Next Article in Journal
Degradation of Ciprofloxacin in Water by Magnetic-Graphene-Oxide-Activated Peroxymonosulfate
Previous Article in Journal
Metals in Cow Milk and Soy Beverages: Is There a Concern?
Previous Article in Special Issue
Impacts of Indoor Dust Exposure on Human Colonic Cell Viability, Cytotoxicity and Apoptosis
 
 
Font Type:
Arial Georgia Verdana
Font Size:
Aa Aa Aa
Line Spacing:
Column Width:
Background:
Review

Methylomic, Proteomic, and Metabolomic Correlates of Traffic-Related Air Pollution in the Context of Cardiorespiratory Health: A Systematic Review, Pathway Analysis, and Network Analysis

by
Cameron Casella
1,
Frances Kiles
1,
Catherine Urquhart
1,
Dominique S. Michaud
1,
Kipruto Kirwa
1,2 and
Laura Corlin
1,3,*
1
Department of Public Health and Community Medicine, Tufts University School of Medicine, Boston, MA 02111, USA
2
Department of Environmental Health, Boston University School of Public Health, Boston, MA 02118, USA
3
Department of Civil and Environmental Engineering, Tufts University School of Engineering, Medford, MA 02155, USA
*
Author to whom correspondence should be addressed.
Toxics 2023, 11(12), 1014; https://doi.org/10.3390/toxics11121014
Submission received: 3 October 2023 / Revised: 18 November 2023 / Accepted: 6 December 2023 / Published: 12 December 2023
(This article belongs to the Special Issue Long-Term PM2.5 Exposure and Cardiometabolic Health Effects)

Abstract

:
A growing body of literature has attempted to characterize how traffic-related air pollution (TRAP) affects molecular and subclinical biological processes in ways that could lead to cardiorespiratory disease. To provide a streamlined synthesis of what is known about the multiple mechanisms through which TRAP could lead to cardiorespiratory pathology, we conducted a systematic review of the epidemiological literature relating TRAP exposure to methylomic, proteomic, and metabolomic biomarkers in adult populations. Using the 139 papers that met our inclusion criteria, we identified the omic biomarkers significantly associated with short- or long-term TRAP and used these biomarkers to conduct pathway and network analyses. We considered the evidence for TRAP-related associations with biological pathways involving lipid metabolism, cellular energy production, amino acid metabolism, inflammation and immunity, coagulation, endothelial function, and oxidative stress. Our analysis suggests that an integrated multi-omics approach may provide critical new insights into the ways TRAP could lead to adverse clinical outcomes. We advocate for efforts to build a more unified approach for characterizing the dynamic and complex biological processes linking TRAP exposure and subclinical and clinical disease and highlight contemporary challenges and opportunities associated with such efforts.

1. Introduction

It is well established that exposure to traffic-related air pollution (TRAP) is associated with adverse respiratory and cardiovascular outcomes [1,2,3]. Research suggests that the pathways underlying associations between TRAP exposure and cardiorespiratory outcomes likely involve oxidative stress, endothelial dysfunction, and inflammatory responses [1,4,5,6,7,8,9]. A growing number of epidemiological studies are investigating how changes in DNA methylation patterns (methylomics), proteomic profiles, and metabolomic profiles underlie the physiological pathways linking TRAP exposure to respiratory and cardiovascular health (e.g., [10,11,12,13,14,15]). Nevertheless, no large-scale longitudinal study to date has identified common biological pathways involving TRAP-related methylomic, proteomic, and metabolomic patterns. Such evidence could help establish a unified multi-omics framework to gain a better understanding of the adverse health consequences of air pollutants. Furthermore, this knowledge could be used to help design relevant interventions.
Previous work has outlined many of the challenges of establishing a unified multi-omics approach to air pollution epidemiology. Common challenges include the need for repeated samples, the identification of an appropriate exposure metric, and the availability of appropriate statistical techniques to handle the large number of omics analytes [16,17,18,19,20]. Furthermore, challenges related to heterogeneity in study designs, populations, air pollutants of interest, exposure windows, omics measurement methods, and analytic techniques arise when synthesizing the literature [10,11,20,21,22,23]. Despite these challenges, multi-omics integration (i.e., integrating across multiple levels of biology such as methylation patterns, proteomic profiles, and metabolomic profiles) aimed at understanding mechanisms linking environmental risk factors to chronic disease can advance clinical and public health knowledge and inform the design and implementation of relevant interventions [24,25,26]. To advance the goal of developing an integrated multi-omics approach, we conducted the first systematic review focused on the associations between three types of omic markers and ambient TRAP exposure. Using these signals from across omics types, we aimed to pinpoint common biological pathways known to be involved in respiratory and cardiovascular disease (CVD), assess the challenges and benefits of a multi-omics approach, and identify research needs. The number of studies directly linking TRAP exposure to clinical outcomes through changes in omics signals is relatively small. Despite this, we believe that identifying omics signals and pathways known to be associated with both TRAP exposure and cardiorespiratory disease is a prudent step toward advancing clinical and public health decision-making.

2. Materials and Methods

2.1. Search Strategy and Study Selection

We searched Embase and PubMed for English-language epidemiologic articles published between January 2010 and February 2023 that reported on the association between TRAP exposure and one or more of three omics types (DNA methylation [methylomics], proteomics, and metabolomics). We included both studies that examined at least one targeted biomarker in association with TRAP (some of which were not truly ‘omics’ approaches given the small number of biomarkers assayed), as well as studies that assessed a large number of omic markers through an untargeted approach. Given the rapid expansion of the omics field, 2010 was chosen as a date that could capture the important recent developments in technology and understanding. Indeed, metabolomics was considered an “emerging field” up until 2010, top-down proteomics was not widely used until 2011 [27], and methylation research had just benefited from landmark technological developments in the form of upgraded methylation arrays. For example, the Illumina Infinium Methylation 450 K array was released in 2011 and represented a leap forward compared to the previous model (450,000 versus 27,000 CpG sites) [28]. Additionally, foundational databases that annotate genes, proteins, and metabolites, such as KEGG and UniProt, underwent major changes post-2010 and continue to update their knowledge banks routinely [29]. Furthermore, although pathway analysis tools such as Reactome and NIH-DAVID were released in 2003, the addition of the open-source platform MetaboAnalyst in 2009 allowed researchers to gain more insight from their omics data without significant training [30]. Search terms included DNA methylation, proteomics, metabolomics, TRAP, and particulate matter (PM). The search strategy and screening process are described in detail in Supplementary File S1. We screened the extracted articles by title and abstract. We excluded reviews and reports, as well as in vitro, in silico, ex vivo, and animal studies. We excluded articles not containing one or more TRAP exposures. Relevant pollutants included particulate matter < 2.5 microns (PM2.5), particulate matter < 10 microns (PM10), PM constituents, ultrafine particulate matter (UFP), black carbon (BC), elemental carbon (EC), organic carbon (OC), nitrogen dioxide (NO2), nitrogen oxides (NOx), carbon monoxide (CO), sulfur dioxide (SO2), sulfate (SO42−), ozone (O3), diesel exhaust (DE), and polycyclic aromatic hydrocarbons (PAHs). Some studies that examined high versus low traffic scenarios did not specify individual pollutants but rather called the pollution mixture “TRAP”. Such pollutant mixtures have been called “TRAP” throughout this review. Studies containing TRAP without further specification were either (1) traffic-specific and focused on pollutants originating directly from traffic or commuter exposures, or (2) levels of ambient pollutants typically associated with traffic. We excluded studies that identified the source of air pollution as anything other than traffic-related (e.g., we excluded occupational exposures); however, we did not require source apportionment, nor did we comment on whether ambient pollution is necessarily due to TRAP. Studies focused on people who were pregnant or under 18 years of age were also excluded. The focus of this review was to capture the available literature regarding adult exposure to TRAP, given the importance of examining these sub populations separately and the likelihood of different physiological responses to TRAP in terms of disease risks [31]. In addition to the 115 articles that remained after screening, we identified 24 papers through expert knowledge, for a total of 139 unique studies. There were 54 methylomic, 57 proteomic, 37 metabolomic, and 9 overlapping studies—four of which included both proteomics and metabolomics and five that included both proteomics and methylation (Figure 1).

2.2. Data Extraction and Organization

We extracted the following from each article: study design and sample size, air pollution exposure methods, exposure metrics, omics assay methods, participant demographics, statistical methods, and results (Table 1 and Supplementary File S2 Tables S1–S3). Statistically significant associations between different TRAP exposures and each omics article type (methylomic, proteomic, and metabolomic) were identified (Supplementary File S2, Tables S4–S6). We used statistical significance thresholds determined by the original authors, which included both adjusted and non-adjusted p-values. The specific statistical thresholds used in each study to determine the significance of association among TRAP and various omics signals are given in Supplementary File S2, Tables S1–S3. Air pollution exposures were split by pollutant type and averaging period (short-term: ≤30 days; long-term: >30 days).
Using the significant associations shown in Supplementary File S2 Tables S4–S6, we identified common biological processes and types of biomarkers represented across the omics types (an abbreviated version of results shown in Table S7 and full results shown in Supplementary File S2 Table S8). Gene Ontology (GO) molecular functions (molecular-level activities performed by gene products, e.g., glucose transmembrane transport) were extracted for each gene and protein [32]. Where available, Kyoto Encyclopedia of Genes and Genomes (KEGG) pathways (pathways of common molecular interaction, e.g., tumor necrosis factor signaling) were indicated for all genes, proteins, and metabolites [29,33,34]. For genes and proteins without KEGG data, GO biological processes (functions of gene products) were used instead. The neXtProt knowledgebase [35] was used to extract GO molecular functions, GO biological processes, and KEGG pathways for all genes and proteins. The GenomeNet KEGG COMPOUND Database [36] was used to extract KEGG functions for all available metabolite markers. To integrate omics signals in terms of their biological function (regardless of the omics approaches that were used or not in the original literature), we categorized each biomarker and their assigned biological functions (both KEGG and GO) to create a list of all biological functions that could be involved in respiratory and CVD processes. Within these lists, we identified methylomic, proteomic, and metabolomic signals involved in particular pathways. Based on this analysis, the analyses described in Section 2.3 below, and the relevant literature, we theorized about possible interactions among these markers that may affect disease states. Based on Supplementary File S2 Tables S4–S8, we created a simplified conceptual diagram of the putative relationships among TRAP, omics signals, subclinical processes, and clinical outcomes (Figure 2).

2.3. Pathway and Network Analyses

We conducted bioinformatics analyses synthesizing the results across the omics studies using the lists of relevant biomarkers shown in Supplementary File S2 Table S9 (representing all significant associations shown in Supplementary File S2 Tables S4–S6). We included all biomarkers identified as significantly associated, even if individual studies chose different statistical significance thresholds (reflecting in part differences in omic assay approaches, the number of biomarkers assessed, and study-specific analytic approaches). This reflects the individual study authors’ decisions about which biomarkers were most salient given the methodological characteristics of the study and allows us to be most comprehensive in including a large set of possible biomarkers. We used the open-source tools Reactome (Version 85) [37] and MetaboAnalyst 5.0 [38] to conduct pathway analyses. Specifically, we used Reactome to perform overrepresentation pathway analyses on the gene methylation sites and proteins that were significantly associated with TRAP exposure (separately for each omic type and associations with short- and long-term TRAP exposures). We chose Reactome because it allows for pathway analysis with methylation markers and proteins, its strength in providing visualization of salient pathways, and its clear cross-linkages to other databases. For our Reactome analysis, relevant parameters selected to perform these analyses included “project to human” and “include interactors,” limiting the results to human genes and proteins, and drawing from the IntAct database to increase the analysis background, respectively. MetaboAnalyst was used to conduct a KEGG pathway analysis of all metabolites that were significantly associated with TRAP (separately for short- and long-term exposures) since this software is commonly used with metabolites and provides additional analytic features. Relevant parameters selected included a hypergeometric test for enrichment analysis and relative betweenness centrality topology analysis. These programs generate lists of pathways indicated by the extracted analytes. Some pathways discussed in this review were not on the indicated lists of these pathway analyses, and therefore statistical significance values were not given. Given that we extracted the KEGG functions and/or GO data for each analyte, we were able to group omics signals effectively, despite pathway analysis-related statistical thresholds that may be limiting in representing all biological pathways involved in TRAP exposure.
MetaboAnalyst was also used to conduct four KEGG network analyses representing the functional relationships among biomarkers. We created two networks incorporating methylation markers and metabolites that were significantly associated with short- and long-term TRAP exposure (Figure 3 and Figure 4) and two networks incorporating proteins and metabolites that were significantly associated with short- and long-term TRAP exposure (Figure 5 and Figure 6). In each case, we used separate networks for short- and long-term exposures. In network analyses, networks are parameterized by degree (i.e., the number of incoming/outgoing edges on each node) and betweenness (i.e., the number of shortest paths between each pair of nodes). Higher values for degree and betweenness restrict the network to only the most highly connected and relevant nodes [39,40]. For our two short-term network analyses, degree and betweenness filters were constrained to a degree of at least three. In the long-term exposure analyses, networks did not contain enough nodes to apply these filters. This is due to the relative sparsity of literature examining associations between long-term exposures and omics signals.
Table 1. Overview of the literature.
Table 1. Overview of the literature.
Omics TypeStudy DesignExposure AssessmentExposure WindowStudy Populations aCountrySample SizeSex DistributionOmics Approach
Methylomics
n = 54 studies
Cross-sectional: 29
Panel: 9
Cohort: 5
Cross-over: 9
Quasi-experimental: 2
Fixed site measurement: 16
Spatiotemporal model: 21
Personal measurement: 12
Controlled exposure: 5
Short-term: 29
Long-term: 25
NAS: 10 [41,42,43,44,45,46,47,48,49,50]
KORA: 3 [45,49,51]
WHI: 3 [52,53,54]
ARIC: 3 [52,53,54]
EPIC-Italy: 2 [55,56]
MESA: 2 [57,58]
Sister Study: 2 [59,60]
BAPE: 2 [61,62]
Taiwan Biobank: 2 [63,64]
REGICOR: 1 [55]
EPIC-Netherlands: 1 [56]
Lifelines: 1 [51]
EXPOsOMICS: 1 [65]
SAPALDIA: 1 [66]
Lothian Birth Cohort: 1 [67]
SPHERE: 1 [68]
USA: 17
China: 15
Italy: 8
Canada: 4
Netherlands: 3
Taiwan: 3
Germany: 2
Switzerland: 2
UK: 2
Belgium: 2
Spain: 1
South Korea: 1
Czech Republic: 1
<50: 20
50–99: 3
100–1000: 20
>1000: 11
100% female: 4
100% male: 11
Other: 39
Candidate gene: 26
Epigenome-wide association study: 24
Global methylation: 4
Proteomics
n = 57 studies
Cross-sectional: 28
Panel: 8
Cohort: 3
Cross-over: 10
Quasi-experimental: Case-control: 3
Fixed site measurement: 24
Spatiotemporal mode: 19
Personal measurement: 9
Biomarker: 2
Controlled exposure: 4
Short-term: 36
Long-term: 21
NAS: 3 [69,70,71]
SWAN: 3 [72,73,74]
KORA: 3 [75,76,77]
Heinz–Nixdorf Recall: 3 [75,78,79]
Framingham Offspring: 2 [80,81]
AIRCHD: 2 [82,83]
EPIC-Italy: 1 [84]
BPRHS: 1 [85]
Malmo Diet and Cancer: 1 [86]
AHAB-II: 1 [87]
SAGE: 1 [88]
Nurse’s Health Study: 1 [89]
ELISABET: 1 [90]
ESCAPE: 1 [91]
SAPALDIA: 1 [75]
FINRISK: 1 [75]
TwinGene: 1 [75]
MESA: 1 [92]
CAFEH: 1 [93]
CoLaus: 1 [94]
USA: 17
China: 17
Canada: 6
Germany: 4
India: 3
Taiwan: 3
Italy: 2
Sweden: 1
UK: 1
France: 1
Brazil: 1
Sweden: 1
Finland: 1
Switzerland: 1
<50: 15
50–99: 10
100–1000: 13
>1000: 19
100% female: 3
100% male: 6
Other: 48
Targeted: 54
Untargeted: 3
Metabolomics
n = 37 studies
Cross-sectional: 15
Panel: 7
Cohort: 2
Cross-over: 7
Natural Experiment: 1
Fixed site measurement: 8
Spatiotemporal model: 10
Personal measurement: 14
Biomarker: 1
Controlled exposure: 4
Short-term: 26
Long-term: 11
DRIVE: 3 [95,96,97]
NAS: 2 [98,99]
Children’s Health Study: 2 [100,101]
KORA: 2 [102,103]
SAPALDIA: 1 [104]
EPIC-Italy: 1 [104]
ACE: 1 [105]
ACE-2: 1 [106]
Oxford St. 2: 1 [13]
TAPAS II: 1 [13]
CAFEH: 1 [107]
EARTH: 1 [108]
AIRCHD: 1 [83]
SCOPE: 1 [109]
TwinsUK: 1 [110]
USA: 17
China: 12
Germany: 2
UK: 2
Sweden: 1
Switzerland: 1
Italy: 1
India: 1
Spain: 1
Netherlands: 1
Brazil: 1
<50: 15
50–99: 6
100–1000: 7
>1000: 4
100% female: 1
100% male: 5
Other: 31
Targeted: 8
Untargeted: 29
a Numbers represent the number of papers reviewed that contain the given characteristic. Where the original study included multiple study populations, all study populations and countries were counted. Abbreviations: ACE—Atlanta Commuters Exposure; AHAB-II—Adult Health and Behavior; AIRCHD—Air Pollution and Cardiovascular Dysfunctions in Healthy Adults Living in Beijing: ARIC—Atherosclerosis Risk in Communities; BPRHS—Boston Puerto Rican Health Study; CAFEH—Community Assessment of Freeway Exposure and Health; DRIVE—Dorm Room Inhalation to Vehicle Emissions; EARTH—Environmental and Reproductive Health; ELISABET—Enquête Littoral Souffle Air Biologie Environnement; EPIC—European Prospective Investigation into Cancer and Nutrition; ESCAPE—European Study of Cohorts for Air Pollution Effects; KORA—Cooperative Health Research in the Region of Augsburg; MESA—Multiethnic Study of Atherosclerosis; NAS—Normative Aging Study: REGICOR—REgistre GIroní del COR; SAGE—Study on Global Aging and Adult Health; SAPALDIA—Swiss Study on Air Pollution and Lung Disease in Adults; SCOPE—A Prospective Study Comparing the Cardiometabolic and Respiratory Effects of Air Pollution Exposure on Healthy and Prediabetic Individuals; SPHERE—Susceptibility to Particle Health Effects, miRNA and Exosomes; SWAN—Study of Women’s Health Across the Nation; TAPAS—Transportation, Air Pollution, and Physical Activities; WHI—Women’s Health Initiative.

3. Results and Discussion

3.1. Overview of the Literature

Table 1 provides an overview of the study designs, exposure assessment approaches, study populations, sample sizes, sex distributions, and omics approaches used in the studies included in this review.
We did not conduct a formal analysis of study quality for two primary reasons. First, for our hypothesis-generating study, our goal was to be as comprehensive as possible in identifying biomarkers and biological processes putatively important to the relationship between air pollution and respiratory disease and/or CVD. Second, given that the omics field is relatively new and is rapidly evolving, the common study quality assessment criteria ‘checklists’ would not be appropriate for the types of studies we included in our review. Some elements—such as study design, sample size, adjustment for confounders, exposure assessment methods, etc.—were elements we considered and discussed below. However, we suggest that, moving forward as a field, the assessment of multi-omics studies requires study quality evaluation criteria. Some work has already been published to this effect (e.g., [111]), but a more general guideline is warranted. Relevant considerations could include whether the study was targeted or untargeted, assay technology and process (e.g., assay size, laboratory quality checks), relevance of the biological matrix used, and appropriateness of the bioinformatics approaches.

3.1.1. TRAP Exposure Assessment

Exposure assessment approaches differed by omics type: spatiotemporal modeling was most common for methylomic papers, fixed site monitoring was most common for proteomics papers, and personal monitoring was most common for metabolomics papers (Table 1). Short-term exposures were more commonly assessed than long-term exposures for each omic type. For long-term exposures, the most common exposure window was an annual average (44, 28, and 22% of methylomic, proteomic, and metabolomic studies, respectively). As in air pollution epidemiology generally, each exposure assessment approach and exposure window have strengths and weaknesses in the context of different study designs; a potential benefit of a multi-omics approach is the enhanced reliability of knowledge obtained from triangulating findings from studies that employ the diverse combinations of exposure assessment techniques and windows.
The most common pollutant studied across all three omics (regardless of exposure window) was PM2.5. Forty-six methylation papers, 41 proteomics papers, and 32 metabolomics papers measured PM2.5 exposure. PM10, UFP, BC, NO2, NOx, and O3 were all considered in each omic type; however, they were less commonly studied in papers focused on long-term exposures. Papers that did not investigate PM2.5 generally focused on O3 or diesel exhaust. Given the study designs and exposure assessment methods, time-varying exposures and TRAP mixtures were generally not accounted for in the analyses; future studies should consider time-varying exposures and mixtures.

3.1.2. Study Populations

Research in this field predominantly draws from populations in North America, China, and Western Europe (Table 1); future studies should include more geographic diversity, requiring an investment in TRAP exposure and omics assessment in other geographic regions. Additionally, although most study populations included people regardless of sex, single-sex cohorts were common (especially for methylomic papers, where 28% were single-sex). Three methylomic, two proteomic, and four metabolomic papers considered effect modification by sex [45,57,67,86,101,102,112,113,114] (Supplementary File S2, Tables S1–S3). Fourteen methylomic, 16 proteomic, and 21 metabolomic studies contained populations with a mean age or entire age range of 35 years old or younger. Twenty-three methylomic, nine proteomic, and four metabolomic studies contained populations with a mean age or entire age range of 60 years or older. In general, the methylomic literature had slightly older participants, and the metabolomics literature had slightly younger participants. However, there was adequate representation of all ages throughout all three omics types. Most studies included healthy participants or did not specify health conditions as criteria for eligibility.

3.1.3. Biological Matrices

Methylomic, proteomic, and metabolomic markers were assessed using a variety of biological matrices (Supplementary File S2 Tables S1–S3). Leukocytes and whole blood were the most common biological matrices for methylomic papers (27 and 17 papers, respectively). All studies adjusted for cell composition except those exclusively using CD4+ helper cells or buccal cells as the matrix of interest or those using paired samples with a short lag time [115,116,117,118,119,120]. Methylation data can readily be obtained from blood samples. It is shown that blood methylation levels correlate with methylation levels in other tissues and relate to external exposures [121]. Given that leukocytes are derived from whole blood, these biological matrices are equivalent. Peripheral blood mononuclear cells (PBMCs), however, are a specific subset of leukocytes. The choice to utilize PBMCs or leukocytes in methylomic research depends on research goals and the cell type of interest; however, both are sufficient [122,123]. For proteomic papers, serum and plasma were the most common biological matrices (34 and 21 papers, respectively). Nine proteomics papers used both serum and plasma, with the inclusion of plasma serving primarily to measure fibrinogen levels [71,72,75,81,92,124,125,126,127]. Three proteomics papers used bronchoalveolar lavage fluid to understand the associations between TRAP and the bronchoalveolar proteome, serving as a more direct measure of TRAP’s influence [128,129,130]. Both serum and plasma matrices in proteomics research are well-accepted; however, some studies suggest that plasma has superior predictive power for physiological outcomes [131], while others suggest that serum is preferred for clinical chemistry [132]. Plasma is used over serum for the exploration of coagulation proteins; however, the presence of added anticoagulants in plasma can influence research outcomes [132]. Similar to proteomics, serum and plasma were the most common biological matrices for metabolomics papers (17 and 14 papers, respectively). Serum is currently considered the gold standard in metabolomics research, providing more sensitive results in biomarker detection; however, plasma also provides accurate results and has high reproducibility [133,134]. Five metabolomics papers utilized urine [101,135,136,137,138] and two used bronchoalveolar lavage fluid [139,140].
In general, decisions about the biological matrix were largely determined based on the availability of samples within a cohort rather than on the biological relevance of a given matrix for TRAP-cardiorespiratory relationships. Although other matrices (e.g., myocytes, bronchiolar cells, endothelial cells, etc.) may serve as a more direct source of omics signals, they are often inaccessible and/or invasive to procure [141,142]. Additionally, none of the studies explicitly considered biomarker interactions (e.g., protein–protein or protein–metabolite) or the possibility of biomarker degradation or metabolism (e.g., considering how TRAP exposure may only affect biomarker levels over a specific temporal window) [141,143,144,145]. Finally, without the ability to obtain repeated measures of multiple omics types within individuals over relevant periods, it is not possible to directly assess putative relationships between TRAP exposure and cascading biological processes. That is, although we can view the associations among multiple omics layers and pollutants across similar short- and long-term exposure windows, we do not have a direct means to measure the exact temporal changes in methylomic, proteomic, and metabolomic makers occurring at consistent points post-exposure.

