Abstract
Ozone (O3) inhalation triggers asthmatic airway hyperresponsiveness (AHR), but the mechanisms
by which this occurs are unknown. Previously , we developed a murine model of dust mite,
ragweed, and aspergillus (DRA)-induced allergic lung inflammation followed by O3 exposure for
mechanistic investigation. The present study used single cell RNA -sequencing for unbiased
profiling of immune cells within the lungs of mice exposed to DRA, O 3, or DRA+O3, to identify
the components of the immune cell niche that contribute to AHR. A lveolar macrophages (AMs)
had the greatest number of differentially expressed genes following DRA+O3, most of which were
unique to the 2-hit exposure. Following DRA+O3, AMs activated transcriptional pathways related
to cholesterol biosynthesis, degradation of the extracellular matrix, endosomal TLR processing,
and various cytokine signals . We also identified AM and monocyte subset populations that were
unique to the DRA+O3 group. These unique AMs activated gene pathways related to inflammation,
sphingolipid metabolism, and bronchial constriction. The unique monocyte population had a gene
signature that suggested phospholipase activation and increased degradation of the extracellular
matrix. Flow cytometry analysis of BAL immune cells showed recruited monocyte-derived AMs
after DRA and DRA+O3, but not after O3 exposure alone. O3 alone increased BAL neutrophils but
this response was attenuated in DRA+O3 mice. DRA-induced changes in the airspace immune cell
profile were reflected in elevated BAL cytokine/chemokine levels following DRA+O3 compared
to O3 alone. The present work highlights the role of monocytes and AMs in the response to O3 and
suggests that the presence of distinct subpopulations following allergic inflammation may
contribute to O3-induced AHR.
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Keywords
Asthma, ozone, macrophage, monocyte, single cell RNA sequencing
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Introduction
Clinically, asthma is characterized by airway remodeling and episodic exacerbations that lead to
increased shortness of breath and wheezing. Asthma exacerbations occur in response to respiratory
infections or environmental exposures and result in significant morbidity and even mortality (1).
One common environmental exposure that leads to asthma exacerbations is ambient (ground-level)
ozone (O3). Ground-level O3 is an air pollutant formed as a byproduct from the photochemical
reactions between primary air pollutants such as volatile organic compounds and nitrogen oxides
with UV light (2). Epidemiologic studies have linked exposure to ambient O3 to increased use of
asthma rescue medication s and increased hospital visits (3). Observational studies suggest that
asthmatics have increased susceptibility to the adverse effects of O 3 compared to non-asthmatics
(4). However, the cell ular and molecular mechanisms by which O 3 exposure leads to asthma
exacerbations are not known.
Many of the clinical manifestations of O 3 induced asthma exacerbations are due to
bronchoconstriction and airway hyperresponsiveness (AHR). AHR is a complex process mediated
by increased contraction (or impaired relaxation) of airway smooth muscle (5). Airway smooth
muscle hyper contractility is mediated, in part, by inflammatory cells recruited to asthmatic
airways. Previous studies have identified recruited granulocytes such as eosinophils, neutrophils,
and mast cells as potential mediators of asthmatic AHR in response to O3 (6). It has also been
observed that there is an increase in other immune cells including alveolar macrophages (AMs) in
the airways of asthmatic patients following experimental O 3 exposure (7). AMs, along with
recruited granulocytes, create an inflamed niche around the airways that mediate O3 induced AHR.
Current treatment for asthma exacerbations, regardless of the precipitant , includes the use of
corticosteroids and bronchodilators . This “one size fits all” approach to inhibit airway
inflammation and promote airway relaxation may not fully a ddress the complex biological and
environmental factors that initiate AHR and acute exacerbation. In fact, studies have shown that
O3 impairs the efficacy of glucocorticoid treatment in experimental models (8–10). Therefore, it is
essential to understand the underlying mechanisms by which O 3 triggers asthmatic AHR. To
address this issue, our group recently developed a model of acute O 3 exacerbation in mice with
allergic airway inflammation. Using this model, we demonstrated that mice exposed to O3 in the
setting of allergic inflammation had both increased AHR and changes in the innate and adaptive
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immune cell populations that comprise the inflammatory microenvironment within the lungs (11).
In the present study , we build upon our prior work by utiliz ing single cell RNA sequencing to
perform an unbiased analysis of immune cell transcriptomic changes in this niche to identify the
cell populations responsible for O3 induced AHR during asthma exacerbations.
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Methods
Mice. Male and female C57BL/6 J (stock number: 000664) mice (8-9 weeks old) were purchased
from The Jackson Laboratory (Bay Harbor, ME) and allowed to rest for 1 week prior to
experiments. Animals were housed in specific pathogen- free conditions within The Ohio State
University Animal Care Facility (Columbus, OH). All animal experiments were performed in
compliance with the U.S. Department of Health and Human Services Guide for the Care and U se
of Laboratory Animals and were reviewed and approved by the Institutional Animal Care and Use
Committee at The Ohio State University (Animal Use Protocol #2017A00000074-R2).
Mixed allergen model of allergic asthma. The DRA triple -allergen mixture was made in PBS,
with a final concentration of the following extracts: 0.83 mg/ml of house dust mite
(Dermatophagoides farina), 8.33 mg/ml of short ragweed (Ambrosia artenmisiifolia), and 0.83
mg/ml of Aspergillus fumigatus , as previously described (11) . All allergens were sourced from
Stallergenes Greer . Mice were lightly anesthetized with 2- 4% isoflurane before intranasal
administration of 20 μl DRA mixture on experimental days 0, 5, 12, 14, and 17 (Fig. 1A). Under
the same protocol, control mice were administered 20 μl PBS.
