP, IL1B (PM vs. control) and S100A9, SPRR2D, SPRR2B, S100A8, SPRR2A3 (OVA + PM vs. control). In comparing the groups OVA + PM with OVA, 818 genes were differentially expressed with S100A9, SPRR2B, SAA3, S100A8, SPRR2D being the most highly upregulated in the OVA + PM group. Taken together, our study demonstrates that PM10 exposure induces/aggravates skin inflammation via the differential expression of genes controlling skin barrier integrity and immune response. We provide evidence on the importance of public awareness in PM-associated skin inflammation. Vigilant attention should be paid to all individuals, especially to those with AD.

Keywords: air pollution, atopic dermatitis, particulate matter, AD mouse model, genetic analysis

1. Introduction

Air pollution is an important environmental issue and a major threat to global health [1]. Particulate matter (PM), a key component of air pollution, is a designated carcinogen [2], and is well known to increase the risk of cardiovascular and respiratory diseases [3,4]. In recent years, the damaging effect of PM on the skin has raised great interest [5,6,7].

Atopic dermatitis (AD) is an inflammatory, chronically relapsing, and intensely pruritic skin condition. With a prevalence of 2 to 5% (approximately 15% in children and young adults), it is one of the most common skin diseases in industrialized countries. AD has a strong genetic predisposition, but its recent surge in incidence also stresses the role of the environment in the pathogenesis of AD. According to epidemiologic studies, air pollution/PM significantly influences the symptoms of AD [1,8,9,10,11,12,13,14]. However, there is little definitive mechanistic evidence supporting this [15].

PM is a heterogenous mixture of solid and liquid particles suspended in air. Based on particle size, PM is categorized into PM0.1 (ultrafine particles, ≤0.1 μm), PM2.5 (fine particles, ≤2.5 μm), and PM10 (inhalable particles, ≤10 μm). PM10 encompasses PM2.5 and varies in composition depending on the source [16]. For this study, we employed a standard reference material® 2787 (SRM 2787), issued by the National Institutes of Standards and Technology (NIST). The SRM 2787 is “natural” (field collected) PM composed of polycyclic aromatic hydrocarbons (PAHs), nitro-PAHs, polybrominated diphenyl ethers (PBDEs), dioxins, sugars, and trace elements (i.e., Hg, Al, Ca, Cu, Fe, Pb, Mn, Mg, Ni), with a mean particle diameter of ≤10 μm [17].

As an important interface with the outside environment, the skin, along with the oral and respiratory routes, is a common pathway, through which ambient pollutants enter the body [18,19]. With that said, the potential mechanisms by which PM10 exerts cutaneous detrimental effects include direct insult by localization (adherence or penetration of PM to the skin) and indirect injury by systemic inflammation and oxidative stress (i.e., systemic increase of reactive oxygen species (ROS) through the respiratory system) [7].

Taking into account that epithelial barrier dysfunction and cutaneous inflammation are crucial in the pathogenesis of AD [20], the aim of the present work was to evaluate the ability of topically delivered PM to clinically promote AD, and to assess the mechanisms involved in this process by gene analysis (i.e., focusing on genes associated with skin barrier function and the inflammatory pathway). To approximate the condition of AD, we used ovalbumin (OVA)-challenged mice as the animal model.

2. Results

2.1. Gross Observation and Physiologic Parameters

Repeated topical application of OVA to the dorsal skin (2 × 2 cm) of BALB/c mice induced AD-like skin lesions with erythema, edema, excoriation, and scaling (Figure 1A). The skin severity score at Week 6 was higher in the OVA group (5.79 ± 0.91) and the PM group (4.94 ± 1.08) compared to control (0.08 ± 0.14) (p < 0.01). The skin severity score of the OVA + PM group (7.63 ± 1.73) was significantly higher than that of the OVA group and the PM group (p < 0.05). The skin severity score was similar between the OVA group and the PM group (p > 0.05) (Figure 1B).

Figure 1.

Figure 1

(A) Macroscopic findings of the dorsal skin of mice. (B) The modified scoring atopic dermatitis (SCORAD) index. (C) The trans-epidermal water loss (TEWL). * p < 0.05 compared to control, † p < 0.05 compared to OVA, § p < 0.05 compared to PM10.

OVA (OVA group) and PM10 (PM group) application caused an increase in trans-epidermal water loss (TEWL). TEWL at Week 6 was significantly higher in the OVA group (15.9 ± 3.66) and the PM group (13.9 ± 1.99), compared to control (9.20 ± 0.56) (p < 0.01). TEWL of the OVA + PM group (29.0 ± 3.61) was significantly higher than that of the OVA group and the PM group at Week 6 (p < 0.01). The TEWL was similar between the OVA and the PM group (p > 0.05) (Figure 1C).

2.2. Hisopathologic Findings

Figure 2A demonstrates the hematoxylin and eosin (H&E) and toluidine blue staining of the dorsal skin. There was marked epidermal thickening after OVA (OVA group) and PM10 (PM group) application at Week 6 compared to control (59.8 ± 16.3 and 45.1 ± 16.3 μm vs. 23.2 ± 8.42 μm) (p < 0.05). The epidermis of the OVA + PM group (82.6 ± 15.0) was significantly thicker than that of the OVA group and the PM group at Week 6 (p < 0.05). The epidermal thickness was similar between the OVA and the PM group (p > 0.05) (Figure 2B).

Figure 2.

Figure 2

(A) (upper) Histologic effects of ovalbumin (OVA) and particulate matter (PM)10 on the back skin of mice (hematoxylin and eosin (H&E); ×100), (lower) mast cell infiltration following OVA and PM10 exposure (toluidine blue; ×400). (B) Epidermal thickness. (C) The number of mast cells in five randomly chosen high power fields at ×400 magnification. (D) Serum IgE. * p < 0.05 compared to control, † p < 0.05 compared to OVA, § p < 0.05 compared to PM10.

As shown in Figure 2A, OVA and PM10 increased mast cell infiltration in the dermis. The mast cell number was significantly higher in the OVA group (14.5 ± 3.04/5 high power fields) and the PM group (10.7 ± 1.10), compared to control (4.17 ± 0.72) (p < 0.01). The number of mast cells in OVA treated groups (the OVA group, the OVA + PM group: 16.4 ± 3.19/5 high power fields) were significantly higher than that of the PM treated group (p < 0.05). The mast cell number was similar between the OVA + PM and the OVA group (p > 0.05) (Figure 2C).

2.3. Total Serum IgE

Total serum IgE at Week 6 was higher in OVA treated groups (the OVA group: 755 ± 231, the OVA + PM group: 558 ± 131 ng/mL), compared to control (162 ± 41.5 ng/mL) (p < 0.01) and the PM group (174 ± 94 ng/mL) (p < 0.01). Total serum IgE was similar between the OVA group and the OVA + PM group, and between the PM group and control (p > 0.05) (Figure 2D).

