What this study adds
This study analyzed over 6 million emergency department (ED) visits for four nervous system conditions, including Parkinson disease, multiple sclerosis, seizures, and migraines, and evaluated their short-term associations with exposure to PM 2.5 , NO 2 , and CO. This study represents the largest US investigation linking air pollution to neurological morbidity and uniquely considers both ED visits and hospitalizations. We found that same-day high ambient air pollution levels were associated with increased ED visits for migraine, Parkinson disease, and seizures, but not for multiple sclerosis. This adds to growing epidemiological evidence that short-term exposure to ambient air pollution may affect patients with neurological conditions.
Introduction
Ambient air pollution is a significant threat to public health, affecting millions of individuals worldwide. Ambient air pollution has been linked to various adverse health outcomes such as cardiovascular diseases (CVDs), respiratory issues, and immune system dysregulation. 1 – 5 Recent studies have also reported associations between air pollution and the development, progression, and exacerbation of neurological conditions. 6 , 7 Particulate matter (PM), nitrogen dioxide (NO 2 ), and carbon monoxide (CO) have been the most widely studied air pollutants. Fine PM with diameters ≤ 2.5 µm (PM 2.5 ) can reach the bloodstream through the respiratory system, causing systemic inflammation that may affect the nervous system. 8 , 9 PM 2.5 can also directly enter the brain through olfactory nerves. 10 NO 2 , primarily produced by vehicle emissions and industrial activities, contributes to oxidative stress and cellular damage. 11 CO disrupts oxygen transport in the blood, leading to hypoxia and potential neurological effects. 12 Given the high prevalence of neurological conditions globally 13 and their considerable impacts on patient quality of life and healthcare burden, 14 , 15 understanding risks associated with ambient air pollution is critical for public health.
Parkinson disease (PD), seizures, and other nervous system disorders are particularly susceptible to environmental influences. 16 – 18 Several recent studies have investigated both long-term and short-term effects of air pollution exposure. For short-term exposure, in France (2009–2017), PM 10 , PM 2.5 , and NO 2 were linked to a rise in hospital admissions for PD, particularly during cold and warm seasons. 19 In a study of European cities, short-term exposure to PM 2.5 was associated with increased emergency admissions for both Alzheimer disease (AD) and PD, with older individuals being more affected and AD showing stronger effects at shorter lags. 20 Additionally, in Taiwan (2009–2013), pollutants such as CH 4 , NO, and PM 2.5 were associated with hospital visits for seizures, with the strongest associations observed during winter. 21 In Seoul (2008–2014), researchers found that higher air pollution levels were associated with a higher risk of migraines in various lag structures . 22 And a study in Strasbourg (2000–2009) found that short-term exposures to NO 2 , PM 10 , and O 3 were associated with an increased risk of multiple sclerosis (MS) relapses. 23
For long-term exposures, a large nationwide cohort study in the United States reported that PM 2.5 was associated with increased risks of PD- and AD-related dementias. 24 Meanwhile, in a large Medicare cohort across northeastern US cities (1999–2010), the study found that long-term PM 2.5 exposure was significantly associated with increased risks of first hospital admission for dementia, AD, and PD. 25 A large UK Biobank cohort study found that long-term exposures to multiple air pollutants (PM 2.5 , PM 10 , and NO x ) were associated with an increased risk of new-onset migraine. 26 However, a large Canadian population-based cohort study did not find significant associations between long-term exposure to PM 2.5 , NO 2 , or O 3 and the incidence of MS. 27
Despite growing evidence from short-term studies of air pollution and neurological conditions such as PD, most prior work has focused on single conditions or non-US populations, and evidence based on emergency department (ED) visits in the United States remains scarce. ED care represents a crucial indicator for disease burden and is an understudied outcome compared with hospital admission and mortality. 28 The ED is the only component in the US healthcare system that is accessible at any time of day and plays important roles in disaster response and syndromic surveillance. 29 – 31 Also, because EDs provide treatment regardless of the ability to pay, they often serve as the safety net for populations with care-seeking barriers. 32 – 34 Finally, the role of ambient CO in contributing to acute neurological outcomes remains underexplored despite known pathophysiological mechanisms.
This study aims to investigate associations between short-term exposure to PM 2.5 , CO, and NO 2 and ED visits for four neurological conditions, including PD, MS, migraine, and seizure, to address these research gaps. These conditions were selected due to their significant public health importance and the limited but emerging evidence linking them to environmental exposures. Together, they represent a significant healthcare burden in the United States—migraine alone affects 1 of every 6 American, 35 while seizures affect approximately 3.4 million. 36 MS 37 and PD, 38 although less prevalent, are associated with high treatment costs and long-term disability.
We utilized patient-level hospital discharge data from California during 2005–2018 to examine lag effects and subgroup analyses based on age, sex, race, and ethnicity. Our findings aim to provide evidence of the short-term health effects of ambient air pollution on the nervous system, helping guide public health efforts and policies to reduce these risks.