3.1.4. Omics Assessment

In the methylomics literature, multiple high-throughput approaches and bioinformatics technologies were used (Supplementary File S2, Table S1). The most common forms of methylation quantification were methylation arrays (37 papers) and bisulfite polymerase chain reaction (PCR) sequencing (13 papers). The PCR sequencing papers focused on candidate gene approaches (primarily for inflammatory and immune-related proteins, as well as genes related to circadian rhythm and epigenetic age) [41,50,118,119,120,125,146,147,148,149,150,151,152]. Analyses using arrays took advantage of the evolving technology to capture the most comprehensive set of biomarkers possible: one paper utilized a 385 K array [46], twenty-four utilized a 450 K array [42,43,44,45,47,48,49,51,52,53,54,55,56,57,58,59,60,65,66,67,153,154,155,156], and twelve utilized an 850 K array [61,62,63,64,116,117,157,158,159,160,161,162]. Although we recommend the use of the most comprehensive technology available, the contribution of groundbreaking studies using older arrays to the current body of knowledge should not be understated [163,164]. Similarly, for the bioinformatics analyses of the methylomics results, researchers took advantage of the rapidly evolving tools such as KEGG for pathway analysis [42,46,116,140,160,161], the National Institutes of Health Databases for Annotation, Visualization, and Integrated Discovery (NIH-DAVID) [42,56,65,155,156], Ingenuity Pathway Analysis (IPA) [43,66,130,153,157,165], Mummichog [14,95,96,97,104,105,106,107,108,166,167], and MetaboAnalyst [98,99,100,102,136,168,169,170,171].
Compared to the methylomics literature, there was homogeneity in approaches used across the proteomics literature (Supplementary File S2, Table S2). Only three of the fifty-seven proteomics papers used untargeted omics approaches (and therefore, the use of bioinformatics approaches for analysis was limited to relatively few studies) [130,138,165]. Instead, many studies assessed the concentration of approximately 20 targeted proteins (e.g., cytokines, chemokines, and other immune/inflammatory-related markers). This led to abundant data on the associations among TRAP and the concentration of key proteins related to inflammation and immunity, and therefore cardiorespiratory disease. The proteins represented often overlapped well with the proteins encoded by candidate genes targeted in methylation studies. While this is useful for multi-omics interpretation, the relative lack of untargeted analyses may limit our understanding of the complete proteomic response to TRAP and potentially bias our analyses by over-representing certain processes already considered important in cardiorespiratory disease. Furthermore, it can make it difficult to integrate methylomic, proteomic, and metabolomic results together.
In contrast to the proteomics literature, most (28/37) of the metabolomics papers used untargeted approaches and twenty-two incorporated bioinformatics approaches for the interpretation of results (e.g., eleven used Mummichog [14,95,96,97,104,105,106,107,108,166,167] and nine used MetaboAnalyst [98,99,100,102,136,168,169,170,171]; Supplementary File S2, Table S3). Specific to metabolomics is the challenge of metabolite identification. Fourteen of the thirty-seven metabolomics papers had level one confidence (the highest level of confidence confirmed by the reference standard) [83,97,100,103,104,105,108,109,110,113,139,166,171,172], whereas an additional six studies contained some level one matches mixed with lower confidence findings [13,96,106,107,167,173]. Thirteen studies had level two confidence, primarily confirmed by library spectrum match [14,99,102,119,135,136,138,140,168,169,170,174,175]. Only two studies did not contain metabolites with level two or greater confidence [99,101]. The variation in metabolite identification confidence reflects a level of uncertainty in the metabolomics signals observed across different studies [176,177].

3.2. Omics Markers and Associated Biological Pathways

Omics markers representing biological pathways related to lipid metabolism, cellular energy production, amino acid metabolism, inflammation and immunity, coagulation, endothelial function, and oxidative stress were present across the literature. In this section, we outline trends in common biological pathways and molecular functions associated with methylomic, proteomic, and metabolomic markers of TRAP exposure, along with the hypothesized connections to cardiorespiratory disease. Not all omics markers may be related to clinical outcomes, and further research is needed to identify the most critical pathways underlying the relationship between TRAP exposure and disease. Figure 2 shows a simplified diagram of the relationships. The supporting literature is summarized in Supplementary File S2, Tables S4–S8. Throughout this section, ‘TRAP’ refers to the air pollutant mixture (or studies in which individual pollutants are not specified). We also identified individual pollutants in all cases where the original researchers did. For the pathway and network analyses, we combined all results regardless of the specific pollutant and thus used the more general ‘TRAP’.
Table S7 synthesizes the methylomic, proteomic, and metabolomic literature together. The table is organized by KEGG pathway and only includes those pathways most represented and explored in the literature: lipid metabolism, cellular energy production, amino acid metabolism, inflammation and immunity, coagulation, endothelial function, and oxidative stress. Within each KEGG pathway, all methylomic, proteomic, and metabolic markers significantly associated with short- and/or long-term TRAP are noted. Each omics type was separated into associations for short- and long-term exposure. Details are given in the following sections.

3.2.1. Lipid Metabolism

Phospholipids, sphingolipids, and acylcarnitines were represented throughout the metabolomics literature. However, no studies explored the associations between TRAP and methylomic or proteomic markers related to lipid metabolism (Supplementary File S2, Tables S6–S8). In the metabolomics literature, both short- and long-term PM2.5 exposures were negatively associated with phospholipid levels [25,26,27,28,29]. In contrast, short-term UFP, NO2, and O3 were consistently and positively associated with levels of phospholipids [98,103,140]. Phospholipid metabolism is essential for normal cellular function as it is involved in generating biological membranes and plays an important role in cellular signaling processing in nearly all tissues [178]. Phospholipid imbalances are implicated in neurological disorders and neurodegenerative diseases, while damaged and oxidized phospholipids are associated with atherosclerosis and CVD (Figure 2) [179,180]. It is not understood exactly how TRAP associations with phospholipid metabolites contribute to the aforementioned diseases.
Sphingolipids, such as sphingosines and some sphingomyelins, were negatively associated with short- and long-term PM2.5 as well as with short-term UFP [98,101,171] but were positively associated with short-term O3 and Ni [98,101,140,181]. For example, sphingosine 1-phosphate (a known risk factor for coronary artery disease (CAD)) [182] was negatively associated with short-term UFP and positively associated with short-term Ni [98]. Additionally, ceramide (a reaction product of sphingomyelin and/or sphingosine that is elevated in patients with hypertension, angina pectoris, myocardial infarction, and stroke [183,184,185]) was negatively associated with short-term PM2.5 and UFP exposure [98,171]. However, eight sphingomyelins were positively associated with long-term PM2.5 and short-term O3 [98,140]. Given these findings, it is possible that TRAP (and particularly the PM components) may not predominately work through pathways involving sphingolipids to affect CVD. However, future studies should confirm this hypothesis and also consider whether methylation patterns or proteins related to lipid metabolism are implicated.
In contrast to the trends with sphingolipids, acylcarnitines were positively associated with short-term TRAP and negatively associated with short-term NO2 [13,98,114,138,168,173,175]. It has been shown that higher levels of medium- and long-chain acylcarnitines are positively associated with both CVD and the risk of cardiovascular death in patients with stable angina pectoris [186,187,188].
Although most markers of lipid metabolism were considered only in the metabolomics literature, arachidonic acid and linoleic acid metabolism KEGG pathways were considered in both the proteomics (one protein involved in each) and metabolomics (20 and 13 metabolites, respectively) literature (Table S7). Synthesizing the results from these studies, our MetaboAnalyst pathway analyses suggested that the arachidonic acid metabolism KEGG pathway was significantly enriched by metabolites associated with both short- and long-term TRAP exposure (p = 4.29 × 10−4 and p = 0.01, respectively). Specifically, exposure to short-term diesel exhaust was associated with higher concentrations of the protein arachidonate 15-lipoxygenase (ALOX15). This enzyme helps generate bioactive lipid molecules, such as eicosanoids, hepoxilins, and lipoxins [189]. Interestingly, short-term diesel exhaust was also associated with lower levels of multiple metabolites related to ALOX15 [130,139]. The metabolomics literature also considered other components of the arachidonic acid and linoleic acid metabolism pathways. For example, short-term PM2.5 and diesel exhaust exposure were associated with higher and lower levels of eicosanoids, respectively [109,139]. These signaling lipids regulate homeostatic and inflammatory processes, making them important markers in the progression of CVD [189,190]. Additionally, short-term PM2.5 and other TRAP exposures were associated with higher levels of thromboxane, prostaglandin, and leukotriene metabolites [101,139,167,168,172]. These metabolites are associated with modifications of the immune and inflammatory responses and help mediate leukocyte accumulation [191]. Finally, short-term PM2.5, NO2, and other short-term TRAP exposures, as well as long-term PM2.5 and NO2, were associated with higher levels of metabolites involved in linoleic acid metabolism [102,103,139,167,168,170]. Dysregulated linoleic acid metabolism is traditionally considered pro-inflammatory and pathological, but the linoleic acid pathway is still not well understood [190].
The network analyses we conducted consistently identified metabolites related to arachidonic and linoleic metabolism, such as arachidonic acid, leukotrienes, prostaglandins, and thromboxanes (Figure 3, Figure 4, Figure 5 and Figure 6; green symbols correspond to lipid metabolism). These metabolites associated with short-term air pollution exposures were connected with genes and proteins related to inflammation and the immune system (red symbols), endothelial function (pink symbols), and coagulation (yellow symbols; Figure 3 and Figure 5). Lipid metabolism markers associated with long-term air pollution exposures had similar trends, though fewer nodes were identified for the gene–metabolite network overall (Figure 4 and Figure 6).

3.2.2. Cellular Energy Production

Three cellular energy production KEGG pathways were associated with short- and long-term TRAP exposure: (1) the citric acid cycle, (2) glycolysis/gluconeogenesis, and (3) the pentose phosphate pathway (Table S7, Figure 2). Although no methylomic or proteomic markers related to the citrate cycle were identified as significantly associated with TRAP, our MetaboAnalyst pathway analyses synthesizing results across studies identified the citric acid cycle KEGG pathway as being significantly enriched by the metabolites significantly associated with short- and long-term TRAP exposure (p = 8.86 × 10−3 and p = 1.65 × 10−3, respectively). Specifically, exposure to short-term TRAP was associated with higher levels of some citric acid cycle intermediates (e.g., succinyl-CoA, succinate, cis-aconitic acid, and alpha-ketoglutaric acid) [136,137,138,168]. But short-term PM2.5 exposure was associated with lower levels of pyruvate, while short-term EC was associated with lower levels of citric acid and isocitric acid [97]. In contrast, long-term PM2.5 exposure was associated with higher levels of malic acid and succinic acid [98,166]. Notably, citric acid cycle dysregulation has been associated with CVD [192,193]. For example, one case-cohort study found an increased risk of CVD with higher concentrations of fasting plasma malic acid, 2-hydroxyglutarate, and fumarate [193], while a nested case-control study found higher levels of succinic acid, malic acid, citric acid, and 2-hydroxyglutarate to be associated with a higher risk of atrial fibrillation [192]. Higher levels of malic acid and succinic acid associated with long-term PM2.5 exposure may underlie part of the known association between TRAP and the risk of CVD. Future studies could explore whether TRAP exposure is also associated with the methylation of genes encoding for key rate limiting and regulatory enzymes in the citric acid cycle, such as citrate synthase, isocitrate dehydrogenase, and alpha-ketoglutarate dehydrogenase, as well as the concentrations of these enzymes. Additionally, future studies could explore functional relationships among citric acid, coagulation, and endothelial function, given the relationships we identified in the long-term air pollution and protein–metabolite network analysis (Figure 6).
The central carbohydrate metabolism pathways represented by biomarkers associated with TRAP include the glycolysis/gluconeogenesis and pentose phosphate pathways (Figure 2). The glycolysis/gluconeogenesis KEGG pathway was represented by two proteomic and five metabolomic markers significantly associated with TRAP, but no methylomic markers (Table S7). Similarly, five metabolomic (but no methylomic or proteomic) markers identified as belonging to the pentose phosphate KEGG pathway were significantly associated with TRAP (Table S7). For the glycolysis/gluconeogenesis KEGG pathway, exposure to short-term diesel exhaust was associated with lower levels of the protein alcohol dehydrogenase class four mu/sigma chain and higher levels of the protein aldehyde dehydrogenase dimeric nicotinamide adenine dinucleotide phosphate-preferring [130]. In metabolomics studies, exposure to short-term PM2.5 was associated with lower levels of the metabolites lactate, pyruvate, and glyceric acid 1,3-bisphosphate [96,97,135], and exposure to long-term PM2.5 was associated with lower levels of 3-phosphoglycerate and lactate [98]. Short-term exposure to O3 was associated with higher levels of glucose and lactate [140], whereas exposure to short-term TRAP was associated with lower levels of glucose and 3-phosphoglycerate [98,138]. For the pentose phosphate KEGG pathway, short-term PM2.5, PM components, and certain other TRAP exposures were associated with lower levels of the metabolites glyceraldehyde, glycerate, 3-phosphoglycerate, and pyruvate [96,97,98], and long-term PM2.5 was associated with lower levels of glycerate and 3-phosphoglycerate [96,97,98,110,138,140,166]. However, short-term exposure to O3 was associated with higher levels of glucose and glycerate [140]. In pathological circumstances such as CVD, glucose metabolism (glycolysis and the pentose phosphate pathway) typically increases relative to fatty acid oxidation [194,195,196]. Further longitudinal research exploring multi-omic markers of carbohydrate metabolism in response to TRAP exposure would help clarify the salient relationships.

3.2.3. Amino Acid Metabolism

Although no methylomic or proteomic markers related to the alanine, aspartate, and glutamate metabolism KEGG pathway were identified as significantly associated with TRAP, our MetaboAnalyst pathway analysis synthesizing results from across studies identified the alanine, aspartate, and glutamate metabolism KEGG pathway as significantly enriched by metabolites associated with short- and long-term TRAP exposure (p = 3.39 × 10−4 and p = 6.0 × 10−3, respectively). There were 14 metabolites representing the KEGG pathway, but there were no consistent patterns of associations among short- and long-term TRAP exposure and concentrations of these metabolites [83,97,98,100,107,110,135,136,137,140,166,167,168,168,170] (Supplementary File S2, Tables S6–S8).
The arginine and proline metabolism KEGG pathway was represented by biomarkers of all three omics types (two genes, one protein, and fourteen metabolites) (Table S7), and our MetaboAnalyst pathway analysis synthesizing the metabolomics literature suggested this pathway was significantly enriched by metabolites significantly associated with short-term TRAP exposure (p = 6.62 × 10−4) but not long-term TRAP exposure. Taken together, there is moderately strong evidence that arginine and proline metabolism may affect the relationship between TRAP and CVD. For example, in the methylomics literature, exposure to short-term PM2.5 was associated with hypomethylation of the genes that code for nitric oxide synthase 2 (NOS2) and arginase 2 (ARG2) [61,118,137]. These are key enzymes for macrophage pathways linking L-arginine metabolism to inflammation and immunity [197]. The protein NOS2 catalyzes the reaction of L-arginine to nitric oxide (NO), which inhibits cell proliferation and kills pathogens [198,199]. The protein ARG2 catalyzes the reaction of L-arginine to L-ornithine, which can metabolize further into polyamines and L-proline. Notably, L-ornithine production promotes cell proliferation and repairs tissue damage [200,201]. ARG2 activity is also associated with the killer-type macrophage response [197,202,203]. Many of the metabolites related to this arginine and proline metabolism pathway were implicated across the metabolomics literature, though some of the results were inconsistent in terms of direction of association (Supplementary File S2 Table S6) [83,96,97,98,101,107,110,136,138,166,167]. For example, short-term PM2.5 was associated with lower levels of L-arginine, L-glutamate, phosphocreatine, and pyruvate and with higher levels of L-ornithine and nitric oxide [83,97,101,113,119]. However, short-term O3 exposure was associated with higher levels of creatinine, L-arginine, L-glutamate, L-ornithine, and L-proline [113,140]. Furthermore, other short-term PM exposures were associated with lower levels of creatinine and higher levels of L-arginine, L-glutamate, L-ornithine, L-proline, D-proline, and sarcosine [138,168]. Finally, in the proteomics literature, short-term diesel exhaust was associated with lower levels of the protein creatine kinase B-type [130], and in our network analysis for short-term exposure to TRAP, the protein creatine kinase B-type was also associated with a metabolite related to lipid metabolism (Figure 5). Given the overlap in the biomarkers identified using the three omics types, further research is warranted into how TRAP exposure may plausibly result in clinically meaningful biological cascades involving arginine and proline metabolism. Such an undertaking would require repeated measures of exposures and omics markers to ensure that the relevant temporal relationships are captured for different levels of biology along the pathway (e.g., how methylation changes related to NOS2 and ARG2 could affect protein expression and subsequent metabolic processes). Future work should also explore the potential connections among amino acid metabolism (blue symbols), coagulation (yellow symbols), inflammation (red symbols), and endothelial pathways (pink symbols) given the results of our network analyses for both short- and long-term TRAP exposures (Figure 3, Figure 4, Figure 5 and Figure 6).

3.2.4. Inflammation and Immunity

Many methylomic and proteomic markers (but not metabolomic markers) identified in the literature review as associated with TRAP exposure were involved in pathways involved in inflammation and immunity (Figure 2). The most enriched pathways included cytokine and chemokine signaling, toll-like receptor (TLR) signaling, and mitogen-activated protein kinase (MAPK) signaling. Biomarkers of these pathways (especially of the cytokine and chemokine signaling pathways) were also well-represented in our network analyses (Figure 3, Figure 4, Figure 5 and Figure 6; red symbols correspond to inflammation and immunity).
Our Reactome pathway analysis identified cytokine signaling in the immune system as significantly enriched by genes related to the methylation sites and proteins associated with short-term TRAP exposure (p = 1.11 × 10−16 and p = 1.11 × 10−16, respectively). This pathway was also significantly enriched by proteins associated with long-term TRAP exposure (p = 1.11 × 10−16), but not genes related to the methylation sites. In particular, there were 13 genes and 40 proteins (with 10 overlapping gene–protein markers) that were part of the cytokine–cytokine receptor interaction KEGG pathway, as well as eight genes and nineteen proteins (with four overlapping gene–protein markers) that were part of the chemokine signaling KEGG pathway (Table S7). Short-term PM2.5 exposure was associated with hypermethylation of the genes encoding for cytokines and chemokines, such as Interleukin 6 (IL6), Interleukin 10 (IL10), granulocyte-macrophage colony-stimulating factor 2 (CSF2), fractalkine (CX3CL1), interferon-gamma inducible protein 10 (CXCL10), and macrophage inflammatory protein 1 alpha (CCL3) [61,117]. In contrast, short-term PM2.5 was associated with hypomethylation of the genes that encode monocyte chemoattractant protein 1 (CCL2) and a cluster of differentiation 40 ligands (CD40LG) [61,117,125,147,148]. Additionally, long-term PM2.5 exposure was associated with hypomethylation of tumor necrosis factor (TNF) and TNF receptor superfamily member 13C (TNFRSF13C) [48,147]. Consistent with some but not all of the methylation trends, proteomics studies found that both short- and long-term exposure to TRAP was associated with higher levels of most cytokine and chemokine proteins (exceptions included inverse associations with tumor necrosis factor receptor superfamily member 11B, Interleukin 4, Interleukin 8, and eotaxin-1) [76,82,84,89,91,93,94,105,115,117,125,128,138,147,165,204,205,206,207]. These observations were consistent across pollutants and exposure windows. Additional research on the associations among pollutants other than PM2.5 and the methylation of genes encoding for cytokines and chemokines would further strengthen the already compelling evidence that TRAP may impact cytokine and chemokine signaling in ways that could affect respiratory and cardiovascular outcomes. Cytokines and chemokines regulate the immune response by controlling immune cell trafficking and the cellular arrangement of immune organs [208,209]. High levels of both cytokines and chemokines represent immune activation and inflammation and are predictive of CVD and adverse cardiovascular events, such as heart failure and myocardial infarction [209,210,211,212]. In addition, many of the key cytokines identified here are involved in the pathogenesis of asthma, COPD, and pulmonary fibrosis [213]. Finally, as shown in our network analyses, many of the genes and proteins associated with short-term TRAP exposure (e.g., IL6/IL6, CXCL10/CXCL10, CCL2/CCL2) were interconnected and were also connected to metabolites of amino acid and lipid metabolism (Figure 5 and Figure 6)—strengthening the argument for the involvement of cytokine signaling in the physiological response to TRAP.
Eight methylomic markers and eleven proteomic markers, with four overlapping gene–protein markers and no metabolomic markers, represented the TLR signaling KEGG pathway (Table S7). Short-term exposure to PM2.5 and BC was associated with hypomethylation and hypermethylation of TLR2, respectively [41,61]. Exposure to short-term PM10 and other short-term TRAP was associated with hypomethylation of TLR4 [150,151]. Exposure to short-term PM10 and SO4 were associated with hypomethylation of CD14 and MAP3K7, respectively [46,151]. The remaining methylomic and proteomic markers belonging to the TLR KEGG pathway overlapped with the cytokine–cytokine receptor interaction KEGG pathway described previously and in Table S7. These trends are important because the TLR signaling pathway detects pathogen-associated molecular patterns, stimulating both the nuclear factor kappa-light-chain-enhancer of activated B cells (NF-kB) and MAPK pathways, as well as cytokine production, thereby affecting inflammatory and immune responses associated with CVD and adverse respiratory outcomes [214,215].
In addition to the trends for cytokine and chemokine signaling and the TLR signaling pathways, we identified 12 methylomic markers and nine proteomic markers associated with TRAP as belonging to the MAPK signaling KEGG pathway, with two overlapping gene-protein markers and no metabolomic markers (Table S7). In the methylomics literature, short-term BC exposure was associated with hypermethylation of MAP3K2 and MAP3K6, as well as hypomethylation of MAP4K3 and MKNK2 [46]. Short-term SO4 exposure is associated with hypermethylation of MAP3K11 and hypomethylation of RPS6KA3, MAP3K7, and TGFB1 [46]. Long-term exposure to PM10 and NO2 was associated with hypomethylation and hypermethylation of PDGFB and CACNA2D1, respectively [48,56]. Lastly, for the methylomics literature, short-term PM2.5 exposure was associated with hypermethylation of FGF2 [117]. In the proteomics literature, short-term PM2.5, UFP, BC, NO2, and CO exposures were associated with higher levels of fibroblast growth factor 2 protein [117,138]. In addition, short-term diesel exhaust exposure was associated with higher levels of MAPK 1 and cell division control protein homolog 42 and lower levels of protein kinase C beta type [130,165]. Finally, short-term UFP, BC, NO2, and CO were associated with higher levels of tropomyosin receptor kinase B [138]. Synthesizing across the studies, our Reactome pathway analysis identified the MAPK signaling cascade pathway as significantly enriched by proteins associated with short-term TRAP exposure (p = 4.35 × 10−8). Although this pathway was not significantly enriched by methylation markers associated with TRAP exposure, the body of evidence taken together suggests that TRAP exposures may affect MAPK signaling cascades, which is critical since this pathway has implications for oxidative stress, vascular remodeling and dysfunction, cardiac hypertrophy, cardiac remodeling, and atherosclerosis [216,217,218,219,220,221].

3.2.5. Coagulation

The complement and coagulation cascade KEGG pathway was represented by four methylomic markers and fourteen proteomic markers significantly associated with TRAP, with two overlapping gene–protein markers. There were no metabolomic markers of this pathway identified as significantly associated with TRAP (Table S7). Short-term exposure to PM2.5 was associated with hypomethylation of the genes that encode plasminogen activator inhibitor type I (SERPINE1), coagulation factor III (F3), and coagulation factor II receptor (F2R), as well as hypermethylation of coagulation factor II (F2) [41,49,125,148,160]. Within the proteomics literature, short-term exposure to PM10 and PM2.5–10 was associated with lower levels of the protein plasminogen activator inhibitor type 1, whereas long-term exposure to PM2.5, NO2, CO, and O3 was associated with higher levels of this protein [72,74,76]. Additionally, short-term exposure to PM2.5, UFP, BC, NO2, and CO was associated with higher levels of coagulation factor III protein (F3) [127,138]. The combination of associations with short-term exposures and methylation markers and long-term exposures and proteins (e.g., SERPINE1) may provide evidence for time-dependent biological cascades or effects; future research should explore this possibility using a study design that can take advantage of repeated measures for exposures and outcomes. Further research could explore the possibility of similar overlap across omics types by building on the TRAP and proteomics literature suggesting significant and generally positive associations with other key coagulation and complement proteins (e.g., complement component 3, complement component 4B, fibrinogen, Von Willebrand factor, coagulation factor VII, D-dimer, alpha-1 antitrypsin, protein C inhibitor, complement C1q subcomponent subunit A, and tissue-type plasminogen activator; Supplementary File S2, Table S5) [71,73,74,76,78,86,92,124,125,126,127,130,138,207]. The importance of complement and coagulation cascades is also underscored by the connections of coagulation factors, coagulation factor responses, plasminogen activators, and plasminogen activator inhibitors in the network analyses (represented by yellow markers) to biomarkers of amino acid metabolism (blue markers), lipid metabolism (green markers), and inflammation and immunity (red markers; Figure 3, Figure 4, Figure 5 and Figure 6). Taken together, there is strong evidence supporting the putative links between TRAP exposure, coagulation and complement cascades, and CVD (Figure 2). This is supported by other studies that show that higher levels of plasminogen activator inhibitor 1, fibrinogen, Von Willebrand factor, coagulation factor VII, and complement component 3 are each associated with the risk of CVD and atherosclerosis [220,221,222,223,224,225,226,227]. Furthermore, higher levels of plasminogen activator inhibitor 1 and Von Willebrand factor have been associated with increased odds of myocardial infarction [220,227].

