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Background:
Systematic Review

Severe Acute Respiratory Syndrome and Particulate Matter Exposure: A Systematic Review

by
Sanjiti Podury
1,†,
Sophia Kwon
1,†,
Urooj Javed
1,
Muhammad S. Farooqi
1,
Yiwei Li
2,
Mengling Liu
2,3,
Gabriele Grunig
3 and
Anna Nolan
1,3,*
1
Department of Medicine, Division of Pulmonary, Critical Care and Sleep Medicine, New York University Grossman School of Medicine (NYUGSoM), New York, NY 10016, USA
2
Department of Population Health, Division of Biostatistics, New York University Grossman School of Medicine (NYUGSoM), New York, NY 10016, USA
3
Department of Medicine, Division of Environmental Medicine, New York University Grossman School of Medicine (NYUGSoM), New York, NY 10016, USA
*
Author to whom correspondence should be addressed.
†
These authors contributed equally to this work.
Life 2023, 13(2), 538; https://doi.org/10.3390/life13020538
Submission received: 12 January 2023 / Revised: 30 January 2023 / Accepted: 3 February 2023 / Published: 15 February 2023 / Corrected: 13 September 2023
(This article belongs to the Section Medical Research)
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Abstract

:
Background: Particulate matter (PM) exposure is responsible for seven million deaths annually and has been implicated in the pathogenesis of respiratory infections such as severe acute respiratory syndrome (SARS). Understanding modifiable risk factors of high mortality, resource burdensome C19 and exposure risks such as PM is key to mitigating their devastating effects. This systematic review focuses on the literature available, identifying the spatial and temporal variation in the role of quantified PM exposure in SARS disease outcome and planning our future experimental studies. Methods: The systematic review utilized keywords adhered to the PRISMA guidelines. We included original human research studies in English. Results: Initial search yielded N = 906, application of eligibility criteria yielded N = 46. Upon analysis of risk of bias N = 41 demonstrated high risk. Studies found a positive association between elevated PM2.5, PM10 and SARS-related outcomes. A geographic and temporal variation in both PM and C19’s role was observed. Conclusion: C19 is a high mortality and resource intensive disease which devastated the globe. PM exposure is also a global health crisis. Our systematic review focuses on the intersection of this impactful disease-exposure dyad and understanding the role of PM is important in the development of interventions to prevent future spread of viral infections.

1. Introduction

Coronaviruses (CoV) are a common cause of respiratory disease. However, at least two novel CoVs have plagued humanity [1,2]. In 2003, the severe acute respiratory syndrome-CoV-1 (SARS-CoV-1) virus caused SARS, which affected over 8000 people worldwide and caused the death of over 700. In 2019, the latest novel CoV was identified in Wuhan, China, and was named SARS-CoV-2 [1]. By early 2020 the spread of SARS-CoV-2 was declared a pandemic [3]. Coronavirus disease 2019 (COVID-19; C19) was the official name given by the World Health Organization (WHO) to the disease caused by SARS-CoV-2 [3]. In addition, to the clinical signs and symptoms of cough and fever, radiographic findings in severe cases include lung infiltrates that require hospitalization. The COVID-19 pandemic is the third leading cause of death since 2020, and continues to threaten the health and well-being of humanity [4]. Therefore, it is imperative that we further evaluate exacerbating factors such as particulate matter (PM) that may allow us to mitigate morbidity and mortality.
Elevated PM exposure is associated with cancer, obstructive airway disease, ischemic heart disease, stroke, and respiratory infections resulting in 7-million deaths annually [5,6,7]. PM-induced pulmonary inflammation causes acute exacerbation of cardiovascular disease due to hypercoagulability [8]. PM2.5 is known to activate tumor-associated signaling pathways by microRNA dysregulation, DNA methylation and by increasing the levels of inflammatory cells, cytokines. Altered macrophage-mediated inflammatory response to viral infections due to PM exposure has been hypothesized to play a role in these adverse outcomes [9]. Exposure to PM10 increases RNA viral replication and worsens infections in human lung epithelial cells [10]. PM is a known carrier for several viruses and increased the transportation of avian influenza virus H5N1 across long distances during dust storms in Beijing, China [11]. A 10 µg/m3 increase in PM2.5 concentration per day was associated with a significant rise in the incidence of measles [12]. A high incidence of influenza, hospitalization with culture negative pneumonia and respiratory syncytial virus spread in children was observed with increased PM exposure [13,14,15]. These PM-associated end-organ effects are biologically plausible mediators of C19-related morbidity. Transmissibility, severity, and mortality of COVID infection was variable throughout the pandemic, likely from innate, genetic, socioeconomic, and environmental contributors such as PM. With growing exposures due to wildfires, dust storms, and domestic cooking, it is important to further understand the role of PM in susceptibility, severity, and mortality due to viral respiratory illnesses like SARS [16,17,18].
Prior reviews investigating SARS and PM have focused on acute vs. chronic duration of exposure to air pollution, including PM and other ambient exposures such as NO2, SO2, O3 [19] and PM as a transmitting vector [20]. Several studies have implicated PM as a severity risk of C19 [21,22,23,24]. Specifically, mortality doubled in regions with higher pollution compared to less polluted areas despite similar ICU admission rates [25]. Each 1 ng/m3 increase in PM was associated with 8% higher C19 confounder adjusted deaths [22,23]. These reviews were limited in terms of quantifying exposure levels of PM, lack of analysis of spatial/temporal variation and inadequate assessment of bias. Our systematic review focuses on the literature available, identifying the spatial, temporal variation and thereby laying the foundation for planning our future experimental studies that will quantify the adverse effects of PM exposure in SARS disease susceptibility, severity and mortality.

2. Materials and Methods

Details of our systematic review were registered with PROSPERO (CRD42022316121; https://www.crd.york.ac.uk/prospero/#myprospero, accessed on 15 April 2022). A systematic review of the literature was performed adhering to the Preferred Reporting Items for Systematic Reviews and Meta-analysis (PRISMA) guidelines (Figure 1) [26]. Our Population, Exposure, Outcome (PEO) question was “In the adult population (P) with diagnosed SARS infection we performed a systematic review to identify the role of quantifiable particulate matter exposure (E) in disease susceptibility, severity and mortality (O)”.

2.1. Search Terms

A PUBMED Medical Subject Headings (MeSH) search was performed and the following entry terms were identified: (Severe Acute Respiratory Syndrome Virus OR SARS-Related Coronavirus OR SARS Related Coronavirus OR SARS-CoV OR Urbani SARS-Associated Coronavirus OR Urbani SARS Associated Coronavirus OR SARS Coronavirus OR Severe acute respiratory syndrome-related coronavirus OR Severe acute respiratory syndrome related coronavirus OR SARS-Associated Coronavirus OR SARS Associated Coronavirus) and (Ultrafine Fibers OR Fiber, Ultrafine OR Airborne Particulate Matter OR Air Pollutants, Particulate OR Ambient Particulate Matter OR Ultrafine Particulate Matter OR Ultrafine Particles OR Ultrafine Particle).
We then searched for articles that addressed how quantifiable particulate matter exposure is associated with the risk, severity and mortality due to SARS infection.
For the purposes of this review we define PM as a mixture of solid particles and liquid droplets found in the air [27]. Severe acute respiratory syndrome is a viral respiratory illness caused by coronaviruses first detected in 2003. This review focuses on both SARS-CoV-1 and SARS-CoV-2.
Articles were selected based on the following inclusion criteria: (1) adult population; (2) articles written in English; (3) articles should include the concentration of the PM exposure in association with incidence, prevalence, severity and mortality due to SARS (SARS-CoV-1 and SARS-CoV-2); (4) studies after November 2002.
Articles were excluded if they: (1) were not in English language; (2) did not quantify the concentration of PM exposure; (3) involved any non-human subjects/in vitro work/cell studies/immunohistochemistry; (4) were conducted on pediatric population; (5) focused on gaseous pollutants; or (6) were not original research. Two independent researchers conducted the literature search and determined studies that met the inclusion/exclusion criteria. A third investigator resolved disagreements.

2.2. Quality Assessment and Risk of Bias (RoB)

The overall RoB of the Cohort studies included in this review was determined with the approach described by Lee et al., 2020 (Figure 2A,B) [28]. We assessed three key domains of interest in the studies:

2.2.1. Assessment of Outcomes

Studies that performed Nucleic Acid Amplification Test (NAAT) using reverse-transcription polymerase chain reaction (RT-PCR) to detect SARS-CoV-2 RNA from the upper respiratory tract, physician diagnosis or other clinical tests, were categorized as low risk for detection bias. For studies with unknown methods of diagnosis, we categorized them as unclear risk of detection bias.

2.2.2. Adjustment for Confounding

Studies that adjusted for age, gender, individual levels of exposure or any other relevant covariates were categorized as low risk for this domain. Studies that did not adjust results for at least one covariate were categorized as high risk.

2.2.3. Control/Dose–Response Comparator Was Used for Comparative Analysis

Studies that included a control group were categorized as low risk for this domain, whereas those that did not were categorized as high risk. The three key domains were assessed for overall risk of bias judgment. Studies were categorized as low overall risk of bias if it was at low risk for all key domains, and high if any of the domains were high. For the time series studies only two domains, i.e., assessment of outcomes and adjustment for confounding were considered to analyze the risk of bias.

2.3. Data Management/Extraction

Based on the inclusion and exclusion criteria, we screened and selected manuscripts (EndNote™ 20.1). Each article was screened for study design, patient characteristics, sample size, tools used, incidence, severity and mortality of SARS in association with quantifiable PM exposure. Results from each database search were filtered for human subjects, English language, publication date (after November 2002) and imported into EndNote. The references were then screened for duplicates. Only original research papers were then reviewed for title, abstract and full text to ascertain eligibility. The references cited in the relevant articles were also examined. All results were screened by SP and MSF and further independently evaluated by AN. Disagreements were resolved by consensus (see Supplementary Tables S1–S3).