Ozone exposure. On experimental day 18 (24 hr after the last DRA challenge), mice were exposed
to room air (control) or O 3 at an average of 2 ppm for 3 hr. This exposure paradigm was chosen
to ensure O3-induced toxic effects in mice and is comparable to an O 3 concentration of 400 ppb
for humans (12). Whole- body exposures were performed using a custom -designed plexiglass
chamber (13). O3 was generated by directing 100% oxygen over an ultraviolet light, which was
then mixed with room air using an air pump and directed into the exposure chamber. O 3
concentrations within the exposure chamber were monitored continuously (Photometric Ozone
Analyzer – Model 400E, Teledyne Technologies) and adjusted accordingly. The temperature
(average 21.6° C) and humidity ( average dew point 17° C and relative humidity (80% ) of the
exposure chamber were also monitored.
Euthanasia. Mice were euthanized on experimental day 19 (24 hr after O
3 exposure / 48 hr after
final DRA challenge) using pentobarbital ( 100 mg/kg I.P) or ketamine+xylazine ( 300 and 30
mg/kg, respectively) overdose.
Bronchoalveolar lavage. 0.9 ml of PBS was instilled into the bilateral lungs and withdrawn. This
was repeated t wo times with the same fluid for cytokine analysis. The bronchoalveolar lavage
(BAL) was centrifuged at ~900g for 5 minutes to pellet any cells and the supernatant was collected
for cytokine measurements. Four additional, separate washes (1 ml of PBS each) were performed,
and the collected cells were pooled with those from the first aliquot for airway immune cell
analysis. Total cell counts were determined by TC20™ Automated Cell Counter (BioRad).
Single cell RNA sequencing sample preparation and library generation . Each treatment group
was comprised of 4 male and 4 female mice. At the time of harvest, cells were isolated from whole
lung tissue by collagenase digestion, as previously described (14). Lung cells from all males and
all females were then pooled for each respective exposure group (n = 2 per exposure group; 1
pooled male sample and 1 pooled female sample). Live cells were then enriched using fluorescence
activated cell sorting for DAPI- cells. The live cell suspensions were then prepared for sequencing
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library generation by the Genomics Shared Resource at The Ohio State University Comprehensive
Cancer Center according to the manufacturer’s protocol CG000315 Rev C for the Chromium Next
GEM Single Cell 3’ Kit v3.1 (10X Genomics, Pleasanton, CA, USA).
Single Cell Data processing. After demultiplexing, the filtered matrices where loaded into a Seurat
(15) individually (min.cells = 0, min.genes=0, min.features=0), and percentage of mitochondrial
content marked. To reduce noise in the data, cells with greater than 1% mitochondria and nFeatures
greater than one where selected. Doublets (doublets_table.csv) were found and removed with
scDblFinder (16) . SCTransform (method = glmGamPoi, vars.to.regress = “perMito”) and
Harmony (17) (group.by.vars = “orig.ident”, reduction = “pca”) was then performed to normalize
and combine samples. The Azimuth (18) feature was used with LungMap (19) to annotate cell
types. The mbkmeans (20) package was used to determine appropriate principle component
analysis, dimensional reduction (PCA, UMAP, tSNE) was performed in Seurat and rendered using
ggplot2 (21), and cell type annotation was compared to clustering to assure proper alignment.
Pseudo-bulk RNA -Seq analysis. The 10x Genomics de -multiplexing pipeline retains many
unwanted gene types; to reduce this unwanted noise, the Bioconductor (22) Mus.musculus package
was used to annotate gene types, and non- protein coding genes removed from the Seurat object.
Sequencing counts were aggregated, and differential analysis performed with EdgeR (23) as
described in the EdgeR handbook (estimateDisp, qlmQLFit, qlmQLFTest) on cell types with
greater than 1,000 cells.
Transcriptional pathway enrichment analysis. Ingenuity Pathway Analysis (IPA; QIAGEN Inc.)
was used to analyze all differentially expressed genes (DEG; FDR < .05, log(fold change) ≥ |1.0|)
for transcriptional pathway enrichment analysis. The canonical and machine learning pathways
presented in the main text were chosen based on biological relevance, statistical significance (p <
.05), activation score (z-score ≥ |2.0|), and DEG overlap ratio. For AMs, DCs, and monocytes, a
full list of IPA canonical pathways is provided in the supplemental text.
Flow Cytometry. 500,000 cells collected by BAL were stained with 1 μ l LIVE/DEAD™ Fixable
Dead Cell Stain (ThermoFisher) in 1 ml PBS for 15 minutes at room temperature. Cells were then
incubated with Fc receptor block (anti-mouse CD16/32; BD biosciences) and subsequently stained
with primary antibodies in 100 μ l Flow Staining Buffer (I nvitrogen) for 15 minutes at room
temperature. Anti-mouse primary antibodies were used at the following dilutions to define immune
cell populations (Fig. S3): Ly6G (1:100; Biolegend, 127628), CD45 (1:100; Biolegend, 103155),
CD11b (1:100; Biolegend, 101241), CD8α (1:100; Biolegend, 100706), CD19 (1:100; Biolegend,
152407), CD64 (1:50; Biolegend, 139319), CD24 (1:100; Biolegend, 101824), CD4 (1:100;
Biolegend, 100422), Siglec F (1:100, BD Pharmigen, 562680), CD11c (1:100; Biolegend,
117320), and CD3 (1:100; Biolegend, 100222). Spectral flow cytometry was performed using the
Cytek® Northern Lights 3000 3- laser System in the Flow Cytometry Core at The Ohio State
University Davis Heart and Lung Research Institute . All data analysis was performed in FlowJo
version 10 software.