3.2.6. Endothelial Function

Methylomic, proteomic, and metabolomic markers associated with TRAP exposure were associated with five KEGG pathways related to endothelial function: cell adhesion molecules, vascular endothelial growth factor (VEGF) signaling, vascular smooth muscle contraction, lipid and atherosclerosis, and leukocyte transendothelial migration (Table S7).
The first KEGG pathway, cell adhesion molecules, was represented by five methylomic markers, five proteomic markers (including three overlapping with the methylomic markers), and no metabolomic markers (Supplementary File S2, Tables S4 and S5). The three overlapping markers were a cluster of differentiation 40 ligands (CD40LG), p-selectin (SELP), and intercellular adhesion molecule 1 (ICAM1). For CD40LG, short-term PM2.5 was associated with hypomethylation of the corresponding gene [117,125,148], whereas short-term PM2.5, NO2, SO2, SO4, EC, and multiple PM components were associated with higher levels of the protein [76,115,117,125,127,147,148,205,207]. For SELP, long-term PM2.5 was associated with hypomethylation of the corresponding gene, and long-term PAHs were associated with lower levels of the protein [48,125,172,207]. For ICAM1, short-term BC and O3 were associated with hypomethylation of the corresponding gene [41], short-term PM2.5 had inconsistent associations with the corresponding gene [41,61,125,147], and both short- and long-term TRAP exposures were generally associated with higher levels of the protein [69,70,71,92,105,124,147,205,228]. Biomarkers of the cell adhesion molecule pathway (e.g., SELP, ICAM1) were also identified in our network analysis for both short- and long-term TRAP exposures as being highly connected to markers of other biological processes (e.g., lipid metabolism; Figure 3, Figure 4, Figure 5 and Figure 6). Cell adhesion molecules are essential in the normal development of the heart and blood vessels; however, they play a role in the development of respiratory diseases and CVD, such as pulmonary fibrosis and atherosclerosis [229].
The second KEGG pathway, the VEGF signaling pathway, was represented by no methylomic, three proteomic, and two metabolomic markers associated with TRAP exposure (Supplementary File S2, Tables S5 and S6). For proteomics, short-term exposure to diesel exhaust was associated with higher levels of the cell division control protein 42 homolog and lower levels of protein kinase C beta type [130]. In addition, exposure to short-term NO2 and long-term NOx was associated with higher levels of VEGF-alpha (VEGFA) [84,115]. VEGFA was also identified as connected to markers of lipid metabolism and amino acid metabolism in our network analysis for short-term TRAP exposure (Figure 5). For metabolomics, short-term PM2.5 was associated with higher levels of nitric oxide, and short-term EC was associated with higher levels of prostaglandin I2 [118,119,167]. Upregulation of VEGF signaling is involved in angiogenesis and can be a response to hypoxia [230]. Higher concentrations of these analytes associated with TRAP exposure could indicate difficulty delivering oxygen from the lungs to the periphery; however, VEGF signaling is not always pathological.
The third KEGG pathway, vascular smooth muscle contraction, was represented by one methylomic, three proteomic, and four metabolomic markers associated with TRAP exposure (Supplementary File S2 Tables S4–S6). For methylomics, long-term PM2.5 was associated with hypomethylation of the guanine-nucleotide-binding protein alpha subunit complex locus (GNAS) [48]. For proteomics, short-term UFP, BC, NO2, and CO were associated with higher levels of endoglin [138], and short-term diesel exhaust was positively associated with mitogen-activated protein kinase 1 and negatively associated with protein kinase C beta type [130]. For metabolomics, short-term PM2.5 was positively associated with nitric oxide and 20-hydroxyeicosatetraenoic (HETE) acid [109,118,119], and short-term TRAP was positively associated with arachidonate and prostaglandin I2 [167,168,173]. Contraction of the vascular smooth muscle within arteries, arterioles, veins, and lymphatic vessels increases resistance in the cardiovascular system and decreases blood flow [231]. TRAP-associated modulation in these signals could inform part of the relationship between TRAP exposure and blood pressure, and therefore CVD. Further research is needed to clarify the exact physiological mechanisms linking TRAP, omics signals, blood pressure, and CVD.
The fourth KEGG pathway, lipid and atherosclerosis, was represented by no methylomic or proteomic markers but three metabolomic markers associated with TRAP exposure (Supplementary File S2 Table S6). Short-term PM2.5 was positively associated with nitric oxide, and short-term TRAP was positively associated with cholesterol and triglyceride [118,119,138]. Cholesterol and triglycerides, both positively associated with TRAP exposure, are risk factors for atherosclerosis. Furthermore, TRAP is already known to be associated with atherosclerosis through the exacerbation of risk factors such as hypertension and insulin resistance [232].
The final KEGG pathway, leukocyte transendothelial migration, was represented by three methylomic markers, six proteomic markers (one overlapping with a methylomic marker), and no metabolomic markers associated with TRAP exposure (Supplementary File S2, Tables S4 and S5). The trends for the overlapping marker (ICAM1), as well as two of the other proteomic markers (i.e., protein kinase C beta type and cell division control protein homolog 42), were described previously. The other methylation markers associated with short-term PM2.5 encode protein subunit alpha 13 (positive association) and actinin alpha 3 (negative association) [43,161]. The other proteomic markers positively associated with short-term TRAP exposure included vascular cellular adhesion molecule 1 (VCAM1; with PM2.5, NO2, CO, SO4, and O3) [71,92,205], matrix metalloproteinase (MMP2; with BC and PNC), and MMP9 (with SO2) [82]. In our network analysis for short-term TRAP exposures, MMPs shared network connections with markers of processes such as lipid and amino acid metabolism (Figure 5). Leukocyte trans-endothelial migration is critical in the immune response and responsible for facilitating a systemic reaction upon exposure to a pathogen [233]. The subclinical effects of differential leukocyte count post-TRAP exposure have previously been noted [234] and represent part of the well-documented inflammatory response to TRAP.

3.2.7. Oxidative Stress

Multiple KEGG pathways represented in the methylomic, proteomic, and metabolomic literature are associated with the oxidative stress response (Table S7; Figure 2). For example, the citrate cycle, pentose phosphate metabolism, MAPK signaling, p53 signaling, Janus Kinase/signal transducers and activators of transcription (JAK–STAT) signaling, apoptosis, and regulation of autophagy KEGG pathways are all known to be activated in response to oxidative stress [217,235,236,237,238,239,240,241]. The biomarkers related to several of these pathways were described previously. Others are described in this section.
The p53 signaling pathway is activated in response to oxidative stress and TRAP exposure and helps to ensure cell survival [236,237]. For this pathway, one methylomic and seven proteomic markers (including one overlapping gene–protein marker) were identified as significantly associated with TRAP (Supplementary File S2, Tables S4, S6, and S8). Short-term exposure to PM2.5 was associated with hypomethylation of SERPINE1 [148]. Additionally, short-term exposure to PM10 and PM2.5–10 was associated with lower levels of the corresponding protein, whereas long-term exposure to PM2.5, PM2.5–10, NO2, CO, and O3 were associated with higher levels [72,74,76]. Furthermore, short-term BC and NO2 were associated with higher levels of insulin-like growth factor binding proteins 1 and 3, while short-term diesel exhaust was associated with lower levels of insulin-like growth factor binding protein 2 and 14-3-3 protein sigma [82,130]. Finally, long-term PM2.5 and PM10 exposures were associated with higher levels of alpha-1 antitrypsin [86]. Given the role of p53 signaling in anti-angiogenesis, programmed cell death, metabolism regulation, and vasodilation, this pathway can affect cardiovascular outcomes [242,243]. In addition, p53 signaling plays a supportive role in the maintenance of lung homeostasis; therefore, dysregulation and deficiency of p53 signaling can be associated with respiratory diseases [244].
Similarly to the p53 signaling pathway, the JAK–STAT signaling pathway is activated by oxidative stress and reactive oxygen species [240]. This signaling pathway is mainly involved in coordinating immune responses, including cytokine signaling [245]. Four methylomic markers and fourteen proteomic markers (including four overlapping gene-protein markers) of this pathway were identified as significantly associated with TRAP (Supplementary File S2, Tables S4, S6, and S8). Three of the methylomic markers (for the genes CSF2, IL6, and IL10) were described in the section on inflammation and immunity. Briefly, short- and long-term TRAP was associated with hypomethylation of these markers and higher levels of the proteins they encode [61,76,91,92,93,94,115,117,127,128,147,165,204,228,246,247]. Hypermethylation of one methylomic marker relevant here (related to a gene that encodes interferon gamma (IFNG)) was associated with short-term TRAP exposure (though short-term BC was associated with hypomethylation) [41,120]. Relatedly, short-term PM2.5, NO2, CO, PAHs, and PM constituents were associated with higher levels of the protein IFNG [115,204]. Short-term TRAP was also positively associated with other proteins involved in JAK–STAT signaling, including granulocyte colony-stimulating factor 3, granulocyte-macrophage colony-stimulating factor receptor alpha, Interleukin 2 alpha, Interleukin 5, Interleukin 7, Interleukin 12, and signal transducer and activator of transcription 3 (STAT3) [115,117,128,138,165,206]. In contrast, short-term TRAP was associated with lower levels of Interleukin 4, Interleukin 13, and protein tyrosine phosphatase non-receptor type 6 [115,117,165]. These associations with markers related to JAK-STAT signaling are important for the relationship between TRAP exposure and CVD outcomes because dysregulation of JAK–STAT signaling is associated with CVD [248,249]. Furthermore, cytokine signaling induced through the JAK–STAT pathway is implicated in COPD, asthma, and other respiratory conditions [250,251].
Apoptosis, or programmed cell death, can be caused by oxidative stress [238]. Representing the apoptosis KEGG pathway, TRAP was associated with one methylomic marker, three proteomic markers (including one overlapping with a methylomic marker), and one metabolomic marker (Supplementary File S2, Tables S4–S6). Trends for the overlapping methyl-omic-proteomic marker, tumor necrosis factor-alpha, were described previously. For the other proteomic markers, short-term PM10, UFP, NO2, CO, and PAHs were positively associated with Interleukin 1 beta, whereas short-term UFP, BC, NO2, and CO were inversely associated with tropomyosin receptor kinase B [94,138,204]. For metabolomics, short-term PM2.5, UFP, and long-term PM2.5 were associated with lower levels of the sole metabolite, sphingosine [98,101,171]. Apoptosis is a vital part of normal cell turnover and immune system functioning, implicating this pathway in cardiorespiratory disease [252,253,254].
The final oxidative-stress-related KEGG pathway, the regulation of autophagy, is involved in apoptosis and helps maintain cellular homeostasis [238,239,241,255]. This pathway was represented by one methylomic marker and two proteomic markers (including one overlapping marker) associated with TRAP. Trends were previously described for the overlapping marker, interferon-gamma. The other protein, interferon alpha 2, was positively associated with short-term PM2.5 [117]. Proper functioning of adaptive autophagy processes is important for cardiovascular health and aging [256,257,258].

3.2.8. TRAP, Omics, and Respiratory Disease

Short- and long-term TRAP exposure is associated with worse respiratory outcomes, including worse lung function [61,90,110,154,259,260,261,262,263], and with more asthma exacerbation and COPD burden [262,264,265,266,267]. In our review, three methylomic markers, seven proteomic markers (including three overlapping methylomic–proteomic markers), and three metabolomic markers were represented in the KEGG pathway for asthma (Table S7). The overlapping markers included three inflammation and immunity markers (TNF, CD40LG, and IL-10); we described trends for these previously [61,72,91,94,115,117,125,128,147,147,204,205,207,228,247,260]. For the other proteomics markers, short-term PM2.5, PM10, NO2, CO, and SO2 were inversely associated with IL-4; short-term CO was inversely associated with IL-13 [115,117,128]; and short-term NO2 and diesel exhaust were positively associated with IL-5 [115,128]. Additionally, short-term PM2.5, PM10, CO, and SO2 were inversely associated with monocyte chemoattractant protein 1, whereas long-term PM2.5, NO2, and NOx were positively associated with this protein [84,115,117]. For metabolomic markers, short-term TRAP was positively associated with leukotriene C4 and inversely associated with prostaglandin D2 [168], and short-term NO2, CO, and EC were inversely associated with histamine [166]. These trends, along with others described in previous sections, suggest plausible biological processes that affect the TRAP exposure-respiratory disease relationship. For example, it has been observed that linoleate metabolism is associated with asthma [104], and arginine and proline metabolism as well as methionine and cysteine metabolism are associated with asthma and COPD [106]; these are processes associated with TRAP exposures. Additionally, elevated NO is characteristic of airway inflammation [268], and we previously described trends relating TRAP to higher NO [61,118,119]. Similar trends are observed between TRAP exposures and markers of systemic inflammation (e.g., CRP, fibrinogen) that are associated with worse lung function [269,270,271,272]. Finally, the associations we described previously relating TRAP exposures to cytokines and chemokines have implications for airway remodeling, asthma, and COPD [213].

3.2.9. TRAP, Omics, and CVD

As described above and elsewhere, many studies have observed associations between TRAP exposure and biomarkers related to CVD (e.g., [273,274,275]). A subset of studies used meet-in-the-middle approaches (i.e., identifying common associations of exposures and CVD outcomes with biomarkers), mediation analyses, and other approaches to more directly link TRAP exposures to CVD outcomes (e.g., heart rate [120], blood pressure [149,150], and incident CVD [84]). As in our review, these studies considered biomarkers for processes related to inflammation and immunity, endothelial function, and oxidative stress. Most of these studies considered only single omic types, but one that considered both proteomic and metabolomic biomarkers identified 20 biomarkers associated with both short-term TRAP and changes in blood pressure or heart rate variability [138]. As in our review, that study identified biomarkers implicated in lipid metabolism (e.g., trimethylamine N-oxide), cellular energy production (e.g., succinic acid), inflammation (e.g., C-reactive protein), coagulation (tissue factor pathway inhibitor), endothelial function (e.g., angiotensin-converting enzyme), and oxidative stress (e.g., malondialdehyde). Our review was able to take this type of logic one step further—with the network analyses (Figure 3, Figure 4, Figure 5 and Figure 6). By integrating information across multi-omic types, we can build on the systems biology approaches now being used to understand the pathophysiology of CVD (e.g., [276,277]). Specifically, our network analyses suggest that interconnections among amino acid metabolism, lipid metabolism, inflammation, coagulation, and endothelial function are important to the relationship between TRAP exposures and CVD.

4. Conclusions

To our knowledge, this is the first systematic review synthesizing the literature focused on TRAP-associated methylomic, proteomic, and metabolomic biomarkers in the context of respiratory and cardiovascular outcomes. Through a comprehensive, integrated lens, we explored TRAP-associated pathways involving lipid metabolism, cellular energy production, amino acid metabolism, inflammation and immunity, coagulation, endothelial function, and oxidative stress. We find that a multi-omics synthesis provides new insights into the biological pathways associated with TRAP and has advantages over single-omics approaches. Synthesizing results from the (predominately single-omic) literature, we showed that similar or analogous biomarker signals were observed across multiple omic types (e.g., TRAP exposure associated with methylation of genes encoding for proteins that are also associated with TRAP). Specifically, we identified consistent patterns between methylation status and protein levels within cytokine–cytokine signaling, TLR signaling, MAPK signaling, complement and coagulation cascades, cell adhesion molecules, and asthma KEGG pathways. Additionally, we observed analogous proteomic and metabolomic associations with TRAP exposure within certain lipid and amino acid metabolism KEGG pathways. Finally, within the arginine and proline metabolism KEGG pathway, we were able to integrate methylomic, proteomic, and metabolomic findings to provide evidence suggesting possible mechanistic linkages between TRAP exposure, subclinical indicators, and clinical disease. Corroborating evidence across multiple levels of biology—including with a focus on functional interrelationships and network analyses—is only possible with multi-omics. Furthermore, multi-omics has the potential to aid in the discovery and assessment of quantitative biomarkers at different levels of biology (related methylation patterns, proteins, and metabolites) that could predict subclinical and perhaps clinical respiratory and cardiovascular responses to TRAP exposure, thereby improving clinical and public health decision-making. This could perhaps be clinically translated using advances to epigenetic clocks and other risk prediction tools that address residual risk remaining after the use of current risk prediction tools [211,278,279,280,281]. The continued development of omics technologies represents immense potential for the advancement of personalized medicine. Researchers and clinicians should continue to collaborate on the identification of omics signals associated with air pollution exposure, preclinical disease, and clinical disease to develop helpful risk prediction tools.

4.1. Strengths and Limitations

A major strength of our systematic review is that we provided a synthesis of findings from across three types of omics markers. This multi-omics process offers superior insight into the biological underpinnings of respiratory diseases and CVD than single-omics methods alone. We compiled methylomic, proteomic, and metabolomic evidence from methodologically diverse studies in a novel way to understand how short- and long-term TRAP exposure-associated multi-omics signals relate to one another, allowing us to identify the most relevant biological pathways that may be involved in the pathogenesis of cardiorespiratory disease and help inform clinical risk prediction. Nevertheless, our review had several limitations. First, to synthesize results across studies that used heterogeneous exposure metrics and methods, we made the simplifying assumption of categorizing short- and long-term exposures as ≤30 days and >30 days, respectively. This decision was supported by convention within the literature but does not necessarily reflect a critical biological change occurring at 30 days. Additionally, due to the availability of published studies, there were fewer long-term exposures represented in our analysis. This limitation of our review is a limitation of the field in general. Given the relative sparsity of long-term exposure periods as well as a tendency to select targeted rather than untargeted omics approaches, the omics signals and pathways associated with long-term TRAP exposure may be incomplete or less comprehensive relative to short-term TRAP exposure. Second, to synthesize the biological implications of the individual biomarkers identified as associated with TRAP, we made simplifying assumptions that we could include all individually identified biomarkers together in our pathway and network analyses, and although we considered short- and long-term exposures separately, we did not separate results by pollutant type. Different TRAP components likely have different biological impacts. This could even be true of the same TRAP component; for example, PM2.5 toxicity could vary by source and composition, and we did not account for these differences. More generally, it is possible that direct comparisons or synthesis were not warranted in each case due to certain differences in the study population, exposure metric, or other methodological choices within the individual studies that would result in meaningful differences in the true underlying biology. Third, our synthesis of the results and identification of relevant pathways were necessarily limited by the choices of the individual studies (including those related to the ways ‘statistical significance’ was defined). If the studies did not include certain biomarkers that may be important to the physiological response to TRAP, we could not capture them—particularly for proteomics, this may have limited our findings since there were somewhat fewer studies with large numbers of proteins assayed, and the literature may have overrepresented certain biological pathways due to precedent rather than biology. Targeted omics approaches (as employed with many of the proteomics studies) allow for focused, relatively resource-efficient confirmatory investigations following earlier studies identifying potentially important biomarkers; however, future studies leveraging evolving technology may consider a more comprehensive set of proteins. Conversely, untargeted approaches (as employed with many of the metabolomics studies) are exploratory. They analyze the broadest set of possible biomarkers. While this has the advantage of helping identify the most expansive set of possible biologically relevant biomarkers and pathways, they need to be followed up with confirmatory studies to test the hypotheses they generate. Relatedly, if metabolite identification with a high level of confidence was not provided by the individual untargeted studies, we may have missed critical biological pathways. Next, we limited the scope of our review to exclude people who were pregnant and/or under 18 years old. Future research should consider these important populations. Fourth, reflecting the literature, this review contains a relatively large number of studies representing only single-sex cohorts. Their inclusion is critical to this review as it represents a large proportion of our current knowledge; however, single-sex research limits our understanding of the potentially variable response to TRAP exposure between sexes. Future work should consider sex and gender more fully, including the possibility for effect modification by sex and/or gender. Similarly, our results may not be transportable to children who were not in our study population. Finally, and perhaps most critically, we could not assess whether TRAP exposures resulted in meaningful biological cascades following the gene-to-protein-to-metabolite paradigm, as no study we reviewed included all three omics types and none included the repeated measures of the omics markers that would be needed to assess dynamic biological processes. This is apparent in the occasional inconsistent associations with short- versus long-term exposure windows of the same pollutant (in terms of strength and/or direction of association). It is possible that these differences arise from true differences among study populations and their responses to pollution, or alternatively, from an inability to accurately capture the biological cascades occurring at various time points.

4.2. Future Directions

Building on the strengths of the studies presented in this review and the conclusions that could be drawn by comparing the results using heterogeneous research methodologies, several critical areas for further research are warranted. The primary challenges our field currently faces are related to the true integration of multi-omics signals within studies that can appropriately characterize the dynamic and complex biological processes linking TRAP exposure to subclinical and clinical diseases. To address this critical challenge, we need large, longitudinal studies representing diverse study populations. Ideal features include time-varying, high-resolution exposure assessment coupled with repeated quantification of multi-omics signals in multiple tissue types with comprehensive assay coverage. If multiple cohorts are included in a study, standardization of methods across cohorts would facilitate interpretation and comparability of results. A major goal of such a study would be to consider how air pollution exposures might lead to physiological signals suggestive of the biological cascades leading from exposure to sub-clinical disease to clinical disease (necessitating several repeated measures of the biological matrix over different time courses). A consideration of both the short- and long-term physiological effects of TRAP would be warranted, including a consideration of individual TRAP components and TRAP mixtures. Ideally—and expected based on the historic evolution of technology—omics technology will continue to evolve to analyze larger numbers of biomarkers more quickly and cheaply. It would also be worth examining sex and gender differences, along with other differences that could lead to disparities in health consequences attributed to air pollution exposure. The use of emerging and novel data management and analysis approaches that can handle large and complex data structures inherent in multi-omics studies will be important (e.g., multiblock methods and tensor decomposition methods) [23,276,282,283,284,285,286,287]. Open-source bioinformatics platforms are an important resource and should be invested in to ensure they are kept up-to-date and able to handle multi-omics analyses. Relatedly, it would be critical to consider the optimal multi-omics integration approach (e.g., whether each omics type is analyzed first and then types are synthesized, or whether processing integrates across omics types earlier) [288,289,290]. If such a comprehensive study could be conducted, it would provide mechanistic insight into the pathophysiology and progression of the disease and would inform the identification of multi-omic signatures of air pollution exposure that could be predictive of key health outcomes. Insights gained from such studies could inform screening priorities, clinical decision-making, and public policy.