2.4. Data Synthesis (GraphPad Prism 9; Ver 9.2.0)

Data was generated from sources using our review PEO question and summarized into tables and plots (Figure 3). Qualitative data synthesis was performed for studies, using thematic analysis that included three stages: (i). identifying information about the selected studies’ methodology and findings; (ii). organizing them into subheadings and descriptive categories; and (iii). developing these categories into analytic themes [29].

3. Results/Synthesis

3.1. Literature Search

A total of 906 studies (334 PubMed and 572 Embase) were identified after filtering for relevant studies (Figure 1, Supplementary Tables S1 and S2). After removing duplicates, N = 732 were assessed for inclusion (abstract and title review). Finally, 46 original research articles were considered eligible [25,30,31,32,33,34,35,36,37,38,39,40,41,42,43,44,45,46,47,48,49,50,51,52,53,54,55,56,57,58,59,60,61,62,63,64,65,66,67,68,69,70,71,72,73,74] Table 1. Data from screening and extraction is available (Supplementary Tables S1–S3).
Risk of bias assessment was performed for outcome, confounders and control group assessment. Of the three domains assessed for cohort studies, N = 2 studies were high risk for outcome assessment, N = 24 were high risk due to lack of adjustment for confounders and N = 39 were high risk due to lack of a control group in their studies. Overall, N = 3 studies had low risk of bias, whereas N = 40 had high risk of bias
For the time series studies of the two domains assessed (outcome and confounders), N = 3 were low risk for outcome assessment and N= 1 was considered high risk for due to lack of adjustment for confounders. Overall, N = 2 were low risk for bias and N = 1 had high risk of bias.
Life 13 00538 g002
Figure 2. (A) Risk of Bias Assessment. Cohort Studies were evaluated in three main domains, i.e., outcome assessment, risk of confounding and presence of control dose-response comparator. (B) Risk of bias assessment. Time series studies, which were evaluated in two domains, i.e., outcome assessment, risk of confounding. Studies were color coded red or green for high vs. low risk of bias. Studies were categorized as low overall risk of bias if they were at low risk (green) for all key domains and high if any of the domains were high (red). RoB of * Meo [59]; † Meo [60]; ‡ Meo [61]; § Meo [68]; ‖ Meo [45]; Meo [62].
Figure 2. (A) Risk of Bias Assessment. Cohort Studies were evaluated in three main domains, i.e., outcome assessment, risk of confounding and presence of control dose-response comparator. (B) Risk of bias assessment. Time series studies, which were evaluated in two domains, i.e., outcome assessment, risk of confounding. Studies were color coded red or green for high vs. low risk of bias. Studies were categorized as low overall risk of bias if they were at low risk (green) for all key domains and high if any of the domains were high (red). RoB of * Meo [59]; † Meo [60]; ‡ Meo [61]; § Meo [68]; ‖ Meo [45]; Meo [62].
Life 13 00538 g002
Life 13 00538 g003
Figure 3. Overview of Data Synthesis. (A) Correlation coefficients were estimate for: PM2.5 and 10 and C19 Incidence and mortality for * Low green space countries and † High green space countries: Meo [62]; PM2.5 and 10 and C19 Incidence in Akan, Li, Sahoo and Fattorini, Sangkham; PM2.5 and 10 and C19 Prevalence in Zoran, Dragone; PM2.5 and C19 Incidence in Meo § [68], Meo ‖ [59], Meo Δ [60]; Bolano Ortiz; PM2.5 and C19 Prevalence in Semczuk; PM2.5 and C19 Mortality in Beig; PM2.5 and C19 Incidence, Prevalence, Mortality in Meo [61]; PM2.5 and C19 spread in Rovetta; PM2.5 and C19 Morbidity, Prevalence in Frontera; PM10 and C19 Incidence in Maatoug; PM10 and Mortality in Ghanim; PM10 and C19 Standardized (age) mortality ratio in Dettori. ‡ For studies where more than one city was analyzed, the highest correlation coefficient was plotted. Data grouped by region. (B) Relative risk of a mortality from C19 due to PM exposure and b Incidence of C19 due to PM exposure. Studies are grouped based on regions. (C) Odds ratios of α Hospitalization from C19 due to PM exposure and β Incidence of C19 due to PM exposure. Additional Information provided for relevant articles within each panel description.
Figure 3. Overview of Data Synthesis. (A) Correlation coefficients were estimate for: PM2.5 and 10 and C19 Incidence and mortality for * Low green space countries and † High green space countries: Meo [62]; PM2.5 and 10 and C19 Incidence in Akan, Li, Sahoo and Fattorini, Sangkham; PM2.5 and 10 and C19 Prevalence in Zoran, Dragone; PM2.5 and C19 Incidence in Meo § [68], Meo ‖ [59], Meo Δ [60]; Bolano Ortiz; PM2.5 and C19 Prevalence in Semczuk; PM2.5 and C19 Mortality in Beig; PM2.5 and C19 Incidence, Prevalence, Mortality in Meo [61]; PM2.5 and C19 spread in Rovetta; PM2.5 and C19 Morbidity, Prevalence in Frontera; PM10 and C19 Incidence in Maatoug; PM10 and Mortality in Ghanim; PM10 and C19 Standardized (age) mortality ratio in Dettori. ‡ For studies where more than one city was analyzed, the highest correlation coefficient was plotted. Data grouped by region. (B) Relative risk of a mortality from C19 due to PM exposure and b Incidence of C19 due to PM exposure. Studies are grouped based on regions. (C) Odds ratios of α Hospitalization from C19 due to PM exposure and β Incidence of C19 due to PM exposure. Additional Information provided for relevant articles within each panel description.
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3.2. Study Characteristics

As the C19 pandemic swept the globe from 31 December 2019, understanding the phenotype of both the disease and associated risk factors of disease severity has been challenging. Cohort studies were the predominant type (N = 43), while N = 3 were time-series studies [31,33,43]. The association of PM in the context of C19 surges, geographic location, and type of SARS infection are also of great interest and were further examined. In the context of these categories we will also discuss how PM2.5 and PM10 have played a role in SARS severity and spread.

3.3. Coronaviruses Have Been the Cause of Several Outbreaks

SARS-1 originated in Guangdong, China in 2003, and in six months had spread to more than two dozen countries resulting in at least 774 deaths [75]. Due to limited transmission, there are few studies that focus on this pathogen. Only one study that analyzed and noted positive association between PM and SARS-1 infection was noted by Kan et al., who found that for every 10 μg/m3 increase in PM10 the Relative risk (RR) of daily SARS mortality was 1.06 (1.00–1.12) [30]. There were few variants or recurrence of SARS-1 [76]. In contrast, the SARS-CoV-2 virus has several variants and lineages, and been responsible for at least 6 million deaths worldwide [77,78].

3.4. Temporal Relationship of PM and SARS

A decline in the incidence, mortality, and hospitalization was observed during the later pandemic period, from approximately late April–June 2020. A temporal analysis in Beijing from 25 April–31 May 2020 showed a declining trend in daily mortality count [30]. While this could be attributed to the implementation of more stringent mitigation measures, there are several other factors that may be relevant [79]. To understand the role of PM in the temporal variegation of outcomes, investigators have examined the impact of PM during the early and later phase of the pandemic. Dragone et al. noted that PM levels exceeded the daily limit during two early pandemic periods (16–25 February and 17–20 March 2020) in Italy. During this period, areas with the highest levels of ambient PM also had the highest number of infected populations [40]. Similarly, Li et al. noted a positive association between C19 cases and PM2.5 through a risks study using days with the highest and lowest incidence numbers in February [31]. Analysis investigating C19 cases in January–April 2020 in India showed that a 10 µg/m3 increase in PM2.5 and PM10 resulted in 2.21% (95% CI:1.13–3.29), 2.67% (95% CI: 0.33–5.01), increase in daily counts of C19 infected cases, respectively [33]. The early pandemic was the focus of 14/46 studies. PM was positively associated with C19 for a number of studies in the following aspects: incidence (N = 6); prevalence (N = 2); morbidity (N = 1) and mortality (N = 6). Negative association was observed with mortality (N = 1) and incidence (N = 1), and equivocal results were reported by N = 1 [34,52,63]. Of the 32 studies from the later pandemic period, PM was positively associated with C19 based on: incidence (N = 17); prevalence (N = 4); morbidity (N = 6) and mortality (N = 18). Negative association with incidence was observed in N = 2. Equivocal results reported by N = 4 [72].

