Pregnancy loss is the death of an unborn baby at any time during pregnancy [1]. Pregnancy loss is generally grouped into two categories including miscarriage or spontaneous abortion, defined as a loss before 20 weeks of gestation; and stillbirth, defined as a loss at or after 20 weeks of gestation [1]. The incidence of pregnancy loss is estimated to be around 15% of all recognized pregnancies [2], and approximately 30% in prospective cohorts of couples attempting to become pregnant [3, 4]. The true incidence of pregnancy loss in the general population is difficult to ascertain but expected to be higher as a significant proportion of losses occur early, even before clinical recognition.

Globally, one in 10 women experiences a miscarriage in their lifetime, equivalent to approximately 23 million cases annually [5]. Meanwhile, approximately two million babies are stillborn each year [6]. The impact of pregnancy loss is beyond the loss of a life [2]. In addition to the considerably high financial cost associated with medical management [2], affected families experience significantly higher levels of emotional and psychological burden. Parents who experience a pregnancy loss are more likely to experience depression, anxiety, and post-traumatic stress symptoms after delivery [7, 8]. Moreover, they also have higher risk of recurrent pregnancy loss, and all-cause as well as cardiovascular mortality [2, 9].

Several potential causes of pregnancy loss have been identified in the literature. These include complications of the placenta, cervix, or uterus; chromosomal abnormalities, abnormal fetal development; trauma or injury; and selected maternal comorbidities such as infection and autoimmune disorders [2, 6]. In addition, known risk factors for pregnancy loss include advanced maternal age, history of pregnancy loss, maternal smoking, alcohol consumption, illicit drug use, obesity, gestational complications, and certain environmental exposures [2, 6]. Nevertheless, the cause of a significant proportion of pregnancy loss is unclear, which contributes to the lack of effective prevention strategies. As such, identifying and understanding the etiology of pregnancy loss remain among the top priorities in maternal and child health initiatives.

Based on the 2020 State of Global Air report, air pollution is the fourth leading risk factor for premature mortality globally [10]. It is responsible for approximately 12% of all deaths, equivalent to about 6.67 million deaths in 2019 [10]. While the impacts of air pollution on mortality and cardiorespiratory health have received significant attention in the past few decades [11,12,13,14], we are only beginning the effort to understand how air pollution affects pregnancy. These efforts should be continued, strengthened, and expanded given pregnancy is a vulnerable period during which small environmental perturbations may have serious short- and long-term impacts on both the mother and developing fetus [15, 16]. In addition, while health impacts attributable to household air pollution have decreased by 30% in recent years, the health burden of outdoor air pollution remains elevated [17]. This is concerning given the context of climate change and its expected role in exacerbating air pollution burden. Furthermore, health effects of air pollution are seen at levels experienced by almost the entire (~ 99%) world’s population, who lives in areas with air quality below the World Health Organization’s recommended standards [18].

As air pollution is now a leading contributor to the global health burden [19], research has given increasing attention to its relationship with pregnancy loss risk. To date, six systematic reviews have summarized the existing literature on the relationship between air pollution exposure and pregnancy loss risk (Supplemental Table S1) [20,21,22,23,24,25]. Zhu et al. 2015 evaluates associations between particulate matter < 2.5 μm (PM2.5) and pregnancy outcomes, but this review focuses on one pollutant and includes one study on stillbirth [25]. Siddika et al. 2016 [22] (n = 15), Bekkar et al. 2020 [20] (n = 5), Zhang et al. 2021 [24] (n = 15), and Xie et al. 2021 [23] (n = 7) also reviewed studies on the associations between air pollution and stillbirth, but these reviews do not include spontaneous abortion. Grippo et al. (2018), to date, is the most comprehensive review, which includes 35 studies on air pollution and both categories of pregnancy loss [21]. However, given multiple studies have emerged since 2018, we seek to review the recent literature regarding the impacts of outdoor air pollution on both categories of pregnancy loss.