2.4. Gene Transcription Profile

According to RNA-Seq analysis, a total of 635 genes were found to be differentially expressed by OVA exposure (greater than 1.5-log2 folds up and down and a raw p-value < 0.05). Among the 635 genes, 451 genes were upregulated, and 184 downregulated. In the PM exposed group, a total of 501 genes were differentially expressed (270 upregulated and 231 downregulated). With OVA + PM10 application, the differentially expressed gene (DEG) count was 2149 (1387 upregulated and 762 downregulated). Between the OVA + PM and the OVA group, the number of DEGs was 818 (539 upregulated and 279 genes downregulated). In comparing OVA + PM10 application to PM10 alone, a total of 861 DEGs were found (591 upregulated and 270 downregulated). Between the PM and the OVA group, 71 genes were differentially expressed (54 genes upregulated and 17 downregulated) (Figure 3). The heat map and volcano plots comparing the OVA + PM group and the OVA group and the PM group vs. control are presented in Figure 4 and Figure 5, respectively.

Figure 3.

Figure 3

An overview of the differentially expressed genes (DEGs).

Figure 4.

Figure 4

Figure 4

(A) Heat map of the one-way hierarchical clustering (OVA + PM vs. OVA). (B) Distribution of gene expression level between the OVA + PM and the OVA group. (C) Scatter plot of gene expression level. (D) Significant gene count by fold change and p-value. n = 4 in each group (OVA + PM, OVA). Only those genes exhibiting log2 fold change (FC) ≥ 1.5 and p < 0.05 were considered differentially expressed genes. For the DEG (differentially expressed gene) set, hierarchical clustering analysis was done using complete linkage and Euclidean distance as a measure of similarity.

Figure 5.

Figure 5

Figure 5

(A) Heat map of the one-way hierarchical clustering (PM vs. control). (B) Distribution of gene expression level between the PM and the control group. (C) Scatter plot of gene expression level. (D) Significant gene count by fold change and p-value. n = 4 in each group (PM, control). Only those genes exhibiting log2 fold change (FC) ≥ 1.5 and p < 0.05 were considered differentially expressed genes.

The top 50 significantly up-regulated genes ranked according to the fold change are presented in Supplementary Table S1. Among them, SPRR2D, S100A9, STFA3, CHIL1, DBP, IL1b, SPRR2A1, LCE1H, SPRR2B, LCE1G (Group PM vs. control), RNASE2A, S100A9, SPRR2D, THRSP, SPRR2A1, S100A8, SERPINB3A, SPRR2B, C1QTNF3, CXCL1 (Group OVA vs. control), S100A9, SPRR2D, SPRR2B, S100A8, SPRR2A3, SERPINB3A, STFA3, SPRR2A1, SPRR2E, BC100530 (Group OVA + PM vs. control), S100A9, SPRR2B, SAA3, S100A8, SPRR2D, SPRR2A3, SERPINB3A, SPRR2E, GM5416, STFA3 (Group OVA + PM vs. Group OVA), S100A9, S100A8, SAA3, SPRR2B, SPRR2D, SPRR2A3, SERPINB3A, SPRR2E, GM5416, SPRR2A1 (Group OVA + PM vs. Group PM), NPY, FAM3B, GUCA2A, WFDC3, IL22RA2, UGT1A1, TESC, SERPINE2, CRABP1, PTGS1 (Group PM vs. Group OVA) were most significantly up-regulated (Table 1). The DEGs are also presented in Table 2 according to their function.

Table 1.

Top 10 significantly upregulated genes.

PM vs. Control OVA vs. Control OVA + PM vs. Control OVA + PM vs. OVA OVA + PM vs. PM PM vs. OVA
1 SPRR2D RNASE2A S100A9 S100A9 S100A9 NPY
Log2FC 4.537781 15.353418 175.102606 21.032206 43.232510 2.912855
2 S100A9 S100A9 SPRR2D SPRR2B S100A8 FAM3B
Log2FC 4.050253 8.325451 122.348283 19.765663 36.247161 2.237210
3 STFA3 SPRR2D SPRR2B SAA3 SAA3 GUCA2A
Log2FC 3.884888 7.414729 99.190350 16.871093 33.226551 2.082410
4 CHIL1 THRSP S100A8 S100A8 SPRR2B WFDC3
Log2FC 3.852430 6.074408 86.466724 16.615182 30.495545 2.057602
5 DBP SPRR2A1 SPRR2A3 SPRR2D SPRR2D IL22RA2
Log2FC 3.637145 5.429848 68.747026 16.500708 26.962138 1.771707
6 IL1B S100A8 SEPINB3A SPRR2A3 SPRR2A3 UGT1A1
Log2FC 3.375845 5.204079 65.385001 14.139278 21.554361 1.765702
7 SPRR2A1 SERPINB3A STFA3 SERPINB3A SERPINB3A TESC
Log2FC 3.293317 5.127475 51.600623 12.751891 21.542993 1.728145
8 LCE1H SPRR2B SPRR2A1 SPRR2E SPRR2E SERPINE2
Log2FC 3.272727 5.018316 50.181213 12.506733 16.809473 1.705879
9 SPRR2B C1QTNF3 SPRR2E GM5416 GM5416 CRABP1
Log2FC 3.252618 4.536723 43.315581 10.651026 16.545459 1.702428
10 2610528A11RIK CXCL1 BC100530 STFA3 SPRR2A1 PTGS1
Log2FC 3.202117 3.865055 29.494805 9.717934 15.237285 1.689424

Table 2.

DEGs according to their function.