3.5. Understanding Geographic Epidemiology Based on Region-Based Outcomes

Few, if any, areas of the globe have been left unaffected by the C19 pandemic. Meo et al. studied 17 countries across the globe and noted a significant positive association between PM and C19 incidence [45]. Certain areas like Malawi and Indonesia have been disproportionately impacted, and reported the highest case fatality rates on 8/26/22 [80].
Europe was the setting of (N = 16) studies [25,39,40,41,42,43,44,45,46,47,48,49,50,51,52,53]. A statistically significant correlation between PM2.5 and C19 cases was observed in Lombardy, Italy by Rovetta et al. [42]. With 1 unit increase in PM2.5 levels, the number of SARS-CoV-2 infections significantly increased by 0.1% in London [45]. Similarly, Scalsky et al. observed that PM2.5 levels recorded in 2010 were significantly associated with an increased SARS-CoV-2 positive testing likelihood (OR = 1.063, 95% CI 1.04–1.09) [46]. Overall, PM was positively associated with C19: mortality (N = 9); incidence (N = 6); prevalence (N = 4); morbidity (N = 2). Equivocal results were reported by (N = 2) [52,53].
Similarly, of the nine studies dedicated to Asia [30,31,32,33,34,35,36,37,38], a significant positive association was seen between PM2.5 and C19 cases in Wuhan (R2 = 0.13, p < 0.05) and Xiagan (R2 = 0.223, p < 0.01) [31]. In Hubei, a 10-µg/m3 rise in levels of PM2.5 (lag 0–14 was positively associated with RR of 1.050 (95% CI: 1.028–1.073) daily newly confirmed cases [32]. Overall, a positive association was observed between PM and C19 incidence (N = 4); mortality (N = 3); prevalence (N = 1).
Six studies with a focus on the Middle East were identified [66,67,68,69,70,71]. In a study conducted in Riyadh, Jeddah and Makkah, PM10 positively correlated to daily cases of C19 (Pearson correlation coefficients were 0.68, 0.54, 0.38, respectively) [66]. Similar observations were made in three Iranian cities where exposure to PM2.5 for several days showed significant association to confirmed cases [67]. Increase in PM2.5 due to a sandstorm in Saudi Arabia was associated with a significant increase in the number of SARS-CoV-2 cases (Spearman’s correlation coefficient ρ = 0.944 (<0.0001)) [68].
In the U.S, data from seven New York City (NYC) hospitals concluded that higher and long-term exposure to PM2.5 was associated with an increased risk of mortality (RR 1.11, 95%CI: 1.02–1.21) and ICU admission (RR 1.13, 95%CI: 1.00–1.28) per 1-µg/m3 increase in PM2.5 [55]. Similarly, a study from five regions noted that the number of cases significantly augmented with a rise in the levels of PM2.5 (ρ = 0.176, p < 0.001). PM was positively associated with C19: incidence rate (N = 7); mortality (N = 4) and prevalence (N = 1). A negative association with mortality was observed by N = 2 [63,64].
Similarly, as in 2/3 Latin American countries, PM and C19 incidence and mortality had a positive association. In contrast, one study reported equivocal results [72]. Specifically, an increase of 1 µg/m3 in PM2.5 increased the mortality risk by approximately 7.4% in Mexico City metropolitan area in October 2020 [73].

3.6. Aerodynamic Diameter of PM and SARS (PM2.5 vs. PM10)

PM is a heterogeneous mixture of solid particles and liquid droplets found in the air. It is commonly grouped by diameter into fine PM2.5 (<2.5 mm) and coarse PM10 (<10 mm). PM2.5 is more likely to travel and deposit deeper in the lungs like the alveolus, whereas PM10 can deposit on the surfaces of larger airways inducing inflammation. Ambient air pollutants are risk factors for cardiopulmonary diseases and responsible for over 6 million annual deaths.
The role of PM2.5 was assessed by 19/46 studies. PM2.5 was positively associated with C19: incidence (N = 11); mortality (N = 6); morbidity (N = 5); and prevalence (N = 1). Negative association with prevalence was seen in only one study [63].
PM10 was evaluated in eight studies, and it was positively associated with C19 incidence (N = 5); prevalence (N = 1); and mortality (N = 1). Finally, PM10 and PM2.5 were evaluated by N = 19 studies. A positive association with C19 incidence (N = 9); mortality (N = 5) was seen. Negative association was seen in N = 2 and equivocal results were identified in N = 1.

4. Discussion

Our systematic review identified the role of PM to be important in the incidence, mortality and morbidity due to SARS infection. These studies had significant differences in the populations, methods, and outcomes that were studied (Table 1). We identified three themes, temporality, PM size/dose, and spatial, which define the relationship of C19 with PM exposure. Evaluating the heterogeneous characteristics of the disease across different territories and phases of the pandemic is important to implement measures to contain spread.
Longer durations and higher levels of PM increased the risk of ICU admissions and deaths due to C19. Several mechanisms have been hypothesized. Oxidative stress and disruptive immune and/or neuroendocrine function can result in increased severity of viral pulmonary infections [81,82].
PM has been associated with enhanced infection with RNA viruses such as SARS [83]. PM concentration and virus dissemination were positively correlated in the spread of measles in several studies [12]. A 10 µg/m3 increase in PM2.5 was associated with increased measles incidence. A similar observation was also noted with respiratory syncytial virus, which causes bronchiolitis and pneumonia [15]. A study in Kuala Lumpur collected PM2.5 in four study sites and found the highest levels of SARS-CoV-2 RNA on PM2.5 [84]. PM exposure in murine models was associated with upregulated Angiotensin converting enzyme 2 (ACE2) and Transmembrane protease serine 2 (TMPRSS2), receptors required for SARS entry into host cells [85,86]. Exposure to PM induced Renin Angiotensin—aldosterone (RAAS) and Kallikrein—kinin systems (KKS), involved in cardiovascular and lung diseases. PM-induced damage to lung cells increases the inflammatory state which can increase the mortality and severity of C19 [87,88]. Therefore, it may be important to implement measures to reduce PM emissions in the atmosphere. Studies in this review further highlighted the importance of measures such as lockdown and movement restrictions, public awareness regarding pollution via media tools and professional programs and strengthening rural infrastructure that may limit the infectivity of SARS [69,72].

4.1. Geographic Epidemiology

Variation in C19 outcomes in different regions could be attributed to social determinants of health such as poverty, access to health care facilities and health literacy. Populations with limited resources also have a high prevalence of chronic health conditions [89,90]. Urban areas with industries had elevated levels of PM2.5. Spatial variation in the concentration of PM2.5 in some areas such as California’s central valley and Italy’s Po Valley can be contributed to geographical features with climate inversion events that trap these pollutants. The air trapping in these regions can also lead to chronic exposure to these particulates increasing the risk for respiratory and cardiovascular diseases which further enhances the risk [91].

4.2. Temporal Association

Worsening asthma and COPD leading to hospitalization has been noted with short-term (up to 24 h) exposures to PM10 [92]. Long-term PM2.5 is known to increase the risk of COPD, a known risk factor for severe C19 infection [93].
An NYC hospital-based study noted that mortality rates dropped from 25.6% in March to 7.6% in August 2020 [94]. This reduction in the number of severe C19 cases that was observed during the later pandemic phase could be attributed to multiple reasons, including the development of immunity due to availability of vaccinations, and treatment modalities including corticosteroids, targeted antiviral therapy, and anti-cytokine treatments. The quarantine restrictions and mask policies enforced by many countries also could have reduced exposure to ambient PM [95,96,97].
Strengths of Systematic Review. This review focuses on the environmental inducers of infectious diseases, a global health issue. It incorporates the variation in PM and the risk of Coronaviruses geographically. Manuscripts from across the globe were reviewed, which made this study more generalizable. Each article was screened for study design and was further subcategorized to understand temporal, spatial variability.
Our systematic review has several limitations. Since assessing the risk of bias inherently has some level of subjectivity, we categorized high- vs. low-risk studies using a determined set of criteria. While many of the studies that we assessed had a high risk of bias, future studies would benefit from assessing their data in the context of potential confounders including age, gender, and comorbidities. Several variants have been identified since the 2019; however, our manuscript does not discuss the disparity in disease outcomes for different variants [77]. The manuscripts that have been included in our review have not determined the variants that were present in their communities during their data acquisition [30,72,73]. There is also a variation in the PM concentration across countries and regions that could add to the bias. However, only N = 6 studies analyzed the spatial variation [32,38,40,55,62,65]. Also, additional studies not identified in the two large databases could have caused selection bias. There is a limitation in data available on SARS-1, which could be due to selection of manuscripts in the English language. Finally, while meta-analysis in the context of a systematic review may provide a more accurate effects estimate, for this to occur we would require source data availability and methodologic similarity. We therefore reviewed all 46 studies for available supplemental data and for similar methodologies and outcomes. Studies were grouped according to the statistical outcomes measured, i.e., relative risk vs. odd’s ratio. Seven out of 46 evaluated relative risks. Four out of these seven had supplementary data available. Out of the three studies that evaluated the odds ratio, one had supplementary data available. Unfortunately, only two studies performed the Generalized additive models (GAM) to analyze the association between PM and C19 outcomes; however, the C19 outcomes were different (Incidence vs. morbidity), which limits our ability to perform meta-analysis.

5. Conclusions

In conclusion, these studies have expanded our knowledge of PM exposure and its association with SARS infection. The review highlights the clinical impact of PM and the need for implementing measures to combat climate change and dangerous levels of environmental toxin. There was a spatial and temporal variation in the characteristics of the disease. Overall, it was seen that exposure to quantified PM was associated with increased incidence, mortality and morbidity to C19. Measures can be taken on both global and a personal level, such as improving air ventilation design and systems in enclosed spaces and buildings, restricting wildlife trading and deforestation, and training our healthcare professionals to educate masses on taking personal steps to ensure less production and exposure to pollution, such as using facemasks, and walking/cycling instead of motorized transport.

6. Future Plans

Future experimental studies will include developing our understanding of the role of PM in accentuating the response to pathogens such as C19, understanding the effects estimate for chronic vs. short-term exposure to PM, and in furthering our management of PM exposure to limit severity of viral infections. These projects will focus on quantifying the association of PM concentrations (by zip code and/or geocoding) and the incidence of C19 related morbidity and mortality.

Supplementary Materials

The following supporting information can be downloaded at: https://www.mdpi.com/2075-1729/13/2/538/s1. Supplementary Table S1. EMBASE Identified Manuscripts (N = 572); Supplementary Table S2. PUBMED Identified Manuscripts (N = 334); Supplementary Table S3. Manuscript Exclusions. S3a. Case reports/series; S3b. Commentary/Expert opinion/Conference Abstracts; S3c. Duplicates S3d. in vitro/Cell studies; S3e. Letters to the editor; S3f. Non-English Manuscripts; S3g. Pediatric Studies; S3h. Pilot studies/Study designs; S3i. Reviews/Meta-analysis; S3j. Unrelated.

Author Contributions

All authors made substantial contributions to the study. All authors participated in study conception and design, data analysis/interpretation, and manuscript preparation. Primary investigator A.N.; Study design A.N., S.P., U.J., S.K.; Statistical Analysis A.N., S.P., M.S.F., M.L., Y.L.; Data interpretation A.N., S.P., M.S.F., S.K., U.J. All authors participated in writing, revising and approve the final manuscript. All authors have read and agreed to the published version of the manuscript.