Supplementary Materials

The following supporting information can be downloaded at: https://www.mdpi.com/article/10.3390/toxics11121014/s1, Supplementary File S1: Search strategy for systematic review article selection process; Supplementary File S2: Multi-omics synthesis tables and data extraction spreadsheets used in the systematic review process, Table S1: Methylomics data extraction table. Information regarding study author, design, participant demographics, and basic methodology were extracted. Each row corresponds to a unique study. (ACE—Atlanta Commuters Exposure; ARIC—Atherosclerosis Risk in Communities; BPRHS—Boston Puerto Rican Health Study; EPIC—European Prospective Investigation into Cancer and Nutrition; KORA—Cooperative health Research in the Region of Augsburg; MESA—Multi Ethnic Study of Atherosclerosis; NAS—Normative Aging Study: REGICOR—REgistre GIroní del COR; SAPALDIA—Swiss Study on Air Pollution and Lung Disease in Adults; SPHERE—Susceptibility to Particle Health Effects, miRNA and exo-somes; WHI—Women’s Health Initiative); Table S2: Proteomics data extraction table. Information regarding study author, design, participant demographics, and basic methodology were extracted. Each row corresponds to a unique study. (ACE—Atlanta Commuters Exposure; AHAB-II—Adult Health and Behavior; AIRCHD—Air Pollution and Cardiovascular Dys-functions in Healthy Adults Living in Beijing; BPRHS—Boston Puerto Rican Health Study; CAFEH—Community Assessment of Freeway Exposure and Health; ELISABET—Enquête Littoral Souffle Air Biologie Environnement; EPIC—European Prospective Investigation into Cancer and Nutrition; ESCAPE—European Study of Cohorts for Air Pollution Effects; KORA—Cooperative Health Research in the Region of Augsburg; MESA—Multi Ethnic Study of Atherosclerosis; NAS—Normative Aging Study; SAGE—Study on Global Aging and Adult Health; SAPALDIA—Swiss Study on Air Pollution and Lung Disease in Adults; SWAN—Study of Women’s Health Across the Nation); Table S3: Metabolomics data extraction table. Information regarding study author, design, participant demographics, and basic methodology were extracted. Each row corresponds to a unique study. (ACE—Atlanta Commuters Exposure; AIRCHD—Air pollution and Cardiovascular Dys-functions in Healthy Adults Living in Beijing; CAFEH—Community Assessment of Freeway Exposure and Health; DRIVE—Dorm Room Inhalation to Vehicle Emissions; EARTH—Environmental and Reproductive Health; EPIC—European Prospective Investigation into Cancer and Nutrition; KORA—Cooperative Health Research in the Region of Augsburg; NAS—Normative Aging Study; SAPALDIA—Swiss Study on Air Pollution and Lung Disease in Adults; SCOPE—A Prospective Study Comparing the Cardiometabolic and Respiratory Effects of Air Pollution Exposure on Healthy and Prediabetic Individuals; TAPAS—Transportation, Air Pollution and Physical Activites); Table S4: Methylomics synthesis table. All statistically significant associations between TRAP and methylomics markers from the methylomics literature were compiled into this table. For each gene, KEGG pathways and Gene Ontology (GO) molecular functions were indicated. If available, sepcific CpG sites corresponding to the genes were given. Each pollutant was broken down into short-term (<30 days) and long-term (>30 days) exposure. (PM2.5—Particulate Matter 2.5 Microns or Less; PM10—Particulate Matter 10 Microns or Less; BC—Black Carbon; NO2—Nitrogen Dioxide; NOx—Nitrogen Oxides; SO4—Sulfate; O3—Ozone; TRAP—Traffic-Related Air Pollution); Table S5: Proteomics synthesis table. All statistically significant associatons between TRAP and proteomics markers within the proteomics literature were compiled into this table. For each protein, KEGG pathways and Gene Ontology (GO) molecular functions were indicated. Each pollutant was broken down into short-term (<30 days) and long-term (≥30 days) exposure. (PM2.5—Particulate Matter 2.5 Microns or Less; PM10—Particulate Matter 10 Microns or Less; PM1—Particulate Matter 1 Micron or Less; UFP—Ultrafine Particulate Matter; BC—Black Carbon; NO2—Nitrogen Dioxide; NOx—Nitrogen Oxides; CO—Carbon Monoxide; SO4—Sulfate; O3—Ozone); Table S6: Metabolomics synthesis table. All statisically significant associations between TRAP and metabolomics markers within the metabolomics literature were compiled into this table. For each metabolite, KEGG pathways were indicated. Each pollutant was broken down into short-term (<30 days) and long-term (≥30 days) exposure. (PM2.5—Particulate Matter 2.5 Microns or Less; PM10—Particulate Matter 10 Microns or Less; PM1—Particulate Matter 1 micron or Less; UFP—Ultrafine Particulate Matter; BC—Black Carbon; EC—Elemental Carbon; NO2—Nitrogen Dioxide; NOx—Nitrogen Oxides; CO—Carbon Monoxide; SO2—Sulfur Dioxide; O3—Ozone; Ni—Nickel; V—Vanadium; Al—Aluminium; Si—Silicon; K—Potassium; Cu—Copper; Zn—Zinc; Fe—Iron; Pb—Lead; Se—Selenium; TRAP—Traffic-Related Air pollution); Table S7: Combined synthesis of significant associations; Table S8: Complete synthesis table. This table synthesizes the methylomic, proteomic, and metabolomic literature. The table is organized by KEGG pathway. Within each KEGG pathway, all methylomic, proteomic, and metabolic markers significantly associated with short and/or long-term TRAP are noted. Each pollutant was broken down into short-term (<30 days) and long-term (≥30 days) exposure. (PM2.5—Particulate Matter 2.5 Microns or Less; PM10—Particulate Matter 10 Microns or Less; UFP—Ultrafine Particulate Matter; BC—Black Carbon; EC—Elemental Carbon; NO2—Nitrogen Dioxide; NOx—Nitrogen Oxides; CO—Carbon Monoxide; SO2—Sulfur Dioxide; S04—Sulfate; O3—Ozone; Ni—Nickel; V—Vanadium; Al—Aluminium; Si—Silicon; K—Potassium; Cu—Copper; Zn—Zinc; Fe—Iron; Pb—Lead; Se—Selenium; TRAP—Traffic-Related Air Pollution); Table S9: The list of all methylomic, proteomic, and metabolomic markers used for pathway and network analyses in both MetaboAnalyst and KEGG.

Author Contributions

Conceptualization, F.K., C.U. and L.C.; methodology, C.C., F.K., K.K. and L.C.; formal analysis, C.C.; investigation, C.C., F.K. and C.U.; resources, L.C.; data curation, C.C., F.K. and C.U.; writing—original draft preparation, C.C., F.K., K.K. and L.C.; writing—review and editing, C.C., F.K., C.U., D.S.M., K.K. and L.C.; visualization, C.C., F.K. and C.U.; supervision, L.C.; funding acquisition, L.C. All authors have read and agreed to the published version of the manuscript.

Funding

This research was funded by the National Institute of Child Health and Human Development at the National Institutes of Health, grant number K12HD092535.

Institutional Review Board Statement

Not applicable.

Informed Consent Statement

Not applicable.

Data Availability Statement

The datasets generated and analyzed for this study can be found in the manuscript and supplements.

Conflicts of Interest

The authors declare no conflict of interest. The funders had no role in the design of the study; in the collection, analyses, or interpretation of data; in the writing of the manuscript; or in the decision to publish the results.