Genes PM vs. Control OVA vs. Control OVA + PM vs. Control OVA + PM vs. OVA OVA + PM vs. PM PM vs. OVA
Xenobiotic Metabolizing Enzyme
CYP1A1 2.364800
UGT1A1 1.968411 1.765702
UGT1A7C 1.563135 4.020299 2.571945 2.447144
Immune Response
IL1B 3.375845 2.144279 15.898589 7.414423 4.709514
IL1F6 2.459084 2.677326 10.362620 3.870511 4.214016
IL1F8 1.682234 1.930127 5.440192 2.818568 3.220411
IL1F9 2.309176 1.647147 6.738345 4.090919
IL-13ra1 2.339857 1.786709 1.753326
IL-13ra2 2.445235 1.997591
IL-33 1.652810 5.151400 3.116752 3.571956
CXCL1 2.034245 3.865055 15.266021 7.504513
CCL2 2.414083 3.966503
CCL7 3.176686 6.829295 2.149817 3.330636
CCL8 3.262495 9.964881 3.054375 7.572985
CCR1 1.977892 7.166230 3.623166 5.588996
CXCR2 5.409111 3.934086 4.409069
TNFAIP2 2.981176 2.211034 2.536282
TNFAIP6 3.665933 3.788700
FCER1A 3.066804 5.700756 3.742706
FCER1G 1.866897 4.525466 2.424057 3.528595
CHIL1 3.852430 3.413080 23.799435 6.973008 6.177772
RNASE2A 15.353418 17.480094 5.250776 −4.611952
Skin Barrier
Epidermal Differentiation Complex
KRT1 2.012479 5.013296 3.007899 2.4911105
KRT6b 9.746359 7.671900 10.906282
KRT16 14.027059 8.550596 9.550772
LCE1F 2.848601 1.856882 2.793710
LCE1G 3.202117 2.625508 3.709355
LCE1H 3.272727 2.649690 3.867855
LCE3A 1.985872 11.751650 5.917627 7.581050
LCE3B 12.008217 6.312606 9.559686
LCE3E 1.877260 9.465151 5.314134 5.042002
LCE3F 1.999833 11.052984 4.905179 5.526953
S100A8 2.385476 5.204079 86.466724 16.615182 36.247161
S100A9 4.050253 8.325451 175.102606 21.032206 43.232510
SPRR2A1 3.293317 5.429848 50.181213 9.241734 15.237285
SPRR2A3 3.189472 68.747026 14.139278 21.554361
SPRR2B 3.252618 5.018316 99.190350 19.765663 30.495545
SPRR2D 4.537781 7.414729 122.348283 16.500708 26.962138
SPRR2E 2.576855 3.463381 43.315581 12.506733 16.809473
SPRR2I 1.924438 2.981781 26.165916 8.775266 13.596652
FLG −1.749558 −2.481263
Protease
MMP3 2.031330 10.906441 5.369114 6.745412
SERPINB3A 3.035094 5.127475 65.385001 12.751891 21.542993
SERPINB3B 2.497089 2.768278 17.026990 6.150751 6.818736
STFA1 2.008981 17.513492 6.855981 8.717599
STFA3 3.884888 51.600623 9.717934 13.282395
BC100530 2.912126 29.494805 7.555283 10.128274
KLK6 3.837728
KLK8 2.456366 1.996790 6.233008 3.121514
KLK9 2.747518 1.846616 9.784243 5.298470
KLK13 2.201600 2.251518 13.571149 6.027555 6.164222
Antimicrobial Response
DEFB6 1.852542 1.683457 3.312694
DEFB14 2.278557 5.154124 2.628721
Other
2610528A11RIK 3.128210 3.748969 27.119970 7.233981 8.669484

The major gene ontology (GO) terms and pathways of OVA + PM vs. OVA group are shown in Figure 6. As for the biological process, the top 10 terms of GO functional analysis were immune system process, immune response, regulation of immune system process, defense response, positive regulation of immune system process, response to external stimulus, response to other organism, response to external biotic stimulus, response to biotic stimulus, and inflammatory response (Figure 6A). The cellular component included cornified envelope and the NADPH (nicotinamide adenine dinucleotide phosphate oxidase) complex (Figure 6B), and the molecular function included cytokine binding, oxidoreductase activity acting on NADPH, pattern recognition receptor activity and peptidase regulator activity (Figure 6C). KEGG analysis showed that up-regulated DEGs for both OVA + PM vs. OVA group and PM vs. control group were enriched in metabolic pathways (mmu01100), Ras signaling pathway (mmu04014), Rap1 signaling pathway (mmu04015), MAPK signaling pathway (mmu04010), Jak-STAT signaling pathway (mmu04630), NF-kappa B signaling pathway (mmu04064), TNF signaling pathway (mmu04668), HIF-1 signaling pathway (mmu04066), calcium signaling pathway (mmu04020), cytokine-cytokine receptor interaction (mmu04060), toll-like receptor signaling pathway (mmu04620), nodulation (NOD)-like receptor signaling pathway (mmu04621), c-type lectin receptor signaling pathway (mmu04625), Th17 cell differentiation (mmu04659), IL-17 signaling pathway (mmu04657), inflammatory mediator regulation of TRP channels (mmu04750), and pathways in cancer (mmu05200).

Figure 6.

Figure 6

Figure 6

Figure 6

The major gene ontology (GO) terms and pathways of OVA + PM vs. OVA group. (A) Biologic process, (B) Cellular component, (C) molecular function.

The NOD-like receptor signaling pathway is shown in Figure 7. Among the relevant genes, cutaneous PM10 exposure induced up-regulation of NOD2 (log2 FC: 1.505669), NFKBIA (log2 FC: 1.856415), CARD9 (log2 FC: 1.655884), IL1B (log2 FC: 3.375845), IL18 (log2 FC: 1.545413), CXCL1 (log2 FC: 2.034245), CCL5 (log2 FC: 1.608780), DEFB14 (log2 FC: 2.276974), and BIRC3 (log2 FC: 1.60949) (p-value < 0.05).

Figure 7.

Figure 7

Nodulation (NOD)-like receptor signaling pathway (PM vs. control). The orange star signifies genes with a p < 0.05. +p: phosphorylation; +u: ubiquitination; −u: de-ubiquitination; - - ->: activation.

The cytokine-cytokine receptor interaction pathway of OVA + PM group showed up-regulation of IL1B (log2 FC: 7.414423), CCL8 (log2 FC: 3.054375), CCL20 (log2 FC: 3.529423), CCR1 (log2 FC: 3.623166), CCR2 (log2 FC: 2.525612), CCR9 (log2 FC: 1.530475), CXCR2 (log2 FC: 3.934086), CSFLR (log2 FC: 2.709420), Il10RA (log2 FC: 2.133591), Il1F5 (log2 FC: 2.587269), Il1F6 (log2 FC: 3.870511), Il1F8 (log2 FC: 2.818568), Il1F9 (log2 FC: 4.090919), PF4 (log2 FC: 3.212812), Il33 (log2 FC: 3.116752), Il18RAP (log2 FC: 1.976295), Il12RB2 (log2 FC: 1.938648), Il13RA1 (log2 FC: 1.786709), LTB (log2 FC: 1.560564), TNFRSF1B (log2 FC: 1.784543), TNFRSF14 (log2 FC: 1.711990), IFNAR2 (log2 FC: 1.628548), CD4 (log2 FC: 1.621931), IL6RA (log2 FC: 1.616884) and the downregulation of BMP2 (log2 FC: −2.171518) and NGFR (log2 FC: −1.737021) compared to the OVA group (p-value < 0.05) (Figure 8).

Figure 8.

Figure 8

The cytokine-cytokine receptor interaction pathway (OVA + PM vs. OVA). The orange star signifies genes with a p < 0.05; ?: unknown.

3. Discussion

This study explored how exposure to PM10 modulates the development and exacerbation of AD using OVA-treated BALB/c mice. The endpoints of this study included: (1) the extent of clinical and histological skin inflammation including hallmarks of allergic inflammation; and (2) the expression of various genes involved in the skin barrier and immune response to gain insight into the PM modulation of AD.