Cytokine measurements. Cytokines in the BAL and plasma (Fig. S7) were measured using a Meso
Scale Discovery Multiplex Assay according to manufacturer instructions. For the V-PLEX Mouse
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Cytokine 19-Plex Kit (IFNγ, IL-1β, IL-2, IL-4, IL-5, IL-6, KC/GRO, IL-10, TNFα, MCP-1, IL-
33, MIP-1α, IP-10, MIP-2) BAL and plasma were diluted 1:4 and the extended sample incubation
protocol was used as recommended . A custom U-PLEX Assay (mouse) was used to measure
Eotaxin, IL-13, IL-17E/25, MCP-5/Ccl12, MIP-1β, MIP-3α, and VEGF-A in BAL and plasma;
samples were diluted 1:2 and incubated for 1 hr.
Statistics. For laboratory-based experiments, data sets were tested for normality via a Shapiro-
Wilk test and statistical analyses were performed by comparison of means using a one -way
ANOV A followed by Tukey’s post hoc testing. Statistical significance was defined as a probability
of type I error occurring at less than 5% ( p < 0.05). Graphics and analyses were performed in
PRISM v 9 (GraphPad, San Diego, CA).
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Results
Single cell RNA sequencing of lung immune cells after allergen and ozone exposure(s)
The DRA triple-allergen model (11) was used to induce allergic airway inflammation in wild-type
mice. Both control and DRA sensitized mice were then exposed to O 3 and sacrificed 24 hr post-
exposure (Fig. 1A). The lungs were collected from all four treatment groups (control, DRA, O 3,
and DRA+O3) and processed for scRNA sequencing. A total of 49, 806 cell transcriptomes were
profiled and passed quality control filtering; subsequent cell cluster annotation was performed
using published studies (19). t-SNE dimensionality reduction technique was used to visualize all
cell clusters, including structural and immune cells (Fig. S1A). The number of cells sequenced in
each exposure group and a full list of marker genes can be found in the supplemental data (Table
S1 & Fig. S1B). For immune cells, we captured both innate and adaptive immune cell populations
(Fig. 1B). The top 50 marker genes used to identify immune cell populations are shown in Fig. 1C.
Cell populations that were sufficient ly abundant for subsequent differential expression analyses
(>1,000 cells) included monocytes, alveolar macrophages (AMs), dendritic cells (DCs), T cells, B
cells, and NK cells (Table S1).
Alveolar macrophages from DRA+O
3 exposed animals exhibit a unique transcriptional profile
compared to DRA or O3 alone.
AMs are the primary resident immune cells within the airways and play a critical role in regulating
and directing inflammatory and functional responses to inhaled xenobiotics, including O
3 (24).
The transcriptional response of AMs to O 3 exposure in the setting of pre -existing allergic
inflammation has yet to be defined. When examining all immune cells, scRNA -seq analysis
revealed that AMs displayed the greatest number of DEG s (Table S2). Therefore, we chose to
perform subsequent analyses on these cells. AMs were identified in all four treatment groups (Fig.
2A, B) but differential expression analysis showed that AMs from the DRA+O 3 group exhibited
the greatest number of DEGs compared to controls (Fig. 2C, Table S2); a 300% and 900% increase
compared to individual DRA and O3 exposures, respectively. Transcriptional changes in AMs from
the DRA+O3 exposure were predominantly driven by the response to DRA (Fig. 2D); however,
over half of the upregulated DEGs were unique to the DRA+O3 exposure group (Fig. 2D). AMs
from DRA+O3 exposed mice demonstrated an alternative activation phenotype (increased Arg1,
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Ccl24, Rnase2a) , which appeared to be driven by the DRA exposure (Fig. 2E) . However,
transcriptional pathway analysis revealed that after DRA+O 3 exposure AMs had enhanced
activation of interferon and interleukin signaling, and a relative inhibition of phagocytic and
hypoxic pathways compared to DRA alone (Fig. 2F). In contrast, exposure to O 3 alone enhanced
gene expression in pathways related to sterol and cholesterol biosynthesis and cell cycle
progression in AMs (Fig 2F). AMs from the 2- hit group also activated sterol and cholesterol
biosynthesis, but without activating cell cycle-related pathways (Fig. 2F). Pathway analysis of
AMs from DRA+O 3 mice also revealed the unique activation of various pathways such as
degradation of the extracellular matrix, differential regulation of cytokine production by IL-17A/F,
cytokine storm signaling, response of EIF2AK1 to heme deficiency, and trafficking and processing
of endosomal TLR (Fig. 2F). Taken together, these data highlight t he divergence in biological
processes involved in the AM response(s) to DRA-induced allergic inflammation compared to O3
alone, and further demonstrate that AMs developed unique transcriptomic profile s following
exposure to DRA+O3 that were distinct from the individual exposures.
O3 exposure in the setting of allergic inflammation leads to the presence of a unique monocyte
population within the lungs.
Circulating monocytes survey the lung during homeostasis (25) but can also be recruited during
inflammation and injury to serve as precursors for resident macrophage populations such as AMs.
Initial transcriptomic analysis revealed that there was a unique population of lung monocytes in
the 2-hit group (Fig. 3B). Compared to controls, monocytes from the lungs of DRA exposed mice
only had 35 DEGs, while O3 and DRA+O3 exposure induced differential expression of 179 and 91
genes, respectively (Fig. 3C , Table S2). The transcriptional changes in monocytes from t he O3
exposure group were predominantly downregulation of gene expression (Fig. 3C, Table S2) , so
>90% of the DEGs upregulated in DRA+O3 monocytes were unique to the 2- hit exposure (Fig.
3D). The DEGs with the greatest increase in expression in DRA monocytes relative to controls
were Clca1 (6.485 fold increase) which promotes mucus production (26) and Reg3g (6.553 fold
increase) which has been reported to suppress allergic airway inflammation (27) (Fig. 3E). In DRA
mice subsequently exposed to O 3, these genes were no longer increased; instead, DRA+O 3
monocytes showed high expression of chemokine Cxcl3 (Fig. 3E). Pathway analysis of significant
DEGs (Fig. 3C) showed that there were few differentially regulated pathways in lung monocytes
following DRA and O 3 exposures compared to controls (Fig. 3F) . After O 3 exposure alone,
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monocytes in the lungs showed an inhibition of interferon signaling (Fig. 3F). Alternatively,
exposure to both DRA+O 3 caused activation of pro-inflammatory pathways in lung monocytes,
such as cytokine s torm and S100 family signaling, as well as GPCR signaling and phagosome
formation (Fig. 3F). These data demonstrate that transcriptional pathways in lung monocytes differ
in the DRA+ O3 model compared to uninjured controls or either exposure alone.