Methods
Emergency department visits and air pollution data
We obtained patient-level hospital discharge data from the California Office of Statewide Health Planning and Development during the period 2005–2018. Our definition of ED visits included patients who were discharged from the ED, as well as those that led to hospital admission. ED records included the admission date, age at the visit, self-reported residential ZIP codes, race, ethnicity, and International Classification of Diseases version 9/10 (ICD-9/10) diagnosis codes. Using both primary and secondary diagnosis codes, we identified visits with at least one of the following four nervous system-related outcomes: PD (ICD-9 codes 332, ICD-10 codes G20, G21), MS (ICD-9 codes 340, ICD-10 codes G35), migraine (ICD-9 codes 346, ICD-10 codes G43), or seizures (ICD-9 codes 345, 780.39, ICD-10 codes G40, G41). The occurrence of PD in individuals under 18 is extremely rare, so we excluded PD-related ED visits for individuals under the age of 18.
ED visit data were linked to daily estimated air pollution concentrations at the ZIP-code level using the date of visit and patients’ residential ZIP code. The daily air pollution data were based on bias-corrected outputs of the Community Multiscale Air Quality model, which provides pollutant concentrations at a 12-km spatial resolution. 39 Bias correction was performed using observations from the air quality monitoring network and land use variables. These data were aggregated to the ZIP-code level by averaging grid cell values overlapping with each ZIP code. Daily specific humidity and average temperature were processed similarly using the 1-km High-resolution Urban Meteorology for Impacts Dataset. 40
Statistical analyses
Short-term associations between air pollutant concentrations and ED visits were estimated via a case-crossover design. For each ED visit, we defined visit-specific controls as the same day of the week falling in the same month, year, and ZIP codes. We examined lag effects by including air pollutant concentrations from the same day (lag 0) and the three previous days (lag 1, lag 2, and lag 3) in the model and focused on cumulative lag effects, which aligns with our research objective to capture the total impact of exposure over time and helps to reduce potential issues of collinearity among adjacent lag days. Due to the large sample size, we utilized conditional Poisson for computation with strata defined by ZIP code, day of week, month, and year. The conditional Poisson approach also has the advantage of allowing for overdispersion via the quasi-Poisson specification. 41 Associations between each pollutant (PM 2.5 , CO, and NO 2 ) and each ED visit outcome were analyzed separately.
Our models accounted for several time-varying confounders. To control within-month residual temporal trends, we used natural cubic splines on the day of the year (1, 2, …, 365 or 366 for leap years) with 6 degrees of freedom and indicators for federal holidays. Nonlinear associations for daily average temperature and specific humidity were specified as natural cubic splines with 6 degrees of freedom. We conducted several sensitivity analyses to evaluate the robustness of the results from our primary analysis. First, we assessed the impact of varying degrees of freedom (8, 10, and 12) for the day-of-year spline used to model the overall temporal trend. Second, we assessed associations of air pollutant concentrations separately at different cumulative lags (lag 0–1, lag 0–2, and lag 0–3) to investigate cumulative effects. To address potential residual confounding by temperature, we conducted additional analyses using a distributed lag nonlinear model approach, in which temperature was modeled using a cross-basis function including lags up to 3 days (lag 0–3). Risk ratios (RRs) are reported per interquartile range (IQR) increase in exposure. All data analyses were performed in R 4.3.1. 42
We conducted stratified analyses based on age, sex, and race/ethnicity, respectively. Age groups were categorized as <18, 19–44, 45–64, and ≥65 years. Sex was stratified into male and female groups. Race and ethnicity were classified into six categories: Hispanic, non-Hispanic Black, non-Hispanic White, non-Hispanic Asian, non-Hispanic American Indian or Alaska Native, and other. Given that younger onset PD cases may also experience exacerbations of PD and/or comorbid conditions, we have elected to include them in the analysis. Finally, we examined associations separately for visits that were discharged from the ED and those that led to hospital admission.
Results
Table 1 gives descriptive statistics of ED visits for PD, MS, migraine, and seizure stratified by age, sex, and race/ethnicity. Overall, this study included over 6 million ED visits (609,213 for PD, 250,027 for MS, 1,950,387 for migraine, and 3,281,504 for seizure). For ED visits of PD, more than 86% of the patients were aged 65 or older, while for MS, migraines, and seizures, the majority of patients were adults aged 18–64 years. For ED visits related to MS and migraines, female patients significantly outnumbered male patients. Table S1; https://links.lww.com/EE/A391 summarizes the distribution of ED visits identified for each outcome by primary and secondary discharge diagnosis codes and by hospitalization status. Most ED visits for PD (96.3%) and MS (85.8%) were ascertained based on secondary diagnoses. Across conditions, the proportion of ED visits that resulted in hospitalization varied substantially, with approximately 50% for PD, 41% for MS, 38% for seizure, and only 19% for migraine.
Table 1.