Our OVA exposed mice successfully captured the characteristics of AD (i.e., increase in serum IgE, mast cell infiltration in the dermis, elevated gene expression of CHIL1 (related to Th2 response), FCER1A (Fc fragment of IgE receptor 1a), IL-33 (an epithelial cell-derived cytokine that promotes Th2 cytokine responses), and RNASE2A (important for eosinophil recruitment and function)). Key AD genes, including the Th2 and Th22 cytokines (IL-4, IL-13, IL-22) are usually present at less than detection level on microarrays, requiring real-time PCR (RT-PCR) [21,22,23]. This was also the case with our samples—although absent from microarray, we were able to detect IL-13 in the OVA treated groups through real-time PCR (RT-PCR) (data not shown).

No single murine model fully captures all aspects of the AD profile. Ewald et al. [24] have recently compared the transcriptomic profiles of common AD-like murine models and identified that the OVA-challenged model has significant overlap with genes upregulated in human AD, but does not capture the downregulated signature of human AD. Accordingly, we tried to focus on the upregulated genes in our study. The DEGs of our OVA exposed mice and those of Ewald et al.’s [24] OVA-challenged model were highly similar, which confirmed the reliability of our AD mouse model.

PM10 displayed adjuvant-like effects, enhancing skin inflammation/barrier damage upon OVA challenge (i.e., enhanced skin severity scores, TEWL, epidermal thickness, and increased expression of skin barrier genes (epidermal differentiation complex: KRT1, 6b, 16; LCE3A, 3B, 3E, 3F; S100A8, A9; SPRR2A1, 2A3, 2B, 2D, 2E, 2I; protease: MMP3; SERPINB3A, 3B; STFA1, 3; BC100530; KLK8, 9, 13; antimicrobial response: DEFB14), and pro-inflammatory genes (IL-1B, TNF1IP2). The expression of allergy genes (IL-13RA1, IL-33, FCERIG, CHIL1) was also enhanced in the OVA + PM group when compared to the OVA group indicating the possible exacerbation of AD.

We were also intrigued to see if PM10 affects intact skin. In a prior study, Jin et al. [25] have detected PM inside hair follicles in both intact and barrier-disrupted skin. Additionally, repeated PM application was shown to induce epidermal thickening and dermal inflammation with neutrophil infiltration. Although we failed to detect PM in the appendageal structures/dermis of our skin sections, our findings were similar with that of Jin et al. [25], where enhanced skin severity scores, TEWL, epidermal thickness, and increased expression of skin barrier genes (epidermal differentiation complex: KRT1; LCE1F, 1G, 1H; LCE3E, 3F; S100A8, A9; SPRR2A1, 2A3, 2B, 2D, 2E, 2I; protease: SERPINB3A, 3B; STFA1, 3; BC100530; KLK8, 9, 13; antimicrobial response: DEFB14; other: 2610528A11RIK) and pro-inflammatory genes (IL-1B, CXCL1) were noted. The increase in mast cell number, heightened expression of an allergy-related gene (CHIL1), and detection of IL-13 through RT-PCR (data not shown) suggest that AD can perhaps develop following PM10 exposure alone.

The main cause of PM-inflicted skin damage has been identified as polycyclic aromatic hydrocarbons (PAHs), the main organic constituent of PM [15,26,27]. PAHs exert their biological effect via binding to the ligand-activated transcription factor aryl hydrocarbon receptor (AHR), which is widely expressed on skin cells [28]. AHR is a major sensor of environmental signals, but at the same time, AHR ligands are abundant in the skin from exogenous or endogenous sources [28].

The quality and duration of AHR activation by various ligands directs the level and spectrum of the genes which are induced, and are thus pivotal in the outcome, including a “toxic” outcome [29,30]. Three important groups of genes are targeted by AHR [29]. First, a battery of genes encoding detoxifying enzymes (xenobiotic metabolizing enzymes, XMEs), such as the cytochrome P450 (CYP) gene CYP1A1 (Phase I XME) and Phase II enzymes (NADPH dehydrogenase quinone 1, NQO1; glutathione S-transferases, GSTA2; uridine 5-diphospho-glucuronosyltransferases; UGT1A1, UGT1A6, UGT1A7) [31,32,33]; second, genes related to epidermal differentiation and skin barrier integrity; and finally, genes related to immunity.

The AHR battery genes are noteworthy in that we have found evidence of aberrant AHR activation with our model (OVA group, PM group, OVA + PM group) based on elevated gene expression levels of XMEs. Xenobiotic small chemicals have strong affinity to AHR and cause persistent activation of the receptor [28]. The pathogenic implication of AHR and its gene polymorphism in AD remain elusive but it has been suggested that most AHRs lack physiological ligands in the Th2-prone milieu in AD [31,34].

Transgenic mice expressing constitutively active form of AHR (AHR-CA) [35] (surmised to be equivalent to PAH-liganded AHR) have shown a gene profile with an increase in structural protein genes (KRT1, 6B, 16), protease genes (i.e., MMP), interleukins/chemokine genes (i.e., IL-1B, CXCL1, CCL8), Fc receptor genes (FCERIG), and antimicrobial peptide genes (i.e., DEFB) reproduced in our mouse models (PM group, OVA + PM group), which indicates the role of the PAH-liganded AHR in PM induced skin barrier dysfunction/immune deviation.

The ligation of AHR by xenobiotic small chemicals (i.e., PAH, dioxin) was reported to preferentially affect the differentiation and propagation of Th 17 cells [31,36,37], as seen in our PM exposed mouse models (enrichment of upregulated DEGs in the Th17 cell differentiation (mmu04659), and IL-17 signaling pathway (mmu04657)), which too suggests that the PAH-AHR axis underlies the allergic response to PM.

PAH itself has also been suggested to provoke inflammation as a primary irritant or allergen [35,38,39,40]. Other lines of evidence suggest that reactive oxygen species (ROS) generated by oxygenated PAHs enhance the allergic response [41,42]. PAHs have also been shown to stimulate an increase in the DNA-binding activity of NF-kB [43], which, in turn, induces cytokine gene expression provoking the allergic response. To note, the NF-kappa B signaling pathway (mmu04064) was found to be enriched with upregulated DEGs in our OVA + PM and PM group.

In summary, we demonstrate that PM exacerbates AD when exposure occurs during simultaneous allergen sensitization/elicitation. The enhancement of the allergic immune response by PM is characterized by increased mast cells in the dermis, elevated serum IgE level, upregulated expression of the skin barrier genes (epidermal differentiation complex; protease; antimicrobial response), pro-inflammatory genes, and allergy genes (microarray: IL-13RA1, IL-33, FCERIG, CHIL1; RT-PCR: IL-13; KEGG analysis: Th17 cell differentiation, IL-17 signaling pathway). PM-mediated toxicity may be the result of PAHs modulating immunity and the epidermal barrier via the AHR.

Since PM is also able to initiate AD in intact skin, further work is needed to investigate if PM enhances the antigen-presenting capabilities of dendritic cells, and if this translates to enhanced B and T cell adaptive responses, as well as the critical role of the AHR in these processes. Our identification of the molecular mechanisms through which PM mediates its toxicological effects and enhances immune-mediated inflammation and barrier damage sheds light on the sharp rise of AD in the past decades.