Funding

National Institutes of Health (NIH): National Heart Lung and Blood Institute (NHLBI) R01HL119326; National Institute of Environmental Health Science (NIEHS) R01ES032808; National Center for Advancing Translational Sciences (NCATS) KL2TR001446; Centers for Disease Control/National Institute for Occupational Safety and Health (CDC/NIOSH) U01-[OH011300, OH012069, OH011855] and Stony Wold-Herbert Fund.

Institutional Review Board Statement

Not applicable.

Informed Consent Statement

Not applicable.

Data Availability Statement

No new data were created in this study.

Conflicts of Interest

The authors declare no conflict of interest.

Abbreviations

PMParticulate matter
SARSSevere acute respiratory syndrome
CoVCoronaviruses
ARDSAcute respiratory distress syndrome
C19COVID-19
PEOPopulation, Exposure, Outcome
RoBRisk of bias
RT-PCRReverse transcription polymerase chain reaction
RAASRenin angiotensin aldosterone system
TMPRSS2Transmembrane serine protease 2
ACEAngiotensin converting enzyme
KKS(Kallikrein-kinin) systems
COPDChronic Obstructive Pulmonary Disease
PRISMAPreferred Reporting Items for Systematic Reviews and Meta-Analyses
UKUnited Kingdom
USUnited States
CFRCase Fatality Rate