Study population characteristics of ED visits for four neurological conditions in California (2005–2018)
| Parkinson | Multiple sclerosis | Seizures | Migraines | |
| Overall | 609,213 | 250,027 | 3,281,504 | 1,950,387 |
| <18 | 122 (0.0%) | 1,257 (0.5%) | 380,160 (11.6%) | 83,817 (4.3%) |
| 18–44 | 5,800 (1.0%) | 72,192 (28.9%) | 1,171,058 (35.7%) | 1,079,566 (55.4%) |
| 45–64 | 75,841 (12.4%) | 121,063 (48.4%) | 1,051,428 (32.0%) | 633,897 (32.5%) |
| >64 | 527,450 (86.6%) | 55,515 (22.2%) | 678,858 (20.7%) | 153,107 (7.9%) |
| Female | 249,459 (40.9%) | 170,965 (68.4%) | 1,505,183 (45.9%) | 1,544,629 (79.2%) |
| Male | 303,074 (49.7%) | 61,872 (24.7%) | 1,607,818 (49.0%) | 338,234 (17.3%) |
| Missing | 56,680 (9.3%) | 17,190 (6.9%) | 168,503 (5.1%) | 338,234 (3.5%) |
| Hispanic | 101,897 (16.7%) | 34,600 (13.8%) | 878,841 (26.8%) | 514,113 (26.4%) |
| Non-Hispanic Black | 27,936 (4.6%) | 33,532 (13.4%) | 510,220 (15.5%) | 205,454 (10.5%) |
| Non-Hispanic White | 397,502 (65.2%) | 166,000 (66.4%) | 1,576,760 (48.0%) | 1,062,657 (54.5%) |
| Non-Hispanic Asian | 53,458 (8.8%) | 3,826 (1.5%) | 131,056 (4.0%) | 63,306 (3.2%) |
| Non-Hispanic American Indian or Alaska Native | 1,498 (0.2%) | 553 (0.2%) | 12,743 (0.4%) | 9,733 (0.5%) |
| Non-Hispanic other | 16,048 (2.6%) | 6,208 (2.5%) | 87,010 (2.7%) | 45,933 (2.4%) |
| Missing | 10,874 (1.8%) | 5,308 (2.1%) | 84,874 (2.6%) | 49,191 (2.5%) |
Mean, standard deviation, and IQR for pollutant concentrations are presented in Table 2 . The three pollutants are positively correlated, with the strongest correlation observed between CO and NO 2 (Pearson correlation = 0.73) compared with 0.46 for PM 2.5 and NO 2 and 0.49 for PM 2.5 and CO.
Table 2.
Mean, standard deviation (SD), and IQR of daily ZIP-code level pollutant concentrations (n = 9,328,664 ZIP code days)
| Pollutant | Mean | SD | IQR |
| 1-hour carbon monoxide (CO) (ppm) | 0.57 | 0.45 | 0.43 |
| 1-hour nitrogen dioxide (NO 2 ) (ppb) | 17.24 | 14.98 | 21.3 |
| 24-hour PM 2.5 (µg/m 3 ) | 8.67 | 5.52 | 5.18 |
Figure 1 and Table S2; https://links.lww.com/EE/A391 present the estimated RR between ED visits and exposures to PM 2.5 , CO, and NO 2 across different lag periods (lag 0 and cumulative lag up to 3 days). Overall, we observed positive associations between air pollutants and ED visits that varied by pollutants and outcomes. For PD, short-term association was strongest with CO exposure (lag 0 RR = 1.007, 95% confidence interval [CI]: 1.003, 1.011). We did not observe associations between MS and the three pollutants. For migraines, the strongest association per IQR increase in exposure was observed for NO 2 exposure at lag 0 (lag 0 RR = 1.009, 95% CI: 1.005, 1.015), compared with CO (lag 0 RR = 1.006, 95% CI: 1.003, 1.008) and PM 2.5 (lag 0 RR = 1.003, 95% CI: 1.001, 1.005). A decreasing trend in cumulative lag effects for migraines was observed with CO and NO 2 , whereas the lag effects with PM 2.5 remained consistent. Similarly, associations for seizures were most prominent with NO 2 exposure (lag 0 RR = 1.006, 95% CI: 1.003, 1.010) across different lag periods.

Sensitivity analysis was performed to evaluate the impact of degrees of freedom for temporal confounding (the day of the year). The results indicated that using 8, 10, and 12 degrees of freedom did not affect the short-term associations, supporting the robustness of our findings (Figure S1; https://links.lww.com/EE/A391 ). In addition, results from the temperature-lag sensitivity analysis (Figure S2; https://links.lww.com/EE/A391 ) were consistent with the primary analysis, showing no substantial changes in the estimated associations.
In analyses by ED visit disposition, estimates for PD, migraine, and seizures were broadly similar between patients who were admitted to the hospital and those who were discharged from the ED, with only slightly higher estimated NO 2 effects among discharged PD ED visits. For MS, inpatient analyses suggested stronger positive associations with CO and NO 2 , whereas noninpatient results were closer to null (Figure S3; https://links.lww.com/EE/A391 ).