References

  1. Brook, R.D.; Rajagopalan, S.; Pope, C.A.; Brook, J.R.; Bhatnagar, A.; Diez-Roux, A.V.; Holguin, F.; Hong, Y.; Luepker, R.V.; Mittleman, M.A.; et al. Particulate Matter Air Pollution and Cardiovascular Disease. Circulation 2010, 121, 2331–2378. [Google Scholar] [CrossRef]
  2. Hoek, G.; Krishnan, R.M.; Beelen, R.; Peters, A.; Ostro, B.; Brunekreef, B.; Kaufman, J.D. Long-Term Air Pollution Exposure and Cardio-Respiratory Mortality: A Review. Environ. Health 2013, 12, 43. [Google Scholar] [CrossRef] [PubMed]
  3. Künzli, N.; Kaiser, R.; Medina, S.; Studnicka, M.; Chanel, O.; Filliger, P.; Herry, M.; Horak, F.; Puybonnieux-Texier, V.; Quénel, P.; et al. Public-Health Impact of Outdoor and Traffic-Related Air Pollution: A European Assessment. Lancet 2000, 356, 795–801. [Google Scholar] [CrossRef]
  4. Anderson, J.O.; Thundiyil, J.G.; Stolbach, A. Clearing the Air: A Review of the Effects of Particulate Matter Air Pollution on Human Health. J. Med. Toxicol. 2012, 8, 166–175. [Google Scholar] [CrossRef] [PubMed]
  5. Bourdrel, T.; Bind, M.-A.; Béjot, Y.; Morel, O.; Argacha, J.-F. Cardiovascular Effects of Air Pollution. Arch. Cardiovasc. Dis. 2017, 110, 634–642. [Google Scholar] [CrossRef] [PubMed]
  6. Brucker, N.; do Nascimento, S.N.; Bernardini, L.; Charão, M.F.; Garcia, S.C. Biomarkers of Exposure, Effect, and Susceptibility in Occupational Exposure to Traffic-Related Air Pollution: A Review. J. Appl. Toxicol. 2020, 40, 722–736. [Google Scholar] [CrossRef]
  7. Laumbach, R.J.; Kipen, H.M. Acute Effects of Motor Vehicle Traffic-Related Air Pollution Exposures on Measures of Oxidative Stress in Human Airways. Ann. N. Y. Acad. Sci. 2010, 1203, 107–112. [Google Scholar] [CrossRef]
  8. Miller, M.R. Oxidative Stress and the Cardiovascular Effects of Air Pollution. Free Radic. Biol. Med. 2020, 151, 69–87. [Google Scholar] [CrossRef]
  9. Rajagopalan, S.; Al-Kindi, S.G.; Brook, R.D. Air Pollution and Cardiovascular Disease. J. Am. Coll. Cardiol. 2018, 72, 2054–2070. [Google Scholar] [CrossRef]
  10. Ferrari, L.; Carugno, M.; Bollati, V. Particulate Matter Exposure Shapes DNA Methylation through the Lifespan. Clin. Epigenet. 2019, 11, 129. [Google Scholar] [CrossRef]
  11. Rider, C.F.; Carlsten, C. Air Pollution and DNA Methylation: Effects of Exposure in Humans. Clin. Epigenet. 2019, 11, 131. [Google Scholar] [CrossRef] [PubMed]
  12. Shukla, A.; Bunkar, N.; Kumar, R.; Bhargava, A.; Tiwari, R.; Chaudhury, K.; Goryacheva, I.Y.; Mishra, P.K. Air Pollution Associated Epigenetic Modifications: Transgenerational Inheritance and Underlying Molecular Mechanisms. Sci. Total Environ. 2019, 656, 760–777. [Google Scholar] [CrossRef] [PubMed]
  13. van Veldhoven, K.; Kiss, A.; Keski-Rahkonen, P.; Robinot, N.; Scalbert, A.; Cullinan, P.; Chung, K.F.; Collins, P.; Sinharay, R.; Barratt, B.M.; et al. Impact of Short-Term Traffic-Related Air Pollution on the Metabolome—Results from Two Metabolome-Wide Experimental Studies. Environ. Int. 2019, 123, 124–131. [Google Scholar] [CrossRef] [PubMed]
  14. Vlaanderen, J.J.; Janssen, N.A.; Hoek, G.; Keski-Rahkonen, P.; Barupal, D.K.; Cassee, F.R.; Gosens, I.; Strak, M.; Steenhof, M.; Lan, Q.; et al. The Impact of Ambient Air Pollution on the Human Blood Metabolome. Environ. Res. 2017, 156, 341–348. [Google Scholar] [CrossRef] [PubMed]
  15. Yang, L.; Hou, X.-Y.; Wei, Y.; Thai, P.; Chai, F. Biomarkers of the Health Outcomes Associated with Ambient Particulate Matter Exposure. Sci. Total Environ. 2017, 579, 1446–1459. [Google Scholar] [CrossRef] [PubMed]
  16. Leon-Mimila, P.; Wang, J.; Huertas-Vazquez, A. Relevance of Multi-Omics Studies in Cardiovascular Diseases. Front. Cardiovasc. Med. 2019, 6, 91. [Google Scholar] [CrossRef] [PubMed]
  17. Mars, R.A.T.; Yang, Y.; Ward, T.; Houtti, M.; Priya, S.; Lekatz, H.R.; Tang, X.; Sun, Z.; Kalari, K.R.; Korem, T.; et al. Longitudinal Multi-Omics Reveals Subset-Specific Mechanisms Underlying Irritable Bowel Syndrome. Cell 2020, 182, 1460–1473. [Google Scholar] [CrossRef]
  18. Schüssler-Fiorenza Rose, S.M.; Contrepois, K.; Moneghetti, K.J.; Zhou, W.; Mishra, T.; Mataraso, S.; Dagan-Rosenfeld, O.; Ganz, A.B.; Dunn, J.; Hornburg, D.; et al. A Longitudinal Big Data Approach for Precision Health. Nat. Med. 2019, 25, 792–804. [Google Scholar] [CrossRef]
  19. Beale, D.J.; Karpe, A.V.; Ahmed, W. Beyond Metabolomics: A Review of Multi-Omics-Based Approaches. In Microbial Metabolomics: Applications in Clinical, Environmental, and Industrial Microbiology; Beale, D.J., Kouremenos, K.A., Palombo, E.A., Eds.; Springer International Publishing: Cham, Switzerland, 2016; pp. 289–312. ISBN 978-3-319-46326-1. [Google Scholar]
  20. Hasin, Y.; Seldin, M.; Lusis, A. Multi-Omics Approaches to Disease. Genome Biol. 2017, 18, 83. [Google Scholar] [CrossRef]
  21. Chu, S.H.; Huang, M.; Kelly, R.S.; Benedetti, E.; Siddiqui, J.K.; Zeleznik, O.A.; Pereira, A.; Herrington, D.; Wheelock, C.E.; Krumsiek, J.; et al. Integration of Metabolomic and Other Omics Data in Population-Based Study Designs: An Epidemiological Perspective. Metabolites 2019, 9, 117. [Google Scholar] [CrossRef]
  22. Everson, T.M.; Marsit, C.J. Integrating-Omics Approaches into Human Population-Based Studies of Prenatal and Early-Life Exposures. Curr. Environ. Health Rep. 2018, 5, 328–337. [Google Scholar] [CrossRef]
  23. Subramanian, I.; Verma, S.; Kumar, S.; Jere, A.; Anamika, K. Multi-Omics Data Integration, Interpretation, and Its Application. Bioinform. Biol. Insights 2020, 14, 1177932219899051. [Google Scholar] [CrossRef]
  24. Kellogg, R.A.; Dunn, J.; Snyder, M.P. Personal Omics for Precision Health. Circ. Res. 2018, 122, 1169–1171. [Google Scholar] [CrossRef]
  25. Olivier, M.; Asmis, R.; Hawkins, G.A.; Howard, T.D.; Cox, L.A. The Need for Multi-Omics Biomarker Signatures in Precision Medicine. Int. J. Mol. Sci. 2019, 20, 4781. [Google Scholar] [CrossRef] [PubMed]
  26. Riggs, D.W.; Yeager, R.A.; Bhatnagar, A. Defining the Human Envirome. Circ. Res. 2018, 122, 1259–1275. [Google Scholar] [CrossRef] [PubMed]
  27. Savaryn, J.P.; Catherman, A.D.; Thomas, P.M.; Abecassis, M.M.; Kelleher, N.L. The Emergence of Top-down Proteomics in Clinical Research. Genome Med. 2013, 5, 53. [Google Scholar] [CrossRef] [PubMed]
  28. Dedeurwaerder, S.; Defrance, M.; Calonne, E.; Denis, H.; Sotiriou, C.; Fuks, F. Evaluation of the Infinium Methylation 450K Technology. Epigenomics 2011, 3, 771–784. [Google Scholar] [CrossRef] [PubMed]
  29. Kanehisa, M.; Furumichi, M.; Tanabe, M.; Sato, Y.; Morishima, K. KEGG: New Perspectives on Genomes, Pathways, Diseases and Drugs. Nucleic Acids Res. 2017, 45, D353–D361. [Google Scholar] [CrossRef]
  30. Xia, J.; Psychogios, N.; Young, N.; Wishart, D.S. MetaboAnalyst: A Web Server for Metabolomic Data Analysis and Interpretation. Nucleic Acids Res. 2009, 37, W652–W660. [Google Scholar] [CrossRef] [PubMed]
  31. Soma-Pillay, P.; Nelson-Piercy, C.; Tolppanen, H.; Mebazaa, A. Physiological Changes in Pregnancy. CVJA 2016, 27, 89–94. [Google Scholar] [CrossRef]
  32. Hill, D.P.; Smith, B.; McAndrews-Hill, M.S.; Blake, J.A. Gene Ontology Annotations: What They Mean and Where They Come From. BMC Bioinform. 2008, 9, S2. [Google Scholar] [CrossRef]
  33. Kanehisa, M.; Sato, Y.; Kawashima, M.; Furumichi, M.; Tanabe, M. KEGG as a Reference Resource for Gene and Protein Annotation. Nucleic Acids Res. 2016, 44, D457–D462. [Google Scholar] [CrossRef] [PubMed]
  34. Aoki-Kinoshita, K.F. Overview of KEGG Applications to Omics-Related Research. J. Pestic. Sci. 2006, 31, 296–299. [Google Scholar] [CrossRef]
  35. Zahn-Zabal, M.; Michel, P.-A.; Gateau, A.; Nikitin, F.; Schaeffer, M.; Audot, E.; Gaudet, P.; Duek, P.D.; Teixeira, D.; Rech de Laval, V.; et al. The neXtProt Knowledgebase in 2020: Data, Tools and Usability Improvements. Nucleic Acids Res. 2020, 48, D328–D334. [Google Scholar] [CrossRef]
  36. Kanehisa, M. KEGG: Kyoto Encyclopedia of Genes and Genomes. Nucleic Acids Res. 2000, 28, 27–30. [Google Scholar] [CrossRef] [PubMed]
  37. Gillespie, M.; Jassal, B.; Stephan, R.; Milacic, M.; Rothfels, K.; Senff-Ribeiro, A.; Griss, J.; Sevilla, C.; Matthews, L.; Gong, C.; et al. The Reactome Pathway Knowledgebase 2022. Nucleic Acids Res. 2022, 50, D687–D692. [Google Scholar] [CrossRef] [PubMed]
  38. Lu, Y.; Pang, Z.; Xia, J. Comprehensive Investigation of Pathway Enrichment Methods for Functional Interpretation of LC–MS Global Metabolomics Data. Brief. Bioinform. 2023, 24, bbac553. [Google Scholar] [CrossRef]
  39. Jiang, D.; Armour, C.R.; Hu, C.; Mei, M.; Tian, C.; Sharpton, T.J.; Jiang, Y. Microbiome Multi-Omics Network Analysis: Statistical Considerations, Limitations, and Opportunities. Front. Genet. 2019, 10, 995. [Google Scholar] [CrossRef]
  40. Zhou, G.; Pang, Z.; Lu, Y.; Ewald, J.; Xia, J. OmicsNet 2.0: A Web-Based Platform for Multi-Omics Integration and Network Visual Analytics. Nucleic Acids Res. 2022, 50, W527–W533. [Google Scholar] [CrossRef]
  41. Bind, M.-A.; Lepeule, J.; Zanobetti, A.; Gasparrini, A.; Baccarelli, A.A.; Coull, B.A.; Tarantini, L.; Vokonas, P.S.; Koutrakis, P.; Schwartz, J. Air Pollution and Gene-Specific Methylation in the Normative Aging Study: Association, Effect Modification, and Mediation Analysis. Epigenetics 2014, 9, 448–458. [Google Scholar] [CrossRef]
  42. Dai, L.; Mehta, A.; Mordukhovich, I.; Just, A.C.; Shen, J.; Hou, L.; Koutrakis, P.; Sparrow, D.; Vokonas, P.S.; Baccarelli, A.A.; et al. Differential DNA Methylation and PM2.5 Species in a 450K Epigenome-Wide Association Study. Epigenetics 2017, 12, 139–148. [Google Scholar] [CrossRef]
  43. Wang, C.; Cardenas, A.; Hutchinson, J.N.; Just, A.; Heiss, J.; Hou, L.; Zheng, Y.; Coull, B.A.; Kosheleva, A.; Koutrakis, P.; et al. Short- and Intermediate-Term Exposure to Ambient Fine Particulate Elements and Leukocyte Epigenome-Wide DNA Methylation in Older Men: The Normative Aging Study. Environ. Int. 2022, 158, 106955. [Google Scholar] [CrossRef]
  44. Wang, C.; Koutrakis, P.; Gao, X.; Baccarelli, A.; Schwartz, J. Associations of Annual Ambient PM2.5 Components with DNAm PhenoAge Acceleration in Elderly Men: The Normative Aging Study. Environ. Pollut. 2020, 258, 113690. [Google Scholar] [CrossRef] [PubMed]
  45. Ward-Caviness, C.K.; Nwanaji-Enwerem, J.C.; Wolf, K.; Wahl, S.; Colicino, E.; Trevisi, L.; Kloog, I.; Just, A.C.; Vokonas, P.; Cyrys, J.; et al. Long-Term Exposure to Air Pollution Is Associated with Biological Aging. Oncotarget 2016, 7, 74510–74525. [Google Scholar] [CrossRef] [PubMed]
  46. Carmona, J.J.; Sofer, T.; Hutchinson, J.; Cantone, L.; Coull, B.; Maity, A.; Vokonas, P.; Lin, X.; Schwartz, J.; Baccarelli, A.A. Short-Term Airborne Particulate Matter Exposure Alters the Epigenetic Landscape of Human Genes Associated with the Mitogen-Activated Protein Kinase Network: A Cross-Sectional Study. Environ. Health 2014, 13, 94. [Google Scholar] [CrossRef] [PubMed]
  47. Nwanaji-Enwerem, J.C.; Bind, M.-A.; Dai, L.; Oulhote, Y.; Colicino, E.; Di, Q.; Just, A.C.; Hou, L.; Vokonas, P.; Coull, B.A.; et al. Editor’s Highlight: Modifying Role of Endothelial Function Gene Variants on the Association of Long-Term PM2.5 Exposure with Blood DNA Methylation Age: The VA Normative Aging Study. Toxicol. Sci. 2017, 158, 116–126. [Google Scholar] [CrossRef] [PubMed]
  48. Nwanaji-Enwerem, J.C.; Dai, L.; Colicino, E.; Oulhote, Y.; Di, Q.; Kloog, I.; Just, A.C.; Hou, L.; Vokonas, P.; Baccarelli, A.A.; et al. Associations between Long-Term Exposure to PM2.5 Component Species and Blood DNA Methylation Age in the Elderly: The VA Normative Aging Study. Environ. Int. 2017, 102, 57–65. [Google Scholar] [CrossRef]
  49. Panni, T.; Mehta, A.J.; Schwartz, J.D.; Baccarelli, A.A.; Just, A.C.; Wolf, K.; Wahl, S.; Cyrys, J.; Kunze, S.; Strauch, K.; et al. Genome-Wide Analysis of DNA Methylation and Fine Particulate Matter Air Pollution in Three Study Populations: KORA F3, KORA F4, and the Normative Aging Study. Environ. Health Perspect. 2016, 124, 983–990. [Google Scholar] [CrossRef]
  50. Madrigano, J.; Baccarelli, A.; Mittleman, M.A.; Wright, R.O.; Sparrow, D.; Vokonas, P.S.; Tarantini, L.; Schwartz, J. Prolonged Exposure to Particulate Pollution, Genes Associated with Glutathione Pathways, and DNA Methylation in a Cohort of Older Men. Environ. Health Perspect. 2011, 119, 977–982. [Google Scholar] [CrossRef]
  51. De F.C. Lichtenfels, A.J.; Van Der Plaat, D.A.; De Jong, K.; Van Diemen, C.C.; Postma, D.S.; Nedeljkovic, I.; Van Duijn, C.M.; Amin, N.; La Bastide-van Gemert, S.; De Vries, M.; et al. Long-Term Air Pollution Exposure, Genome-Wide DNA Methylation and Lung Function in the LifeLines Cohort Study. Environ. Health Perspect. 2018, 126, 027004. [Google Scholar] [CrossRef]
  52. Gondalia, R.; Baldassari, A.; Holliday, K.M.; Justice, A.E.; Méndez-Giráldez, R.; Stewart, J.D.; Liao, D.; Yanosky, J.D.; Brennan, K.J.M.; Engel, S.M.; et al. Methylome-Wide Association Study Provides Evidence of Particulate Matter Air Pollution-Associated DNA Methylation. Environ. Int. 2019, 132, 104723. [Google Scholar] [CrossRef] [PubMed]
  53. Holliday, K.M.; Gondalia, R.; Baldassari, A.; Justice, A.E.; Stewart, J.D.; Liao, D.; Yanosky, J.D.; Jordahl, K.M.; Bhatti, P.; Assimes, T.L.; et al. Gaseous Air Pollutants and DNA Methylation in a Methylome-Wide Association Study of an Ethnically and Environmentally Diverse Population of U.S. Adults. Environ. Res. 2022, 212, 113360. [Google Scholar] [CrossRef] [PubMed]
  54. Gondalia, R.; Baldassari, A.; Holliday, K.M.; Justice, A.E.; Stewart, J.D.; Liao, D.; Yanosky, J.D.; Engel, S.M.; Sheps, D.; Jordahl, K.M.; et al. Epigenetically Mediated Electrocardiographic Manifestations of Sub-Chronic Exposures to Ambient Particulate Matter Air Pollution in the Women’s Health Initiative and Atherosclerosis Risk in Communities Study. Environ. Res. 2021, 198, 111211. [Google Scholar] [CrossRef]
  55. Sayols-Baixeras, S.; Fernández-Sanlés, A.; Prats-Uribe, A.; Subirana, I.; Plusquin, M.; Künzli, N.; Marrugat, J.; Basagaña, X.; Elosua, R. Association between Long-Term Air Pollution Exposure and DNA Methylation: The REGICOR Study. Environ. Res. 2019, 176, 108550. [Google Scholar] [CrossRef] [PubMed]
  56. Plusquin, M.; Guida, F.; Polidoro, S.; Vermeulen, R.; Raaschou-Nielsen, O.; Campanella, G.; Hoek, G.; Kyrtopoulos, S.A.; Georgiadis, P.; Naccarati, A.; et al. DNA Methylation and Exposure to Ambient Air Pollution in Two Prospective Cohorts. Environ. Int. 2017, 108, 127–136. [Google Scholar] [CrossRef] [PubMed]
  57. Chi, G.C.; Liu, Y.; MacDonald, J.W.; Reynolds, L.M.; Enquobahrie, D.A.; Fitzpatrick, A.L.; Kerr, K.F.; Budoff, M.J.; Lee, S.-I.; Siscovick, D.; et al. Epigenome-Wide Analysis of Long-Term Air Pollution Exposure and DNA Methylation in Monocytes: Results from the Multi-Ethnic Study of Atherosclerosis. Epigenetics 2022, 17, 1900028. [Google Scholar] [CrossRef]
  58. Chi, G.C.; Liu, Y.; MacDonald, J.W.; Barr, R.G.; Donohue, K.M.; Hensley, M.D.; Hou, L.; McCall, C.E.; Reynolds, L.M.; Siscovick, D.S.; et al. Long-Term Outdoor Air Pollution and DNA Methylation in Circulating Monocytes: Results from the Multi-Ethnic Study of Atherosclerosis (MESA). Environ. Health 2016, 15, 119. [Google Scholar] [CrossRef]
  59. White, A.J.; Kresovich, J.K.; Keller, J.P.; Xu, Z.; Kaufman, J.D.; Weinberg, C.R.; Taylor, J.A.; Sandler, D.P. Air Pollution, Particulate Matter Composition and Methylation-Based Biologic Age. Environ. Int. 2019, 132, 105071. [Google Scholar] [CrossRef]
  60. Wang, C.; O’Brien, K.M.; Xu, Z.; Sandler, D.P.; Taylor, J.A.; Weinberg, C.R. Long-Term Ambient Fine Particulate Matter and DNA Methylation in Inflammation Pathways: Results from the Sister Study. Epigenetics 2020, 15, 524–535. [Google Scholar] [CrossRef]
  61. Fang, J.; Gao, Y.; Zhang, M.; Jiang, Q.; Chen, C.; Gao, X.; Liu, Y.; Dong, H.; Tang, S.; Li, T.; et al. Personal PM2.5 Elemental Components, Decline of Lung Function, and the Role of DNA Methylation on Inflammation-Related Genes in Older Adults: Results and Implications of the BAPE Study. Environ. Sci. Technol. 2022, 56, 15990–16000. [Google Scholar] [CrossRef]
  62. Shi, W.; Tang, S.; Fang, J.; Cao, Y.; Chen, C.; Li, T.; Gao, X.; Shi, X. Epigenetic Age Stratifies the Risk of Blood Pressure Elevation Related to Short-Term PM2.5 Exposure in Older Adults. Environ. Res. 2022, 212, 113507. [Google Scholar] [CrossRef]
  63. Tantoh, D.M.; Lee, K.-J.; Nfor, O.N.; Liaw, Y.-C.; Lin, C.; Chu, H.-W.; Chen, P.-H.; Hsu, S.-Y.; Liu, W.-H.; Ho, C.-C.; et al. Methylation at Cg05575921 of a Smoking-Related Gene (AHRR) in Non-Smoking Taiwanese Adults Residing in Areas with Different PM2.5 Concentrations. Clin. Epigenet. 2019, 11, 69. [Google Scholar] [CrossRef] [PubMed]
  64. Tantoh, D.M.; Wu, M.-C.; Chuang, C.-C.; Chen, P.-H.; Tyan, Y.S.; Nfor, O.N.; Lu, W.-Y.; Liaw, Y.-P. AHRR Cg05575921 Methylation in Relation to Smoking and PM2.5 Exposure among Taiwanese Men and Women. Clin. Epigenet. 2020, 12, 117. [Google Scholar] [CrossRef] [PubMed]
  65. Mostafavi, N.; Vermeulen, R.; Ghantous, A.; Hoek, G.; Probst-Hensch, N.; Herceg, Z.; Tarallo, S.; Naccarati, A.; Kleinjans, J.C.S.; Imboden, M.; et al. Acute Changes in DNA Methylation in Relation to 24 h Personal Air Pollution Exposure Measurements: A Panel Study in Four European Countries. Environ. Int. 2018, 120, 11–21. [Google Scholar] [CrossRef] [PubMed]
  66. Eze, I.C.; Jeong, A.; Schaffner, E.; Rezwan, F.I.; Ghantous, A.; Foraster, M.; Vienneau, D.; Kronenberg, F.; Herceg, Z.; Vineis, P.; et al. Genome-Wide DNA Methylation in Peripheral Blood and Long-Term Exposure to Source-Specific Transportation Noise and Air Pollution: The SAPALDIA Study. Environ. Health Perspect. 2020, 128, 067003. [Google Scholar] [CrossRef] [PubMed]
  67. Baranyi, G.; Deary, I.J.; McCartney, D.L.; Harris, S.E.; Shortt, N.; Reis, S.; Russ, T.C.; Ward Thompson, C.; Vieno, M.; Cox, S.R.; et al. Life-Course Exposure to Air Pollution and Biological Ageing in the Lothian Birth Cohort 1936. Environ. Int. 2022, 169, 107501. [Google Scholar] [CrossRef]
  68. Monti, P.; Iodice, S.; Tarantini, L.; Sacchi, F.; Ferrari, L.; Ruscica, M.; Buoli, M.; Vigna, L.; Pesatori, A.C.; Bollati, V. Effects of PM Exposure on the Methylation of Clock Genes in A Population of Subjects with Overweight or Obesity. Int. J. Environ. Res. Public Health 2021, 18, 1122. [Google Scholar] [CrossRef]
  69. Bind, M.-A.; Baccarelli, A.; Zanobetti, A.; Tarantini, L.; Suh, H.; Vokonas, P.; Schwartz, J. Air Pollution and Markers of Coagulation, Inflammation, and Endothelial Function: Associations and Epigene-Environment Interactions in an Elderly Cohort. Epidemiology 2012, 23, 332–340. [Google Scholar] [CrossRef] [PubMed]
  70. Alexeeff, S.E.; Coull, B.A.; Gryparis, A.; Suh, H.; Sparrow, D.; Vokonas, P.S.; Schwartz, J. Medium-Term Exposure to Traffic-Related Air Pollution and Markers of Inflammation and Endothelial Function. Environ. Health Perspect. 2011, 119, 481–486. [Google Scholar] [CrossRef]
  71. Bind, M.-A.; Peters, A.; Koutrakis, P.; Coull, B.; Vokonas, P.; Schwartz, J. Quantile Regression Analysis of the Distributional Effects of Air Pollution on Blood Pressure, Heart Rate Variability, Blood Lipids, and Biomarkers of Inflammation in Elderly American Men: The Normative Aging Study. Environ. Health Perspect. 2016, 124, 1189–1198. [Google Scholar] [CrossRef]
  72. Davis, E.; Malig, B.; Broadwin, R.; Ebisu, K.; Basu, R.; Gold, E.B.; Qi, L.; Derby, C.A.; Park, S.K.; Wu, X. Association between Coarse Particulate Matter and Inflammatory and Hemostatic Markers in a Cohort of Midlife Women. Environ. Health 2020, 19, 111. [Google Scholar] [CrossRef] [PubMed]
  73. Wu, X.; Basu, R.; Malig, B.; Broadwin, R.; Ebisu, K.; Gold, E.B.; Qi, L.; Derby, C.; Green, R.S. Association between Gaseous Air Pollutants and Inflammatory, Hemostatic and Lipid Markers in a Cohort of Midlife Women. Environ. Int. 2017, 107, 131–139. [Google Scholar] [CrossRef] [PubMed]
  74. Green, R.; Broadwin, R.; Malig, B.; Basu, R.; Gold, E.B.; Qi, L.; Sternfeld, B.; Bromberger, J.T.; Greendale, G.A.; Kravitz, H.M.; et al. Long-and Short-Term Exposure To Air Pollution and Inflammatory/Hemostatic Markers in Midlife Women. Epidemiology 2016, 27, 211–220. [Google Scholar] [CrossRef] [PubMed]
  75. Lanki, T.; Hampel, R.; Tiittanen, P.; Andrich, S.; Beelen, R.; Brunekreef, B.; Dratva, J.; De Faire, U.; Fuks, K.B.; Hoffmann, B.; et al. Air Pollution from Road Traffic and Systemic Inflammation in Adults: A Cross-Sectional Analysis in the European ESCAPE Project. Environ. Health Perspect. 2015, 123, 785–791. [Google Scholar] [CrossRef] [PubMed]
  76. Rückerl, R.; Hampel, R.; Breitner, S.; Cyrys, J.; Kraus, U.; Carter, J.; Dailey, L.; Devlin, R.B.; Diaz-Sanchez, D.; Koenig, W.; et al. Associations between Ambient Air Pollution and Blood Markers of Inflammation and Coagulation/Fibrinolysis in Susceptible Populations. Environ. Int. 2014, 70, 32–49. [Google Scholar] [CrossRef]
  77. Pilz, V.; Wolf, K.; Breitner, S.; Rückerl, R.; Koenig, W.; Rathmann, W.; Cyrys, J.; Peters, A.; Schneider, A. C-Reactive Protein (CRP) and Long-Term Air Pollution with a Focus on Ultrafine Particles. Int. J. Hyg. Environ. Health 2018, 221, 510–518. [Google Scholar] [CrossRef]
  78. Viehmann, A.; Hertel, S.; Fuks, K.; Eisele, L.; Moebus, S.; Möhlenkamp, S.; Nonnemacher, M.; Jakobs, H.; Erbel, R.; Jöckel, K.-H.; et al. Long-Term Residential Exposure to Urban Air Pollution, and Repeated Measures of Systemic Blood Markers of Inflammation and Coagulation. Occup. Environ. Med. 2015, 72, 656–663. [Google Scholar] [CrossRef]
  79. Hertel, S.; Viehmann, A.; Moebus, S.; Mann, K.; Bröcker-Preuss, M.; Möhlenkamp, S.; Nonnemacher, M.; Erbel, R.; Jakobs, H.; Memmesheimer, M.; et al. Influence of Short-Term Exposure to Ultrafine and Fine Particles on Systemic Inflammation. Eur. J. Epidemiol. 2010, 25, 581–592. [Google Scholar] [CrossRef]
  80. Li, W.; Dorans, K.S.; Wilker, E.H.; Rice, M.B.; Ljungman, P.L.; Schwartz, J.D.; Coull, B.A.; Koutrakis, P.; Gold, D.R.; Keaney, J.F.; et al. Short-Term Exposure to Ambient Air Pollution and Circulating Biomarkers of Endothelial Cell Activation: The Framingham Heart Study. Environ. Res. 2019, 171, 36–43. [Google Scholar] [CrossRef]
  81. Li, W.; Dorans, K.S.; Wilker, E.H.; Rice, M.B.; Ljungman, P.L.; Schwartz, J.D.; Coull, B.A.; Koutrakis, P.; Gold, D.R.; Keaney, J.F.; et al. Short-Term Exposure to Ambient Air Pollution and Biomarkers of Systemic Inflammation: The Framingham Heart Study. ATVB 2017, 37, 1793–1800. [Google Scholar] [CrossRef]
  82. Xu, H.; Wang, T.; Liu, S.; Brook, R.D.; Feng, B.; Zhao, Q.; Song, X.; Yi, T.; Chen, J.; Zhang, Y.; et al. Extreme Levels of Air Pollution Associated With Changes in Biomarkers of Atherosclerotic Plaque Vulnerability and Thrombogenicity in Healthy Adults: The Beijing AIRCHD Study. Circ. Res. 2019, 124, e30–e43. [Google Scholar] [CrossRef] [PubMed]
  83. Feng, B.; Liu, C.; Yi, T.; Song, X.; Wang, Y.; Liu, S.; Chen, J.; Zhao, Q.; Zhang, Y.; Wang, T.; et al. Perturbation of Amino Acid Metabolism Mediates Air Pollution Associated Vascular Dysfunction in Healthy Adults. Environ. Res. 2021, 201, 111512. [Google Scholar] [CrossRef] [PubMed]
  84. Fiorito, G.; Vlaanderen, J.; Polidoro, S.; Gulliver, J.; Galassi, C.; Ranzi, A.; Krogh, V.; Grioni, S.; Agnoli, C.; Sacerdote, C.; et al. Oxidative Stress and Inflammation Mediate the Effect of Air Pollution on Cardio- and Cerebrovascular Disease: A Prospective Study in Nonsmokers: Effect of Air Pollution on Cardio- and Cerebrovascular Disease. Environ. Mol. Mutagen. 2018, 59, 234–246. [Google Scholar] [CrossRef] [PubMed]
  85. Corlin, L.; Woodin, M.; Hart, J.E.; Simon, M.C.; Gute, D.M.; Stowell, J.; Tucker, K.L.; Durant, J.L.; Brugge, D. Longitudinal Associations of Long-Term Exposure to Ultrafine Particles with Blood Pressure and Systemic Inflammation in Puerto Rican Adults. Environ. Health 2018, 17, 33. [Google Scholar] [CrossRef]
  86. Azzouz, M.; Xu, Y.; Barregard, L.; Fagerberg, B.; Zöller, B.; Molnár, P.; Oudin, A.; Spanne, M.; Engström, G.; Stockfelt, L. Air Pollution and Biomarkers of Cardiovascular Disease and Inflammation in the Malmö Diet and Cancer Cohort. Environ. Health 2022, 21, 39. [Google Scholar] [CrossRef]
  87. Tripathy, S.; Marsland, A.L.; Kinnee, E.J.; Tunno, B.J.; Manuck, S.B.; Gianaros, P.J.; Clougherty, J.E. Long-Term Ambient Air Pollution Exposures and Circulating and Stimulated Inflammatory Mediators in a Cohort of Midlife Adults. Environ. Health Perspect. 2021, 129, 057007. [Google Scholar] [CrossRef]
  88. Elbarbary, M.; Oganesyan, A.; Honda, T.; Morgan, G.; Guo, Y.; Guo, Y.; Negin, J. Systemic Inflammation (C-Reactive Protein) in Older Chinese Adults Is Associated with Long-Term Exposure to Ambient Air Pollution. Int. J. Environ. Res. Public Health 2021, 18, 3258. [Google Scholar] [CrossRef]
  89. Iyer, H.S.; Hart, J.E.; Fiffer, M.R.; Elliott, E.G.; Yanosky, J.D.; Kaufman, J.D.; Puett, R.C.; Laden, F. Impacts of Long-Term Ambient Particulate Matter and Gaseous Pollutants on Circulating Biomarkers of Inflammation in Male and Female Health Professionals. Environ. Res. 2022, 214, 113810. [Google Scholar] [CrossRef]
  90. Dauchet, L.; Hulo, S.; Cherot-Kornobis, N.; Matran, R.; Amouyel, P.; Edmé, J.-L.; Giovannelli, J. Short-Term Exposure to Air Pollution: Associations with Lung Function and Inflammatory Markers in Non-Smoking, Healthy Adults. Environ. Int. 2018, 121, 610–619. [Google Scholar] [CrossRef]
  91. Mostafavi, N.; Vlaanderen, J.; Chadeau-Hyam, M.; Beelen, R.; Modig, L.; Palli, D.; Bergdahl, I.A.; Vineis, P.; Hoek, G.; Kyrtopoulos, S.A.; et al. Inflammatory Markers in Relation to Long-Term Air Pollution. Environ. Int. 2015, 81, 1–7. [Google Scholar] [CrossRef]
  92. Hajat, A.; Allison, M.; Diez-Roux, A.V.; Jenny, N.S.; Jorgensen, N.W.; Szpiro, A.A.; Vedal, S.; Kaufman, J.D. Long-Term Exposure to Air Pollution and Markers of Inflammation, Coagulation, and Endothelial Activation: A Repeat-Measures Analysis in the Multi-Ethnic Study of Atherosclerosis (MESA). Epidemiology 2015, 26, 310–320. [Google Scholar] [CrossRef] [PubMed]
  93. Lane, K.J.; Levy, J.I.; Scammell, M.K.; Peters, J.L.; Patton, A.P.; Reisner, E.; Lowe, L.; Zamore, W.; Durant, J.L.; Brugge, D. Association of Modeled Long-Term Personal Exposure to Ultrafine Particles with Inflammatory and Coagulation Biomarkers. Environ. Int. 2016, 92–93, 173–182. [Google Scholar] [CrossRef] [PubMed]
  94. Tsai, D.-H.; Amyai, N.; Marques-Vidal, P.; Wang, J.-L.; Riediker, M.; Mooser, V.; Paccaud, F.; Waeber, G.; Vollenweider, P.; Bochud, M. Effects of Particulate Matter on Inflammatory Markers in the General Adult Population. Part. Fibre Toxicol. 2012, 9, 24. [Google Scholar] [CrossRef] [PubMed]
  95. Li, Z.; Sarnat, J.A.; Liu, K.H.; Hood, R.B.; Chang, C.-J.; Hu, X.; Tran, V.; Greenwald, R.; Chang, H.H.; Russell, A.; et al. Evaluation of the Use of Saliva Metabolome as a Surrogate of Blood Metabolome in Assessing Internal Exposures to Traffic-Related Air Pollution. Environ. Sci. Technol. 2022, 56, 6525–6536. [Google Scholar] [CrossRef]
  96. Liang, D.; Moutinho, J.L.; Golan, R.; Yu, T.; Ladva, C.N.; Niedzwiecki, M.; Walker, D.I.; Sarnat, S.E.; Chang, H.H.; Greenwald, R.; et al. Use of High-Resolution Metabolomics for the Identification of Metabolic Signals Associated with Traffic-Related Air Pollution. Environ. Int. 2018, 120, 145–154. [Google Scholar] [CrossRef]
  97. Tang, Z.; Sarnat, J.A.; Weber, R.J.; Russell, A.G.; Zhang, X.; Li, Z.; Yu, T.; Jones, D.P.; Liang, D. The Oxidative Potential of Fine Particulate Matter and Biological Perturbations in Human Plasma and Saliva Metabolome. Environ. Sci. Technol. 2022, 56, 7350–7361. [Google Scholar] [CrossRef]
  98. Nassan, F.L.; Kelly, R.S.; Kosheleva, A.; Koutrakis, P.; Vokonas, P.S.; Lasky-Su, J.A.; Schwartz, J.D. Metabolomic Signatures of the Long-Term Exposure to Air Pollution and Temperature. Environ. Health 2021, 20, 3. [Google Scholar] [CrossRef]
  99. Nassan, F.L.; Wang, C.; Kelly, R.S.; Lasky-Su, J.A.; Vokonas, P.S.; Koutrakis, P.; Schwartz, J.D. Ambient PM2.5 Species and Ultrafine Particle Exposure and Their Differential Metabolomic Signatures. Environ. Int. 2021, 151, 106447. [Google Scholar] [CrossRef]
  100. Liao, J.; Gheissari, R.; Thomas, D.C.; Gilliland, F.D.; Lurmann, F.; Islam, K.T.; Chen, Z. Transcriptomic and Metabolomic Associations with Exposures to Air Pollutants among Young Adults with Childhood Asthma History. Environ. Pollut. 2022, 299, 118903. [Google Scholar] [CrossRef]
  101. Chen, C.; Li, H.; Niu, Y.; Liu, C.; Lin, Z.; Cai, J.; Li, W.; Ge, W.; Chen, R.; Kan, H. Impact of Short-Term Exposure to Fine Particulate Matter Air Pollution on Urinary Metabolome: A Randomized, Double-Blind, Crossover Trial. Environ. Int. 2019, 130, 104878. [Google Scholar] [CrossRef]
  102. Yao, Y.; Schneider, A.; Wolf, K.; Zhang, S.; Wang-Sattler, R.; Peters, A.; Breitner, S. Longitudinal Associations between Metabolites and Long-Term Exposure to Ambient Air Pollution: Results from the KORA Cohort Study. Environ. Int. 2022, 170, 107632. [Google Scholar] [CrossRef] [PubMed]
  103. Ward-Caviness, C.K.; Breitner, S.; Wolf, K.; Cyrys, J.; Kastenmüller, G.; Wang-Sattler, R.; Schneider, A.; Peters, A. Short-Term NO 2 Exposure Is Associated with Long-Chain Fatty Acids in Prospective Cohorts from Augsburg, Germany: Results from an Analysis of 138 Metabolites and Three Exposures. Int. J. Epidemiol. 2016, 45, 1528–1538. [Google Scholar] [CrossRef] [PubMed]
  104. Jeong, A.; Fiorito, G.; Keski-Rahkonen, P.; Imboden, M.; Kiss, A.; Robinot, N.; Gmuender, H.; Vlaanderen, J.; Vermeulen, R.; Kyrtopoulos, S.; et al. Perturbation of Metabolic Pathways Mediates the Association of Air Pollutants with Asthma and Cardiovascular Diseases. Environ. Int. 2018, 119, 334–345. [Google Scholar] [CrossRef] [PubMed]
  105. Ladva, C.N.; Golan, R.; Liang, D.; Greenwald, R.; Walker, D.I.; Uppal, K.; Raysoni, A.U.; Tran, V.; Yu, T.; Flanders, W.D.; et al. Particulate Metal Exposures Induce Plasma Metabolome Changes in a Commuter Panel Study. PLoS ONE 2018, 13, e0203468. [Google Scholar] [CrossRef]
  106. Liang, D.; Ladva, C.N.; Golan, R.; Yu, T.; Walker, D.I.; Sarnat, S.E.; Greenwald, R.; Uppal, K.; Tran, V.; Jones, D.P.; et al. Perturbations of the Arginine Metabolome Following Exposures to Traffic-Related Air Pollution in a Panel of Commuters with and without Asthma. Environ. Int. 2019, 127, 503–513. [Google Scholar] [CrossRef] [PubMed]