References

  1. Basics of COVID-19. Available online: https://www.cdc.gov/coronavirus/2019-ncov/your-health/about-covid-19/basics-covid-19.html (accessed on 7 January 2023).
  2. Chafekar, A.; Fielding, B.C. MERS-CoV: Understanding the Latest Human Coronavirus Threat. Viruses 2018, 10, 93. [Google Scholar] [CrossRef] [PubMed]
  3. COVID-19 Timeline. Available online: https://www.cdc.gov/museum/timeline/covid19.html#:~:text=February%2011%2C%202020,of%20%E2%80%9CCoronavirus%20Disease%202019.%E2%80%9D (accessed on 7 January 2023).
  4. COVID-19 Was Third Leading Cause of Death in U.S. Available online: https://www.cdc.gov/media/releases/2022/s0422-third-leading-cause.html (accessed on 21 November 2022).
  5. U.S. Environmental Protection Agency. Health and Environmental Effects of Particulate Matter (PM). Available online: https://www.epa.gov/pm-pollution/health-and-environmental-effects-particulate-matter-pm (accessed on 24 June 2022).
  6. Cai, B.; Xia, T.; Qian, Y.; Lu, H.; Cai, R.; Wang, C. Association Between Fine Particulate Matter and Fatal Hemorrhagic Stroke Incidence: A Time Stratified Case-Crossover Study in Shanghai, China. J. Occup. Environ. Med. 2020, 62, 916–921. [Google Scholar] [CrossRef] [PubMed]
  7. 9 out of 10 People Worldwide Breathe Polluted Air, but More Countries Are Taking Action. Available online: https://www.who.int/news/item/02-05-2018-9-out-of-10-people-worldwide-breathe-polluted-air-but-more-countries-are-taking-action (accessed on 7 July 2022).
  8. Seaton, A.; MacNee, W.; Donaldson, K.; Godden, D. Particulate air pollution and acute health effects. Lancet 1995, 345, 176–178. [Google Scholar] [CrossRef]
  9. Becker, S.; Soukup, J.M. Exposure to urban air particulates alters the macrophage-mediated inflammatory response to respiratory viral infection. J. Toxicol. Environ. Health A 1999, 57, 445–457. [Google Scholar] [CrossRef]
  10. Mishra, R.; Krishnamoorthy, P.; Gangamma, S.; Raut, A.A.; Kumar, H. Particulate matter (PM10) enhances RNA virus infection through modulation of innate immune responses. Environ. Pollut. 2020, 266, 115148. [Google Scholar] [CrossRef] [PubMed]
  11. Chen, P.S.; Tsai, F.T.; Lin, C.K.; Yang, C.Y.; Chan, C.C.; Young, C.Y.; Lee, C.H. Ambient influenza and avian influenza virus during dust storm days and background days. Environ. Health Perspect. 2010, 118, 1211–1216. [Google Scholar] [CrossRef] [PubMed]
  12. Chen, G.; Zhang, W.; Li, S.; Williams, G.; Liu, C.; Morgan, G.G.; Jaakkola, J.J.K.; Guo, Y. Is short-term exposure to ambient fine particles associated with measles incidence in China? A multi-city study. Environ. Res. 2017, 156, 306–311. [Google Scholar] [CrossRef]
  13. Croft, D.P.; Zhang, W.; Lin, S.; Thurston, S.W.; Hopke, P.K.; Masiol, M.; Squizzato, S.; van Wijngaarden, E.; Utell, M.J.; Rich, D.Q. The Association between Respiratory Infection and Air Pollution in the Setting of Air Quality Policy and Economic Change. Ann. Am. Thorac. Soc. 2019, 16, 321–330. [Google Scholar] [CrossRef]
  14. Croft, D.P.; Zhang, W.; Lin, S.; Thurston, S.W.; Hopke, P.K.; van Wijngaarden, E.; Squizzato, S.; Masiol, M.; Utell, M.J.; Rich, D.Q. Associations between Source-Specific Particulate Matter and Respiratory Infections in New York State Adults. Environ. Sci. Technol. 2020, 54, 975–984. [Google Scholar] [CrossRef]
  15. Ye, Q.; Fu, J.F.; Mao, J.H.; Shang, S.Q. Haze is a risk factor contributing to the rapid spread of respiratory syncytial virus in children. Environ. Sci. Pollut. Res. Int. 2016, 23, 20178–20185. [Google Scholar] [CrossRef]
  16. Aguilera, R.; Corringham, T.; Gershunov, A.; Benmarhnia, T. Wildfire smoke impacts respiratory health more than fine particles from other sources: Observational evidence from Southern California. Nat. Commun. 2021, 12, 1493. [Google Scholar] [CrossRef] [PubMed]
  17. Khaniabadi, Y.O.; Daryanoosh, S.M.; Amrane, A.; Polosa, R.; Hopke, P.K.; Goudarzi, G.; Mohammadi, M.J.; Sicard, P.; Armin, H. Impact of Middle Eastern Dust storms on human health. Atmos. Pollut. Res. 2017, 8, 606–613. [Google Scholar] [CrossRef]
  18. Kim Oanh, N.T.; Nghiem, L.H.; Phyu, Y.L. Emission of Polycyclic Aromatic Hydrocarbons, Toxicity, and Mutagenicity from Domestic Cooking Using Sawdust Briquettes, Wood, and Kerosene. Environ. Sci. Technol. 2002, 36, 833–839. [Google Scholar] [CrossRef]
  19. Copat, C.; Cristaldi, A.; Fiore, M.; Grasso, A.; Zuccarello, P.; Signorelli, S.S.; Conti, G.O.; Ferrante, M. The role of air pollution (PM and NO2) in COVID-19 spread and lethality: A systematic review. Environ. Res. 2020, 191, 110129. [Google Scholar] [CrossRef]
  20. Maleki, M.; Anvari, E.; Hopke, P.K.; Noorimotlagh, Z.; Mirzaee, S.A. An updated systematic review on the association between atmospheric particulate matter pollution and prevalence of SARS-CoV-2. Environ. Res. 2021, 195, 110898. [Google Scholar] [CrossRef]
  21. Frontera, A.; Martin, C.; Vlachos, K.; Sgubin, G. Regional air pollution persistence links to COVID-19 infection zoning. J. Infect. 2020, 81, 318–356. [Google Scholar] [CrossRef]
  22. Wu, X.; Nethery, R.C.; Sabath, B.M.; Braun, D.; Dominici, F. Exposure to air pollution and COVID-19 mortality in the United States: A nationwide cross-sectional study. medRxiv 2020. [Google Scholar] [CrossRef]
  23. Wang, B.; Chen, H.; Chan, Y.L.; Oliver, B.G. Is there an association between the level of ambient air pollution and COVID-19? Am. J. Physiol. Lung Cell. Mol. Physiol. 2020, 319, L416–L421. [Google Scholar] [CrossRef] [PubMed]
  24. Coker, E.S.; Cavalli, L.; Fabrizi, E.; Guastella, G.; Lippo, E.; Parisi, M.L.; Pontarollo, N.; Rizzati, M.; Varacca, A.; Vergalli, S. The Effects of Air Pollution on COVID-19 Related Mortality in Northern Italy. Environ. Resour. Econ. 2020, 76, 611–634. [Google Scholar] [CrossRef]
  25. Frontera, A.; Cianfanelli, L.; Vlachos, K.; Landoni, G.; Cremona, G. Severe air pollution links to higher mortality in COVID-19 patients: The “double-hit” hypothesis. J. Infect. 2020, 81, 255–259. [Google Scholar] [CrossRef] [PubMed]
  26. Page, M.J.; McKenzie, J.E.; Bossuyt, P.M.; Boutron, I.; Hoffmann, T.C.; Mulrow, C.D.; Shamseer, L.; Tetzlaff, J.M.; Akl, E.A.; Brennan, S.E.; et al. The PRISMA 2020 statement: An updated guideline for reporting systematic reviews. Rev. Esp. Cardiol. 2021, 74, 790–799. [Google Scholar] [CrossRef]
  27. Particulate Matter (PM) Basics. Available online: https://www.epa.gov/pm-pollution/particulate-matter-pm-basics (accessed on 26 November 2022).
  28. Lee, K.K.; Bing, R.; Kiang, J.; Bashir, S.; Spath, N.; Stelzle, D.; Mortimer, K.; Bularga, A.; Doudesis, D.; Joshi, S.S.; et al. Adverse health effects associated with household air pollution: A systematic review, meta-analysis, and burden estimation study. Lancet Glob. Health 2020, 8, e1427–e1434. [Google Scholar] [CrossRef]
  29. Systematic Reviews. Available online: https://rmit.libguides.com/systematicreviews/synthesise (accessed on 6 January 2022).
  30. Kan, H.D.; Chen, B.H.; Fu, C.W.; Yu, S.Z.; Mu, L.N. Relationship between ambient air pollution and daily mortality of SARS in Beijing. Biomed. Environ. Sci. 2005, 18, 1–4. [Google Scholar]
  31. Li, H.; Xu, X.L.; Dai, D.W.; Huang, Z.Y.; Ma, Z.; Guan, Y.J. Air pollution and temperature are associated with increased COVID-19 incidence: A time series study. Int. J. Infect. Dis. 2020, 97, 278–282. [Google Scholar] [CrossRef]
  32. Lu, B.; Wu, N.; Jiang, J.; Li, X. Associations of acute exposure to airborne pollutants with COVID-19 infection: Evidence from China. Environ. Sci. Pollut. Res. Int. 2021, 28, 50554–50564. [Google Scholar] [CrossRef] [PubMed]
  33. Sahoo, M.M. Significance between air pollutants, meteorological factors, and COVID-19 infections: Probable evidences in India. Environ. Sci. Pollut. Res. Int. 2021, 28, 40474–40495. [Google Scholar] [CrossRef]
  34. Sangkham, S.; Thongtip, S.; Vongruang, P. Influence of air pollution and meteorological factors on the spread of COVID-19 in the Bangkok Metropolitan Region and air quality during the outbreak. Environ. Res. 2021, 197, 111104. [Google Scholar] [CrossRef]
  35. Shao, L.; Cao, Y.; Jones, T.; Santosh, M.; Silva, L.F.O.; Ge, S.; da Boit, K.; Feng, X.; Zhang, M.; BéruBé, K. COVID-19 mortality and exposure to airborne PM(2.5): A lag time correlation. Sci. Total Environ. 2022, 806, 151286. [Google Scholar] [CrossRef]
  36. Yao, Y.; Pan, J.; Wang, W.; Liu, Z.; Kan, H.; Qiu, Y.; Meng, X.; Wang, W. Association of particulate matter pollution and case fatality rate of COVID-19 in 49 Chinese cities. Sci. Total Environ. 2020, 741, 140396. [Google Scholar] [CrossRef]
  37. Beig, G.; Bano, S.; Sahu, S.K.; Anand, V.; Korhale, N.; Rathod, A.; Yadav, R.; Mangaraj, P.; Murthy, B.S.; Singh, S.; et al. COVID-19 and environmental -weather markers: Unfolding baseline levels and veracity of linkages in tropical India. Environ. Res. 2020, 191, 110121. [Google Scholar] [CrossRef]
  38. Laxmipriya, S.; Narayanan, R.M. COVID-19 and its relationship to particulate matter pollution—Case study from part of greater Chennai, India. Mater. Today Proc. 2021, 43, 1634–1639. [Google Scholar] [CrossRef]
  39. Bianconi, V.; Bronzo, P.; Banach, M.; Sahebkar, A.; Mannarino, M.R.; Pirro, M. Particulate matter pollution and the COVID-19 outbreak: Results from Italian regions and provinces. Arch. Med. Sci. 2020, 16, 985–992. [Google Scholar] [CrossRef]
  40. Dragone, R.; Licciardi, G.; Grasso, G.; Del Gaudio, C.; Chanussot, J. Analysis of the Chemical and Physical Environmental Aspects that Promoted the Spread of SARS-CoV-2 in the Lombard Area. Int. J. Environ. Res. Public Health 2021, 18, 1226. [Google Scholar] [CrossRef]
  41. Fattorini, D.; Regoli, F. Role of the chronic air pollution levels in the COVID-19 outbreak risk in Italy. Environ. Pollut. 2020, 264, 114732. [Google Scholar] [CrossRef] [PubMed]