A comprehensive literature search spanning from March 2018 to March 25, 2022 was performed using PubMed. The search included terms related to air pollution and spontaneous abortion or stillbirth. We also used various alternative search terms for pregnancy loss including miscarriage, stillborn, fetal/foetal mortality, and intrauterine mortality (Supplemental Table S2). The articles were carefully reviewed and were excluded if they were (a) not an original study, (b) qualitative studies, (c) animal studies, (d) did not include specific outdoor air pollutant, (e) did not include any pregnancy loss outcomes, or (f) were not published in English. We also searched reference lists of relevant articles for additional publications.

Due to high heterogeneity between studies in terms of study design, exposure assessment, outcome assessment, and statistical analysis, we were unable to perform a systematic meta-analysis and presented a narrative review instead. We assessed the quality of each included study using an adapted version of the Effective Public Health Practice Project Quality Assessment tool [26]. This is a validated and widely used instrument to assess quality of epidemiologic research with respect to selection bias, study design, confounding, data collection, and attrition (or missing data). A detailed description of our qualitative review strategy is presented in Supplemental Table S3. Each study was assessed by two independent reviewers. Discrepancies were reconciled after a thorough discussion and any remaining differences were resolved by a third reviewer.


Study Characteristics

A total of 21 articles were included in this review (Table 1). Supplemental Table S4 presents all existing articles on air pollution and pregnancy loss before this review period. Since these articles were included in previous reviews, they are not the focus of this review. The majority of the studies included in this review were conducted in the USA (n = 6, 28.6%) [27,28,29,30,31,32] and China (n = 6, 28.6%) [33,34,35,36,37,38], followed by Iran (n = 2, 9.5%) [39, 40], South Asia (n = 2, 9.5%) [41, 42], Africa (n = 1, 4.8%) [43], Australia (n = 1, 4.8%) [44], England (n = 1, 4.8%) [45], Israel (n = 1, 4.8%) [46], and Korea (n = 1, 4.8%) [47]. Retrospective cohort (n = 6) [31, 34, 44,45,46,47] and case–control designs (n = 6) [30, 35, 38, 41,42,43] were most popular, followed by times series (n = 3) [33, 39, 40], prospective cohort (n = 2) [27, 37], and case-crossover designs (n = 2) [28, 32]. Two studies also used multiple designs to ensure robustness of findings [29, 36]. Most studies (n = 12) [27, 29, 31, 32, 36, 38, 41,42,43, 45,46,47] assessed exposures using the modeling approaches, while the rest used measurements from fixed-site air monitors (n = 9) [28, 30, 33,34,35, 37, 39, 40, 44]. In terms of exposure, 12 studies assessed long-term exposures across different periods of pregnancy [30, 34,35,36,37,38, 41, 42, 44,45,46,47], five studies assessed short-term impacts of exposures within the last week [28, 32, 33, 39, 40], three studies assessed both short- and long-term impacts [27, 31, 43], and one study investigated average exposure in the study area with no specific window [29]. In terms of study outcome, 10 studies investigated stillbirth [28, 30, 31, 34, 37, 40, 44,45,46,47], five studies assessed spontaneous abortion [29, 32, 33, 35, 38], four studies evaluated both pregnancy loss outcomes [39, 41,42,43], and two studies evaluated any loss without categorization based on gestational age [27, 36]. One study measured pregnancy loss prospectively using clinical assessment [27], five used questionnaires [29, 36, 41,42,43], and 15 relied on administrative data or medical records [28, 30,31,32,33,34,35, 37,38,39,40, 44,45,46,47]. Studies also vary in quality ranging from weak to strong, as presented in Supplemental Table S5.