  107. Walker, D.I.; Lane, K.J.; Liu, K.; Uppal, K.; Patton, A.P.; Durant, J.L.; Jones, D.P.; Brugge, D.; Pennell, K.D. Metabolomic Assessment of Exposure to Near-Highway Ultrafine Particles. J. Expo. Sci. Environ. Epidemiol. 2019, 29, 469–483. [Google Scholar] [CrossRef]
  108. Hood, R.B.; Liang, D.; Tang, Z.; Kloog, I.; Schwartz, J.; Laden, F.; Jones, D.; Gaskins, A.J. Length of PM2.5 Exposure and Alterations in the Serum Metabolome among Women Undergoing Infertility Treatment. Environ. Epidemiol. 2022, 6, e191. [Google Scholar] [CrossRef] [PubMed]
  109. Wang, T.; Han, Y.; Li, H.; Wang, Y.; Chen, X.; Chen, W.; Qiu, X.; Gong, J.; Li, W.; Zhu, T. Proinflammatory Lipid Signals Trigger the Health Effects of Air Pollution in Individuals with Prediabetes. Environ. Pollut. 2021, 290, 118008. [Google Scholar] [CrossRef]
  110. Menni, C.; Metrustry, S.J.; Mohney, R.P.; Beevers, S.; Barratt, B.; Spector, T.D.; Kelly, F.J.; Valdes, A.M. Circulating Levels of Antioxidant Vitamins Correlate with Better Lung Function and Reduced Exposure to Ambient Pollution. Am. J. Respir. Crit. Care Med. 2015, 191, 1203–1207. [Google Scholar] [CrossRef]
  111. Khan, A.T.; Gogarten, S.M.; McHugh, C.P.; Stilp, A.M.; Sofer, T.; Bowers, M.L.; Wong, Q.; Cupples, L.A.; Hidalgo, B.; Johnson, A.D.; et al. Recommendations on the Use and Reporting of Race, Ethnicity, and Ancestry in Genetic Research: Experiences from the NHLBI TOPMed Program. Cell Genom. 2022, 2, 100155. [Google Scholar] [CrossRef]
  112. Zhang, Z.; Chang, L.; Lau, A.K.; Chan, T.-C.; Chieh Chuang, Y.; Chan, J.; Lin, C.; Kai Jiang, W.; Dear, K.; Zee, B.C.; et al. Satellite-Based Estimates of Long-Term Exposure to Fine Particulate Matter Are Associated with C-Reactive Protein in 30,034 Taiwanese Adults. Int. J. Epidemiol. 2017, 46, 1126–1136. [Google Scholar] [CrossRef]
  113. Breitner, S.; Schneider, A.; Devlin, R.B.; Ward-Caviness, C.K.; Diaz-Sanchez, D.; Neas, L.M.; Cascio, W.E.; Peters, A.; Hauser, E.R.; Shah, S.H.; et al. Associations among Plasma Metabolite Levels and Short-Term Exposure to PM2.5 and Ozone in a Cardiac Catheterization Cohort. Environ. Int. 2016, 97, 76–84. [Google Scholar] [CrossRef] [PubMed]
  114. Chen, Z.; Newgard, C.B.; Kim, J.S.; IIkayeva, O.; Alderete, T.L.; Thomas, D.C.; Berhane, K.; Breton, C.; Chatzi, L.; Bastain, T.M.; et al. Near-Roadway Air Pollution Exposure and Altered Fatty Acid Oxidation among Adolescents and Young Adults—The Interplay with Obesity. Environ. Int. 2019, 130, 104935. [Google Scholar] [CrossRef] [PubMed]
  115. Gao, N.; Xu, W.; Ji, J.; Yang, Y.; Wang, S.-T.; Wang, J.; Chen, X.; Meng, S.; Tian, X.; Xu, K.-F. Lung Function and Systemic Inflammation Associated with Short-Term Air Pollution Exposure in Chronic Obstructive Pulmonary Disease Patients in Beijing, China. Environ. Health 2020, 19, 12. [Google Scholar] [CrossRef] [PubMed]
  116. Jiang, M.; Wang, X.; Gao, X.; Cardenas, A.; Baccarelli, A.A.; Guo, X.; Huang, J.; Wu, S. Association of DNA Methylation in Circulating CD4+T Cells with Short-Term PM2.5 Pollution Waves: A Quasi-Experimental Study of Healthy Young Adults. Ecotoxicol. Environ. Saf. 2022, 239, 113634. [Google Scholar] [CrossRef] [PubMed]
  117. Sun, Y.; Huang, J.; Zhao, Y.; Xue, L.; Li, H.; Liu, Q.; Cao, H.; Peng, W.; Guo, C.; Xie, Y.; et al. Inflammatory Cytokines and DNA Methylation in Healthy Young Adults Exposure to Fine Particulate Matter: A Randomized, Double-Blind Crossover Trial of Air Filtration. J. Hazard. Mater. 2020, 398, 122817. [Google Scholar] [CrossRef]
  118. Chen, R.; Qiao, L.; Li, H.; Zhao, Y.; Zhang, Y.; Xu, W.; Wang, C.; Wang, H.; Zhao, Z.; Xu, X.; et al. Fine Particulate Matter Constituents, Nitric Oxide Synthase DNA Methylation and Exhaled Nitric Oxide. Environ. Sci. Technol. 2015, 49, 11859–11865. [Google Scholar] [CrossRef]
  119. Zhang, Q.; Wang, W.; Niu, Y.; Xia, Y.; Lei, X.; Huo, J.; Zhao, Q.; Zhang, Y.; Duan, Y.; Cai, J.; et al. The Effects of Fine Particulate Matter Constituents on Exhaled Nitric Oxide and DNA Methylation in the Arginase–Nitric Oxide Synthase Pathway. Environ. Int. 2019, 131, 105019. [Google Scholar] [CrossRef]
  120. Tobaldini, E.; Bollati, V.; Prado, M.; Fiorelli, E.M.; Pecis, M.; Bissolotti, G.; Albetti, B.; Cantone, L.; Favero, C.; Cogliati, C.; et al. Acute Particulate Matter Affects Cardiovascular Autonomic Modulation and IFN-γ Methylation in Healthy Volunteers. Environ. Res. 2018, 161, 97–103. [Google Scholar] [CrossRef]
  121. Husby, A. On the Use of Blood Samples for Measuring DNA Methylation in Ecological Epigenetic Studies. Integr. Comp. Biol. 2020, 60, 1558–1566. [Google Scholar] [CrossRef]
  122. Dunnet, M.J.; Ortega-Recalde, O.J.; Waters, S.A.; Weeks, R.J.; Morison, I.M.; Hore, T.A. Leukocyte-Specific DNA Methylation Biomarkers and Their Implication for Pathological Epigenetic Analysis. Epigenet. Commun. 2022, 2, 5. [Google Scholar] [CrossRef]
  123. Koestler, D.C.; Christensen, B.C.; Karagas, M.R.; Marsit, C.J.; Langevin, S.M.; Kelsey, K.T.; Wiencke, J.K.; Houseman, E.A. Blood-Based Profiles of DNA Methylation Predict the Underlying Distribution of Cell Types: A Validation Analysis. Epigenetics 2013, 8, 816–826. [Google Scholar] [CrossRef] [PubMed]
  124. Lin, Y.; Ramanathan, G.; Zhu, Y.; Yin, F.; Rea, N.D.; Lu, X.; Tseng, C.-H.; Faull, K.F.; Yoon, A.J.; Jerrett, M.; et al. Pro-Oxidative and Proinflammatory Effects after Traveling from Los Angeles to Beijing: A Biomarker-Based Natural Experiment. Circulation 2019, 140, 1995–2004. [Google Scholar] [CrossRef] [PubMed]
  125. Lei, X.; Chen, R.; Wang, C.; Shi, J.; Zhao, Z.; Li, W.; Yan, B.; Chillrud, S.; Cai, J.; Kan, H. Personal Fine Particulate Matter Constituents, Increased Systemic Inflammation, and the Role of DNA Hypomethylation. Environ. Sci. Technol. 2019, 53, 9837–9844. [Google Scholar] [CrossRef]
  126. Midouhas, E.; Kokosi, T.; Flouri, E. Neighbourhood-Level Air Pollution and Greenspace and Inflammation in Adults. Health Place 2019, 58, 102167. [Google Scholar] [CrossRef] [PubMed]
  127. Chen, S.-Y.; Chan, C.-C.; Su, T.-C. Particulate and Gaseous Pollutants on Inflammation, Thrombosis, and Autonomic Imbalance in Subjects at Risk for Cardiovascular Disease. Environ. Pollut. 2017, 223, 403–408. [Google Scholar] [CrossRef] [PubMed]
  128. Ryu, M.H.; Lau, K.S.-K.; Wooding, D.J.; Fan, S.; Sin, D.D.; Carlsten, C. Particle Depletion of Diesel Exhaust Restores Allergen-Induced Lung-Protective Surfactant Protein D in Human Lungs. Thorax 2020, 75, 640–647. [Google Scholar] [CrossRef] [PubMed]
  129. Biagioni, B.J.; Tam, S.; Chen, Y.-W.R.; Sin, D.D.; Carlsten, C. Effect of Controlled Human Exposure to Diesel Exhaust and Allergen on Airway Surfactant Protein D, Myeloperoxidase and Club (Clara) Cell Secretory Protein 16. Clin. Exp. Allergy 2016, 46, 1206–1213. [Google Scholar] [CrossRef]
  130. Mookherjee, N.; Piyadasa, H.; Ryu, M.H.; Rider, C.F.; Ezzati, P.; Spicer, V.; Carlsten, C. Inhaled Diesel Exhaust Alters the Allergen-Induced Bronchial Secretome in Humans. Eur. Respir. J. 2018, 51, 1701385. [Google Scholar] [CrossRef]
  131. Espinosa, C.; Ali, S.M.; Khan, W.; Khanam, R.; Pervin, J.; Price, J.T.; Rahman, S.; Hasan, T.; Ahmed, S.; Raqib, R.; et al. Comparative Predictive Power of Serum vs Plasma Proteomic Signatures in Feto-Maternal Medicine. AJOG Glob. Rep. 2023, 3, 100244. [Google Scholar] [CrossRef]
  132. Paul, J.; Veenstra, T.D. Separation of Serum and Plasma Proteins for In-Depth Proteomic Analysis. Separations 2022, 9, 89. [Google Scholar] [CrossRef]
  133. Sotelo-Orozco, J.; Chen, S.-Y.; Hertz-Picciotto, I.; Slupsky, C.M. A Comparison of Serum and Plasma Blood Collection Tubes for the Integration of Epidemiological and Metabolomics Data. Front. Mol. Biosci. 2021, 8, 682134. [Google Scholar] [CrossRef]
  134. Yu, Z.; Kastenmüller, G.; He, Y.; Belcredi, P.; Möller, G.; Prehn, C.; Mendes, J.; Wahl, S.; Roemisch-Margl, W.; Ceglarek, U.; et al. Differences between Human Plasma and Serum Metabolite Profiles. PLoS ONE 2011, 6, e21230. [Google Scholar] [CrossRef]
  135. Huang, Q.; Hu, D.; Wang, X.; Chen, Y.; Wu, Y.; Pan, L.; Li, H.; Zhang, J.; Deng, F.; Guo, X.; et al. The Modification of Indoor PM2.5 Exposure to Chronic Obstructive Pulmonary Disease in Chinese Elderly People: A Meet-in-Metabolite Analysis. Environ. Int. 2018, 121, 1243–1252. [Google Scholar] [CrossRef] [PubMed]
  136. Pradhan, S.N.; Das, A.; Meena, R.; Nanda, R.K.; Rajamani, P. Biofluid Metabotyping of Occupationally Exposed Subjects to Air Pollution Demonstrates High Oxidative Stress and Deregulated Amino Acid Metabolism. Sci. Rep. 2016, 6, 35972. [Google Scholar] [CrossRef]
  137. Zhang, Y.; Chu, M.; Zhang, J.; Duan, J.; Hu, D.; Zhang, W.; Yang, X.; Jia, X.; Deng, F.; Sun, Z. Urine Metabolites Associated with Cardiovascular Effects from Exposure of Size-Fractioned Particulate Matter in a Subway Environment: A Randomized Crossover Study. Environ. Int. 2019, 130, 104920. [Google Scholar] [CrossRef]
  138. Zhang, Q.; Du, X.; Li, H.; Jiang, Y.; Zhu, X.; Zhang, Y.; Niu, Y.; Liu, C.; Ji, J.; Chillrud, S.N.; et al. Cardiovascular Effects of Traffic-Related Air Pollution: A Multi-Omics Analysis from a Randomized, Crossover Trial. J. Hazard. Mater. 2022, 435, 129031. [Google Scholar] [CrossRef] [PubMed]
  139. Gouveia-Figueira, S.; Karimpour, M.; Bosson, J.A.; Blomberg, A.; Unosson, J.; Sehlstedt, M.; Pourazar, J.; Sandström, T.; Behndig, A.F.; Nording, M.L. Mass Spectrometry Profiling Reveals Altered Plasma Levels of Monohydroxy Fatty Acids and Related Lipids in Healthy Humans after Controlled Exposure to Biodiesel Exhaust. Anal. Chim. Acta 2018, 1018, 62–69. [Google Scholar] [CrossRef]
  140. Cheng, W.; Duncan, K.E.; Ghio, A.J.; Ward-Caviness, C.; Karoly, E.D.; Diaz-Sanchez, D.; Conolly, R.B.; Devlin, R.B. Changes in Metabolites Present in Lung-Lining Fluid Following Exposure of Humans to Ozone. Toxicol. Sci. 2018, 163, 430–439. [Google Scholar] [CrossRef]
  141. Lam, M.P.Y.; Ping, P.; Murphy, E. Proteomics Research in Cardiovascular Medicine and Biomarker Discovery. J. Am. Coll. Cardiol. 2016, 68, 2819–2830. [Google Scholar] [CrossRef] [PubMed]
  142. Marshall, K.D.; Edwards, M.A.; Krenz, M.; Davis, J.W.; Baines, C.P. Proteomic Mapping of Proteins Released during Necrosis and Apoptosis from Cultured Neonatal Cardiac Myocytes. Am. J. Physiol.-Cell Physiol. 2014, 306, C639–C647. [Google Scholar] [CrossRef]
  143. Fang, M.; Ivanisevic, J.; Benton, H.P.; Johnson, C.H.; Patti, G.J.; Hoang, L.T.; Uritboonthai, W.; Kurczy, M.E.; Siuzdak, G. Thermal Degradation of Small Molecules: A Global Metabolomic Investigation. Anal. Chem. 2015, 87, 10935–10941. [Google Scholar] [CrossRef]
  144. Lu, W.; Su, X.; Klein, M.S.; Lewis, I.A.; Fiehn, O.; Rabinowitz, J.D. Metabolite Measurement: Pitfalls to Avoid and Practices to Follow. Annu. Rev. Biochem. 2017, 86, 277–304. [Google Scholar] [CrossRef]
  145. Kurbatov, I.; Dolgalev, G.; Arzumanian, V.; Kiseleva, O.; Poverennaya, E. The Knowns and Unknowns in Protein–Metabolite Interactions. Int. J. Mol. Sci. 2023, 24, 4155. [Google Scholar] [CrossRef]
  146. Cantone, L.; Tobaldini, E.; Favero, C.; Albetti, B.; Sacco, R.M.; Torgano, G.; Ferrari, L.; Montano, N.; Bollati, V. Particulate Air Pollution, Clock Gene Methylation, and Stroke: Effects on Stroke Severity and Disability. Int. J. Mol. Sci. 2020, 21, 3090. [Google Scholar] [CrossRef]
  147. Wang, C.; Chen, R.; Shi, M.; Cai, J.; Shi, J.; Yang, C.; Li, H.; Lin, Z.; Meng, X.; Liu, C.; et al. Possible Mediation by Methylation in Acute Inflammation Following Personal Exposure to Fine Particulate Air Pollution. Am. J. Epidemiol. 2018, 187, 484–493. [Google Scholar] [CrossRef]
  148. Chen, R.; Meng, X.; Zhao, A.; Wang, C.; Yang, C.; Li, H.; Cai, J.; Zhao, Z.; Kan, H. DNA Hypomethylation and Its Mediation in the Effects of Fine Particulate Air Pollution on Cardiovascular Biomarkers: A Randomized Crossover Trial. Environ. Int. 2016, 94, 614–619. [Google Scholar] [CrossRef]
  149. Wang, C.; Chen, R.; Cai, J.; Shi, J.; Yang, C.; Tse, L.A.; Li, H.; Lin, Z.; Meng, X.; Liu, C.; et al. Personal Exposure to Fine Particulate Matter and Blood Pressure: A Role of Angiotensin Converting Enzyme and Its DNA Methylation. Environ. Int. 2016, 94, 661–666. [Google Scholar] [CrossRef] [PubMed]
  150. Bellavia, A.; Urch, B.; Speck, M.; Brook, R.D.; Scott, J.A.; Albetti, B.; Behbod, B.; North, M.; Valeri, L.; Bertazzi, P.A.; et al. DNA Hypomethylation, Ambient Particulate Matter, and Increased Blood Pressure: Findings from Controlled Human Exposure Experiments. JAHA 2013, 2, e000212. [Google Scholar] [CrossRef]
  151. Cantone, L.; Iodice, S.; Tarantini, L.; Albetti, B.; Restelli, I.; Vigna, L.; Bonzini, M.; Pesatori, A.C.; Bollati, V. Particulate Matter Exposure Is Associated with Inflammatory Gene Methylation in Obese Subjects. Environ. Res. 2017, 152, 478–484. [Google Scholar] [CrossRef]
  152. Barchitta, M.; Maugeri, A.; Quattrocchi, A.; Barone, G.; Mazzoleni, P.; Catalfo, A.; De Guidi, G.; Iemmolo, M.G.; Crimi, N.; Agodi, A. Mediterranean Diet and Particulate Matter Exposure Are Associated with LINE-1 Methylation: Results from a Cross-Sectional Study in Women. Front. Genet. 2018, 9, 514. [Google Scholar] [CrossRef]
  153. The BIOS Consortium; Lee, M.K.; Xu, C.-J.; Carnes, M.U.; Nichols, C.E.; Ward, J.M.; Kwon, S.O.; Kim, S.-Y.; Kim, W.J.; London, S.J. Genome-Wide DNA Methylation and Long-Term Ambient Air Pollution Exposure in Korean Adults. Clin. Epigenet. 2019, 11, 37. [Google Scholar] [CrossRef]
  154. Rabinovitch, N.; Jones, M.J.; Gladish, N.; Faino, A.V.; Strand, M.; Morin, A.M.; MacIsaac, J.; Lin, D.T.S.; Reynolds, P.R.; Singh, A.; et al. Methylation of Cysteinyl Leukotriene Receptor 1 Genes Associates with Lung Function in Asthmatics Exposed to Traffic-Related Air Pollution. Epigenetics 2021, 16, 177–185. [Google Scholar] [CrossRef] [PubMed]
  155. Clifford, R.L.; Jones, M.J.; MacIsaac, J.L.; McEwen, L.M.; Goodman, S.J.; Mostafavi, S.; Kobor, M.S.; Carlsten, C. Inhalation of Diesel Exhaust and Allergen Alters Human Bronchial Epithelium DNA Methylation. J. Allergy Clin. Immunol. 2017, 139, 112–121. [Google Scholar] [CrossRef]
  156. Jiang, R.; Jones, M.J.; Sava, F.; Kobor, M.S.; Carlsten, C. Short-Term Diesel Exhaust Inhalation in a Controlled Human Crossover Study Is Associated with Changes in DNA Methylation of Circulating Mononuclear Cells in Asthmatics. Part. Fibre Toxicol. 2014, 11, 71. [Google Scholar] [CrossRef]
  157. Du, X.; Jiang, Y.; Li, H.; Zhang, Q.; Zhu, X.; Zhou, L.; Wang, W.; Zhang, Y.; Liu, C.; Niu, Y.; et al. Traffic-Related Air Pollution and Genome-Wide DNA Methylation: A Randomized, Crossover Trial. Sci. Total Environ. 2022, 850, 157968. [Google Scholar] [CrossRef]
  158. Gao, X.; Huang, J.; Cardenas, A.; Zhao, Y.; Sun, Y.; Wang, J.; Xue, L.; Baccarelli, A.A.; Guo, X.; Zhang, L.; et al. Short-Term Exposure of PM2.5 and Epigenetic Aging: A Quasi-Experimental Study. Environ. Sci. Technol. 2022, 56, 14690–14700. [Google Scholar] [CrossRef] [PubMed]
  159. Honkova, K.; Rossnerova, A.; Chvojkova, I.; Milcova, A.; Margaryan, H.; Pastorkova, A.; Ambroz, A.; Rossner, P.; Jirik, V.; Rubes, J.; et al. Genome-Wide DNA Methylation in Policemen Working in Cities Differing by Major Sources of Air Pollution. Int. J. Mol. Sci. 2022, 23, 1666. [Google Scholar] [CrossRef] [PubMed]
  160. Duan, R.; Niu, H.; Dong, F.; Yu, T.; Li, X.; Wu, H.; Zhang, Y.; Yang, T. Short-Term Exposure to Fine Particulate Matter and Genome-Wide DNA Methylation in Chronic Obstructive Pulmonary Disease: A Panel Study Conducted in Beijing, China. Front. Public Health 2023, 10, 1069685. [Google Scholar] [CrossRef]
  161. Li, H.; Chen, R.; Cai, J.; Cui, X.; Huang, N.; Kan, H. Short-Term Exposure to Fine Particulate Air Pollution and Genome-Wide DNA Methylation: A Randomized, Double-Blind, Crossover Trial. Environ. Int. 2018, 120, 130–136. [Google Scholar] [CrossRef]
  162. Su, C.-L.; Tantoh, D.M.; Chou, Y.-H.; Wang, L.; Ho, C.-C.; Chen, P.-H.; Lee, K.-J.; Nfor, O.N.; Hsu, S.-Y.; Liang, W.-M.; et al. Blood-Based SOX2-Promoter Methylation in Relation to Exercise and PM2.5 Exposure among Taiwanese Adults. Cancers 2020, 12, 504. [Google Scholar] [CrossRef] [PubMed]
  163. Pidsley, R.; Zotenko, E.; Peters, T.J.; Lawrence, M.G.; Risbridger, G.P.; Molloy, P.; Van Djik, S.; Muhlhausler, B.; Stirzaker, C.; Clark, S.J. Critical Evaluation of the Illumina MethylationEPIC BeadChip Microarray for Whole-Genome DNA Methylation Profiling. Genome Biol. 2016, 17, 208. [Google Scholar] [CrossRef] [PubMed]
  164. Moran, S.; Arribas, C.; Esteller, M. Validation of a DNA Methylation Microarray for 850,000 CpG Sites of the Human Genome Enriched in Enhancer Sequences. Epigenomics 2016, 8, 389–399. [Google Scholar] [CrossRef] [PubMed]
  165. Mookherjee, N.; Ryu, M.H.; Hemshekhar, M.; Orach, J.; Spicer, V.; Carlsten, C. Defining the Effects of Traffic-Related Air Pollution on the Human Plasma Proteome Using an Aptamer Proteomic Array: A Dose-Dependent Increase in Atherosclerosis-Related Proteins. Environ. Res. 2022, 209, 112803. [Google Scholar] [CrossRef] [PubMed]
  166. Li, Z.; Liang, D.; Ye, D.; Chang, H.H.; Ziegler, T.R.; Jones, D.P.; Ebelt, S.T. Application of High-Resolution Metabolomics to Identify Biological Pathways Perturbed by Traffic-Related Air Pollution. Environ. Res. 2021, 193, 110506. [Google Scholar] [CrossRef]
  167. Walker, D.I.; Hart, J.E.; Patel, C.J.; Rudel, R.; Chu, J.; Garshick, E.; Pennell, K.D.; Laden, F.; Jones, D.P. Integrated Molecular Response of Exposure to Traffic-Related Pollutants in the US Trucking Industry. Environ. Int. 2022, 158, 106957. [Google Scholar] [CrossRef]
  168. Du, X.; Zhang, Q.; Jiang, Y.; Li, H.; Zhu, X.; Zhang, Y.; Liu, C.; Niu, Y.; Ji, J.; Jiang, C.; et al. Dynamic Molecular Choreography Induced by Traffic Exposure: A Randomized, Crossover Trial Using Multi-Omics Profiling. J. Hazard. Mater. 2022, 424, 127359. [Google Scholar] [CrossRef]
  169. Cruz, R.; Pasqua, L.; Silveira, A.; Damasceno, M.; Matsuda, M.; Martins, M.; Marquezini, M.V.; Lima-Silva, A.E.; Saldiva, P.; Bertuzzi, R. Traffic-Related Air Pollution and Endurance Exercise: Characterizing Non-Targeted Serum Metabolomics Profiling. Environ. Pollut. 2021, 291, 118204. [Google Scholar] [CrossRef]
  170. Wang, J.; Lin, L.; Huang, J.; Zhang, J.; Duan, J.; Guo, X.; Wu, S.; Sun, Z. Impact of PM2.5 Exposure on Plasma Metabolome in Healthy Adults during Air Pollution Waves: A Randomized, Crossover Trial. J. Hazard. Mater. 2022, 436, 129180. [Google Scholar] [CrossRef]
  171. Zhao, L.; Fang, J.; Tang, S.; Deng, F.; Liu, X.; Shen, Y.; Liu, Y.; Kong, F.; Du, Y.; Cui, L.; et al. PM2.5 and Serum Metabolome and Insulin Resistance, Potential Mediation by the Gut Microbiome: A Population-Based Panel Study of Older Adults in China. Environ. Health Perspect. 2022, 130, 027007. [Google Scholar] [CrossRef]
  172. Lin, Y.; Lu, X.; Qiu, X.; Yin, F.; Faull, K.F.; Tseng, C.-H.; Zhang, J.; Fiehn, O.; Zhu, T.; Araujo, J.A.; et al. Arachidonic Acid Metabolism and Inflammatory Biomarkers Associated with Exposure to Polycyclic Aromatic Hydrocarbons. Environ. Res. 2022, 212, 113498. [Google Scholar] [CrossRef]
  173. Mu, L.; Niu, Z.; Blair, R.H.; Yu, H.; Browne, R.W.; Bonner, M.R.; Fanter, T.; Deng, F.; Swanson, M. Metabolomics Profiling before, during, and after the Beijing Olympics: A Panel Study of Within-Individual Differences during Periods of High and Low Air Pollution. Environ. Health Perspect. 2019, 127, 057010. [Google Scholar] [CrossRef]
  174. Miller, D.B.; Ghio, A.J.; Karoly, E.D.; Bell, L.N.; Snow, S.J.; Madden, M.C.; Soukup, J.; Cascio, W.E.; Gilmour, M.I.; Kodavanti, U.P. Ozone Exposure Increases Circulating Stress Hormones and Lipid Metabolites in Humans. Am. J. Respir. Crit. Care Med. 2016, 193, 1382–1391. [Google Scholar] [CrossRef]
  175. Huan, S.; Jin, S.; Liu, H.; Xia, W.; Liang, G.; Xu, S.; Fang, X.; Li, C.; Wang, Q.; Sun, X.; et al. Fine Particulate Matter Exposure and Perturbation of Serum Metabolome: A Longitudinal Study in Baoding, China. Chemosphere 2021, 276, 130102. [Google Scholar] [CrossRef] [PubMed]
  176. Reisdorph, N.A.; Walmsley, S.; Reisdorph, R. A Perspective and Framework for Developing Sample Type Specific Databases for LC/MS-Based Clinical Metabolomics. Metabolites 2019, 10, 8. [Google Scholar] [CrossRef] [PubMed]
  177. Malinowska, J.M.; Viant, M.R. Confidence in Metabolite Identification Dictates the Applicability of Metabolomics to Regulatory Toxicology. Curr. Opin. Toxicol. 2019, 16, 32–38. [Google Scholar] [CrossRef]
  178. Yang, Y.; Lee, M.; Fairn, G.D. Phospholipid Subcellular Localization and Dynamics. J. Biol. Chem. 2018, 293, 6230–6240. [Google Scholar] [CrossRef] [PubMed]
  179. Boffa, M.B.; Koschinsky, M.L. Oxidized Phospholipids as a Unifying Theory for Lipoprotein(a) and Cardiovascular Disease. Nat. Rev. Cardiol. 2019, 16, 305–318. [Google Scholar] [CrossRef] [PubMed]
  180. Ashraf, M.Z.; Kar, N.S.; Podrez, E.A. Oxidized Phospholipids: Biomarker for Cardiovascular Diseases. Int. J. Biochem. Cell Biol. 2009, 41, 1241–1244. [Google Scholar] [CrossRef] [PubMed]
  181. Guo, C.; Lv, S.; Liu, Y.; Li, Y. Biomarkers for the Adverse Effects on Respiratory System Health Associated with Atmospheric Particulate Matter Exposure. J. Hazard. Mater. 2022, 421, 126760. [Google Scholar] [CrossRef]
  182. Deutschman, D.H.; Carstens, J.S.; Klepper, R.L.; Smith, W.S.; Page, M.T.; Young, T.R.; Gleason, L.A.; Nakajima, N.; Sabbadini, R.A. Predicting Obstructive Coronary Artery Disease with Serum Sphingosine-1-Phosphate. Am. Heart J. 2003, 146, 62–68. [Google Scholar] [CrossRef]
  183. Yu, R.K.; Tsai, Y.-T.; Ariga, T.; Yanagisawa, M. Structures, Biosynthesis, and Functions of Gangliosides-an Overview. J. Oleo Sci. 2011, 60, 537–544. [Google Scholar] [CrossRef]
  184. Spijkers, L.J.A.; Van Den Akker, R.F.P.; Janssen, B.J.A.; Debets, J.J.; De Mey, J.G.R.; Stroes, E.S.G.; Van Den Born, B.-J.H.; Wijesinghe, D.S.; Chalfant, C.E.; MacAleese, L.; et al. Hypertension Is Associated with Marked Alterations in Sphingolipid Biology: A Potential Role for Ceramide. PLoS ONE 2011, 6, e21817. [Google Scholar] [CrossRef] [PubMed]
  185. Pan, W.; Yu, J.; Shi, R.; Yan, L.; Yang, T.; Li, Y.; Zhang, Z.; Yu, G.; Bai, Y.; Schuchman, E.H.; et al. Elevation of Ceramide and Activation of Secretory Acid Sphingomyelinase in Patients with Acute Coronary Syndromes. Coron. Artery Dis. 2014, 25, 230–235. [Google Scholar] [CrossRef] [PubMed]
  186. Strand, E.; Pedersen, E.R.; Svingen, G.F.T.; Olsen, T.; Bjørndal, B.; Karlsson, T.; Dierkes, J.; Njølstad, P.R.; Mellgren, G.; Tell, G.S.; et al. Serum Acylcarnitines and Risk of Cardiovascular Death and Acute Myocardial Infarction in Patients with Stable Angina Pectoris. JAHA 2017, 6, e003620. [Google Scholar] [CrossRef]
  187. Aitken-Buck, H.M.; Krause, J.; Zeller, T.; Jones, P.P.; Lamberts, R.R. Long-Chain Acylcarnitines and Cardiac Excitation-Contraction Coupling: Links to Arrhythmias. Front. Physiol. 2020, 11, 577856. [Google Scholar] [CrossRef] [PubMed]
  188. Ruiz-Canela, M.; Guasch-Ferré, M.; Razquin, C.; Toledo, E.; Hernández-Alonso, P.; Clish, C.B.; Li, J.; Wittenbecher, C.; Dennis, C.; Alonso-Gómez, Á.; et al. Plasma Acylcarnitines and Risk of Incident Heart Failure and Atrial Fibrillation: The Prevención Con Dieta Mediterránea Study. Rev. Española Cardiol. (Engl. Ed.) 2022, 75, 649–658. [Google Scholar] [CrossRef]
  189. Snodgrass, R.G.; Brüne, B. Regulation and Functions of 15-Lipoxygenases in Human Macrophages. Front. Pharmacol. 2019, 10, 719. [Google Scholar] [CrossRef]
  190. Burns, J.L.; Nakamura, M.T.; Ma, D.W.L. Differentiating the Biological Effects of Linoleic Acid from Arachidonic Acid in Health and Disease. Prostaglandins Leukot. Essent. Fat. Acids 2018, 135, 1–4. [Google Scholar] [CrossRef] [PubMed]
  191. Sonnweber, T.; Pizzini, A.; Nairz, M.; Weiss, G.; Tancevski, I. Arachidonic Acid Metabolites in Cardiovascular and Metabolic Diseases. Int. J. Mol. Sci. 2018, 19, 3285. [Google Scholar] [CrossRef]
  192. Bulló, M.; Papandreou, C.; García-Gavilán, J.; Ruiz-Canela, M.; Li, J.; Guasch-Ferré, M.; Toledo, E.; Clish, C.; Corella, D.; Estruch, R.; et al. Tricarboxylic Acid Cycle Related-Metabolites and Risk of Atrial Fibrillation and Heart Failure. Metabolism 2021, 125, 154915. [Google Scholar] [CrossRef] [PubMed]
  193. Santos, J.L.; Ruiz-Canela, M.; Razquin, C.; Clish, C.B.; Guasch-Ferré, M.; Babio, N.; Corella, D.; Gómez-Gracia, E.; Fiol, M.; Estruch, R.; et al. Circulating Citric Acid Cycle Metabolites and Risk of Cardiovascular Disease in the PREDIMED Study. Nutr. Metab. Cardiovasc. Dis. 2023, 33, 835–843. [Google Scholar] [CrossRef]
  194. Tran, D.H.; Wang, Z.V. Glucose Metabolism in Cardiac Hypertrophy and Heart Failure. JAHA 2019, 8, e012673. [Google Scholar] [CrossRef]
  195. Bell, S.M.; Burgess, T.; Lee, J.; Blackburn, D.J.; Allen, S.P.; Mortiboys, H. Peripheral Glycolysis in Neurodegenerative Diseases. Int. J. Mol. Sci. 2020, 21, 8924. [Google Scholar] [CrossRef] [PubMed]
  196. Kuspriyanti, N.P.; Ariyanto, E.F.; Syamsunarno, M.R.A.A. Role of Warburg Effect in Cardiovascular Diseases: A Potential Treatment Option. TOCMJ 2021, 15, 6–17. [Google Scholar] [CrossRef]
  197. Yang, Z.; Ming, X.-F. Functions of Arginase Isoforms in Macrophage Inflammatory Responses: Impact on Cardiovascular Diseases and Metabolic Disorders. Front. Immunol. 2014, 5, 533. [Google Scholar] [CrossRef]
  198. Hibbs, J.B.; Vavrin, Z.; Taintor, R.R. L-Arginine Is Required for Expression of the Activated Macrophage Effector Mechanism Causing Selective Metabolic Inhibition in Target Cells. J. Immunol. 1987, 138, 550–565. [Google Scholar] [CrossRef]
  199. Nathan, C.; Ding, A. Nonresolving Inflammation. Cell 2010, 140, 871–882. [Google Scholar] [CrossRef] [PubMed]
  200. Mills, C. M1 and M2 Macrophages: Oracles of Health and Disease. Crit. Rev. Immunol. 2012, 32, 463–488. [Google Scholar] [CrossRef]
  201. Morris, S.M. Arginine Metabolism: Boundaries of Our Knowledge. J. Nutr. 2007, 137, 1602S–1609S. [Google Scholar] [CrossRef] [PubMed]
  202. Yang, Z.; Ming, X.-F. Arginase: The Emerging Therapeutic Target for Vascular Oxidative Stress and Inflammation. Front. Immunol. 2013, 4, 149. [Google Scholar] [CrossRef] [PubMed]
  203. Caldwell, R.W.; Rodriguez, P.C.; Toque, H.A.; Narayanan, S.P.; Caldwell, R.B. Arginase: A Multifaceted Enzyme Important in Health and Disease. Physiol. Rev. 2018, 98, 641–665. [Google Scholar] [CrossRef]
  204. Gauer, B.; Brucker, N.; Barth, A.; Arbo, M.D.; Gioda, A.; Thiesen, F.V.; Nardi, J.; Garcia, S.C. Are Metals and Pyrene Levels Additional Factors Playing a Pivotal Role in Air Pollution-Induced Inflammation in Taxi Drivers? Toxicol. Res. 2018, 7, 8–12. [Google Scholar] [CrossRef]
  205. Pope, C.A.; Bhatnagar, A.; McCracken, J.P.; Abplanalp, W.; Conklin, D.J.; O’Toole, T. Exposure to Fine Particulate Air Pollution Is Associated With Endothelial Injury and Systemic Inflammation. Circ. Res. 2016, 119, 1204–1214. [Google Scholar] [CrossRef] [PubMed]
  206. Siponen, T.; Yli-Tuomi, T.; Aurela, M.; Dufva, H.; Hillamo, R.; Hirvonen, M.-R.; Huttunen, K.; Pekkanen, J.; Pennanen, A.; Salonen, I.; et al. Source-Specific Fine Particulate Air Pollution and Systemic Inflammation in Ischaemic Heart Disease Patients. Occup. Environ. Med. 2015, 72, 277–283. [Google Scholar] [CrossRef]
  207. Rich, D.Q.; Kipen, H.M.; Huang, W.; Wang, G.; Wang, Y.; Zhu, P.; Ohman-Strickland, P.; Hu, M.; Philipp, C.; Diehl, S.R.; et al. Association between Changes in Air Pollution Levels during the Beijing Olympics and Biomarkers of Inflammation and Thrombosis in Healthy Young Adults. JAMA 2012, 307. [Google Scholar] [CrossRef]
  208. Ramesh, G.; MacLean, A.G.; Philipp, M.T. Cytokines and Chemokines at the Crossroads of Neuroinflammation, Neurodegeneration, and Neuropathic Pain. Mediat. Inflamm. 2013, 2013, 480739. [Google Scholar] [CrossRef] [PubMed]
  209. Borish, L.C.; Steinke, J.W. 2. Cytokines and Chemokines. J. Allergy Clin. Immunol. 2003, 111, S460–S475. [Google Scholar] [CrossRef]
  210. Clarke, R.; Valdes-Marquez, E.; Hill, M.; Gordon, J.; Farrall, M.; Hamsten, A.; Watkins, H.; Hopewell, J.C. Plasma Cytokines and Risk of Coronary Heart Disease in the PROCARDIS Study. Open Heart 2018, 5, e000807. [Google Scholar] [CrossRef]
  211. Tahir, A.; Martinez, P.J.; Ahmad, F.; Fisher-Hoch, S.P.; McCormick, J.; Gay, J.L.; Mirza, S.; Chaudhary, S.U. An Evaluation of Lipid Profile and Pro-Inflammatory Cytokines as Determinants of Cardiovascular Disease in Those with Diabetes: A Study on a Mexican American Cohort. Sci. Rep. 2021, 11, 2435. [Google Scholar] [CrossRef]
  212. Amin, M.N.; Siddiqui, S.A.; Ibrahim, M.; Hakim, M.L.; Ahammed, M.S.; Kabir, A.; Sultana, F. Inflammatory Cytokines in the Pathogenesis of Cardiovascular Disease and Cancer. SAGE Open Med. 2020, 8, 205031212096575. [Google Scholar] [CrossRef]
  213. Atamas, S.P.; Chapoval, S.P.; Keegan, A.D. Cytokines in Chronic Respiratory Diseases. F1000 Biol. Rep. 2013, 5, 3. [Google Scholar] [CrossRef]
  214. Sameer, A.S.; Nissar, S. Toll-Like Receptors (TLRs): Structure, Functions, Signaling, and Role of Their Polymorphisms in Colorectal Cancer Susceptibility. BioMed Res. Int. 2021, 2021, 1157023. [Google Scholar] [CrossRef] [PubMed]
  215. Arora, S.; Ahmad, S.; Irshad, R.; Goyal, Y.; Rafat, S.; Siddiqui, N.; Dev, K.; Husain, M.; Ali, S.; Mohan, A.; et al. TLRs in Pulmonary Diseases. Life Sci. 2019, 233, 116671. [Google Scholar] [CrossRef] [PubMed]
  216. Son, Y.; Cheong, Y.-K.; Kim, N.-H.; Chung, H.-T.; Kang, D.G.; Pae, H.-O. Mitogen-Activated Protein Kinases and Reactive Oxygen Species: How Can ROS Activate MAPK Pathways? J. Signal Transduct. 2011, 2011, 792639. [Google Scholar] [CrossRef] [PubMed]
  217. Takata, T.; Araki, S.; Tsuchiya, Y.; Watanabe, Y. Oxidative Stress Orchestrates MAPK and Nitric-Oxide Synthase Signal. Int. J. Mol. Sci. 2020, 21, 8750. [Google Scholar] [CrossRef]
  218. Muslin, A.J. MAPK Signalling in Cardiovascular Health and Disease: Molecular Mechanisms and Therapeutic Targets. Clin. Sci. 2008, 115, 203–218. [Google Scholar] [CrossRef] [PubMed]
  219. Jubaidi, F.F.; Zainalabidin, S.; Taib, I.S.; Abdul Hamid, Z.; Mohamad Anuar, N.N.; Jalil, J.; Mohd Nor, N.A.; Budin, S.B. The Role of PKC-MAPK Signalling Pathways in the Development of Hyperglycemia-Induced Cardiovascular Complications. Int. J. Mol. Sci. 2022, 23, 8582. [Google Scholar] [CrossRef]