In conclusion, we provide evidence on the importance of public awareness in PM-associated skin inflammation. Vigilant attention and preventive measures should be paid to all individuals, especially to those with AD.

4. Materials and Methods

4.1. Particulate Matter

PM10 was collected in 2005 from an air intake filtration system of a major exhibition center in Prague, Czech Republic (NIST, SRM 2787). PM suspension was freshly prepared by resuspending PM particles in phosphate-buffered saline (PBS) at a concentration of 2.5 mg/mL, and vortexing for 30 min at maximum speed.

4.2. Animals

Four-week-old female BALB/c mice were procured from Orient Bio Inc., Sungnam, Korea. Animals were housed in specific pathogen-free (SPF) environment, exposed to a 12-h light/dark cycle, and were provided with autoclaved water and food ad libitum. The mice were randomly divided into 4 groups (control group, OVA group, PM group, OVA + PM group; n = 6). After a week of acclimatization, the back of the mice was shaved with an electric clipper (day 0) and was kept hair-free with hair removal cream (Veet) and tape strips (Nad’s body wax strip) twice weekly for the entire study period. The study protocol was approved by the Institutional Animal Care and Use Committees (IACUCs) of the College of Medicine, The Catholic University of Korea (2019-0207-03, 1 August 2019).

4.3. Sensitization and Challenge

The schematic experimental procedure is described in Figure 9. The mice in the OVA group and OVA + PM group were intraperitoneally (IP) injected with 20 μg chicken egg ovalbumin (OVA) (A5503-1G, Sigma-Aldrich, St. Louis, MO, USA) and 2 mg of aluminum hydroxide (769460-100G, Sigma-Aldrich, St. Louis, MO, USA) in 200 μL of PBS on days 0, and 7 using a modified protocol [44,45]. Those in the control group and the PM group were IP injected with an equal volume of PBS on the same date. From day 0, a PM patch (250 μg/cm2 of PM10 applied on a nonwoven 2 × 2 cm2 polyethylene sheet (Scotch BriteTM, 3M, St. Paul, MN, USA) and fixed with a transparent adhesive film dressing (TegadermTM, 3M, St. Paul, MN, USA) was applied daily to the backs of the PM group (until Week 6) and the OVA + PM group (until Week 2) mice. A PBS patch (400 μL of PBS applied on a 2 × 2 cm2 nonwoven polyethylene sheet and fixed with a transparent adhesive film dressing) was employed in the same manner in the control group (until Week 6) and the OVA group (until Week 2). Seven days after the final IP injection, mice in the OVA group and the OVA + PM group were challenged with OVA (400 μg of OVA dissolved in 400 μL of PBS applied on a 2 × 2 cm2 nonwoven polyethylene sheet and fixed with a transparent adhesive film dressing) and OVA + PM (400 μg of OVA + 250 μg/cm2 of PM10 in 400 μL of PBS applied on a nonwoven 2 × 2 cm2 polyethylene sheet and fixed with a transparent adhesive film dressing patches respectively, until the end of the study (Week 6).

Figure 9.

Figure 9

Experimental protocol for assessing the effects of OVA (IP + cutaneous) and PM10 (cutaneous) exposure in BALB/c mice.

4.4. Assessment of Clinical Parameters

Clinical assessments were made twice a week for the entire study period. The trans-epidermal water loss (TEWL) was assessed on the dorsal skin of the BALB/c mice using the VapoMeter (Delfin Technologies, Kuopio, Finland). A modified scoring atopic dermatitis (SCORAD) (defined as the sum of individual scores for each of the following 4 signs and symptoms: erythema, edema, excoriation, and dryness. Each item was scored as 0 (none), 1 (mild), 2 (moderate), and 3 (severe), as previously described) was used to measure the clinical severity. Scoring was performed by 2 assessors masked to the study purpose and hypothesis. They were not involved in treatment administration or assignment.

4.5. Histopathology

The mice were sacrificed in Week 6. The dorsal skin samples were fixed in 10% vol. phosphate-buffered formalin solution, embedded in paraffin, and sectioned at 4 μm. The tissue sections were stained with hematoxylin and eosin (H&E) for microscopic examination. For identification of mast cells, skin sections were stained with toluidine blue. The mast cells were counted in 5 randomly chosen visuals fields at ×0400 magnification. The evaluation was performed at a central laboratory, where slides were made available for a central reading by an assessor masked to the experiment.

4.6. Enzyme-Linked Immunosorbent Assay (ELISA)

Blood was collected from the retroorbital plexus using heparinized glass capillary tubes at the end of the experiment (Week 6). Serum samples obtained by centrifugation (3000× g for 4 min at 4 °C) were stored at −80 °C until use. Concentration of total IgE serum was determined using the mouse IgE ELISA kit (Shibayagi Co. Ltd., Gunma, Japan), according to the manufacturer’s instruction. Laboratory evaluations were performed at a central laboratory.

4.7. mRNA-Seq

Total RNA concentration was calculated by Quant-IT RiboGreen (R11490, Invitrogen, Carlsbad, CA, USA). To assess the integrity of the total RNA, samples were run on the TapeStation RNA screentape (#5067-5576, Agilent, Santa Clara, CA, USA). Only high-quality RNA preparations, with RIN greater than 7.0, were used for RNA library construction.

cDNA libraries were constructed with the TruSeq RNA library kit (RS-122-2101, Illumina Inc., San Diego, CA, USA) where 1 μg of RNA was used per sample. RNA was polyA-selected, fragmented, reverse transcribed and sequenced with Illumina HiSeq4000 (San Diego, CA, USA). Libraries were quantified with the qPCR-based KAPA Library Quantification Kit (KK4854) and qualified with an Agilent Technologies 2100 Bioanalyzer (Santa Clara, CA, USA).

The raw reads were preprocessed and then aligned to Mus musculus (mm10) with HISAT v2.2.0 (http://ccb.jhu.edu/software/hisat2/) [46]. HISAT employs two kinds of indexes and creates spliced alignments faster than BWA and Bowtie. Downloads of the reference genome sequence and annotation data are available from http://genome.uscs.edu. StringTie v1.3.4d (http://ccb.jhu.edu/software/stringtie/) [47,48] was used to build aligned reads into transcripts and calculate fragments per kilobase of exon per million fragments mapped (FPKM) values. Standardized FPKM values were utilized to compare gene’s expression levels. Sixteen samples (control, OVA, PM, OVA + PM groups; 4 samples per group) were examined in total.

4.8. Statistical Analysis

All data are expressed as the mean ± SD. One-way analysis variance (ANOVA,) followed by the Tukey multiple comparison test, was used to assess differences in the measurements between multiple groups. Statistical analyses were performed using Graph Pad Prism 4.0 (San Diego, CA, USA). A p-value of less than 0.05 was considered statistically significant.