Table 1 Summary of existing studies on air pollution and pregnancy loss (since March 2018)

Air Pollution and Spontaneous Abortion

Eleven studies evaluated associations between various air pollutants and spontaneous abortion/miscarriage (Table 2) [27, 29, 32, 33, 35, 36, 38, 39, 41,42,43]. Particulate matter, especially PM2.5, received the most attention, followed by nitrogen dioxide (NO2), ozone (O3), carbon monoxide (CO), and (particulate matter < 10 μm (PM10). Sulfur dioxide (SO2), fine particles sizes 2.5 to 10 μm, and NO2 appeared to have demonstrated deleterious impacts on spontaneous abortions in at least one study, with fine particles and NO2 showing the most consistent associations.

Table 2 Proportion of studies observing positive associations between air pollution and pregnancy loss (n = 21)

Fine Particles and Constituents

Gaskin et al. (2019) estimated fine particles at residential address using spatiotemporal models and found positive associations between self-reported fetal loss (< 20 weeks) and 1-year average exposure to PM2.5 (OR 1.09; 95% CI 1.03–1.15 per 2.0 μg/m3 increase), PM2.5–10 (OR 1.08; 95% CI 1.03–1.13 per 2.3 μg/m3), and PM10 (OR 1.11; 95% CI 1.05–1.17 per 3.9 μg/m3) in their cross-over analysis [29]. A large self-matched case–control study across 33 African countries also found positive associations between self-reported miscarriage < 5 months and PM2.5 estimated using chemical transport models and remote sensing [43]. Each 10 μg/m3 increase in average PM2.5 exposures across the whole gestational period was associated with 12.5% (95% CI 10.9–14.2%) increased risk of miscarriage. When assessing short-term risks, PM2.5 exposures were also associated with 4–6% increased risk on the same day as well as 2 and 5 days later [43]. Two similar large case–control studies using the same dataset in several South Asian countries also found similar and positive associations between PM2.5 during the entire gestational period and self-reported miscarriage < 5 months (OR 1.04 and 1.05 in both studies) [41, 42]. A case–control study in China also found positive associations between pregnancy loss < 13 weeks (ascertained by transvaginal ultrasonography) and PM2.5 exposures within four weeks after—but not before—conception [38]. Each 10 μg/m3 increase in average PM2.5 exposure during the second week after conception and the entire 4 weeks after conception were associated with a 13% (95 CI 3–23%) and 25% (95% CI 2–46%) increased risk of clinically recognized early loss, respectively [38]. Another study from China also found positive associations between PM2.5 during the entire pregnancy and spontaneous loss [36]. Particulate matter is comprised of a mixture of components that can vary depending on sources. Thus, a couple studies investigated potential impacts of fine particle constituents (e.g., black carbon) on pregnancy loss but found no associations [27, 43]. Despite relatively consistent associations, several large studies also did not detect any significant association between PM2.5 or PM10 and spontaneous loss, although effect estimates were mostly above the null value [27, 32, 33].

Gaseous Pollutants

During the review period, four studies evaluated the impacts of O3 on spontaneous abortion, but none found positive association [27, 32, 33, 39]. On the other hand, NO2 appeared to have consistent associations across four of five relevant studies. For example, in a case-crossover analysis of almost 1400 cases in Utah, USA, Leister et al. (2019) investigated acute associations between spontaneous abortion (< 20 weeks) and exposures to PM2.5, NO2, and O3 within 1 week. While the study found no associations with PM2.5 or O3, a positive association with NO2 was observed [32]. Each 10 parts per billion increase in average NO2 exposure during the 7 days prior was associated with a 16% increase in the odds of spontaneous abortion [32]. A prospective cohort study also found that an 18 parts per billion increase in cumulative NO2 exposures during the entire gestational period was associated with 34% (95% CI 13–58%) increased risk of pregnancy loss after 30 days since positive hCG test [27]. Wang et al. (2020) also evaluated associations between loss (< 20 weeks) and CO2 and CO; positive associations with whole-pregnancy NO2 exposures but not CO was observed [35]. Similarly, a time-series study in China reported associations with NO2 exposure within 1 week, but not with any other pollutant [33]. Meanwhile, a time-series study in Iran showed mostly null or neglectable inverse associations with NO, NO2, SO2, and CO exposures within 1 week [39].