  220. Van Paridon, P.C.S.; Panova-Noeva, M.; Van Oerle, R.; Schulz, A.; Prochaska, J.H.; Arnold, N.; Schmidtmann, I.; Beutel, M.; Pfeiffer, N.; Münzel, T.; et al. Lower Levels of vWF Are Associated with Lower Risk of Cardiovascular Disease. Res. Pract. Thromb. Haemost. 2022, 6, e12797. [Google Scholar] [CrossRef]
  221. Spiel, A.O.; Gilbert, J.C.; Jilma, B. Von Willebrand Factor in Cardiovascular Disease: Focus on Acute Coronary Syndromes. Circulation 2008, 117, 1449–1459. [Google Scholar] [CrossRef]
  222. Hertle, E.; Van Greevenbroek, M.M.J.; Stehouwer, C.D.A. Complement C3: An Emerging Risk Factor in Cardiometabolic Disease. Diabetologia 2012, 55, 881–884. [Google Scholar] [CrossRef] [PubMed]
  223. Olson, N.C.; Raffield, L.M.; Lange, L.A.; Lange, E.M.; Longstreth, W.T.; Chauhan, G.; Debette, S.; Seshadri, S.; Reiner, A.P.; Tracy, R.P. Associations of Activated Coagulation Factor VII and Factor VIIa-antithrombin Levels with Genome-wide Polymorphisms and Cardiovascular Disease Risk. J. Thromb. Haemost. 2018, 16, 19–30. [Google Scholar] [CrossRef] [PubMed]
  224. Junker, R.; Heinrich, J.; Schulte, H.; Van De Loo, J.; Assmann, G. Coagulation Factor VII and the Risk of Coronary Heart Disease in Healthy Men. ATVB 1997, 17, 1539–1544. [Google Scholar] [CrossRef] [PubMed]
  225. Tofler, G.H.; Massaro, J.; O’Donnell, C.J.; Wilson, P.W.F.; Vasan, R.S.; Sutherland, P.A.; Meigs, J.B.; Levy, D.; D’Agostino, R.B. Plasminogen Activator Inhibitor and the Risk of Cardiovascular Disease: The Framingham Heart Study. Thromb. Res. 2016, 140, 30–35. [Google Scholar] [CrossRef]
  226. Stec, J.J.; Silbershatz, H.; Tofler, G.H.; Matheney, T.H.; Sutherland, P.; Lipinska, I.; Massaro, J.M.; Wilson, P.F.W.; Muller, J.E.; D’Agostino, R.B. Association of Fibrinogen with Cardiovascular Risk Factors and Cardiovascular Disease in the Framingham Offspring Population. Circulation 2000, 102, 1634–1638. [Google Scholar] [CrossRef]
  227. Zhao, J.V.; Schooling, C.M. Coagulation Factors and the Risk of Ischemic Heart Disease: A Mendelian Randomization Study. Circ. Genom. Precis. Med. 2018, 11, e001956. [Google Scholar] [CrossRef] [PubMed]
  228. Zhang, Q.; Niu, Y.; Xia, Y.; Lei, X.; Wang, W.; Huo, J.; Zhao, Q.; Zhang, Y.; Duan, Y.; Cai, J.; et al. The Acute Effects of Fine Particulate Matter Constituents on Circulating Inflammatory Biomarkers in Healthy Adults. Sci. Total Environ. 2020, 707, 135989. [Google Scholar] [CrossRef]
  229. Hillis, G.S.; Flapan, A.D. Cell Adhesion Molecules in Cardiovascular Disease: A Clinical Perspective. Heart 1998, 79, 429–431. [Google Scholar] [CrossRef]
  230. Zhou, Y.; Zhu, X.; Cui, H.; Shi, J.; Yuan, G.; Shi, S.; Hu, Y. The Role of the VEGF Family in Coronary Heart Disease. Front. Cardiovasc. Med. 2021, 8, 738325. [Google Scholar] [CrossRef]
  231. Camasão, D.B.; Mantovani, D. The Mechanical Characterization of Blood Vessels and Their Substitutes in the Continuous Quest for Physiological-Relevant Performances. A Critical Review. Mater. Today Bio 2021, 10, 100106. [Google Scholar] [CrossRef]
  232. Bevan, G.H.; Al-Kindi, S.G.; Brook, R.D.; Münzel, T.; Rajagopalan, S. Ambient Air Pollution and Atherosclerosis: Insights Into Dose, Time, and Mechanisms. ATVB 2021, 41, 628–637. [Google Scholar] [CrossRef]
  233. Schwartz, A.B.; Campos, O.A.; Criado-Hidalgo, E.; Chien, S.; Del Álamo, J.C.; Lasheras, J.C.; Yeh, Y.-T. Elucidating the Biomechanics of Leukocyte Transendothelial Migration by Quantitative Imaging. Front. Cell Dev. Biol. 2021, 9, 635263. [Google Scholar] [CrossRef] [PubMed]
  234. Gondalia, R.; Holliday, K.M.; Baldassari, A.; Justice, A.E.; Stewart, J.D.; Liao, D.; Yanosky, J.D.; Engel, S.M.; Jordahl, K.M.; Bhatti, P.; et al. Leukocyte Traits and Exposure to Ambient Particulate Matter Air Pollution in the Women’s Health Initiative and Atherosclerosis Risk in Communities Study. Environ. Health Perspect. 2020, 128, 017004. [Google Scholar] [CrossRef] [PubMed]
  235. Rezatabar, S.; Karimian, A.; Rameshknia, V.; Parsian, H.; Majidinia, M.; Kopi, T.A.; Bishayee, A.; Sadeghinia, A.; Yousefi, M.; Monirialamdari, M.; et al. RAS/MAPK Signaling Functions in Oxidative Stress, DNA Damage Response and Cancer Progression. J. Cell. Physiol. 2019, 234, 14951–14965. [Google Scholar] [CrossRef]
  236. Liu, D.; Xu, Y. P53, Oxidative Stress, and Aging. Antioxid. Redox Signal. 2011, 15, 1669–1678. [Google Scholar] [CrossRef]
  237. Liu, X.; Fan, L.; Lu, C.; Yin, S.; Hu, H. Functional Role of P53 in the Regulation of Chemical-Induced Oxidative Stress. Oxid. Med. Cell. Longev. 2020, 2020, 6039769. [Google Scholar] [CrossRef]
  238. Kannan, K.; Jain, S.K. Oxidative Stress and Apoptosis. Pathophysiology 2000, 7, 153–163. [Google Scholar] [CrossRef] [PubMed]
  239. Chen, Y.; McMillan-Ward, E.; Kong, J.; Israels, S.J.; Gibson, S.B. Oxidative Stress Induces Autophagic Cell Death Independent of Apoptosis in Transformed and Cancer Cells. Cell Death Differ. 2008, 15, 171–182. [Google Scholar] [CrossRef] [PubMed]
  240. Simon, A.R.; Rai, U.; Fanburg, B.L.; Cochran, B.H. Activation of the JAK-STAT Pathway by Reactive Oxygen Species. Am. J. Physiol.-Cell Physiol. 1998, 275, C1640–C1652. [Google Scholar] [CrossRef]
  241. Yun, H.R.; Jo, Y.H.; Kim, J.; Shin, Y.; Kim, S.S.; Choi, T.G. Roles of Autophagy in Oxidative Stress. Int. J. Mol. Sci. 2020, 21, 3289. [Google Scholar] [CrossRef]
  242. Chan, G.H.-H.; Chan, E.; Kwok, C.T.-K.; Leung, G.P.-H.; Lee, S.M.-Y.; Seto, S.-W. The Role of P53 in the Alternation of Vascular Functions. Front. Pharmacol. 2022, 13, 981152. [Google Scholar] [CrossRef] [PubMed]
  243. Men, H.; Cai, H.; Cheng, Q.; Zhou, W.; Wang, X.; Huang, S.; Zheng, Y.; Cai, L. The Regulatory Roles of P53 in Cardiovascular Health and Disease. Cell. Mol. Life Sci. 2021, 78, 2001–2018. [Google Scholar] [CrossRef]
  244. Uddin, M.A.; Barabutis, N. P53 in the Impaired Lungs. DNA Repair. 2020, 95, 102952. [Google Scholar] [CrossRef] [PubMed]
  245. Seif, F.; Khoshmirsafa, M.; Aazami, H.; Mohsenzadegan, M.; Sedighi, G.; Bahar, M. The Role of JAK-STAT Signaling Pathway and Its Regulators in the Fate of T Helper Cells. Cell Commun. Signal. 2017, 15, 23. [Google Scholar] [CrossRef] [PubMed]
  246. Ahmed, H.R.; Manzoor Syed, B.; Laghari, Z.; Pirzada, S. Analysis of Inflammatory Markers in Apparently Healthy Automobile Vehicle Drivers in Response to Exposure to Traffic Pollution Fumes: Inflammatory Markers in Healthy Automobile Vehicle Drivers. Pak. J. Med. Sci. 2020, 36, 657. [Google Scholar] [CrossRef] [PubMed]
  247. Laratta, C.R.; Kendzerska, T.; Carlsten, C.; Brauer, M.; Van Eeden, S.F.; Allen, A.J.M.H.; Fox, N.; Peres, B.U.; Ayas, N.T. Air Pollution and Systemic Inflammation in Patients with Suspected OSA Living in an Urban Residential Area. Chest 2020, 158, 1713–1722. [Google Scholar] [CrossRef]
  248. Mascareno, E.; El-Shafei, M.; Maulik, N.; Sato, M.; Guo, Y.; Das, D.K.; Siddiqui, M.A.Q. JAK/STAT Signaling Is Associated with Cardiac Dysfunction during Ischemia and Reperfusion. Circulation 2001, 104, 325–329. [Google Scholar] [CrossRef] [PubMed]
  249. Kishore, R.; Verma, S.K. Roles of STATs Signaling in Cardiovascular Diseases. JAK-STAT 2012, 1, 118–124. [Google Scholar] [CrossRef]
  250. Purohit, M.; Gupta, G.; Afzal, O.; Altamimi, A.S.A.; Alzarea, S.I.; Kazmi, I.; Almalki, W.H.; Gulati, M.; Kaur, I.P.; Singh, S.K.; et al. Janus Kinase/Signal Transducers and Activator of Transcription (JAK/STAT) and Its Role in Lung Inflammatory Disease. Chem.-Biol. Interact. 2023, 371, 110334. [Google Scholar] [CrossRef]
  251. Yew-Booth, L.; Birrell, M.A.; Lau, M.S.; Baker, K.; Jones, V.; Kilty, I.; Belvisi, M.G. JAK–STAT Pathway Activation in COPD. Eur. Respir. J. 2015, 46, 843–845. [Google Scholar] [CrossRef]
  252. Kim, N.-H.; Kang, P.M. Apoptosis in Cardiovascular Diseases: Mechanism and Clinical Implications. Korean Circ. J. 2010, 40, 299. [Google Scholar] [CrossRef]
  253. Henson, P.M.; Tuder, R.M. Apoptosis in the Lung: Induction, Clearance and Detection. Am. J. Physiol.-Lung Cell. Mol. Physiol. 2008, 294, L601–L611. [Google Scholar] [CrossRef] [PubMed]
  254. Lee, Y.; Gustafsson, Å.B. Role of Apoptosis in Cardiovascular Disease. Apoptosis 2009, 14, 536–548. [Google Scholar] [CrossRef] [PubMed]
  255. Fan, Y.-J.; Zong, W.-X. The Cellular Decision between Apoptosis and Autophagy. Chin. J. Cancer 2013, 32, 121–129. [Google Scholar] [CrossRef] [PubMed]
  256. Jiang, B.; Zhou, X.; Yang, T.; Wang, L.; Feng, L.; Wang, Z.; Xu, J.; Jing, W.; Wang, T.; Su, H.; et al. The Role of Autophagy in Cardiovascular Disease: Cross-Interference of Signaling Pathways and Underlying Therapeutic Targets. Front. Cardiovasc. Med. 2023, 10, 1088575. [Google Scholar] [CrossRef] [PubMed]
  257. Nishida, K.; Kyoi, S.; Yamaguchi, O.; Sadoshima, J.; Otsu, K. The Role of Autophagy in the Heart. Cell Death Differ. 2009, 16, 31–38. [Google Scholar] [CrossRef] [PubMed]
  258. Bravo-San Pedro, J.M.; Kroemer, G.; Galluzzi, L. Autophagy and Mitophagy in Cardiovascular Disease. Circ. Res. 2017, 120, 1812–1824. [Google Scholar] [CrossRef] [PubMed]
  259. Lepeule, J.; Litonjua, A.A.; Coull, B.; Koutrakis, P.; Sparrow, D.; Vokonas, P.S.; Schwartz, J. Long-Term Effects of Traffic Particles on Lung Function Decline in the Elderly. Am. J. Respir. Crit. Care Med. 2014, 190, 542–548. [Google Scholar] [CrossRef] [PubMed]
  260. Jiang, Y.; Niu, Y.; Xia, Y.; Liu, C.; Lin, Z.; Wang, W.; Ge, Y.; Lei, X.; Wang, C.; Cai, J.; et al. Effects of Personal Nitrogen Dioxide Exposure on Airway Inflammation and Lung Function. Environ. Res. 2019, 177, 108620. [Google Scholar] [CrossRef]
  261. Zhou, Y.; Liu, Y.; Song, Y.; Xie, J.; Cui, X.; Zhang, B.; Shi, T.; Yuan, J.; Chen, W. Short-Term Effects of Outdoor Air Pollution on Lung Function among Female Non-Smokers in China. Sci. Rep. 2016, 6, 34947. [Google Scholar] [CrossRef]
  262. Bowatte, G.; Lodge, C.J.; Knibbs, L.D.; Erbas, B.; Perret, J.L.; Jalaludin, B.; Morgan, G.G.; Bui, D.S.; Giles, G.G.; Hamilton, G.S.; et al. Traffic Related Air Pollution and Development and Persistence of Asthma and Low Lung Function. Environ. Int. 2018, 113, 170–176. [Google Scholar] [CrossRef] [PubMed]
  263. Bowatte, G.; Erbas, B.; Lodge, C.J.; Knibbs, L.D.; Gurrin, L.C.; Marks, G.B.; Thomas, P.S.; Johns, D.P.; Giles, G.G.; Hui, J.; et al. Traffic-Related Air Pollution Exposure over a 5-Year Period Is Associated with Increased Risk of Asthma and Poor Lung Function in Middle Age. Eur. Respir. J. 2017, 50, 1602357. [Google Scholar] [CrossRef]
  264. Schraufnagel, D.E.; Balmes, J.R.; Cowl, C.T.; De Matteis, S.; Jung, S.-H.; Mortimer, K.; Perez-Padilla, R.; Rice, M.B.; Riojas-Rodriguez, H.; Sood, A.; et al. Air Pollution and Noncommunicable Diseases. Chest 2019, 155, 417–426. [Google Scholar] [CrossRef] [PubMed]
  265. Boogaard, H.; Patton, A.P.; Atkinson, R.W.; Brook, J.R.; Chang, H.H.; Crouse, D.L.; Fussell, J.C.; Hoek, G.; Hoffmann, B.; Kappeler, R.; et al. Long-Term Exposure to Traffic-Related Air Pollution and Selected Health Outcomes: A Systematic Review and Meta-Analysis. Environ. Int. 2022, 164, 107262. [Google Scholar] [CrossRef] [PubMed]
  266. Zhang, S.; Li, G.; Tian, L.; Guo, Q.; Pan, X. Short-Term Exposure to Air Pollution and Morbidity of COPD and Asthma in East Asian Area: A Systematic Review and Meta-Analysis. Environ. Res. 2016, 148, 15–23. [Google Scholar] [CrossRef] [PubMed]
  267. Duan, R.-R.; Hao, K.; Yang, T. Air Pollution and Chronic Obstructive Pulmonary Disease. Chronic Dis. Transl. Med. 2020, 6, 260–269. [Google Scholar] [CrossRef]
  268. Duong-Quy, S. Clinical Utility of the Exhaled Nitric Oxide (NO) Measurement with Portable Devices in the Management of Allergic Airway Inflammation and Asthma. JAA 2019, 12, 331–341. [Google Scholar] [CrossRef] [PubMed]
  269. Hancox, R.J.; Poulton, R.; Greene, J.M.; Filsell, S.; McLachlan, C.R.; Rasmussen, F.; Taylor, D.R.; Williams, M.J.A.; Williamson, A.; Sears, M.R. Systemic Inflammation and Lung Function in Young Adults. Thorax 2007, 62, 1064–1068. [Google Scholar] [CrossRef]
  270. Baines, K.J.; Backer, V.; Gibson, P.G.; Powel, H.; Porsbjerg, C.M. Impaired Lung Function Is Associated with Systemic Inflammation and Macrophage Activation. Eur. Respir. J. 2015, 45, 557–559. [Google Scholar] [CrossRef]
  271. Nerpin, E.; Jacinto, T.; Fonseca, J.A.; Alving, K.; Janson, C.; Malinovschi, A. Systemic Inflammatory Markers in Relation to Lung Function in NHANES. 2007–2010. Respir. Med. 2018, 142, 94–100. [Google Scholar] [CrossRef] [PubMed]
  272. Kalhan, R.; Tran, B.T.; Colangelo, L.A.; Rosenberg, S.R.; Liu, K.; Thyagarajan, B.; Jacobs, D.R.; Smith, L.J. Systemic Inflammation in Young Adults Is Associated with Abnormal Lung Function in Middle Age. PLoS ONE 2010, 5, e11431. [Google Scholar] [CrossRef]
  273. Ward-Caviness, C.K. A Review of Gene-by-Air Pollution Interactions for Cardiovascular Disease, Risk Factors, and Biomarkers. Hum. Genet. 2019, 138, 547–561. [Google Scholar] [CrossRef]
  274. Al-Kindi, S.G.; Brook, R.D.; Biswal, S.; Rajagopalan, S. Environmental Determinants of Cardiovascular Disease: Lessons Learned from Air Pollution. Nat. Rev. Cardiol. 2020, 17, 656–672. [Google Scholar] [CrossRef]
  275. Xu, Z.; Wang, W.; Liu, Q.; Li, Z.; Lei, L.; Ren, L.; Deng, F.; Guo, X.; Wu, S. Association between Gaseous Air Pollutants and Biomarkers of Systemic Inflammation: A Systematic Review and Meta-Analysis. Environ. Pollut. 2022, 292, 118336. [Google Scholar] [CrossRef]
  276. Joshi, A.; Rienks, M.; Theofilatos, K.; Mayr, M. Systems Biology in Cardiovascular Disease: A Multiomics Approach. Nat. Rev. Cardiol. 2021, 18, 313–330. [Google Scholar] [CrossRef] [PubMed]
  277. Lee, L.Y.; Pandey, A.K.; Maron, B.A.; Loscalzo, J. Network Medicine in Cardiovascular Research. Cardiovasc. Res. 2021, 117, 2186–2202. [Google Scholar] [CrossRef] [PubMed]
  278. Tahir, U.A.; Gerszten, R.E. Omics and Cardiometabolic Disease Risk Prediction. Annu. Rev. Med. 2020, 71, 163–175. [Google Scholar] [CrossRef]
  279. Usova, E.I.; Alieva, A.S.; Yakovlev, A.N.; Alieva, M.S.; Prokhorikhin, A.A.; Konradi, A.O.; Shlyakhto, E.V.; Magni, P.; Catapano, A.L.; Baragetti, A. Integrative Analysis of Multi-Omics and Genetic Approaches—A New Level in Atherosclerotic Cardiovascular Risk Prediction. Biomolecules 2021, 11, 1597. [Google Scholar] [CrossRef] [PubMed]
  280. Battaglini, D.; Al-Husinat, L.; Normando, A.G.; Leme, A.P.; Franchini, K.; Morales, M.; Pelosi, P.; Rocco, P.R. Personalized Medicine Using Omics Approaches in Acute Respiratory Distress Syndrome to Identify Biological Phenotypes. Respir. Res. 2022, 23, 318. [Google Scholar] [CrossRef]
  281. Wang, X.-W.; Wang, T.; Schaub, D.P.; Chen, C.; Sun, Z.; Ke, S.; Hecker, J.; Maaser-Hecker, A.; Zeleznik, O.A.; Zeleznik, R.; et al. Benchmarking Omics-Based Prediction of Asthma Development in Children. Respir. Res. 2023, 24, 63. [Google Scholar] [CrossRef]
  282. Nicora, G.; Vitali, F.; Dagliati, A.; Geifman, N.; Bellazzi, R. Integrated Multi-Omics Analyses in Oncology: A Review of Machine Learning Methods and Tools. Front. Oncol. 2020, 10, 1030. [Google Scholar] [CrossRef]
  283. Nativio, R.; Lan, Y.; Donahue, G.; Sidoli, S.; Berson, A.; Srinivasan, A.R.; Shcherbakova, O.; Amlie-Wolf, A.; Nie, J.; Cui, X.; et al. An Integrated Multi-Omics Approach Identifies Epigenetic Alterations Associated with Alzheimer’s Disease. Nat. Genet. 2020, 52, 1024–1035. [Google Scholar] [CrossRef] [PubMed]
  284. Eddy, S.; Mariani, L.H.; Kretzler, M. Integrated Multi-Omics Approaches to Improve Classification of Chronic Kidney Disease. Nat. Rev. Nephrol. 2020, 16, 657–668. [Google Scholar] [CrossRef] [PubMed]
  285. Gillenwater, L.A.; Helmi, S.; Stene, E.; Pratte, K.A.; Zhuang, Y.; Schuyler, R.P.; Lange, L.; Castaldi, P.J.; Hersh, C.P.; Banaei-Kashani, F.; et al. Multi-Omics Subtyping Pipeline for Chronic Obstructive Pulmonary Disease. PLoS ONE 2021, 16, e0255337. [Google Scholar] [CrossRef] [PubMed]
  286. Smilde, A.K.; Næs, T.; Liland, K.H. Multiblock Data Fusion in Statistics and Machine Learning; John Wiley & Sons: Chichester, UK, 2022; ISBN 978-1-119-60096-1. [Google Scholar]
  287. McCullagh, P. Tensor Methods in Statistics; Dover Publications: Mineola, NY, USA, 2018. [Google Scholar]
  288. Cai, Z.; Poulos, R.C.; Liu, J.; Zhong, Q. Machine Learning for Multi-Omics Data Integration in Cancer. iScience 2022, 25, 103798. [Google Scholar] [CrossRef] [PubMed]
  289. Rappoport, N.; Shamir, R. Multi-Omic and Multi-View Clustering Algorithms: Review and Cancer Benchmark. Nucleic Acids Res. 2018, 46, 10546–10562. [Google Scholar] [CrossRef] [PubMed]
  290. Adossa, N.; Khan, S.; Rytkönen, K.T.; Elo, L.L. Computational Strategies for Single-Cell Multi-Omics Integration. Comput. Struct. Biotechnol. J. 2021, 19, 2588–2596. [Google Scholar] [CrossRef]
Figure 1. Flow diagram of the article selection process with exclusion criteria.
Figure 1. Flow diagram of the article selection process with exclusion criteria.
Toxics 11 01014 g001
Figure 2. Overview of the relationships among traffic-related air pollution, omics markers, and subclinical and clinical cardiovascular and respiratory disease outcomes. Solid arrows indicate a well-established, known relationship, as evidenced by the biomedical literature. Dashed arrows indicate a probable association or an association with possible mediators that needs to be further investigated. The color coding of text within methylomic, proteomic, and metabolomic text boxes corresponds to a category of biological pathways. Green—lipid metabolism; orange—cellular energy production; blue—amino acid metabolism; red—inflammation and immunity; yellow—coagulation; purple—endothelial function; white—oxidative stress; black—analytes that do not fit into the above categories (vitamins, purines, xanthines, etc.). Abbreviations: ARG2—Arginase 2; C1q—Complement component 1q; C3—Complement component 3; C4A—Complement component 4A; CCL2—CC motif chemokine ligand 2/monocyte chemoattractant protein 1; CCL3—CC motif chemokine ligand 3/macrophage inflammatory protein 1 alpha; CD14—Cluster of differentiation 14; CD40LG—Cluster of differentiation 40 ligand; CX3CL1—Fractalkine; CXCL10; CXC motif chemokine ligand 10/interferon gamma inducible protein 10; F2—Coagulation factor 2; F2R- Coagulation factor 2 receptor; F3—Coagulation factor 3; FGF2—Fibroblast growth factor 2; GM-CSF—Granulocyte macrophage colony stimulating factor; ICAM1—Intercellular adhesion molecule 1; IL1b—Interleukin 1 beta; IL4—Interleukin 4; IL6—Interleukin 6; IL10—Interleukin 10; MAPK—Mitogen activated protein kinase; NOS2—Nitric oxide synthase 2; Nf-KB—Nuclear factor kappa light chain enhancer of activated B cells; P13K-AKT—Phosphatidylinositol 3 kinase and AKT/protein kinase B; SERPINE1—Serpin family E member 1/Plasminogen activator inhibitor 1; TLR2—Toll like receptor 2; TLR4—Toll like receptor 4; TNF—Tumor necrosis factor alpha; TNFa—Tumor necrosis factor alpha; VCAM1—Vascular cell adhesion molecule 1; VEGFa—Vascular endothelial growth factor alpha; vWF—Von Willebrand factor.
Figure 2. Overview of the relationships among traffic-related air pollution, omics markers, and subclinical and clinical cardiovascular and respiratory disease outcomes. Solid arrows indicate a well-established, known relationship, as evidenced by the biomedical literature. Dashed arrows indicate a probable association or an association with possible mediators that needs to be further investigated. The color coding of text within methylomic, proteomic, and metabolomic text boxes corresponds to a category of biological pathways. Green—lipid metabolism; orange—cellular energy production; blue—amino acid metabolism; red—inflammation and immunity; yellow—coagulation; purple—endothelial function; white—oxidative stress; black—analytes that do not fit into the above categories (vitamins, purines, xanthines, etc.). Abbreviations: ARG2—Arginase 2; C1q—Complement component 1q; C3—Complement component 3; C4A—Complement component 4A; CCL2—CC motif chemokine ligand 2/monocyte chemoattractant protein 1; CCL3—CC motif chemokine ligand 3/macrophage inflammatory protein 1 alpha; CD14—Cluster of differentiation 14; CD40LG—Cluster of differentiation 40 ligand; CX3CL1—Fractalkine; CXCL10; CXC motif chemokine ligand 10/interferon gamma inducible protein 10; F2—Coagulation factor 2; F2R- Coagulation factor 2 receptor; F3—Coagulation factor 3; FGF2—Fibroblast growth factor 2; GM-CSF—Granulocyte macrophage colony stimulating factor; ICAM1—Intercellular adhesion molecule 1; IL1b—Interleukin 1 beta; IL4—Interleukin 4; IL6—Interleukin 6; IL10—Interleukin 10; MAPK—Mitogen activated protein kinase; NOS2—Nitric oxide synthase 2; Nf-KB—Nuclear factor kappa light chain enhancer of activated B cells; P13K-AKT—Phosphatidylinositol 3 kinase and AKT/protein kinase B; SERPINE1—Serpin family E member 1/Plasminogen activator inhibitor 1; TLR2—Toll like receptor 2; TLR4—Toll like receptor 4; TNF—Tumor necrosis factor alpha; TNFa—Tumor necrosis factor alpha; VCAM1—Vascular cell adhesion molecule 1; VEGFa—Vascular endothelial growth factor alpha; vWF—Von Willebrand factor.
Toxics 11 01014 g002
Figure 3. Short-term air pollution and gene–metabolite network analysis. Circular nodes represent genes, whereas square nodes represent metabolites. The color of each node corresponds to the category of the biological pathway to which that analyte belongs. Green—lipid metabolism; orange—cellular energy production; blue—amino acid metabolism; red—inflammation and immunity; yellow—coagulation; pink—endothelial function; white—oxidative stress; black—analytes that do not fit into the above categories (vitamins, purines, xanthines, etc.). Abbreviations: ACE—Angiotensin converting enzyme; CCL2—Monocyte chemoattractant protein 1; CRP—C-reactive protein; CSF2—Colony stimulating factor 2; CXCL10—Interferon gamma-induced protein 10; EDN1—Endothelin 1; EDNRB—Endothelin receptor type B; F2—Coagulation factor 2; F2R—Coagulation factor 2 receptor; F3—Coagulation factor 3; IL1B—Interleukin 1 beta; IL2—Interleukin 2; IL6—Interleukin 6; IL-8—Interleukin 8; ICAM1—Intercellular adhesion molecule 1; MPO—Myeloperoxidase; NOS2—Nitric oxide synthase 2.
Figure 3. Short-term air pollution and gene–metabolite network analysis. Circular nodes represent genes, whereas square nodes represent metabolites. The color of each node corresponds to the category of the biological pathway to which that analyte belongs. Green—lipid metabolism; orange—cellular energy production; blue—amino acid metabolism; red—inflammation and immunity; yellow—coagulation; pink—endothelial function; white—oxidative stress; black—analytes that do not fit into the above categories (vitamins, purines, xanthines, etc.). Abbreviations: ACE—Angiotensin converting enzyme; CCL2—Monocyte chemoattractant protein 1; CRP—C-reactive protein; CSF2—Colony stimulating factor 2; CXCL10—Interferon gamma-induced protein 10; EDN1—Endothelin 1; EDNRB—Endothelin receptor type B; F2—Coagulation factor 2; F2R—Coagulation factor 2 receptor; F3—Coagulation factor 3; IL1B—Interleukin 1 beta; IL2—Interleukin 2; IL6—Interleukin 6; IL-8—Interleukin 8; ICAM1—Intercellular adhesion molecule 1; MPO—Myeloperoxidase; NOS2—Nitric oxide synthase 2.
Toxics 11 01014 g003
Figure 4. Long-term air pollution and gene–metabolite network analysis. Circular nodes represent genes, whereas square nodes represent metabolites. The color of each node corresponds to the category of the biological pathway to which that analyte belongs. Green—lipid metabolism; orange—cellular energy production; blue—amino acid metabolism; red—inflammation and immunity; yellow—coagulation; pink—endothelial function; white—oxidative stress; black—analytes that do not fit into the above categories (vitamins, purines, xanthines, etc.). Abbreviations: CACNA2D1—Calcium voltage-gated channel auxiliary subunit alpha2delta 1; ENPP2—Ectonucleotide pyrophosphatase 2; F2RL3—Coagulation factor 2 receptor-like thrombin or trypsin receptor 3; GNAS—GNAS complex locus; OXT—Oxytocin prepropeptide; SELP—P selectin.
Figure 4. Long-term air pollution and gene–metabolite network analysis. Circular nodes represent genes, whereas square nodes represent metabolites. The color of each node corresponds to the category of the biological pathway to which that analyte belongs. Green—lipid metabolism; orange—cellular energy production; blue—amino acid metabolism; red—inflammation and immunity; yellow—coagulation; pink—endothelial function; white—oxidative stress; black—analytes that do not fit into the above categories (vitamins, purines, xanthines, etc.). Abbreviations: CACNA2D1—Calcium voltage-gated channel auxiliary subunit alpha2delta 1; ENPP2—Ectonucleotide pyrophosphatase 2; F2RL3—Coagulation factor 2 receptor-like thrombin or trypsin receptor 3; GNAS—GNAS complex locus; OXT—Oxytocin prepropeptide; SELP—P selectin.
Toxics 11 01014 g004
Figure 5. Short-term air pollution and protein–metabolite network analysis. Circular nodes represent proteins, whereas square nodes represent metabolites. The color of each node corresponds to the category of the biological pathway to which that analyte belongs. Green—lipid metabolism; orange—cellular energy production; blue—amino acid metabolism; red—inflammation and immunity; yellow—coagulation; pink—endothelial function; white—oxidative stress; black—analytes that do not fit into the above categories (vitamins, purines, xanthines, etc.). Abbreviations: 15(3)-HETE—15 Hydroxyeicosatetraenoic acid; ACE—Angiotensin converting enzyme; ALOX15—Arachidonate 15 lipoxygenase; APRT—Adenine phosphoribosyltransferase; APOB—Apolipoprotein B; CCL2—monocyte chemoattractant protein 1; CCL20—CC motif chemokine ligand 20; CKB—Creatine kinase B; CRP—C reactive protein; CSF2—Colony stimulating factor 2; CXCL1—CXC motif chemokine ligand 1; CXCL3—CXC motif chemokine ligand 3; CXCL5—CXC motif chemokine ligand 5; CXCL10—Interferon gamma induced protein 10; CXCL11—CXC motif chemokine ligand 11; EGF— Epidermal growth factor; EDN1—Endothelin 1; F3—Coagulation factor 3; IL1B—Interleukin 1 beta; IL2—Interleukin 2; IL4—Interleukin 4; IL6—Interleukin 6; IL8—Interleukin 8, ICAM1—Intercellular adhesion molecule 1; MMP2—Matrix metalloproteinase 2; MMP9—Matrix metalloproteinase 9; MPO—Myeloperoxidase; PLAT—Plasminogen activator, tissue type; VEGFA—Vascular endothelial growth factor A.
Figure 5. Short-term air pollution and protein–metabolite network analysis. Circular nodes represent proteins, whereas square nodes represent metabolites. The color of each node corresponds to the category of the biological pathway to which that analyte belongs. Green—lipid metabolism; orange—cellular energy production; blue—amino acid metabolism; red—inflammation and immunity; yellow—coagulation; pink—endothelial function; white—oxidative stress; black—analytes that do not fit into the above categories (vitamins, purines, xanthines, etc.). Abbreviations: 15(3)-HETE—15 Hydroxyeicosatetraenoic acid; ACE—Angiotensin converting enzyme; ALOX15—Arachidonate 15 lipoxygenase; APRT—Adenine phosphoribosyltransferase; APOB—Apolipoprotein B; CCL2—monocyte chemoattractant protein 1; CCL20—CC motif chemokine ligand 20; CKB—Creatine kinase B; CRP—C reactive protein; CSF2—Colony stimulating factor 2; CXCL1—CXC motif chemokine ligand 1; CXCL3—CXC motif chemokine ligand 3; CXCL5—CXC motif chemokine ligand 5; CXCL10—Interferon gamma induced protein 10; CXCL11—CXC motif chemokine ligand 11; EGF— Epidermal growth factor; EDN1—Endothelin 1; F3—Coagulation factor 3; IL1B—Interleukin 1 beta; IL2—Interleukin 2; IL4—Interleukin 4; IL6—Interleukin 6; IL8—Interleukin 8, ICAM1—Intercellular adhesion molecule 1; MMP2—Matrix metalloproteinase 2; MMP9—Matrix metalloproteinase 9; MPO—Myeloperoxidase; PLAT—Plasminogen activator, tissue type; VEGFA—Vascular endothelial growth factor A.
Toxics 11 01014 g005
Figure 6. Long-term air pollution and protein–metabolite network analysis. Circular nodes represent proteins, whereas square nodes represent metabolites. The color of each node corresponds to the category of the biological pathway to which that analyte belongs. Green—lipid metabolism; orange—cellular energy production; blue—amino acid metabolism; red—inflammation and immunity; yellow—coagulation; pink—endothelial function; white—oxidative stress; black—analytes that do not fit into the above categories (vitamins, purines, xanthines, etc.). Abbreviations: C3—Complement component 3; CCL2—Monocyte chemoattractant protein 1; CCL11—CC motif chemokine ligand 11; CP—Ceruloplasmin; CRP—C reactive protein; CSF3—Colony stimulating factor 3; HP—Haptoglobin; ICAM1—Intercellular adhesion molecule 1; IL6—Interleukin 6; IL8—Interleukin 8; IL10—Interleukin 10; PLAT—Plasminogen activator, tissue type; PLAU—Plasminogen activator, urokinase; SERPINA1—Alpha 1 proteinase inhibitor; SERPINE1—Plasminogen activator inhibitor 1.
Figure 6. Long-term air pollution and protein–metabolite network analysis. Circular nodes represent proteins, whereas square nodes represent metabolites. The color of each node corresponds to the category of the biological pathway to which that analyte belongs. Green—lipid metabolism; orange—cellular energy production; blue—amino acid metabolism; red—inflammation and immunity; yellow—coagulation; pink—endothelial function; white—oxidative stress; black—analytes that do not fit into the above categories (vitamins, purines, xanthines, etc.). Abbreviations: C3—Complement component 3; CCL2—Monocyte chemoattractant protein 1; CCL11—CC motif chemokine ligand 11; CP—Ceruloplasmin; CRP—C reactive protein; CSF3—Colony stimulating factor 3; HP—Haptoglobin; ICAM1—Intercellular adhesion molecule 1; IL6—Interleukin 6; IL8—Interleukin 8; IL10—Interleukin 10; PLAT—Plasminogen activator, tissue type; PLAU—Plasminogen activator, urokinase; SERPINA1—Alpha 1 proteinase inhibitor; SERPINE1—Plasminogen activator inhibitor 1.
Toxics 11 01014 g006
Disclaimer/Publisher’s Note: The statements, opinions and data contained in all publications are solely those of the individual author(s) and contributor(s) and not of MDPI and/or the editor(s). MDPI and/or the editor(s) disclaim responsibility for any injury to people or property resulting from any ideas, methods, instructions or products referred to in the content.