Table S4; https://links.lww.com/EE/A391 presents estimated RRs for same-day (lag 0) exposure from stratified analyses by sex, race/ethnicity, and age. For migraine ED visits, females had higher RRs for PM 2.5 and CO. Older age groups exhibited stronger associations for migraines across all pollutants, particularly for CO and NO 2 exposures. For MS, increased RRs were observed for NO 2 and CO among non-Hispanic American Indian patients. Similarly, for seizures, associations with PM 2.5 and CO were stronger in this population subgroup. Males exhibited higher RRs than females, especially for CO exposure. The pediatric MS group showed markedly higher RRs compared with other age groups. Hispanic patients showed weaker associations compared with non-Hispanic patients for CO and NO 2 . For PD ED visits, RRs for all three pollutants were higher among non-Hispanic American Indian patients compared with other racial/ethnic groups. Meanwhile, higher RRs were among male patients for all three pollutants. For seizures, patients under 18 showed stronger associations compared with other age groups, especially for CO and NO 2 exposures.
Discussion
We analyzed over 6 million ED visits related to four nervous system conditions, including PD, MS, migraines, and seizures, and evaluated their associations with short-term exposures to three air pollutants: PM 2.5 , CO, and NO 2 . This study represents the largest investigation of its kind in the United States and is unique due to the inclusion of both ED visits and acute hospitalization as the morbidity outcome. We found that same-day high ambient air pollution levels were associated with increased ED visits for migraine, PD, and seizures, but not for MS, except among those that led to hospitalization. This study adds to the growing epidemiological evidence that short-term exposure to ambient air pollution may affect the nervous system.
Furthermore, it is important to interpret our findings in the context of the clinical meaning of ED encounters. Previous literature has emphasized that ED visits for chronic neurological conditions such as PD, MS, and seizures typically represent acute exacerbations rather than incident cases. 43 These exacerbations may be triggered or worsened by environmental exposures, aligning with the short-term nature of our study design. 44 In addition, such visits are often influenced by coexisting chronic conditions, particularly cardiovascular, respiratory, and renal comorbidities, 45 which themselves are sensitive to air pollution exposures. 46 We examined other common chronic conditions, such as CVD, respiratory disease, or renal, that are co-diagnosed with the ED visit encounter. According to Table S3; https://links.lww.com/EE/A391 , CVD, respiratory disease, and renal conditions were most common among PD ED visits with percentages of 74.77%, 31.39%, and 24.12%, respectively, and less frequent among patients with MS, seizures, and migraine.
Our study found associations between exposures to PM 2.5 , CO, and NO 2 and the risk of PD-related ED visits. These results align with previous research indicating that air pollutants may exacerbate PD symptoms through pathways such as oxidative stress, neuroinflammation, and vascular dysfunction. 47 Our subgroup analysis indicated that the magnitude of association was largest among non-Hispanic American Indians, likely reflecting a combination of socioeconomic disparities and a greater prevalence of comorbidities that may interact with PD. 48 However, given the relatively small sample size in this group (n = 1,498; 0.2% of the total PD sample), these findings should be interpreted with caution. Furthermore, we found that males are more affected than females, which aligns with results from a previous study in Seoul, 49 potentially due to biological differences, such as heightened dopaminergic neuron susceptibility, as well as occupational exposures and lifestyle factors that increase contact with air pollutants. 50
Migraine is the most frequent neurological condition encountered in primary care. 51 We found that short-term increases in PM 2.5 , CO, and NO 2 levels were associated with elevated risks of migraine-related ED visits, particularly within 0–2 days after the exposure. Furthermore, elderly individuals were identified as being more susceptible to the effects of these pollutants. Although a definitive biomedical mechanism linking migraine to air pollution has not yet been established, emerging evidence suggests that inflammation and oxidative stress play crucial roles in the adverse neurological effects of air pollution. 52 Our findings agree with the results of previous studies on the short-term effects of air pollution on migraine disease, especially among vulnerable age populations. 22 , 53
The associations observed between lag 0 exposure to CO and NO 2 and the risk of seizure-related ED visits suggest that the acute effects of air pollution may pose a health risk to individuals with epilepsy. Notably, non-Hispanic American Indians and young people (under 18) are more vulnerable compared with other racial and age groups. 48 For children and adolescents, the developing brain is particularly susceptible to neuroinflammatory and neurotoxic damage caused by pollutants, potentially amplifying their risk of seizure episodes. 54 The null associations with PM 2.5 warrant further research and could explore longer lag periods or examine how chronic PM 2.5 exposure interacts with seizure susceptibility, particularly in high-pollution regions. 55
We did not observe overall associations between air pollutant exposure and MS ED visits, which is consistent with prior findings in Spain that there was no association between pollutants (PM 2.5 , CO, and NO 2 ) and MS admissions. 56 However, in subgroup analysis, we found that individuals under the age of 18 years with MS were more affected by the three pollutants, highlighting the vulnerability of younger populations with MS. But these findings should be interpreted with caution, given the small number of visits in the pediatric MS subgroup, which may reduce the stability of the estimates. Further investigation is needed to evaluate the robustness of these findings.