Air Pollution and Stillbirth

Sixteen studies evaluated the associations between air pollutants and stillbirth during the review period (Table 2) [27, 28, 30, 31, 34, 36, 37, 39,40,41,42,43,44,45,46,47]. Like the case for spontaneous abortion discussed above, PM2.5, NO2, and O3 received the most attention.

Fine Particles and Constituents

Of the 14 studies evaluating the associations between PM2.5 and stillbirth [28, 31, 34, 36, 37, 39,40,41,42,43,44,45,46,47], seven suggested positive association [34, 36, 37, 41,42,43, 46], six suggested null association [28, 31, 39, 40, 44, 47], and one showed inverse association [45]. Positive associations between stillbirth and whole-pregnancy average PM2.5 exposures were observed in two large case–control analyses of pregnancies from three south Asian countries [41, 42] and several large cohort studies in Southern Israel [46] and China [34, 37]. These positive associations were observed for PM2.5 exposures during all three trimesters [34, 37] and first trimester [46]. Particles with slightly bigger sizes including PM2.5–10 and PM10 were also observed to be associated with stillbirth [28, 37]. On the other hand, a number of studies from Texas and California, USA; Korea; Australia; and Iran showed no associations with particles of any sizes [28, 31, 39, 40, 44, 47]. Constituents of fine particles were also investigated in two studies [31, 43], one of which found that an interquartile range (0.007 μg/m3) increase in average zinc particle exposure during the entire gestational period was associated with an 11% increased risk for stillbirth in Harris County, Texas [31].

Gaseous Pollutants

Eight studies evaluated the impacts of O3 on stillbirth risk, with four showing positive associations [28, 31, 37, 45] and four no association [34, 39, 40, 44]. None of the five studies investigating CO impact observed any relationship [28, 37, 39, 40, 47]. One of 10 studies on NO2 showed positive association with stillbirth [27] while one suggested inverse association for first and second trimester exposures [45], and another showed neglectable inverse association for exposures during the week before the event [39]. NO and NOx were evaluated in two studies [39, 45] with one showing a weak inverse association with NOx [45]. Furthermore, two studies [28, 40] suggested positive associations with SO2 while four did not [34, 37, 39, 47].

Windows of Exposure

Studies considered both acute and chronic windows of exposure (Table 2). Acute windows of exposure generally included daily exposures during the week prior to the pregnancy loss event. Chronic windows include average exposures during preconception (usually within a few months of conception), each trimester, entire pregnancy, or the entire study period. Some studies also considered average exposures during the last 3–6 months of pregnancy. Generally, there is evidence suggesting that air pollution has both acute and chronic impacts on both pregnancy loss outcomes. For chronic exposures, nearly all studies that investigated impacts of average whole-pregnancy and first trimester exposures showed positive associations with both pregnancy loss outcomes. Acute exposures during the week prior to loss were also implicated in numerous studies.

Susceptible Subpopulations

Numerous studies identified subgroups who may be more susceptible to the impacts of air pollution, even at the same level of exposure (i.e., explored potential effect modifiers). Some commonly considered effect modifiers included maternal age, fetal sex, maternal education, race/ethnicity, gestational age, employment status, income/deprivation index, comorbidity, and smoking status (Table 2). Overall, there is some evidence suggesting that more disadvantaged populations and those with extreme maternal age may be more susceptible. However, effect modifier variables were not consistently defined across studies, which contributed to the somewhat inconsistent findings. Rammah et al. (2019) found that the impacts of O3 over the entire gestational period on stillbirth risk was the strongest among Hispanic women and for pregnancies ended before 37 weeks [31]. One study suggests that the impacts of PM2.5 were lower among women with lower maternal age and those with higher educational attainment [43]. Another study found significant impacts for women ages 25–34 but not for any other age groups [28], while others suggested women < 35 years [33, 42] and < 25 years [36] were more susceptible. One study found stronger associations for male fetus and women with no previous pregnancy and delivery experience [34].