Statistical analysis was carried out to find DEGs. Transcripts with zeroed FPKM values were eliminated. Filtered data were log2-transformed and quantile normalized. Statistical significance of the DEG data was verified with independent t-test and fold change with a null (no difference) hypothesis. The false discovery rate (FDR) was corrected with the Benjamini-Hochberg algorithm. Hierarchical clustering analysis was performed employing Euclidean distance and complete linkage. Gene-enrichment and functional annotation analysis and pathway analysis for significant gene list were carried out according to gProfiler (http://biit.cs.ut.ee/gprofiler/orth) and KEGG pathway (http://www.genome.jp/kegg/pathway.html).

Acknowledgments

We acknowledge Jung Woo Suh for technical support.

Abbreviations

AD Atopic dermatitis
PM Particulate matter
OVA Ovalbumin
TEWL Trans-epidermal water loss
PAHs Polyaromatic hydrocarbons
ROS Reactive oxygen species
SCORAD Scoring atopic dermatitis
H&E Hematoxylin and eosin
DEG Differentially expressed genes
SPRR Small proline rich proteins
STFA Stefin A
CHIL Chitinase-like
DBP D site-binding protein
LCE Late cornified envelope
RNASE Ribonuclease
THRSP Thyroid hormone responsive
SERPIN Serine proteinase inhibitor
C1QTNF C1q and tumor necrosis factor
CXCL C-X-C motif chemokine ligand
SAA Serum amyloid A
NPY Neuropeptide Y
FAM3B Family with sequence similarity 3, member B
GUCA Guanylate cyclase activator
WFDC WAP four-disulfide core domain
UGT UDP glucuronosyltransferase
TESC Tescalcin
CRABP Cellular retinoic acid binding protein
GO Gene ontology
NADPH Nicotinamide adenine dinucleotide phosphate
KEGG Kyoto encyclopedia of genes and genomes
RAP Ras-related protein
MAPK Mitogen-activated protein kinase
JAK-STAT Janus kinases-signal transducer and activator of transcription
NF-kB Nuclear factor-kappa B
TNF Tumor necrosis factor
HIF Hypoxia-inducible factor
NOD Nodulation
NFKBIA NF-kappa-B inhibitor alpha
CARD Caspase activation and recruitment domains
CCL CC chemokine ligand
DEFB Defensin beta
BIRC3 Baculovial IAP repeat containing 3
CCR C-C chemokine receptor
CXCR C-X-C chemokine receptor
CSF1R Colony stimulation factor-1 receptor
PF4 Platelet factor 4
LTB Lymphotoxin-beta
TNFRSF Tumor necrosis factor receptor superfamily
IFNAR2 Interferon alpha and beta receptor subunit 2
BMP Bone morphogenetic protein
NGFR Nerve growth factor receptor
FCER Fc fragment of IgE receptor
KRT Keratin
KLK Kallikreins
AHR Aryl hydrocarbon receptor
XME Xenobiotic metabolizing enzyme
CYP Cytochrome P450
NQO NADPH quinone oxidoreductase
GSTA Glutathione S-transferase
UGT UDP-glucuronosyltransferase
IP Intraperitoneal
PBS Phosphate-buffered saline

Supplementary Materials

The following are available online at https://www.mdpi.com/1422-0067/21/17/6079/s1.

Author Contributions

Conceptualization, H.S.K., S.K., Y.R.W.; methodology, S.-Y.P., K.C.; investigation, S.-Y.P.; data curation, E.S.H., Y.R.W.; writing-original draft preparation, Y.R.W., S.-Y.P.; writing—review and editing, H.S.K.; Supervision, H.S.K., S.K., Y.R.W.; Project administration, S.-Y.P., E.S.H.; funding acquisition H.S.K. All authors have read and agreed to the published version of the manuscript.

Funding

Hei Sung Kim is supported by a National Research Foundation of Korea (NRF) grant funded by the South Korean Government (grant number: 2020R1F1A1048238).

Conflicts of Interest

The authors declare no conflict of interest.