Share and Cite

MDPI and ACS Style

Casella, C.; Kiles, F.; Urquhart, C.; Michaud, D.S.; Kirwa, K.; Corlin, L. Methylomic, Proteomic, and Metabolomic Correlates of Traffic-Related Air Pollution in the Context of Cardiorespiratory Health: A Systematic Review, Pathway Analysis, and Network Analysis. Toxics 2023, 11, 1014. https://doi.org/10.3390/toxics11121014

AMA Style

Casella C, Kiles F, Urquhart C, Michaud DS, Kirwa K, Corlin L. Methylomic, Proteomic, and Metabolomic Correlates of Traffic-Related Air Pollution in the Context of Cardiorespiratory Health: A Systematic Review, Pathway Analysis, and Network Analysis. Toxics. 2023; 11(12):1014. https://doi.org/10.3390/toxics11121014

Chicago/Turabian Style

Casella, Cameron, Frances Kiles, Catherine Urquhart, Dominique S. Michaud, Kipruto Kirwa, and Laura Corlin. 2023. "Methylomic, Proteomic, and Metabolomic Correlates of Traffic-Related Air Pollution in the Context of Cardiorespiratory Health: A Systematic Review, Pathway Analysis, and Network Analysis" Toxics 11, no. 12: 1014. https://doi.org/10.3390/toxics11121014

APA Style

Casella, C., Kiles, F., Urquhart, C., Michaud, D. S., Kirwa, K., & Corlin, L. (2023). Methylomic, Proteomic, and Metabolomic Correlates of Traffic-Related Air Pollution in the Context of Cardiorespiratory Health: A Systematic Review, Pathway Analysis, and Network Analysis. Toxics, 11(12), 1014. https://doi.org/10.3390/toxics11121014

Note that from the first issue of 2016, this journal uses article numbers instead of page numbers. See further details here.

Article Metrics

Back to TopTop