This review summarizes the recent literature regarding the impacts of outdoor air pollution on pregnancy loss. Evidence suggests that both short- and long-term exposures to air pollution during pregnancy can increase one’s risk. While associations with fine particles appeared most consistent, there is evidence suggesting pregnancy loss risk associated with SO2, NO2, and O3. These findings are consistent with older literature before the review period. Grippo et al. (2018) conducted a comprehensive review on the impact of air pollution on pregnancy loss and found consistent evidence suggesting that PM10 (during the entire gestational period) and CO (during first trimester) were associated with spontaneous abortion [21]. The same review also suggests that PM2.5, PM10, and CO during the third trimester were also associated with stillbirth risk, while evidence for other pollutants like NO2 and SO2 were somewhat inconsistent [21]. Another review of stillbirth in relation to PM2.5 and O3 also reported consistent positive associations for these two pollutants in four of the five included studies [20]. Two more recent reviews reported positive associations between stillbirth and PM2.5 (third trimester and entire gestational period), CO (third trimester), and O3 (first trimester and 4 days prior) [23, 24]. Despite consistency in findings for many pollutants, there were still some inconsistencies. For example, we did not find evidence of association with CO in recent studies. In general, there were challenges that can explain inconsistencies.

Challenges and Opportunities

Exposure Assessment

To better estimate and understand the causal effects of air pollution on pregnancy loss, accurate assessment of air pollution exposure is crucial. This includes not only the intensity, but also the pattern, timing, and duration of exposure. A few studies estimated exposures by linking residential address of participants (at the time of delivery) to local fixed air monitors [28, 30, 33, 34, 37, 39, 40, 44]. This strategy assumes that people have the same exposure levels as measured at local fixed station(s), regardless of proximity. While highly feasible, especially for studies with large sample size, this approach cannot capture small local variations and is highly prone to misclassification that may vary by distance from the monitor(s). Some studies minimize this issue by restricting to only participants within a certain distance (e.g., 10 km) from a monitor [28]. However, this approach can potentially introduce selection bias and cannot completely address small spatial variation.

A higher proportion of recent studies uses complex mathematical or machine learning models to estimate exposures for individuals located at any location and time. Such approach allows more flexibility for estimation by incorporating factors that can influence air pollution variation such as land use, weather parameters, and photochemical and transport properties of pollutants. Even so, the output resolution of these models differed significantly across studies. Furthermore, many studies do not have residential addresses and had to rely on large geographic unit such as US zip code for estimation. Even for those that do have residential address, it is known that pregnant women are mobile across pregnancy [48]. Thus, while residential history or time activity patterns are valuable for accurate estimation, these data points are not available, leading to potential non-differential misclassification, which would bias results towards the null. It is also important to note that in many regions of the world where stillbirth risk is high, there is no air pollution data for population-based risk estimates. A detailed systematic review of exposure assessment of air pollution exposure in relation to reproductive outcomes (including pregnancy loss) has been published elsewhere [49].

As wearable technologies become more accessible, they can be used for personal monitoring and/or supplementing existing exposure assessment strategies. To date, although no studies on pregnancy loss utilize personal monitoring, studies on other health outcomes have successfully implemented this approach [48, 50,51,52,53,54]. Given pregnancy is a relatively short window of opportunity, this approach is potentially feasible and allows prospective capturing of small variation in timing, pattern, and duration of exposures, which can help explore specific windows of susceptibility. Many wearable devices do not have federal reference quality, but they can help improve exposure assessment and are being increasingly sophisticated.