For PD and MS, ED visits are more likely to reflect exacerbations of comorbid conditions rather than incident cases. Prior literature has shown that PD patients frequently present to the ED due to falls, infections, cardiovascular complications, or neuropsychiatric symptoms. 43 Similarly, MS patients have elevated risks of ED encounters and hospitalizations related to infections and respiratory conditions. 57 These findings are consistent with our observation that PD and MS were mostly identified through secondary diagnoses in our dataset.
Our study has several strengths. First, our exposure data leveraged both monitoring measurements and numerical model simulations. This provides improved spatial and temporal coverage than relying only on monitor data. Second, we utilized statewide hospital discharge data that included patients of all ages, all insurance statuses, and both urban and rural neighborhoods. This enhances the reliability of our risk estimates and increases the applicability of the results to broader populations. Third, we evaluated neurological morbidity using ED visits, which is an important and understudied outcome. Finally, our study has a large sample size, which allowed us to separately examine associations across different demographic groups.
There are also some limitations in this study. First, ED visit outcomes were defined based on ICD codes from discharge records that are less accurate than medical records or adjudicated outcomes from prospective cohort studies. Second, we used temporal variations in outdoor air pollution levels as a proxy for the variations in personal exposure levels. While this could introduce measurement errors, we note that previous studies have shown that the effect of this kind of measurement error often leads to attenuated estimated relative risks. 58 , 59 Case ascertainment is a further limitation of our study because of data limitations, as misclassification of neurological diseases in ED visits may occur. 60 Although ED data provide larger numbers and greater power, diagnostic accuracy is generally lower than for inpatient records, as has been shown for cardiovascular outcomes. 61
In summary, this study found that short-term exposure to PM 2.5 , CO, and NO 2 was associated with increased ED visits for migraine, PD, and seizures, but not for MS. By examining several neurological conditions within one large population-based study in California, our results contribute to the growing evidence that air pollution may influence neurological health. Stratified analyses further suggest that the effects may vary across population subgroups, pointing to the importance of considering differential susceptibility in future research and public health strategies.
Conflicts of interest statement
The authors declare that they have no conflicts of interest with regard to the content of this report.
ACKNOWLEDGMENTS
We are grateful for the support of the health data source: California Department of Health Care Access and Information. Authorization to release this information does not imply endorsement of this study or its findings by any of this data source. The data source, their employees, officers, and agents make no representation, warranty, or guarantee as to the accuracy, completeness, currency, or suitability of the information provided here.
Supplementary Material
Published online 23 December 2025
This work was supported by funding from the National Institute of Environmental Health Sciences (NIEHS) of the National Institutes of Health (NIH) under award numbers R01ES027892 and P20ES036110.
The data used in this study were obtained from the California Department of Health Care Access and Information under a data use agreement and are not publicly available. The analytic code used in this study is available from the corresponding author upon reasonable request.
Supplemental digital content is available through direct URL citations in the HTML and PDF versions of this article ( www.environepidem.com ).
References
1. Zhang H Shi L Ebelt ST . Short-term associations between ambient air pollution and emergency department visits for Alzheimer’s disease and related dementias. Environ Epidemiol . 2022 ; 7 : e237 . 36777523 10.1097/EE9.0000000000000237 PMC9915954