References

  • 1.Hendricks A.J., Eichenfield L.F., Shi V.Y. The impact of airborne pollution on atopic dermatitis: A literature review. Br. J. Dermatol. 2020;183:16–23. doi: 10.1111/bjd.18781. [DOI] [PubMed] [Google Scholar]
  • 2.Greco S.L., MacIntyre E., Young S., Warden H., Drudge C., Kim J., Candido E., Demers P., Copes R. An approach to estimating the environmental burden of cancer from known and probable carcinogens: Application to Ontario, Canada. BMC Public Health. 2020;20:1–3. doi: 10.1186/s12889-020-08771-w. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 3.Mueller W., Loh M., Vardoulakis S., Johnston H.J., Steinle S., Precha N., Kliengchuay W., Tantrakarnapa K., Cherrie J.W. Ambient particulate matter and biomass burning: An ecological time series study of respiratory and cardiovascular hospital visits in northern Thailand. Environ. Health. 2020;19:1–12. doi: 10.1186/s12940-020-00629-3. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 4.Moelling K., Broecker F. Air Microbiome and Pollution: Composition and Potential Effects on Human Health, Including SARS Coronavirus Infection. J. Environ. Public Health. 2020;2020:1646943. doi: 10.1155/2020/1646943. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 5.Kim K.E., Cho D., Park H.J. Air pollution and skin diseases: Adverse effects of airborne particulate matter on various skin diseases. Life Sci. 2016;152:126–134. doi: 10.1016/j.lfs.2016.03.039. [DOI] [PubMed] [Google Scholar]
  • 6.Park S.Y., Byun E.J., Lee J.D., Kim S., Kim H.S. Air Pollution, Autophagy, and Skin Aging: Impact of Particulate Matter (PM(10)) on Human Dermal Fibroblasts. Int. J. Mol. Sci. 2018;19:2727. doi: 10.3390/ijms19092727. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 7.Araviiskaia E., Berardesca E., Bieber T., Gontijo G., Sanchez Viera M., Marrot L., Chuberre B., Dreno B. The impact of airborne pollution on skin. J. Eur. Acad. Dermatol. Venereol. 2019;33:1496–1505. doi: 10.1111/jdv.15583. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 8.Ahn K. The role of air pollutants in atopic dermatitis. J. Allergy Clin. Immunol. 2014;134:993–999. doi: 10.1016/j.jaci.2014.09.023. [DOI] [PubMed] [Google Scholar]
  • 9.Pénard-Morand C., Raherison C., Charpin D., Kopferschmitt C., Lavaud F., Caillaud D., Annesi-Maesano I. Long-term exposure to close-proximity air pollution and asthma and allergies in urban children. Eur. Respir. J. 2010;36:33–40. doi: 10.1183/09031936.00116109. [DOI] [PubMed] [Google Scholar]
  • 10.Lee Y.L., Su H.J., Sheu H.M., Yu H.S., Guo Y.L. Traffic-related air pollution, climate, and prevalence of eczema in Taiwanese school children. J. Investig. Dermatol. 2008;128:2412–2420. doi: 10.1038/jid.2008.110. [DOI] [PubMed] [Google Scholar]
  • 11.Oh I., Lee J., Ahn K., Kim J., Kim Y.M., Sun Sim C., Kim Y. Association between particulate matter concentration and symptoms of atopic dermatitis in children living in an industrial urban area of South Korea. Environ. Res. 2018;160:462–468. doi: 10.1016/j.envres.2017.10.030. [DOI] [PubMed] [Google Scholar]
  • 12.Tang K.T., Ku K.C., Chen D.Y., Lin C.H., Tsuang B.J., Chen Y.H. Adult atopic dermatitis and exposure to air pollutants-a nationwide population-based study. Ann. Allergy Asthma Immunol. 2017;118:351–355. doi: 10.1016/j.anai.2016.12.005. [DOI] [PubMed] [Google Scholar]
  • 13.Kim Y.M., Kim J., Han Y., Jeon B.H., Cheong H.K., Ahn K. Short-term effects of weather and air pollution on atopic dermatitis symptoms in children: A panel study in Korea. PLoS ONE. 2017;12:e0175229. doi: 10.1371/journal.pone.0175229. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 14.Hassoun Y., James C., Bernstein D.I. The Effects of Air Pollution on the Development of Atopic Disease. Clin. Rev. Allergy Immunol. 2019;57:403–414. doi: 10.1007/s12016-019-08730-3. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 15.Hidaka T., Ogawa E., Kobayashi E.H., Suzuki T., Funayama R., Nagashima T., Fujimura T., Aiba S., Nakayama K., Okuyama R., et al. The aryl hydrocarbon receptor AhR links atopic dermatitis and air pollution via induction of the neurotrophic factor artemin. Nat. Immunol. 2017;18:64–73. doi: 10.1038/ni.3614. [DOI] [PubMed] [Google Scholar]
  • 16.Guarnieri M., Balmes J.R. Outdoor air pollution and asthma. Lancet. 2014;383:1581–1592. doi: 10.1016/S0140-6736(14)60617-6. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 17.Schantz M.M., Cleveland D., Heckert N.A., Kucklick J.R., Leigh S.D., Long S.E., Lynch J.M., Murphy K.E., Olfaz R., Pintar A.L., et al. Development of two fine particulate matter standard reference materials (<4 μm and <10 μm) for the determination of organic and inorganic constituents. Anal. Bioanal. Chem. 2016;408:4257–4266. doi: 10.1007/s00216-016-9519-7. [DOI] [PubMed] [Google Scholar]
  • 18.Valacchi G., Sticozzi C., Pecorelli A., Cervellati F., Cervellati C., Maioli E. Cutaneous responses to environmental stressors. Ann. N. Y. Acad. Sci. 2012;1271:75–81. doi: 10.1111/j.1749-6632.2012.06724.x. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 19.Magnani N.D., Muresan X.M., Belmonte G., Cervellati F., Sticozzi C., Pecorelli A., Miracco C., Marchini T., Evelson P., Valacchi G. Skin Damage Mechanisms Related to Airborne Particulate Matter Exposure. Toxicol. Sci. 2016;149:227–236. doi: 10.1093/toxsci/kfv230. [DOI] [PubMed] [Google Scholar]
  • 20.Bieber T. Atopic dermatitis. N. Engl. J. Med. 2008;358:1483–1494. doi: 10.1056/NEJMra074081. [DOI] [PubMed] [Google Scholar]
  • 21.Suárez-Fariñas M., Tintle S.J., Shemer A., Chiricozzi A., Nograles K., Cardinale I., Duan S., Bowcock A.M., Krueger J.G., Guttman-Yassky E. Nonlesional atopic dermatitis skin is characterized by broad terminal differentiation defects and variable immune abnormalities. J. Allergy Clin. Immunol. 2011;127:954–964. doi: 10.1016/j.jaci.2010.12.1124. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 22.Gittler J.K., Shemer A., Suárez-Fariñas M., Fuentes-Duculan J., Gulewicz K.J., Wang C.Q., Mitsui H., Cardinale I., de Guzman Strong C., Krueger J.G., et al. Progressive activation of T(H)2/T(H)22 cytokines and selective epidermal proteins characterizes acute and chronic atopic dermatitis. J. Allergy Clin. Immunol. 2012;130:1344–1354. doi: 10.1016/j.jaci.2012.07.012. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 23.Suárez-Fariñas M., Ungar B., Correa da Rosa J., Ewald D.A., Rozenblit M., Gonzalez J., Xu H., Zheng X., Peng X., Estrada Y.D., et al. RNA sequencing atopic dermatitis transcriptome profiling provides insights into novel disease mechanisms with potential therapeutic implications. J. Allergy Clin. Immunol. 2015;135:1218–1227. doi: 10.1016/j.jaci.2015.03.003. [DOI] [PubMed] [Google Scholar]
  • 24.Ewald D.A., Noda S., Oliva M., Litman T., Nakajima S., Li X., Xu H., Workman C.T., Scheipers P., Svitacheva N., et al. Major differences between human atopic dermatitis and murine models, as determined by using global transcriptomic profiling. J. Allergy Clin. Immunol. 2017;139:562–571. doi: 10.1016/j.jaci.2016.08.029. [DOI] [PubMed] [Google Scholar]