Air pollution is a mixture of different pollutants, each of which may have both independent and joint effects with other pollutants. Many of these pollutants are also highly collinear. As such, sometimes we may be interested in the effects of (a) an aggregate mixture, (b) a sum of components within a mixture, (c) independent effects of components within a mixture, or (d) joint effects of components within a mixture [55]. To date, no study on air pollution and pregnancy loss have considered mixture effects, but multiple approaches have been used in related literatures. For example, Hierarchical Bayesian approach (e.g., Bayesian Kernel Machine Regression), dimension reduction methods (e.g., principal component analysis), clustering, and recursive partitioning have been suggested to address mixture effects [56,57,58]. Machine learning tools can also be used to explore the independent and joint effects air pollution data with high dimension [56]. These tools can include the use of penalized estimators such as partial least absolute shrinkage, selection operator, and ridge regression; and decision trees, which may include techniques such as random forest and Bayesian additive regression trees [56].

Outcome Assessment

A significant challenge for pregnancy loss studies involves the fact that most losses occur early, even before parents are aware that they are pregnant. During the review period, most studies were retrospective and relied on self-report or administrative data such as medical records, vital statistics, or registries to identify pregnancy loss cases. Thus, many early losses were likely excluded, potentially leading to an underestimation of risk. To date, only two studies used prospective clinical assessment of pregnancy loss (with one during the review period) [3, 27]. It is important to note that participants only included couples who were actively planning to become pregnant. These studies therefore excluded unintended pregnancies, which represent nearly half of all US pregnancies [59]. Prospective study designs are necessary for not only effective capture of early losses, but also allow better assessment of exposure and potential confounders that are not available in administrative data.

Another challenge is the inconsistent definition of pregnancy loss. For administrative data, different jurisdictions may be mandated to capture loss/mortality outcomes for births beyond different gestational age. As such while some studies defined stillbirth as death ≥ 20 weeks [28, 30, 31, 34, 44], others use different cutoffs including 22 weeks [40], 24 weeks [45, 46], 28 weeks [37], and 5 months [41,42,43]. For miscarriage/spontaneous abortion, the range of definition included < 20 weeks [29, 32, 35], and < 13 weeks [38], and < 5 months [41,42,43]. Meanwhile, the definition was unclear in a couple studies [33, 39, 47]. As these inconsistencies presents a challenge for direct comparison across studies, it may be helpful for the field to consider at least a more standardized approach to design and report studies.

Susceptible Populations

Even at the same level of exposure, specific subgroups of individuals may experience higher risks because of other intrinsic or extrinsic factors. The general literature regarding the health impacts of air pollution suggests that individuals who are pregnant, have genetic predisposition, have health complications, come from disadvantaged communities, or at the age extremes (i.e., children and the elderly) are more susceptible to the impacts of air pollution [60]. While some studies on air pollution and pregnancy loss attempted to identify these subgroups by incorporating interaction or stratified analyses, efforts and findings are still inconsistent. Some challenges include the inconsistent definition of effect modifiers across studies, and insufficient sample size/power for group-specific analyses, especially when pregnancy loss is a relatively rare outcome. Nevertheless, with limited resources, accurate identification of these susceptible populations is crucial for targeted mitigation efforts. As such, there is a critical need for large and diverse studies, especially among underserved populations, that can allow detailed analyses to identify susceptible subgroups.

Biologic Mechanisms

Although the exact biologic mechanisms remain to be elucidated, the association between air pollution and pregnancy loss is biologically plausible. Exposures to fine particles can induce the release of systemic oxidative stress [61] and inflammation markers [62, 63], which are capable of compromising placental-fetal exchange and disrupt the normal oxygen and nutrients delivery into fetal circulation [64]. Oxidative stress and inflammatory markers can also cross the maternal–fetal blood barrier to perturb fetal development [64, 65]. Fine particles have also been noted in a recent study to be capable of traversing the placental barrier to the fetal side [66]. CO exposures reduce oxygen carrying capacity of maternal hemoglobin, thus can also influence fetal development [67]. More mature literature of reproductive health impacts of smoking, which has many components found in air pollution, suggest that pollutants may trigger irreversible cellular damage, hypoxic damage, or immune mediated injury for both mother and baby [68,69,70,71,72,73].