2. Serafini MM Maddalon A Iulini M Galbiati V . Air pollution: possible interaction between the immune and nervous system? Int J Environ Res Public Health . 2022 ; 19 : 16037 . 36498110 10.3390/ijerph192316037 PMC9738575
3. Guarnieri M Balmes JR . Outdoor air pollution and asthma. Lancet . 2014 ; 383 : 1581 – 1592 . 24792855 10.1016/S0140-6736(14)60617-6 PMC4465283
4. Lepeule J Laden F Dockery D Schwartz J . Chronic exposure to fine particles and mortality: an extended follow-up of the Harvard six cities study from 1974 to 2009. Environ Health Perspect . 2012 ; 120 : 965 – 970 . 22456598 10.1289/ehp.1104660 PMC3404667
5. Padula AM Tager IB Carmichael SL . Ambient air pollution and traffic exposures and congenital heart defects in the San Joaquin Valley of California. Paediatr Perinat Epidemiol . 2013 ; 27 : 329 – 339 . 23772934 10.1111/ppe.12055 PMC3694598
6. Louis S Carlson AK Suresh A . Impacts of climate change and air pollution on neurologic health, disease, and practice: a scoping review. Neurology . 2023 ; 100 : 474 – 483 . 36384657 10.1212/WNL.0000000000201630 PMC9990849
7. Fu P Guo X Cheung FMH Yung KKL . The association between PM2.5 exposure and neurological disorders: a systematic review and meta-analysis. Sci Total Environ . 2019 ; 655 : 1240 – 1248 . 30577116 10.1016/j.scitotenv.2018.11.218
8. Li N Xia T Nel AE . The role of oxidative stress in ambient particulate matter-induced lung diseases and its implications in the toxicity of engineered nanoparticles. Free Radic Biol Med . 2008 ; 44 : 1689 – 1699 . 18313407 10.1016/j.freeradbiomed.2008.01.028 PMC2387181
9. Schraufnagel DE Balmes JR Cowl CT . Air pollution and noncommunicable diseases: a review by the forum of international respiratory societies’ environmental committee, part 2: air pollution and organ systems. Chest . 2019 ; 155 : 417 – 426 . 30419237 10.1016/j.chest.2018.10.041 PMC6904854
10. Oberdörster G Sharp Z Atudorei V . Translocation of inhaled ultrafine particles to the brain. Inhal Toxicol . 2004 ; 16 : 437 – 445 . 15204759 10.1080/08958370490439597
11. Yan W Ji X Shi J Li G Sang N . Acute nitrogen dioxide inhalation induces mitochondrial dysfunction in rat brain. Environ Res . 2015 ; 138 : 416 – 424 . 25791864 10.1016/j.envres.2015.02.022
12. Raub JA Benignus VA . Carbon monoxide and the nervous system. Neurosci Biobehav Rev . 2002 ; 26 : 925 – 940 . 12667497 10.1016/s0149-7634(03)00002-2
13. GBD 2021 Nervous System Disorders Collaborators . Global, regional, and national burden of disorders affecting the nervous system, 1990-2021: a systematic analysis for the Global Burden of Disease Study 2021 [published correction appears in Lancet Neurol . 2024 May;23(5):e9. doi:10.1016/S1474-4422(24)00114-5] [published correction appears in Lancet Neurol . 2024 Jul;23(7):e11. doi:10.1016/S1474-4422(24)00231-X]. Lancet Neurol . 2024 ; 23 : 344 – 381 . 38493795 10.1016/S1474-4422(24)00038-3 PMC10949203
14. Mateen FJ . Progress towards the 2030 sustainable development goals: direct and indirect impacts on neurological disorders. J Neurol . 2022 ; 269 : 4623 – 4634 . 35583660 10.1007/s00415-022-11180-1
15. Gooch CL Pracht E Borenstein AR . The burden of neurological disease in the United States: a summary report and call to action. Ann Neurol . 2017 ; 81 : 479 – 484 . 28198092 10.1002/ana.24897
16. Hu CY Fang Y Li FL . Association between ambient air pollution and Parkinson’s disease: systematic review and meta-analysis. Environ Res . 2019 ; 168 : 448 – 459 . 30391837 10.1016/j.envres.2018.10.008
17. Feigin VL Vos T . Global burden of neurological disorders: from global burden of disease estimates to actions. Neuroepidemiology . 2019 ; 52 : 1 – 2 . 30472717 10.1159/000495197
18. Kasdagli MI Katsouyanni K Dimakopoulou K Samoli E . Air pollution and Parkinson’s disease: a systematic review and meta-analysis up to 2018. Int J Hyg Environ Health . 2019 ; 222 : 402 – 409 . 30606679 10.1016/j.ijheh.2018.12.006
19. Goria S Pascal M Corso M Le Tertre A . Short-term exposure to air pollutants increases the risk of hospital admissions in patients with Parkinson’s disease—a multicentric study on 18 French areas. Atmos Environ . 2021 ; 264 : 118668 .
20. Franco P Gordo C Marques da Costa E Lopes A . Short-term exposure to particulate matter and effects on emergency hospital admissions for Alzheimer’s disease and Parkinson’s disease: an ecological study from an aged European metropolis. Air Qual Atmos Health . 2023 ; 16 : 1619 – 1631 .