DRA-mediated changes in dendritic cell phenotype are maintained after O3 exposure.
DCs are professional phagocyt es and antigen presenting cells that have been shown to play an
important role in allergic lung inflammation. Differential expression analysis demonstrated that
these cells had the second highest number of DEGs in response to DRA+O3 (Table S2); however,
in contrast to AMs and monocytes, tSNE plots of DCs did not indicate any potentially unique
transcriptional subsets between treatment groups (Fig. S2B). Of the 3 exposure groups, DCs from
the 2 -hit group had the greatest number of DEG compared to controls (Fig. S2C , Table S2 ).
Approximately half of the upregulated DEG in DCs from the DRA+O3 group were unique to the
2-hit model and ~25% overlapped with DRA alone (Fig. S2D). Transcriptional pathway analysis
revealed minimal changes after O 3 exposure (Fig. S2F) . T he majority of pathways activated
following DRA, with or without subsequent O3 exposure, were related to cellular division, antigen
presentation, and leukocyte extravasation (Fig. S2F). Interestingly, O3 as a second hit appeared to
impair the DRA-mediated activation of cell cycle pathways in DCs, but increased MHCII antigen
presentation (Fig. S2F). These results suggest that DRA exposure induces activation of cell cycle
pathways in DCs in the lungs and subsequent O3 exposure impairs this response.
Allergic inflammation causes recruitment of macrophage subtypes into the airways but impairs
neutrophil recruitment following ozone.
Transcriptional analysis revealed differences in gene expression of immune cells following DRA
and/or O 3 exposure . Previously, we performed flow cytometry assessment of immune cell
populations in whole lung tissue (11). However, since the current study suggested a predominant
role of AMs in the response to the 2 -hit DRA+O 3 model , we sought to comprehensively
characterize the airspace niche, where the AMs reside, by analyzing the immune cell populations
present in bronchoalveolar lavage (BAL). Compared to controls, total BAL cell counts revealed
significant immune cell infiltration in DRA -treated mice with or without O 3 exposure, but not in
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response to O3 alone (Fig. 4A). Flow cytometry was used to analyze the immune cell populations
from the BAL (Fig. S3, S4). In control mice, tissue -resident ( TR)-AMs ma de up 90% of the
immune cells present in the airspace (Fig. 4B). This proportion decreased following all exposures,
as other immune cells were recruited to the lung (Fig. 4B ). At the time point these samples were
collected, there was no difference in the absolute number of TR-AMs in any of the experimental
groups (Fig. 4C). Exposure to DRA with or without O3 induced recruitment of monocyte-derived
(Mo)-AMs, interstitial macrophages (IMs), and DCs into the airways, but this was not observed in
mice exposed to O3 alone (Fig. 4D-F). Granulocytes were absent in the airspace of control mice,
but DRA exposure induced significant eosinophilia that was not affected by subsequent O 3
exposure (Fig. 4G) . O 3 exposed mice showed a significant increase in neutrophil numbers
compared to controls; however, O3-induced neutrophil recruitment was impaired in the setting of
allergic inflammation in the DRA+O3 group (Fig. 4H). Adaptive immune cells were mostly absent
in the BAL of control mice, but DRA exposure induced a significant increase in the number of B
cells, CD8+ T cells, and CD4+ T cells that was unaffected by subsequent O3 exposure (Fig. 4I-K).
These data highlight the extensive differences in the immune cells present in the airspace niche of
normal and DRA -exposed mice that can alter the microenvironment and consequently the AM
response to inhaled O3.
Pre-existing allergic inflammation alters the inflammatory mediators present within the
airspaces following O3 exposure.
To further characterize the inflammatory signaling within the airspace, we measured cytokine
levels in the BAL fluid (Fig. 5, S 5, S6). Type 2 cytokines IL -4 and IL -13 were increased over
controls in both DRA and DRA+O3 groups (Fig. 5A, B). Although DRA-mediated eosinophilia in
the BAL was unaffected by O3 (Fig. 4G), eosinophil maturation and chemotactic factors, IL-5 and
CCL11 (Eotaxin), were increased in DRA+O 3 compared to DRA alone (Fig. 5C, D ). Despite
reduced neutrophil numbers in the BAL of DRA+ O3 mice compared to O 3 alone (Fig. 4H) ,
neutrophil chemoattractants CXCL1 (KC/GRO) and CXCL2 (MIP-2) were increased over controls
after DRA+O3 exposure; in fact, CXCL2 was significantly higher in the DRA+O3 group compared
to O3 alone (Fig. 5 E, F). CCL2, also known as monocyte chemoattractant protein (MCP)-1, was
only significantly increased after DRA+O 3 (Fig. 5 H). Additional chemokines and pro-
inflammatory cytokines that were increased in the DRA-exposed groups (DRA and DRA+O3), but
not after O3 only exposure, included: CXCL10 (IP-10), CCL3 (MIP-1α), CCL4 (MIP-1β), IL-1β,
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and TNF α ( Fig. 5G, I, J, L, N) . Interestingly, chemokine CCL20 (MIP -3α) was significantly
increased over controls in the individual exposure groups, but there was no difference following
the 2-hit exposure (Fig. 5K). The increase in the acute inflammatory cytokine IL-6 was driven by
O3 exposure (Fig. 5M). Finally, expression of VEGF-A was only increased over controls following
O3 exposure; induction of this factor by O 3 was impaired by allergic inflammation in the DRA+
O3 group (Fig. 5O). We hypothesize that these changes in cytokine and chemokines within the
airspace were due to the cells present in this microenvironment , because there were only limited
changes observed in serum of these mice (Fig. S7). These data demonstrate that the inflammatory
milieu within the airspace after DRA+O3 is primarily driven by the response to DRA allergens,
but pre-existing DRA-induced inflammation alters the microenvironment during subsequent O3
exposure (DRA+O3).