Given the global concerns related to increased air pollution exposure because of climate change, reproductive impact of air pollution is expected to be a growing public health problem. While more research is needed to further understand the causal impact of specific air pollutants on pregnancy health, existing evidence suggests that air pollution exposures during the gestational period can increase the risk of pregnancy loss. Based on the Precautionary Principle adopted by the United Nations in 1992, when threats of serious or irreversible damage is present, the lack of full scientific certainty and understanding should not be the reason to postpone cost-effective measures [74]. As such, efforts to reduce air pollution exposures among pregnant women should be continued, strengthened, and expanded.

Air pollution has no geographic boundaries, an effective mitigation strategy should involve concerted efforts among policy makers, healthcare providers, researchers, industry partners, community partners, and the public. Efforts to reduce emissions for existing sources should be continued. Meanwhile, judicious permission and careful review of new sources, particularly those located in vulnerable populations, are needed. In addition, promotion and expansion of fuel efficient and clean energy should be a priority, especially in places with high pollution. More funding opportunities to support efforts to reduce exposures and foster a more equitable and sustainable environment are also warranted.

As a trusted voice, healthcare providers are uniquely positioned to become advocate in the efforts to minimize exposure. Studies show that very few healthcare provider discuss the effects of air pollution with their patients, and many feel that they are not prepared for such discussion [75, 76]. There is a clear need for efforts that prepare, empower and incentivize healthcare providers to engage in this important discussion with their patients. There are ongoing discussion for medical schools and continuing education opportunities to highlight environmental health [77, 78], and some colleges are prepared to make sure their medical education curriculum ensures physicians better understand the health effects of air pollution [79, 80]. It is also important to recognize that emerging evidence suggests that communication about environmental risks should also move beyond individual behavior education to empower communities to reduce environmental threats. As such, clear and culturally competent resources should be available to educate, mobilize, and incentivize communities to be involved in this important endeavor [81].

Meanwhile, research efforts are further needed to address a few important gaps. First, much of our current knowledge about the biologic mechanisms linking air pollution on health come from the cardiovascular and respiratory literature. Bove et al. (2019), for the first time, demonstrated that fine particles (i.e., black carbon) can cross the human placenta and accumulate on the fetal side [66]. However, further work is needed to understand the biologic mechanisms linking specific pollutants and pregnancy loss. Detailed data that can allow rigorous investigation of biologic mechanisms related to air pollution exposures during pregnancy are extremely scarce due to ethical and financial feasibility. However, the relatively short duration of pregnancy may present an opportunity for detailed prospective data collection that can also permit temporality and assessment of potential confounding.

Second, it is also important for future studies to improve exposure and outcome assessment. As discussed in “Exposure Assessment,” “Outcome Assessment,” and “Susceptible Populations,” existing studies are limited due to indirect measures of pollution exposures, lack of refined windows of measurement to explore windows of susceptibility, inconsistent outcome definition, inability to capture early loss, and lack of data to explore susceptible subpopulations. As such, prospective cohort studies with diverse participants and more direct and refined windows of air pollution measurements are critical. Despite feasibility challenges, the availability of wearable technology and the relatively short window of pregnancy may present a unique opportunity to advance the field. Additionally, efforts are needed to standardize reporting practices, explore interactions between pollutants and mixture effects, and identify windows of susceptibility and vulnerable subpopulation. As the most impacted communities, who know best regarding solutions for their communities, are often excluded from research and other efforts, it is critical to ensure that all our efforts are inclusive. As such, quality data are also needed in underserved areas where environmental issues are common and pregnancy loss risks are high due to structural and social problems.


Mounting evidence suggests both short- and long-term exposures to air pollution may increase the risk of pregnancy loss. As the climate shifts to conditions increasingly conducive to higher air pollution exposure, these risks will likely be a growing public health concern. While awaiting larger preconception studies to further understand the causal impacts, multi-disciplinary efforts to minimize exposures among pregnant women are warranted. These efforts should involve policy makers, public health practitioner, healthcare providers, researcher, industry partners, community partners, and the public.