21. Chiang KL Lee JY Chang YM Kuo FC Huang CY . The effect of weather, air pollution and seasonality on the number of patient visits for epileptic seizures: a population-based time-series study. Epilepsy Behav . 2021 ; 115 : 107487 . 33323341 10.1016/j.yebeh.2020.107487
22. Lee H Myung W Cheong HK . Ambient air pollution exposure and risk of migraine: synergistic effect with high temperature. Environ Int . 2018 ; 121 : 383 – 391 . 30245361 10.1016/j.envint.2018.09.022
23. Jeanjean M Bind MA Roux J . Ozone, NO2 and PM10 are associated with the occurrence of multiple sclerosis relapses. Evidence from seasonal multi-pollutant analyses. Environ Res . 2018 ; 163 : 43 – 52 . 29426027 10.1016/j.envres.2018.01.040 PMC5886008
24. Shi L Wu X Danesh Yazdi M . Long-term effects of PM2·5 on neurological disorders in the American Medicare population: a longitudinal cohort study. Lancet Planet Health . 2020 ; 4 : e557 – e565 . 33091388 10.1016/S2542-5196(20)30227-8 PMC7720425
25. Kioumourtzoglou MA Schwartz JD Weisskopf MG . Long-term PM2.5 exposure and neurological hospital admissions in the Northeastern United States. Environ Health Perspect . 2016 ; 124 : 23 – 29 . 25978701 10.1289/ehp.1408973 PMC4710596
26. Dong HJ Ran P Liao DQ . Long-term exposure to air pollutants and new-onset migraine: a large prospective cohort study. Ecotoxicol Environ Saf . 2024 ; 273 : 116163 . 38442473 10.1016/j.ecoenv.2024.116163
27. Bai L Burnett RT Kwong JC . Long-term exposure to air pollution and the incidence of multiple sclerosis: a population-based cohort study. Environ Res . 2018 ; 166 : 437 – 443 . 29940476 10.1016/j.envres.2018.06.003
28. Rubin R . The costs of US emergency department visits. JAMA . 2021 ; 325 : 333 . 10.1001/jama.2020.26936 33496760
29. Nicholas PK Breakey S McKinnon S Eddy EZ Fanuele J Starodub R . A CLIMATE: a tool for assessment of climate-change-related health consequences in the emergency department. J Emerg Nurs . 2021 ; 47 : 532 – 542.e1 . 33280889 10.1016/j.jen.2020.10.002
30. Hammad KS Arbon P Gebbie K Hutton A . Nursing in the emergency department (ED) during a disaster: a review of the current literature. Australas Emerg Nurs J . 2012 ; 15 : 235 – 244 . 23217657 10.1016/j.aenj.2012.10.005
31. Elliot AJ Bone A Morbey R . Using real-time syndromic surveillance to assess the health impact of the 2013 heatwave in England. Environ Res . 2014 ; 135 : 31 – 36 . 25262071 10.1016/j.envres.2014.08.031
32. Gordon JA Billings J Asplin BR Rhodes KV . Safety net research in emergency medicine: proceedings of the Academic Emergency Medicine Consensus Conference on “The Unraveling Safety Net.” Acad Emerg Med . 2001 ; 8 : 1024 – 1029 . 11691663 10.1111/j.1553-2712.2001.tb01110.x
33. Henderson S Stacey CL Dohan D . Social stigma and the dilemmas of providing care to substance users in a safety-net emergency department. J Health Care Poor Underserved . 2008 ; 19 : 1336 – 1349 . 19029756 10.1353/hpu.0.0088
34. Di Somma S Paladino L Vaughan L Lalle I Magrini L Magnanti M . Overcrowding in emergency department: an international issue. Intern Emerg Med . 2015 ; 10 : 171 – 175 . 25446540 10.1007/s11739-014-1154-8
35. Abbaszadeh S Tabary M Aryannejad A . Air pollution and multiple sclerosis: a comprehensive review. Neurol Sci . 2021 ; 42 : 4063 – 4072 . 34341860 10.1007/s10072-021-05508-4
36. Zack MM Kobau R . National and state estimates of the numbers of adults and children with active epilepsy - United States, 2015. MMWR Morb Mortal Wkly Rep . 2017 ; 66 : 821 – 825 . 28796763 10.15585/mmwr.mm6631a1 PMC5687788
37. Wallin MT Culpepper WJ Campbell JD ; US Multiple Sclerosis Prevalence Workgroup . The prevalence of MS in the United States: a population-based estimate using health claims data [published correction appears in Neurology . 2019 Oct 8;93(15):688. doi:10.1212/WNL.0000000000007915]. Neurology . 2019 ; 92 : e1029 – e1040 . 30770430 10.1212/WNL.0000000000007035 PMC6442006
38. Kowal SL Dall TM Chakrabarti R Storm MV Jain A . The current and projected economic burden of Parkinson’s disease in the United States. Mov Disord . 2013 ; 28 : 311 – 318 . 23436720 10.1002/mds.25292
39. Senthilkumar N Gilfether M Chang HH Russell AG Mulholland J . Using land use variable information and a random forest approach to correct spatial mean bias in fused CMAQ fields for particulate and gas species. Atmos Environ (1994) . 2022 ; 274 : 118982 . 38131016 10.1016/j.atmosenv.2022.118982 PMC10735214
40. Newman AJ Kalb C Chakraborty TC . The high-resolution urban meteorology for impacts dataset (HUMID) daily for the conterminous United States. Sci Data . 2024 ; 11 : 1321 . 39632886 10.1038/s41597-024-04086-2 PMC11618800
41. Armstrong BG Gasparrini A Tobias A . Conditional Poisson models: a flexible alternative to conditional logistic case cross-over analysis. BMC Med Res Methodol . 2014 ; 14 : 122 . 25417555 10.1186/1471-2288-14-122 PMC4280686
42. R Core Team . R: a Language and Environment for Statistical Computing . Vienna, Austria : R Foundation for Statistical Computing ; 2023 . Available at: https://www.R-project.org/ . Accessed 24 April 2025.