  42. Rovetta, A.; Bhagavathula, A.S.; Castaldo, L. Modeling the Epidemiological Trend and Behavior of COVID-19 in Italy. Cureus 2020, 12, e9884. [Google Scholar] [CrossRef] [PubMed]
  43. Moshammer, H.; Poteser, M.; Hutter, H.P. COVID-19 and air pollution in Vienna-a time series approach. Wien. Klin. Wochenschr. 2021, 133, 951–957. [Google Scholar] [CrossRef]
  44. Dettori, M.; Deiana, G.; Balletto, G.; Borruso, G.; Murgante, B.; Arghittu, A.; Azara, A.; Castiglia, P. Air pollutants and risk of death due to COVID-19 in Italy. Environ. Res. 2021, 192, 110459. [Google Scholar] [CrossRef]
  45. Meo, S.A.; Adnan Abukhalaf, A.; Sami, W.; Hoang, T.D. Effect of environmental pollution PM2.5, carbon monoxide, and ozone on the incidence and mortality due to SARS-CoV-2 infection in London, United Kingdom. J. King Saud Univ. Sci. 2021, 33, 101373. [Google Scholar] [CrossRef]
  46. Scalsky, R.J.; Chen, Y.J.; Ying, Z.; Perry, J.A.; Hong, C.C. The Social and Natural Environment′s Impact on SARS-CoV-2 Infections in the UK Biobank. Int. J. Environ. Res. Public Health 2022, 19, 533. [Google Scholar] [CrossRef]
  47. Kogevinas, M.; Castaño-Vinyals, G.; Karachaliou, M.; Espinosa, A.; de Cid, R.; Garcia-Aymerich, J.; Carreras, A.; Cortés, B.; Pleguezuelos, V.; Jiménez, A.; et al. Ambient Air Pollution in Relation to SARS-CoV-2 Infection, Antibody Response, and COVID-19 Disease: A Cohort Study in Catalonia, Spain (COVICAT Study). Environ. Health Perspect. 2021, 129, 117003. [Google Scholar] [CrossRef]
  48. Marquès, M.; Correig, E.; Ibarretxe, D.; Anoro, E.; Antonio Arroyo, J.; Jericó, C.; Borrallo, R.M.; Miret, M.; Näf, S.; Pardo, A.; et al. Long-term exposure to PM10 above WHO guidelines exacerbates COVID-19 severity and mortality. Environ. Int. 2022, 158, 106930. [Google Scholar] [CrossRef]
  49. Veronesi, G.; De Matteis, S.; Calori, G.; Pepe, N.; Ferrario, M.M. Long-term exposure to air pollution and COVID-19 incidence: A prospective study of residents in the city of Varese, Northern Italy. Occup. Environ. Med. 2022, 79, 192–199. [Google Scholar] [CrossRef] [PubMed]
  50. Zoran, M.A.; Savastru, R.S.; Savastru, D.M.; Tautan, M.N.; Baschir, L.A.; Tenciu, D.V. Assessing the impact of air pollution and climate seasonality on COVID-19 multiwaves in Madrid, Spain. Environ. Res. 2022, 203, 111849. [Google Scholar] [CrossRef] [PubMed]
  51. Semczuk-Kaczmarek, K.; Rys-Czaporowska, A.; Sierdzinski, J.; Kaczmarek, L.D.; Szymanski, F.M.; Platek, A.E. Association between air pollution and COVID-19 mortality and morbidity. Intern. Emerg. Med. 2021, 17, 467–473. [Google Scholar] [CrossRef]
  52. Di Ciaula, A.; Bonfrate, L.; Portincasa, P.; Appice, C.; Belfiore, A.; Binetti, M.; Cafagna, G.; Campanale, G.; Carrieri, A.; Cascella, G.; et al. Nitrogen dioxide pollution increases vulnerability to COVID-19 through altered immune function. Environ. Sci. Pollut. Res. Int. 2022, 29, 44404–44412. [Google Scholar] [CrossRef]
  53. Czwojdzińska, M.; Terpińska, M.; Kuźniarski, A.; Płaczkowska, S.; Piwowar, A. Exposure to PM2.5 and PM10 and COVID-19 infection rates and mortality: A one-year observational study in Poland. Biomed. J. 2021, 44, S25–S36. [Google Scholar] [CrossRef] [PubMed]
  54. Berg, K.; Romer Present, P.; Richardson, K. Long-term air pollution and other risk factors associated with COVID-19 at the census tract level in Colorado. Environ. Pollut. 2021, 287, 117584. [Google Scholar] [CrossRef]
  55. Bozack, A.; Pierre, S.; DeFelice, N.; Colicino, E.; Jack, D.; Chillrud, S.N.; Rundle, A.; Astua, A.; Quinn, J.W.; McGuinn, L.; et al. Long-Term Air Pollution Exposure and COVID-19 Mortality: A Patient-Level Analysis from New York City. Am. J. Respir. Crit. Care Med. 2021, 205, 651–662. [Google Scholar] [CrossRef]
  56. Fang, F.; Mu, L.; Zhu, Y.; Rao, J.; Heymann, J.; Zhang, Z.F. Long-Term Exposure to PM2.5, Facemask Mandates, Stay Home Orders and COVID-19 Incidence in the United States. Int. J. Environ. Res. Public Health 2021, 18, 6274. [Google Scholar] [CrossRef]
  57. Kiser, D.; Elhanan, G.; Metcalf, W.J.; Schnieder, B.; Grzymski, J.J. SARS-CoV-2 test positivity rate in Reno, Nevada: Association with PM2.5 during the 2020 wildfire smoke events in the western United States. J. Expo. Sci. Environ. Epidemiol. 2021, 31, 797–803. [Google Scholar] [CrossRef]
  58. Mendy, A.; Wu, X.; Keller, J.L.; Fassler, C.S.; Apewokin, S.; Mersha, T.B.; Xie, C.; Pinney, S.M. Air pollution and the pandemic: Long-term PM2.5 exposure and disease severity in COVID-19 patients. Respirology 2021, 26, 1181–1187. [Google Scholar] [CrossRef]
  59. Meo, S.A.; Abukhalaf, A.A.; Alessa, O.M.; Alarifi, A.S.; Sami, W.; Klonoff, D.C. Effect of environmental pollutants PM2.5, CO, NO2, and O3 on the incidence and mortality of SARS-CoV-2 infection in five regions of the USA. Int. J. Environ. Res. Public Health 2021, 18, 7810. [Google Scholar] [CrossRef]
  60. Meo, S.A.; Abukhalaf, A.A.; Alomar, A.A.; Alessa, O.M. Wildfire and COVID-19 pandemic: Effect of environmental pollution PM2.5 and carbon monoxide on the dynamics of daily cases and deaths due to SARS-CoV-2 infection in San-Francisco USA. Eur. Rev. Med. Pharmacol. Sci. 2020, 24, 10286–10292. [Google Scholar] [CrossRef]
  61. Meo, S.A.; Abukhalaf, A.A.; Alomar, A.A.; Alessa, O.M.; Sami, W.; Klonoff, D.C. Effect of environmental pollutants PM2.5, carbon monoxide, and ozone on the incidence and mortality of SARS-CoV-2 infection in ten wildfire affected counties in California. Sci. Total Environ. 2021, 757, 143948. [Google Scholar] [CrossRef]
  62. Meo, S.A.; Almutairi, F.J.; Abukhalaf, A.A.; Usmani, A.M. Effect of green space environment on air pollutants PM2.5, PM10, CO, O3 and incidence and mortality of SARS-CoV-2 in highly green and less-green countries. Int. J. Environ. Res. Public Health 2021, 18, 13151. [Google Scholar] [CrossRef]
  63. Adhikari, A.; Yin, J. Short-term effects of Ambient Ozone, PM2.5, and meteorological factors on COVID-19 confirmed cases and deaths in Queens, New York. Int. J. Environ. Res. Public Health 2020, 17, 4047. [Google Scholar] [CrossRef]
  64. Gujral, H.; Sinha, A. Association between exposure to airborne pollutants and COVID-19 in Los Angeles, United States with ensemble-based dynamic emission model. Environ. Res. 2021, 194, 110704. [Google Scholar] [CrossRef]
  65. Cortes-Ramirez, J.; Michael, R.N.; Knibbs, L.D.; Bambrick, H.; Haswell, M.R.; Wraith, D. The association of wildfire air pollution with COVID-19 incidence in New South Wales, Australia. Sci. Total Environ. 2022, 809, 151158. [Google Scholar] [CrossRef]
  66. Ben Maatoug, A.; Triki, M.B.; Fazel, H. How do air pollution and meteorological parameters contribute to the spread of COVID-19 in Saudi Arabia? Environ. Sci. Pollut. Res. Int. 2021, 28, 44132–44139. [Google Scholar] [CrossRef]
  67. Hadei, M.; Hopke, P.K.; Shahsavani, A.; Raeisi, A.; Jafari, A.J.; Yarahmadi, M.; Farhadi, M.; Rahmatinia, M.; Bazazpour, S.; Bandpey, A.M.; et al. Effect of short-term exposure to air pollution on COVID-19 mortality and morbidity in Iranian cities. J. Environ. Health Sci. Eng. 2021, 19, 1807–1816. [Google Scholar] [CrossRef]
  68. Meo, S.A.; Almutairi, F.J.; Abukhalaf, A.A.; Alessa, O.M.; Al-Khlaiwi, T.; Meo, A.S. Sandstorm and its effect on particulate matter PM2.5, carbon monoxide, nitrogen dioxide, ozone pollutants and SARS-CoV-2 cases and deaths. Sci. Total Environ. 2021, 795, 148764. [Google Scholar] [CrossRef] [PubMed]
  69. Ghanim, A.A.J. Analyzing the severity of coronavirus infections in relation to air pollution: Evidence-based study from Saudi Arabia. Environ. Sci. Pollut. Res. Int. 2022, 29, 6267–6277. [Google Scholar] [CrossRef] [PubMed]
  70. Akan, A.P. Transmission of COVID-19 pandemic (Turkey) associated with short-term exposure of air quality and climatological parameters. Environ. Sci. Pollut. Res. Int. 2022, 31, 41695–41712. [Google Scholar] [CrossRef]
  71. Norouzi, N.; Asadi, Z. Air pollution impact on the COVID-19 mortality in Iran considering the comorbidity (obesity, diabetes, and hypertension) correlations. Environ. Res. 2022, 204 Pt A, 112020. [Google Scholar] [CrossRef]
  72. Bolano-Ortiz, T.R.; Camargo-Caicedo, Y.; Puliafito, S.E.; Ruggeri, M.F.; Bolano-Diaz, S.; Pascual-Flores, R.; Saturno, J.; Ibarra-Espinosa, S.; Mayol-Bracero, O.L.; Torres-Delgado, E.; et al. Spread of SARS-CoV-2 through Latin America and the Caribbean region: A look from its economic conditions, climate and air pollution indicators. Environ. Res. 2020, 191, 109938. [Google Scholar] [CrossRef]
  73. Lopez-Feldman, A.; Heres, D.; Marquez-Padilla, F. Air pollution exposure and COVID-19: A look at mortality in Mexico City using individual-level data. Sci. Total Environ. 2021, 756, 143929. [Google Scholar] [CrossRef]
  74. Salgado, M.V.; Smith, P.; Opazo, M.A.; Huneeus, N. Long-term exposure to fine and coarse particulate matter and COVID-19 incidence and mortality rate in chile during 2020. Int. J. Environ. Res. Public Health 2021, 18, 7409. [Google Scholar] [CrossRef]
  75. SARS Basics Fact Sheet. Available online: https://www.cdc.gov/sars/about/fs-sars.html (accessed on 22 November 2022).
  76. Chiu, R.W.; Chim, S.S.; Tong, Y.K.; Fung, K.S.; Chan, P.K.; Zhao, G.P.; Lo, Y.M. Tracing SARS-coronavirus variant with large genomic deletion. Emerg. Infect. Dis. 2005, 11, 168–170. [Google Scholar] [CrossRef]
  77. SARS-CoV-2 Variant Classification and Definitions. Available online: https://www.cdc.gov/coronavirus/2019-ncov/variants/variant-classifications.html (accessed on 21 November 2022).
  78. WHO Coronavirus (COVID-19) Dashboard. Available online: https://covid19.who.int/ (accessed on 22 November 2022).