A transcriptionally distinct AM subpopulation unique to the DRA+O3 exposure activates disease
pathways related to AHR.
We further examined AM and monocyte transcriptional subpopulations by performing a manual
sub-setting based on dimensionality reduction t -SNE plots. Using this technique, t here were 3
potentially distinct AM subsets (Fig. 6A). AM subset “A” was comprised of cells primarily from
the DRA+O
3 exposure group, subset “B” contained AMs from both DRA and DRA+O3 exposures,
and “C” was made up of AMs from all 4 exposure groups but predominantly from control and O3
exposures (Fig. 2B, 6A). Pathway analysis of subset “B” revealed enrichment of genes involved
in i nterferon α/β signaling, protein targeting to the membrane, and posttranslational
phosphorylation pathways , but downregulation of genes related to mTOR signaling and nitric
oxide (NO) and reactive oxygen species (ROS) production (Fig. 6B). In AM subset “A” (DRA+O3)
mTORC1 signaling was activated compared to AMs in “C” (control + O 3) (Fig. 6C), which is
consistent with the activation of sphingolipid metabolism pathway and inhibition of fatty acid β -
oxidation pathways also observed in “A” (Fig. 6C). AM subset “A” was also enriched for genes
involved in multiple pathways related to inflammatory signaling (Fig. 6C). Finally, comparing AM
subset “A” (DRA+O3) to “B” (DRA±O3) allowed us to examine the unique transcriptional changes
driven by O3 as a second hit following allergic inflammation (Fig. 6D) . Transcriptional pathway
analysis revealed a relative inhibition of oxidative phosphorylation and chaperone gene pathways
related to ER stress, as well as upregulation of genes involved in NO and ROS synthesis pathways,
sphingolipid metabolism, and inflammatory pathways related to neuroinflammation and cytokine
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storm signaling (Fig. 6D). In contrast to the subgroup analysis of AMs, there were only 2 subgroups
identified on dimensionality reduced monocyte t-SNE plots (Fig. 6E). The cells in subset “D” were
only from the DRA+O 3 exposure group, while “ E” was comprised of monocytes from all 4
exposures (Fig. 3B, 6E). Compared to all other monocytes, the DRA+O3-specific subset (“D”) had
decreased gene expression related to mTOR signaling which was reflected in the activation of
pathways related to degradative phospholipases and inhibition of VEGF family interactions and
the NRF2 oxidative stress response (28, 29)(Fig. 6F).
To further characterize the contributions of these subsets to the functional AHR response to O3, we
utilized IPA’s Machine Learning evaluation of association with disease processes. These analyses
indicated that following DRA treatment, AM subsets “A” and “B” activated processes related to
macrophage activation syndrome and acute lung injury, as compared to subset “C” (Fig. 6G).
Interestingly, subset “A” (overrepresentation by DRA+O 3) was most significantly involved in
processes associated with constriction of bronchus (Fig. 6G), corresponding with the enhanced
functional AHR response (increased airway resistance) previously observed in DRA+O3 mice (11).
Comparison of monocyte subsets did not show significant activation (z-score < 2.0) of any of the
presented disease pathways (Fig. 6G, panel 4). Taken together, these results point towards a unique
transcriptional subset of AMs that contributes to not only inflammatory signaling (Fig. 6C, D) but
functional AHR outcomes following DRA+O3 exposure (Fig. 6G).
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Discussion
More than 350 million people worldwide live with asthma every day (1), but exposure to
various triggers, such as allergens and air pollution can cause exacerbation or worsening of asthma
symptoms and lung function. Previously, we established a murine model of DRA-induced allergic
lung inflammation followed by acute O3 exposure to mimic the human asthmatic AHR response
for mechanistic investigation (11) . In the present study, we bui ld upon this work by performing
scRNA sequencing on lung cells of mice exposed to DRA, O 3, or DRA+O 3 to gather unbiased
insights into the cell types involved in the functional response to inhaled O3 in the context of
allergic lung inflammation. We were able to detect changes in both the innate and adaptive immune
cells within the lung, but the most significant findings were the transcriptional changes observed
in AMs in response to DRA+O 3 (Fig. 2, Table S1). Upon further analysis , there were
transcriptionally distinct groups of both AMs and monocytes that were unique to the DRA+O3
group (Fig. 6). Pathways that were upregulated in these subsets of cells include production of
cytokines and oxidants , lipid metabolism, and bronchial constriction. Taken together these data
highlight an important role for macrophage activation by O3 in the allergic lung niche.
O3 inhalation causes lung injury and since AMs are the primary immune cell present within
the airways, they play an essential role in protecting the host against inflammatory insults . In the
present study, AMs demonstrated minimal transcriptional changes in response to O3 alone, except
for activation of cholesterol biosynthesis and cell cycle pathways (Fig. 2F). AMs from the
DRA+O3 exposure group also upregulated gene pathways related to cholesterol biosynthesis, but
in the absence of cell cycle pathway activation (Fig. 2F). T argeted analysis of unique AM
subpopulations revealed that a subgroup of AM comprised cells mostly from DRA+O3 (group “A”,
Fig 6) had transcriptional changes in canonical pathways related to lipid metabolism, oxidative
phosphorylation, and inflammatory signaling (Fig. 6C, D). Interestingly, altered glycosphingolipid
metabolism has been previously associated with the allergic AHR response to O 3 (30) and
individual sphingolipids have been shown to enhance airway smooth muscle (ASM) cell
proliferation and AHR (31). Furthermore, AMs and monocytes from DRA+O3 exposed mice, but
not DRA alone, activated transcriptional pathways related to degradation of the extracellular
matrix (Fig. 2F, 6F) including the upregulation of matrix metalloprotease (MMP) gene expression
(Fig. 2E, 3E). In accordance with these results, AMs from people with asthma have been shown to
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16
release higher levels of MMPs , which is associated with increased airway thickness and a faster
decline in FEV1 (32). These changes in AM phenotype following the 2-hit exposure demonstrate
that the immune response to inhaled O3 is different in asthmatic lungs compared to normal lungs.