43. Al-Hakeem H Zhang Z DeMarco EC Bitter CC Hinyard L . Emergency department visits in Parkinson’s disease: the impact of comorbid conditions. Am J Emerg Med . 2024 ; 75 : 7 – 13 . 37897921 10.1016/j.ajem.2023.10.017
44. Cannon JR Greenamyre JT . The role of environmental exposures in neurodegeneration and neurodegenerative diseases. Toxicol Sci . 2011 ; 124 : 225 – 250 . 21914720 10.1093/toxsci/kfr239 PMC3216414
45. Öztürk B . Cardiac effects and comorbidities of neurological diseases. Turk J Med Sci . 2024 ; 54 : 1428 – 1437 . 39735485 10.55730/1300-0144.5928 PMC11673671
46. Rajagopalan S Al-Kindi SG Brook RD . Air pollution and cardiovascular disease: JACC state-of-the-art review. J Am Coll Cardiol . 2018 ; 72 : 2054 – 2070 . 30336830 10.1016/j.jacc.2018.07.099
47. Mosley RL Benner EJ Kadiu I . Neuroinflammation, oxidative stress and the pathogenesis of Parkinson’s disease. Clin Neurosci Res . 2006 ; 6 : 261 – 281 . 18060039 10.1016/j.cnr.2006.09.006 PMC1831679
48. Ortiz-Prado E Begay RL Vasconez-Gonzalez J Izquierdo-Condoy JS . Editorial: Promoting health and addressing disparities amongst Indigenous populations. Front Public Health . 2024 ; 12 : 1526515 . 39735746 10.3389/fpubh.2024.1526515 PMC11672117
49. Lee H Kim OJ Jung J Myung W Kim SY . Long-term exposure to particulate air pollution and incidence of Parkinson’s disease: a nationwide population-based cohort study in South Korea. Environ Res . 2022 ; 212 ( Pt A ): 113165 . 35364040 10.1016/j.envres.2022.113165
50. Clougherty JE . A growing role for gender analysis in air pollution epidemiology. Environ Health Perspect . 2010 ; 118 : 167 – 176 . 20123621 10.1289/ehp.0900994 PMC2831913
51. Burch R Rizzoli P Loder E . The prevalence and impact of migraine and severe headache in the United States: updated age, sex, and socioeconomic-specific estimates from government health surveys. Headache . 2021 ; 61 : 60 – 68 . 33349955 10.1111/head.14024
52. Sun B Song J Wang Y . Associations of short-term PM2.5 exposures with nasal oxidative stress, inflammation and lung function impairment and modification by GSTT1-null genotype: a panel study of the retired adults. Environ Pollut . 2021 ; 285 : 117215 . 33932759 10.1016/j.envpol.2021.117215
53. Portt AE Orchard C Chen H Ge E Lay C Smith PM . Migraine and air pollution: a systematic review. Headache . 2023 ; 63 : 1203 – 1219 . 37795754 10.1111/head.14632
54. Herting MM Bottenhorn KL Cotter DL . Outdoor air pollution and brain development in childhood and adolescence. Trends Neurosci . 2024 ; 47 : 593 – 607 . 39054161 10.1016/j.tins.2024.06.008 PMC11324378
55. Mei H Wu D Yong Z . PM2.5 exposure exacerbates seizure symptoms and cognitive dysfunction by disrupting iron metabolism and the Nrf2-mediated ferroptosis pathway. Sci Total Environ . 2024 ; 910 : 168578 . 37981141 10.1016/j.scitotenv.2023.168578
56. Carmona R Linares C Recio A Ortiz C Díaz J . Emergency multiple sclerosis hospital admissions attributable to chemical and acoustic pollution: Madrid (Spain), 2001-2009. Sci Total Environ . 2018 ; 612 : 111 – 118 . 28846902 10.1016/j.scitotenv.2017.08.243
57. Satish S Patel A Mastick ML . Multiple sclerosis in the emergency department: a retrospective case-control study in a large US center. Neurol Neuroimmunol Neuroinflamm . 2025 ; 12 : e200445 . 40674662 10.1212/NXI.0000000000200445 PMC12273709
58. Kioumourtzoglou MA Spiegelman D Szpiro AA . Exposure measurement error in PM2.5 health effects studies: a pooled analysis of eight personal exposure validation studies. Environ Health . 2014 ; 13 : 2 . 24410940 10.1186/1476-069X-13-2 PMC3922798
59. Dionisio KL Baxter LK Chang HH . An empirical assessment of exposure measurement error and effect attenuation in bipollutant epidemiologic models. Environ Health Perspect . 2014 ; 122 : 1216 – 1224 . 25003573 10.1289/ehp.1307772 PMC4216163
60. Pope JV Edlow JA . Avoiding misdiagnosis in patients with neurological emergencies. Emerg Med Int . 2012 ; 2012 : 949275 . 22888439 10.1155/2012/949275 PMC3410308
61. Khan A Ramsey K Ballard C . Limited accuracy of administrative data for the identification and classification of adult congenital heart disease. J Am Heart Assoc . 2018 ; 7 : e007378 . 29330259 10.1161/JAHA.117.007378 PMC5850158