  79. Kanu, F.A.; Smith, E.E.; Offutt-Powell, T.; Hong, R.; Delaware Case, I.; Contact Tracing, T.; Dinh, T.H.; Pevzner, E. Declines in SARS-CoV-2 Transmission, Hospitalizations, and Mortality After Implementation of Mitigation Measures- Delaware, March-June 2020. Morb. Mortal. Wkly. Rep. 2020, 69, 1691–1694. [Google Scholar] [CrossRef]
  80. Mortality Analyses. Available online: https://coronavirus.jhu.edu/data/mortality (accessed on 22 November 2022).
  81. Signorini, C.; Pignatti, P.; Coccini, T. How Do Inflammatory Mediators, Immune Response and Air Pollution Contribute to COVID-19 Disease Severity? A Lesson to Learn. Life 2021, 11, 182. [Google Scholar] [CrossRef]
  82. Mazzoli-Rocha, F.; Fernandes, S.; Einicker-Lamas, M.; Zin, W.A. Roles of oxidative stress in signaling and inflammation induced by particulate matter. Cell Biol. Toxicol. 2010, 26, 481–498. [Google Scholar] [CrossRef] [PubMed]
  83. Cui, Y.; Zhang, Z.F.; Froines, J.; Zhao, J.; Wang, H.; Yu, S.Z.; Detels, R. Air pollution and case fatality of SARS in the People′s Republic of China: An ecologic study. Environ. Health 2003, 2, 15. [Google Scholar] [CrossRef] [PubMed]
  84. Nor, N.S.M.; Yip, C.W.; Ibrahim, N.; Jaafar, M.H.; Rashid, Z.Z.; Mustafa, N.; Hamid, H.H.A.; Chandru, K.; Latif, M.T.; Saw, P.E.; et al. Particulate matter (PM2.5) as a potential SARS-CoV-2 carrier. Sci. Rep. 2021, 11, 2508. [Google Scholar] [CrossRef]
  85. Sagawa, T.; Tsujikawa, T.; Honda, A.; Miyasaka, N.; Tanaka, M.; Kida, T.; Hasegawa, K.; Okuda, T.; Kawahito, Y.; Takano, H. Exposure to particulate matter upregulates ACE2 and TMPRSS2 expression in the murine lung. Environ. Res. 2021, 195, 110722. [Google Scholar] [CrossRef] [PubMed]
  86. Tung, N.T.; Cheng, P.-C.; Chi, K.-H.; Hsiao, T.-C.; Jones, T.; BéruBé, K.; Ho, K.-F.; Chuang, H.-C. Particulate matter and SARS-CoV-2: A possible model of COVID-19 transmission. Sci. Total Environ. 2021, 750, 141532. [Google Scholar] [CrossRef]
  87. Comunian, S.; Dongo, D.; Milani, C.; Palestini, P. Air Pollution and COVID-19: The Role of Particulate Matter in the Spread and Increase of COVID-19’s Morbidity and Mortality. Int. J. Environ. Res. Public Health 2020, 17, 4487. [Google Scholar] [CrossRef]
  88. Aztatzi-Aguilar, O.G.; Uribe-Ramírez, M.; Arias-Montaño, J.A.; Barbier, O.; De Vizcaya-Ruiz, A. Acute and subchronic exposure to air particulate matter induces expression of angiotensin and bradykinin-related genes in the lungs and heart: Angiotensin-II type-I receptor as a molecular target of particulate matter exposure. Part. Fibre Toxicol. 2015, 12, 17. [Google Scholar] [CrossRef]
  89. Chen, J.; Guo, X.; Pan, H.; Zhong, S. What determines city’s resilience against epidemic outbreak: Evidence from China’s COVID-19 experience. Sustain. Cities Soc. 2021, 70, 102892. [Google Scholar] [CrossRef]
  90. Bossak, B.H.; Turk, C.A. Spatial Variability in COVID-19 Mortality. Int. J. Environ. Res. Public Health 2021, 18, 5892. [Google Scholar] [CrossRef] [PubMed]
  91. Bo, M.; Mercalli, L.; Pognant, F.; Cat Berro, D.; Clerico, M. Urban air pollution, climate change and wildfires: The case study of an extended forest fire episode in northern Italy favoured by drought and warm weather conditions. Energy Rep. 2020, 6, 781–786. [Google Scholar] [CrossRef]
  92. Han, C.H.; Pak, H.; Lee, J.M.; Chung, J.H. Short-term effects of exposure to particulate matter on hospital admissions for asthma and chronic obstructive pulmonary disease. Medicine 2022, 101, e30165. [Google Scholar] [CrossRef]
  93. Rice, M.B.; Ljungman, P.L.; Wilker, E.H.; Dorans, K.S.; Gold, D.R.; Schwartz, J.; Koutrakis, P.; Washko, G.R.; O’Connor, G.T.; Mittleman, M.A. Long-term exposure to traffic emissions and fine particulate matter and lung function decline in the Framingham heart study. Am. J. Respir. Crit. Care Med. 2015, 191, 656–664. [Google Scholar] [CrossRef] [PubMed]
  94. Horwitz, L.I.; Jones, S.A.; Cerfolio, R.J.; Francois, F.; Greco, J.; Rudy, B.; Petrilli, C.M. Trends in COVID-19 Risk-Adjusted Mortality Rates. J. Hosp. Med. 2021, 16, 90–92. [Google Scholar] [CrossRef] [PubMed]
  95. Beigel, J.H.; Tomashek, K.M.; Dodd, L.E. Remdesivir for the Treatment of COVID-19—Preliminary Report. Reply. N. Engl. J. Med. 2020, 383, 994. [Google Scholar] [CrossRef]
  96. Group, R.C.; Horby, P.; Lim, W.S.; Emberson, J.R.; Mafham, M.; Bell, J.L.; Linsell, L.; Staplin, N.; Brightling, C.; Ustianowski, A.; et al. Dexamethasone in Hospitalized Patients with COVID-19. N. Engl. J. Med. 2021, 384, 693–704. [Google Scholar] [CrossRef]
  97. Gandhi, M.; Rutherford, G.W. Facial Masking for COVID-19. Reply. N. Engl. J. Med. 2020, 383, 2093–2094. [Google Scholar] [CrossRef] [PubMed]
Life 13 00538 g001
Figure 1. Study Design. Per Preferred reporting Items for systematic reviews and Meta-Analyses (PRISMA) Guidelines. PRISMA is an evidence-based minimum set of items for reporting in systematic reviews and meta-analyses [26]. http://www.prisma-statement.org/, accessed on 7 January 2023.
Figure 1. Study Design. Per Preferred reporting Items for systematic reviews and Meta-Analyses (PRISMA) Guidelines. PRISMA is an evidence-based minimum set of items for reporting in systematic reviews and meta-analyses [26]. http://www.prisma-statement.org/, accessed on 7 January 2023.
Life 13 00538 g001
Table 1. Study Characteristics [30,31,32,33,34,35,36,37,38,39,40,41,42,43,44,45,46,47,48,49,50,51,52,53,54,55,56,57,58,59,60,61,62,63,64,65,66,67,68,69,70,71,72,73,74,75].
Table 1. Study Characteristics [30,31,32,33,34,35,36,37,38,39,40,41,42,43,44,45,46,47,48,49,50,51,52,53,54,55,56,57,58,59,60,61,62,63,64,65,66,67,68,69,70,71,72,73,74,75].
Study
Author [Ref.]		CountryExposure/
Design		Study Size/Time
Period		Specimen/
Assay		End PointsAdditional Findings
1ASIAKan [30] ChinaPM10
Cohort Study		Beijing/N = 37/
25 April–31 May 2003		RT-PCRMortality
  • Mortality (RR) significant for PM10 and NO2
  • No association was seen with SO2
2Li [31] ChinaPM2.5 and 10
Time series Study		Wuhan and Xiaogan
26 January–29 February 2020		RT-PCRIncidence
  • Correlation between the PM2.5 and 10 and incidencewas seen in Wuhan (R2 = 0.105, 0.174, respectively)
  • Ambient air pollutants showed a positive association with incidence.
3Lu [32]ChinaPM2.5
Cohort study		41 cities/N = 22,970/
20 January–29 February 2020		RT-PCRIncidence
  • Incidence and ambient PM2.5 correlation were stronger for cities inside Hubei than those outside (highest RR at lag 0–14)
4Sahoo [33] IndiaPM2.5 and 10
Time series study		32 states and union territories/N = 21,700/30 January–24 April 2020RT-PCRIncidence
  • 10 µg/m3 increase in PM2.5and10 resulted in 2.21% (95%CI: 1.13–3.29), 2.67% (95% CI: 0.33–5.01), increase in daily counts of cases, respectively.
5Sangkham [34]ThailandPM2.5, and 10
Cohort Study		Bangkok City
30 March 2020		RT-PCRIncidence
  • Significant negative association between PM and C19 cases (PM10 rs = −0.506, PM2.5 rs = −0.460)
6Shao [35] ChinaPM2.5 and 10
Cohort Study		Wuhan City
23 January–7 April 2020		RT-PCRMortality
  • Significant positive correlation between PM2.5 and the number of deaths per day.
7Yao [36] ChinaPM2.5 and 10
Cohort Study		49 cities
February 2020		RT-PCRCase fatality rate (CFR)
  • Positive associations between PM pollution and CFR around Hubei Province.
  • Every 10 µg/m3 increase in PM2.5 and 10, the C19 CFR increased by 0.24% (0.01–0.48%) and 0.26% (0.00–0.51%), respectively.
8Beig [37] IndiaPM2.5
Cohort Study		6 Cities
May 2022		RT-PCR Mortality
  • PM2.5 baseline level and mortality/0.1 million population indicates significant correlation (r = 0.84 with p-value < 0.05) at 90% CI
9Laxmipriya [38]IndiaPM2.5 and 10
Cohort study		11 stations in Chennai city/July 2020RT-PCRIncidence
  • Areas with PM concentrations ranging from (38 to 90 mg/m3) reported with fewer positive cases (<5 cases). Areas covering above 91 to 195 mg/m3) had a positive association.
10EUROPEFrontera [25]ItalyPM2.5
Cohort study		21 territories/
March 2020		RT-PCRPrevalence,
ICU admissions, Mortality
  • Positive Correlation between mean PM2.5 and total number of hospitalized patients (r = 0.62 p = 0.008), ICU admissions (r = 0.53 p = 0.005), total cases (r = 0.64 p = 0.007) and deaths r = 0.53 p = 0.032
11Bianconii [39]ItalyPM2.5 and 10
Cohort Study		20 provinces/N = 105,792
31 March 2020		RT-PCRIncidence proportion and
mortality
  • PM2.5 and PM10 were associated with:
  • Incidence proportion irrespective of confounders (ß = 0.71, p = 0.003 and ß = 0.61, p = 0.031, respectively).
  • Death rates across Italian regions PM2.5; ß = 0.68, p = 0.004 PM10; ß = 0.61, p = 0.029)
12Dragone [40]ItalyPM2.5 and 10
Cohort study		Lombard region/
N = 42,283/
1 February–31 March 2020		RT-PCRPrevalence
  • Positive correlation between spatial distribution of Prevalence with PM10 (r = 0.54) and PM2.5 (r = 0.51)
13Fattorini [41]ItalyPM2.5 and 10
Cohort study		N = 18,000
February–April 2020		RT-PCRIncidence
  • Statistical correlation between cases and the air quality parameters in Italy PM10 r = 0.5168 p < 0.01, PM2.5 r = 0.5827 p < 0.01.
14Rovetta [42]ItalyPM2.5 and 10 Cohort studyLombardy; N = 82,992/
February–March 2020		UnclearMortality rate
  • A statistically significant correlation between SARS-CoV-2 spread and PM2.5 in Lombardy during the first two weeks of March, (Correlation coefficient ρ = 0.56)
15Moshammer [43] AustriaPM10
Time Series study		Vienna/N = 1665/
March–April 2020		RT-PCRIncidence
  • PM10 levels positively correlated (r = 0.014) with the risk of infection
16Dettori [44]ItalyPM10
Cohort Study		N = 60,359,546/
June 2020		RT-PCRStandardized Mortality Ratio
  • PM10 (p = 0.001, 95% CI: 0.059–0.234) was independently associated with the case status. (r = 0.147 p-value = 0.001 95% CI 0.059–0.234)