Airway macrophages are comprised of cells from two different ontogenies: fetal yolk sac
derived self-renewing TR-AMs and recruited Mo-AMs differentiated from circulating monocytes
originating from the bone marrow (33). Following exposure to DRA there was recruitment of Mo-
AMs into the airspaces, which remained present during subsequent exposure to O 3; but these
recruited Mo -AMs were absent in mice challenged with O 3 alone (Fig. 4D) . TR-AMs are
considered protective against allergic inflammation and essential for resolution of O 3-induced
inflammation (34, 35) and a recent study also showed a population of recruited CX 3CR1+ AMs
facilitate the resolution of eosinophilic inflammation in the DRA model (36). However, in contrast
to these protective roles , recruited monocytes/Mo-AMs are reported to drive lung inflammation
and injury in a variety of models (33, 37–41), including allergic inflammation and allergen-induced
AHR (34, 42, 43) . In accordance with the present findings (Fig. 4D), a lineage tracing study
recently demonstrated that there is no recruitment of Mo-AMs in healthy mice or humans exposed
to O3 alone (35). Consequently, the influence of Mo-AMs in the asthmatic AHR response to O 3
has yet to be directly investigated.
There are other immune cells present within the allergic asthmatic lung that can also
regulate downstream signaling responses to O3 exposure. Neutrophils are recruited to the airways
following O3 inhalation (Fig. 4) and airway neutrophilia is linked to corticosteroid resistance and
severe asthma (44). Reports on the role of n eutrophils in AHR have been mixed; some studies
report a direct role in AHR (45 –47) while others do not (48, 49). Neutrophils are recruited via
CXCL1 and IL-6, both of which were elevated in the BAL following DRA+O3 (Fig. 5E, M). There
was no significant difference in airspace neutrophilia between O 3 and DRA+O3 exposure groups
(Fig. 4H), however, significant differences were observed when the data was analyzed by sex (Fig.
S4C). Macrophages present within the lung interstitium can also modulate lung inflammation and
remodeling. Previous reports demonstrate that IL -10 production by IMs prevents neutrophilic
asthma (50), but that LPS-mediated replacement of embryonically-derived IMs with bone marrow-
derived IMs reduces BAL IL-10 and AHR in response to subsequent allergen challenge (51). The
current study reports increased IM numbers in the BAL of DRA-exposed mice (Fig. 4E). But, we
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17
have previously demonstrated that O 3 attenuates DRA-induced increases in IM numbers and IL -
10 levels in the lung tissue of male mice (11) , which corresponds with the increased neutrophils
numbers observed in the BAL of DRA+O3 exposed males (Fig. S4C). It is therefore possible that
O3 changes IM function in a deleterious way, however, further work is needed to understand the
role of these cells in regulating the AHR response.
Although inflammatory cells regulate various aspects of lung injury and allergic
inflammation, bronchoconstriction and acute shortness of breath due AHR are mediated by the
contraction of airway smooth muscle ( ASM) cells. ASM contract ion is induced by c ellular
mediators such as histamines, trypase, and eicosanoids , as well as acetylcholine released from
neurons (5). Immune cell inflammatory signaling influence s this contractile response and
contributes to the hypercontractility observed in asthmatic AHR. Previous studies have identified
TNFα, IFNγ, IL-13, and IL -1β as inflammatory cytokines that alter ASM phenotype through
mechanisms such as enhanced proliferation and contractile force, corticosteroid resistance, and
increased expression of adhesion molecules that facilitate ASM interactions with immune cells
(52, 53) . Most of these cytokines were significantly increased in the BAL of DRA+O 3 mice
compared to O3 alone (Fig. 5). Type 2 cytokines IL-4 and IL-5 were also elevated in the BAL of
DRA and DRA+O3 exposed mice (Fig. 5 A, C) ; IL-4 directly promotes AHR in human bronchi
and hypercontractility in ASM cells (54), while IL-5 contributes indirectly to altered ASM function
through the recruitment of eosinophils, which can directly stimulate ASM contraction and increase
acetylcholine signaling from lung neurons, resulting in AHR (55, 56) . In the present study, IL-5
levels were higher in the 2-hit group compared to either exposure alone (Fig. 5C) , but eosinophil
numbers in the BAL were not different between DRA and DRA+O 3 groups (Fig. 4G) and were
reduced in the lung tissue of DRA+O 3 compared to DRA alone (11) . These data imply that
differences in eosinophilia do not explain the increased AHR following DRA+O3 compared to
DRA alone (11) at this time point.
Research examining ozone exacerbation of asthma in humans has been primarily
epidemiological and/or descriptive in nature, not necessarily mechanistic. However, our previous
study (11) recapitulates extensive human data demonstrating that short- term ozone exposure
increases risk of asthma exacerbations ( defined by lung function) for several days post-exposure
(57). H erein we also show that our model aligns with human studies reporting O 3 causes an
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increase in the number of airway immune cells, including macrophages and neutrophils (Fig. 4)
(7, 44). Our model uses a single O 3 exposure while asthmatic patients can experience sustained
exposure(s) over multiple days, which may affect the various inflammatory cells and signals
present in the lungs following O 3 inhalation. However, the cells and inflammatory mediators
necessary to exacerbate the functional AHR response to O3 were present and therefore this model
and time point prove meaningful in elucidating the cellular mechanisms of asthmatic AHR.