  • 25.Jin S.P., Li Z., Choi E.K., Lee S., Kim Y.K., Seo E.Y., Chung J.H., Cho S. Urban particulate matter in air pollution penetrates into the barrier-disrupted skin and produces ROS-dependent cutaneous inflammatory response in vivo. J. Dermatol. Sci. 2018;91:175–183. doi: 10.1016/j.jdermsci.2018.04.015. [DOI] [PubMed] [Google Scholar]
  • 26.Li R., Ning Z., Majumdar R., Cui J., Takabe W., Jen N., Sioutas C., Hsiai T. Ultrafine particles from diesel vehicle emissions at different driving cycles induce differential vascular pro-inflammatory responses: Implication of chemical components and NF-kappaB signaling. Part. Fibre Toxicol. 2010;7:6. doi: 10.1186/1743-8977-7-6. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 27.Totlandsdal A.I., Herseth J.I., Bølling A.K., Kubátová A., Braun A., Cochran R.E., Refsnes M., Ovrevik J., Låg M. Differential effects of the particle core and organic extract of diesel exhaust particles. Toxicol. Lett. 2012;208:262–268. doi: 10.1016/j.toxlet.2011.10.025. [DOI] [PubMed] [Google Scholar]
  • 28.Esser C., Rannug A. The aryl hydrocarbon receptor in barrier organ physiology, immunology, and toxicology. Pharmacol. Rev. 2015;67:259–279. doi: 10.1124/pr.114.009001. [DOI] [PubMed] [Google Scholar]
  • 29.Esser C., Bargen I., Weighardt H., Haarmann-Stemmann T., Krutmann J. Functions of the aryl hydrocarbon receptor in the skin. Semin. Immunopathol. 2013;35:677–691. doi: 10.1007/s00281-013-0394-4. [DOI] [PubMed] [Google Scholar]
  • 30.Mitchell K.A., Elferink C.J. Timing is everything: Consequences of transient and sustained AhR activity. BioChem. Pharmacol. 2009;77:947–956. doi: 10.1016/j.bcp.2008.10.028. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 31.Furue M., Hashimoto-Hachiya A., Tsuji G. Aryl Hydrocarbon Receptor in Atopic Dermatitis and Psoriasis. Int. J. Mol. Sci. 2019;20:5424. doi: 10.3390/ijms20215424. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 32.Köhle C., Bock K.W. Coordinate regulation of Phase I and II xenobiotic metabolisms by the Ah receptor and Nrf2. BioChem. Pharmacol. 2007;73:1853–1862. doi: 10.1016/j.bcp.2007.01.009. [DOI] [PubMed] [Google Scholar]
  • 33.Nebert D.W., Roe A.L., Dieter M.Z., Solis W.A., Yang Y., Dalton T.P. Role of the aromatic hydrocarbon receptor and [Ah] gene battery in the oxidative stress response, cell cycle control, and apoptosis. BioChem. Pharmacol. 2000;59:65–85. doi: 10.1016/S0006-2952(99)00310-X. [DOI] [PubMed] [Google Scholar]
  • 34.Yu J., Luo Y., Zhu Z., Zhou Y., Sun L., Gao J., Sun J., Wang G., Yao X., Li W. A tryptophan metabolite of the skin microbiota attenuates inflammation in patients with atopic dermatitis through the aryl hydrocarbon receptor. J. Allergy Clin. Immunol. 2019;143:2108–2119. doi: 10.1016/j.jaci.2018.11.036. [DOI] [PubMed] [Google Scholar]
  • 35.Tauchi M., Hida A., Negishi T., Katsuoka F., Noda S., Mimura J., Hosoya T., Yanaka A., Aburatani H., Fujii-Kuriyama Y., et al. Constitutive expression of aryl hydrocarbon receptor in keratinocytes causes inflammatory skin lesions. Mol. Cell. Biol. 2005;25:9360–9368. doi: 10.1128/MCB.25.21.9360-9368.2005. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 36.Stockinger B., Di Meglio P., Gialitakis M., Duarte J.H. The aryl hydrocarbon receptor: Multitasking in the immune system. Annu. Rev. Immunol. 2014;32:403–432. doi: 10.1146/annurev-immunol-032713-120245. [DOI] [PubMed] [Google Scholar]
  • 37.Schiering C., Vonk A., Das S., Stockinger B., Wincent E. Cytochrome P4501-inhibiting chemicals amplify aryl hydrocarbon receptor activation and IL-22 production in T helper 17 cells. BioChem. Pharmacol. 2018;151:47–58. doi: 10.1016/j.bcp.2018.02.031. [DOI] [PubMed] [Google Scholar]
  • 38.Anderson C., Hehr A., Robbins R., Hasan R., Athar M., Mukhtar H., Elmets C.A. Metabolic requirements for induction of contact hypersensitivity to immunotoxic polyaromatic hydrocarbons. J. Immunol. 1995;155:3530–3537. [PubMed] [Google Scholar]
  • 39.Davila D.R., Davis D.P., Campbell K., Cambier J.C., Zigmond L.A., Burchiel S.W. Role of alterations in Ca(2+)-associated signaling pathways in the immunotoxicity of polycyclic aromatic hydrocarbons. J. Toxicol. Environ. Health. 1995;45:101–126. doi: 10.1080/15287399509531985. [DOI] [PubMed] [Google Scholar]
  • 40.Yamamoto O., Tokura Y. Photocontact dermatitis and chloracne: Two major occupational and environmental skin diseases induced by different actions of halogenated chemicals. J. Dermatol. Sci. 2003;32:85–94. doi: 10.1016/S0923-1811(03)00097-5. [DOI] [PubMed] [Google Scholar]
  • 41.Bonvallot V., Baeza-Squiban A., Baulig A., Brulant S., Boland S., Muzeau F., Barouki R., Marano F. Organic compounds from diesel exhaust particles elicit a proinflammatory response in human airway epithelial cells and induce cytochrome p450 1A1 expression. Am. J. Respir Cell Mol. Biol. 2001;25:515–521. doi: 10.1165/ajrcmb.25.4.4515. [DOI] [PubMed] [Google Scholar]
  • 42.Kepley C.L., Lauer F.T., Oliver J.M., Burchiel S.W. Environmental polycyclic aromatic hydrocarbons, benzo(a) pyrene (BaP) and BaP-quinones, enhance IgE-mediated histamine release and IL-4 production in human basophils. Clin. Immunol. 2003;107:10–19. doi: 10.1016/S1521-6616(03)00004-4. [DOI] [PubMed] [Google Scholar]
  • 43.Pei X.H., Nakanishi Y., Inoue H., Takayama K., Bai F., Hara N. Polycyclic aromatic hydrocarbons induce IL-8 expression through nuclear factor kappaB activation in A549 cell line. Cytokine. 2002;19:236–241. doi: 10.1006/cyto.2002.1967. [DOI] [PubMed] [Google Scholar]
  • 44.Matsuo K., Hatanaka S., Kimura Y., Hara Y., Nishiwaki K., Quan Y.S., Kamiyama F., Oiso N., Kawada A., Kabashima K., et al. A CCR4 antagonist ameliorates atopic dermatitis-like skin lesions induced by dibutyl phthalate and a hydrogel patch containing ovalbumin. BioMed. Pharmacother. 2019;109:1437–1444. doi: 10.1016/j.biopha.2018.10.194. [DOI] [PubMed] [Google Scholar]
  • 45.Kim S.R., Choi H.S., Seo H.S., Choi Y.K., Shin Y.C., Ko S.G. Topical application of herbal mixture extract inhibits ovalbumin- or 2,4-dinitrochlorobenzene-induced atopic dermatitis. Evid. Based Complement. Altern. Med. 2012;2012:545497. doi: 10.1155/2012/545497. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 46.Kim D., Langmead B., Salzberg S.L. HISAT: A fast spliced aligner with low memory requirements. Nat. Methods. 2015;12:357–360. doi: 10.1038/nmeth.3317. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 47.Pertea M., Pertea G.M., Antonescu C.M., Chang T.C., Mendell J.T., Salzberg S.L. StringTie enables improved reconstruction of a transcriptome from RNA-seq reads. Nat. Biotechnol. 2015;33:290–295. doi: 10.1038/nbt.3122. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 48.Pertea M., Kim D., Pertea G.M., Leek J.T., Salzberg S.L. Transcript-level expression analysis of RNA-seq experiments with HISAT, StringTie and Ballgown. Nat. Protoc. 2016;11:1650–1667. doi: 10.1038/nprot.2016.095. [DOI] [PMC free article] [PubMed] [Google Scholar]

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