17Meo [45]United KingdomPM2.5
Cohort Study		Cases
24 February–2 November 2020		RT-PCRIncidence and Mortality
  • Cases significantly augmented with a rise in the levels of PM2.5 (ρ = 0.176, p < 0.001).
  • Statistically insignificant relationship between PM2.5 and mortality (ρ = 0.029, p = 0.270)
18Scalsky [46]United KingdomPM2.5
Cohort		UK biobank; N = 15,156/16 March 2020–16 March 2021RT-PCRIncidence
  • PM2.5 levels were significantly associated with an increase in SARS-CoV-2 positive testing likelihood (OR = 1.063, 95% CI = 1.04–1.09)
19Kogevinas [47] SpainPM2.5
Cohort Study		Catalonia/N = 9605/June–November 2020RT-PCRIncidence
  • Air pollution levels were not statistically significantly associated with SARS-CoV-2 infection.
20Marques [48]SpainPM10
Cohort Study		Catalan hospitals
N = 2112
April–June 2020		RT-PCRC19 severity and mortality
  • PM10 showed the highest effects estimates (1.65, 95% CI 1.32–2.06) on severity and (2.37, 95% CI 1.71–3.32) mortality.
  • An increase of 1 µg/m3 in PM10 causes an increase in 3.06% (95% CI 1.11–4.25%) of patients suffering severe disease and an increase of 2.68% (95% CI 0.53–5.58%) of deaths.
21Veronesi [49] ItalyPM2.5 and 10
Cohort Study		Varese; N = 62,848
25 February 2020–13 March 2021		RT-PCRIncidence
  • PM2.5 was associated with a 5.1% increase in the incidence (95% CI 2.7% to 7.5%), corresponding to 294 additional cases per 100,000 person-years.
22Zoran [50]SpainPM2.5 and 10 Cohort Study6.61 million Inhabitants January 2020–July 2021RT-PCRIncidence, Prevalence and Mortality
  • Statistically significant correlation between PM2.5 and total cases (r = 0.20 p < 0.05).
  • Significant correlation between PM10 and total cases (r = 0.27 p < 0.05) and daily new cases (r = 0.14 p < 0.05)
23Semczuk–Kaczmarek
[51] 		PolandPM2.5 and 10 Cohort StudyN = 18,016
4 March–15 May 2020		RT-PCRMortality and Morbidity
  • Statistically significant correlation between cases (per 100,000 population) and annual average concentration of PM2.5 (R2 = 0.367, p = 0.016), PM10 (R2 = 0.415, p = 0.009).
  • Long-term exposure to air pollution, especially PM2.5 and 10, seems to play an essential role in prevalence and mortality
24Di Ciaula [52]Italy PM10
Cohort Study		10 cities; N = 147
March–April 2020		RT-PCRMortality
  • PM10 exposure has no significant effect on mortality
25Czwojdzinska [53]PolandPM2.5 and 10
Cohort study		N = 38,411,148
4 March–18 November 2020		RT-PCRIncidence and mortality
  • Incidence independent of PM concentration
26USABerg [54]USAPM2.5
Cohort study		Colorado
N = 34,439
1 March–31 August 2020		RT-PCRIncidence, hospitalization and mortality
  • 1 µg/m3 increase in long-term PM2.5 concentrations is associated with a statistically significant 26% (RR: 1.26, 95% CI: 1.06–1.48) increase in the relative risk of hospitalizations, a 34% increase in mortality RR: 1.34, 95% CI: 1.02–1.77.
  • Positive, insignificant increase in the RR of infections (1.10, 95% CI: 0.98–1.24).
27Bozack [55]USAPM2.5
Cohort Study		Seven NYC hospitals
N = 6542
8 March–30 August 2020		RT-PCRMortality, ICU admission, Intubation
  • PM2.5 exposure was not associated with the risk of intubation and mechanical ventilation (PM2.5: RR, 1.05 [95% CI: 0.91–1.20] per 1-µg/m3 increase.
28Fang [56]USA3096 counties; PM2.5
Cohort Study		Cumulative Cases:
1st [May: 20,764] and 2nd [September: 34,596] surge in 2020		RT-PCRIncidence
  • 1 µg/m3 increase in annual average concentration of PM2.5 was associated with 7.60% increase in the cumulative risk, 95% CI between 3.82% and 11.51%.
29Kiser [57] USANevada/PM2.5/Cohort StudyRegional hospital, Reno/15 May–20 October 2020RT-PCRIncidence
  • 10 µg/m3 increase in the 7-day average PM2.5 concentration was associated with a 6.3% relative increase in the SARS-CoV-2 test positivity rate, with a 95% CI of 2.5 to 10.3%.
30Mendy [58] USAPM2.5/Cohort studyCincinnati/N = 14,783/
13 March–30 September 2020		RT-PCRDisease Severity
  • 1 µg/m3 increase in 10-year annual average PM2.5 was associated with 18% higher hospitalization and 14% higher hospitalization
31Meo [59] USAPM2.5/Cohort study5 regions; N = 1192
13 March–31 December 2020		RT-PCRIncidence and Mortality
  • For every 1 unit increase in PM2.5, the # of C19 infections significantly increased by 0.1%.
  • PM2.5 and mortality were not statistically significant (ρ = 0.029, p = 0.270)
32Meo [60]USAPM2.5/Cohort Study California
20 March–16 September 2020		RT-PCRIncidence, Prevalence and mortality
  • Significant positive correlation environmental pollutants PM2.5 and the number of daily cases
  • PM2.5 µm and daily deaths had no relationship (r = −0.015, p = 0.842).
33Meo [61]USACalifornia /PM2.5/
Cohort study 		California/19 March–15 August 2020RT-PCRIncidence and mortality
  • The rho-coefficient relation showed a significantly increased number of new cases 0.403 (p value < 0.001) and deaths 0.171 (p value < 0.001) with increasing levels of PM2.5
34Meo [62]USAPM2.5
Cohort study		17 countries
25 January 2020–11 July 2021		RT-PCRIncidence and Mortality
  • PM2.5 and 10, were significantly decreased (p < 0.0001) in environmentally highly green space countries compared to less-green countries.
  • SARS-CoV-2- 2 cases and deaths were also significantly decreased in highly green countries compared to less-green countries.
35Adhikari [63]USAPM2.5
Cohort study		New York/N = 42,023 cases/April 2020RT-PCRIncidence Rate Ratio,
Mortality
  • Significant negative association between PM2.5 and new daily confirmed cases.
  • One-unit increase in average PM2.5 (µg/m3) was associated with a 33.11% (95% CI: 31.04–35.22) decrease in daily new cases.
36Gujral [64] USAPM2.5
Cohort study		California
January–July 2020		RT-PCRIncidence
  • Exposure to particulates, PM2.5 and 10, depicts a negative Association.
37AUSTRALIACortes-Ramirez [65]AustraliaPM10
Cohort study		New South Wales/
2 March–2 August 2020		RT-PCRIncidence
  • Higher wildfire burned areas were associated with higher incidence in both the random effects and spatial models after adjustment for sociodemographic factors (posterior mean = 1.32 (99% CI: 1.05–1.67) and 1.31 (99%CI: 1.03–1.65)).
  • No association between the average PM10 level and incidence was found.
38MIDDLE EASTMaatoug [66]Saudi ArabiaPM10
Cohort study		Riyadh, Jeddah, Makkah/N = 354,813
9 March–9 November 2020		RT-PCRIncidence
  • Short-term exposure to PM10, NO2, O3 positively correlated with daily cases.
39Hadei [67]IranPM2.5 and 10 Cohort studyN = 114,964
February–January 2021		RT-PCRMortality and morbidity
  • Meta-analysis estimated that the RR for mortality, due to PM2.5 exposure was 1.06 (95% CI: 0.99, 1.13)
40Meo [68] Saudi ArabiaPM2.5
Cohort Study		Riyadh
20 February–2 April 2021		RT-PCRIncidence and mortality
  • Increased PM2.5, NO2, CO, O3 was associated with a significant increase in cases. Association with mortality was insignificant
41Ghanim [69]Saudi ArabiaPM10
Cohort study		13 regions; N = 194,255
June 2020		RT-PCRIncidence and Mortality
  • Positive correlation between mean PM10 and total number of cases r = 0.178 p = 0.623
42Akan [70] TurkeyPM2.5 and 10 Cohort study15 Provinces
N = 42,618,331
8 February–8 May 2021		RT-PCRIncidence
  • PM2.5 and 10 displayed statistically significant negative associations with the number of cases. The spearman correlation coefficients for PM10 ranged between −0.02 and −0.62 and −0.03 to −0.34 for PM2.5
43Norouzi [71]IranPM2.5
Cohort study		12 cities/N = 73,080/
1 March 2019–31 August 2020		RT-PCRIncidence
  • Increased PM2.5 was not a predictor of mortality.
  • PM10 excluded from the models due to an insignificant association with mortality.
44LATIN AMERICABolano-Ortiz [72] Latin America and CaribbeanPM2.5 and 10
Cohort study		Ten cities/N = 56.95 million/1 April–31 May 2020UnknownIncidence rate and mortality
  • Negative correlation between total cases and PM10 (−0.44; p < 0.05;) in Mexico City and PM2.5 (−0.70; p < 0.01) in Bogota
  • New and total cases showed the highest positive correlations with particulate matter PM10 (Sao Paulo and Santiago (0.35; p < 0.01; and Buenos Aires 0.54; p < 0.01)
45Lopez-Feldman
[73] 		MexicoPM2.5
Cohort study		Residents of (Hidalgo, and Mexico City)
7 October 2020		RT-PCRMortality
  • Three models used to analyze the relationship between long-term exposure and mortality. An average marginal effect of 0.0076 was noted.
46Salgado [74]ChilePM2.5 and 10 Cohort Study188 communes/N = 4574
May 2021		RT-PCRIncidence and mortality
  • For each microgram per cubic meter increase, the incidence rate increased by 1.3% for PM2.5 and 0.9% for PM10. No statistically significant relationship with mortality rate
Subdivided by: Life 13 00538 i001 Positive association Life 13 00538 i002 Negative association Life 13 00538 i003 Unclear/Equivocal association Life 13 00538 i004 Late Pandemic Life 13 00538 i005 SARS-1.
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Podury, S.; Kwon, S.; Javed, U.; Farooqi, M.S.; Li, Y.; Liu, M.; Grunig, G.; Nolan, A. Severe Acute Respiratory Syndrome and Particulate Matter Exposure: A Systematic Review. Life 2023, 13, 538. https://doi.org/10.3390/life13020538

AMA Style

Podury S, Kwon S, Javed U, Farooqi MS, Li Y, Liu M, Grunig G, Nolan A. Severe Acute Respiratory Syndrome and Particulate Matter Exposure: A Systematic Review. Life. 2023; 13(2):538. https://doi.org/10.3390/life13020538

Chicago/Turabian Style

Podury, Sanjiti, Sophia Kwon, Urooj Javed, Muhammad S. Farooqi, Yiwei Li, Mengling Liu, Gabriele Grunig, and Anna Nolan. 2023. "Severe Acute Respiratory Syndrome and Particulate Matter Exposure: A Systematic Review" Life 13, no. 2: 538. https://doi.org/10.3390/life13020538

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