Another limitation of the present study was the number of cells required for pseudo-bulk
sequencing analysis. As such, there were insufficient cell numbers to examine transcriptional
changes in granulocytes, IMs, or structural cells such as ASM. Thus, future work will aim to
investigate the interactions between various granulocyte and macrophage populations with ASM
in the 2-hit model. Additionally, cell number requirements necessitated pooling of data from male
and female mice and limited the ability to determine whether any sex differences in transcriptional
changes following DRA and/or O 3 were present. However, sex -based BAL flow cytometry and
cytokine assessments can be found in the supplemental data (Fig. S4, S6).
In summary, asthma is responsible for over 1,300 deaths per day (1) and ~40% of
asthmatics in the US have had an acute exacerbation (“asthma attack”) in the past year (58) .
Furthermore, as climate change continues to worsen and ambient O 3 levels continue to rise (2),
vulnerable populations will become increasingly at risk of experiencing the deleterious
consequences on lung function. Therefore, expanding asthma research to focus on mechanisms of
non-allergen triggers of AHR, especially pervasive environmental pollutants such as O 3, is
essential to mitigating disease burden. The relationship between asthmatic AHR and
granulocyte/inflammatory cell presence in the airways is still being debated (59, 60), but t here is
a large body of work that points towards a central role for AMs in regulating this process (53).
Nevertheless, there is still a critical gap of knowledge regarding the direct interactions between
AMs and ASM cells. The results of the present study emphasize the significant role AMs play in
the response to inhaled O3 and emphasize the need for further research investigating the cross talk
between macrophage subpopulations and the structural cells responsible for AHR -mediated
bronchoconstriction.
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19
Acknowledgements
The authors would like to thank Dr. Rama Mallampalli, MD ( The Ohio State University,
Department of Internal Medicine) for generously allowing us to use their laboratory’s Meso Scale
Discovery plate imager and Daniela Farkas, BSc for her technical advice and assistance running
our samples.
Sources of Support
This w ork was funded by The Ohio State University College of Medicine Office of Research
Dean’s Discovery Program (MNB and JAE). This work was also supported by funding from the
National Heart, Lung, and Blood Institute (NHLBI) grants R01 HL155095 and R01 H L158532
(RDB) and National Cancer Institute grant P30 CA016058 (Genomics Shared Resource,
OSUCCC). The results herein are based upon data generated by the LungMAP Consortium and
downloaded from ( www.l ungmap.net ) on May 3, 2023. Th e LungMAP consortium and
the LungMAP Data Coordinating Center (U24-HL148865) are funded by NHLBI.
Disclosures
The authors declare no conflicts of interest.
Data availability statement
The raw sequencing data has been uploaded to the National Center for Biotechnology Information
Gene Expression Omnibus database (NCBI GEO), accession number [data deposition pending].
All other data will be made available upon request.
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20
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Figure 1. Identification of immune cell populations in the lungs of DRA+O 3 mice using single cell RNA
sequencing. As shown in (A), male and female C57BL/6 mice were intranasally sensitized and challenged with
triple allergen mixture (DRA) five times over 17 days; 24 hr after the last DRA administration (day 18), mice
were exposed to 2 ppm O 3 for 3 hr; 24 hr after O 3 (day 19) mice were sacrificed and tissues collected [image
created with BioRender.com]. Whole lung tissue was digested using collagenase followed by live cell enrichment
using FACS. Live cells were then processed for scRNA sequencing. (B) t-SNE overview of immune cell clusters
identified in all 4 treatment groups (control, DRA, O 3, DRA+O 3). Clusters were annotated using previously
validated marker genes. ( C) Dot plot showing the average expression level (color) and percentage of cells
expressing each gene (size) for the top 50 marker genes used in cluster identification. Dot plot showing expression
of the top 50 marker genes based on level (color) and percentage of cells (size) for each cluster identified.
was not certified by peer review) is the author/funder. All rights reserved. No reuse allowed without permission.
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Figure 2. scRNA sequencing of AMs. (A) t-SNE plot of all immune cell clusters identified in the lungs of control,
DRA, O3, and DRA+O3 mice, with AMs highlighted in orange . (B) t-SNE plot of AMs from all four groups ;
colors denote exposure(s) as indicated. (C) Volcano plots of differentially expressed genes (DEG) in AMs from
DRA, O3, or DRA+O3 exposed mice (respectively) compared to AMs from the control group. Each dot represents
one gene; “significant” defined as Log10(false discover rate [FDR]) |1.0|, genes meeting both criteria considered differentially expressed ( “relevant”
orange dots above horizontal significance dashed line and outside vertical relevance dashed lines). (D) Venn
diagram of the number of unique and overlapping DEG (upregulated only) in AMs from each treatment group
compared to controls. (E ) Heatmap displaying the top 50 DEGs in AMs from respective treatment groups
compared to controls. (F) Dot plot displaying transcriptional pathway enrichment analysis in AMs from respective
treatment groups compared to control AMs. The x-axis denotes respective pathway activation scores (z-score ≤ -
2 considered inhibited and ≥ 2 considered activated) and dot color corresponds to -log(p-value); -log(0.05) = 1.3,
was not certified by peer review) is the author/funder. All rights reserved. No reuse allowed without permission.
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therefore pathways with -log(p-value) ≤ 1.3 are considered non-significant, as indicated by grey dot color. The
dot size is proportionate to DEG overlap ratio [DEG in data set/total genes in pathway].
was not certified by peer review) is the author/funder. All rights reserved. No reuse allowed without permission.
The copyright holder for this preprint (whichthis version posted July 24, 2024. ; https://doi.org/10.1101/2024.07.23.604740doi: bioRxiv preprint
Figure 3. scRNA sequencing of monocytes present in the lungs of DRA, O 3, and DRA+O3 exposed mice. (A) t-
SNE plot of all immune cell clusters identified in the lungs of control , DRA, O 3, and DRA+O 3 mice, with
monocytes highlighted in orange. (B) t- SNE plot of monocytes from all four groups; colors denote exposure(s)
as indicated. (C) V olcano plots of differentially expressed genes (DEG) in monocytes from DRA, O3, or DRA+O3
exposed mice (respectively) compared to monocytes from the control group. Each dot represents one gene;
“significant” defined as Log10(false discover rate [FDR]) |1.0|, genes meeting both criteria considered differentially expressed (“relevant” red dots
above horizontal significance dashed line and outside vertical relevance dashed lines). ( D) Venn diagram of the
number of unique and overlapping DEG (upregulated only) in monocytes from each treatment group compared
to controls. (E) Heatmap displaying the top 50 DEGs in monocytes from respective treatment groups compared
to controls. (F) Dot plot displaying transcriptional pathway enrichment analysis in monocytes from respective
treatment groups compared to control monocytes. The x-axis denotes respective pathway activation scores (z-
was not certified by peer review) is the author/funder. All rights reserved. No reuse allowed without permission.
The copyright holder for this preprint (whichthis version posted July 24, 2024. ; https://doi.org/10.1101/2024.07.23.604740doi: bioRxiv preprint
score ≤ - 2 considered inhibited and ≥ 2 considered activated) and dot color corresponds to - log(p-value); -
log(0.05) = 1.3, therefore pathways with -log(p-value) ≤ 1.3 are considered non-significant, as indicated by grey
dot color. The dot size is proportionate to DEG overlap ratio [DEG in data set/total genes in pathway].
was not certified by peer review) is the author/funder. All rights reserved. No reuse allowed without permission.
The copyright holder for this preprint (whichthis version posted July 24, 2024. ; https://doi.org/10.1101/2024.07.23.604740doi: bioRxiv preprint
Figure 4. Airspace inflammatory cells in DRA, O 3, and DRA+O 3 exposed mice. DRA triple allergen
administration and O3 exposure was performed in male and female C57BL/6 mice as previously described (Figure
1A). Bronchoalveolar lavage (BAL) was performed and cells within the airspaces collected for ( A) total cell
counts, and flow cytometry used to determine (B) frequency and (C-K) total number of immune cell populations
in the BAL. n = 9-13; *p < .05, **p < .01, ***p < .001 as indicated; statistical significance analyzed using one -
way ANOV A followed by Tukey’s post hoc testing. Data in panels A and C presented as mean ± SEM , data in
panel B presented as mean only. AM, alveolar macrophage; TR, tissue -resident; Mo, monocyte -derived; AM,
alveolar macrophage; IM, interstitial macrophage; DC, dendritic cell.
was not certified by peer review) is the author/funder. All rights reserved. No reuse allowed without permission.
The copyright holder for this preprint (whichthis version posted July 24, 2024. ; https://doi.org/10.1101/2024.07.23.604740doi: bioRxiv preprint
Figure 5. Airspace cytokine levels in DRA, O3, and DRA+O 3 exposed mice. As shown in Figure 1A , male and
female mice were intranasally sensitized and challenged with triple allergen mixture (DRA) five times over 17
days; 24 hr after the last DRA administration, mice were exposed to 2 ppm O3 for 3 hr; 24 hr after O3 concentrated
bronchoalveolar lavage fluid (BALF) was collected for airspace measurement of cytokines and chemokines. All
data presented as mean ± SEM ; n = 9-10; *p < .05, **p < .01, ***p < .001 as indicated; statistical significance
analyzed using one-way ANOV A followed by Tukey’s post hoc testing.
was not certified by peer review) is the author/funder. All rights reserved. No reuse allowed without permission.
The copyright holder for this preprint (whichthis version posted July 24, 2024. ; https://doi.org/10.1101/2024.07.23.604740doi: bioRxiv preprint
Figure 6. Evaluation of AM and monocyte sub populations unique to DRA+O 3 exposure. (A) t -SNE plot
displaying AMs from all 4 exposures (Figure 2B); colors denote unique transcriptional groups manually defined
for differential expression analysis. Group “A” is predominantly AMs from DRA+O3, “B” is comprised of AMs
from DRA and DRA+O3 groups, and “C” contains AMs from all 4 exposures but dominated by control and O3
alone. (B-D) Canonical pathway enrichment analysis (IPA software) of DEGs between AM groups, as indicated.
(C) t-SNE plot displaying monocytes from all 4 exposure groups (Figure 3B); colors denote unique transcriptional
groups manually defined for differential expression analysis. Group “A” contains monocytes exclusively from
the DRA+O3 exposure paradigm, and group “B” is a mixture of cells from all 4 exposures. (F) Canonical pathway
enrichment analysis (IPA software) of DEGs between monocyte groups “D” and “E”. (G) Machine Learning
Disease Pathways based on DEGs between AM or monocyte groups, as indicated. For all dot plots the x-axis
denotes respective pathway activation scores (z-score ≤ -2 considered inhibited and ≥ 2 considered activated) and
dot color corresponds to -log(p-value) ; -log(0.05) = 1.3, therefore pathways with -log(p- value) ≤ 1.3 are
considered non-significant, as indicated by grey dot color. The dot size is proportionate to DEG overlap ratio
[DEG in data set/total genes in pathway].
was not certified by peer review) is the author/funder. All rights reserved. No reuse allowed without permission.
The copyright holder for this preprint (whichthis version posted July 24, 2024. ; https://doi.org/10.1101/2024.07.23.604740doi: bioRxiv preprint
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