Edited by: Pedro M. Baptista, Health Research Institute of Aragon (IIS Aragon), Spain
Reviewed by: Luca Rinaldi, University of Molise, Italy
Cosmin Mihai Vesa, University of Oradea, Romania
Jiaman Xu, Boston University, United States
Farhad Saravani, Tehran University of Medical Sciences, Iran
*Correspondence: Yuzhe Kong,
This is an open-access article distributed under the terms of the Creative Commons Attribution License (CC BY). The use, distribution or reproduction in other forums is permitted, provided the original author(s) and the copyright owner(s) are credited and that the original publication in this journal is cited, in accordance with accepted academic practice. No use, distribution or reproduction is permitted which does not comply with these terms.
This investigation explores the worldwide impact of diabetes burden associated with air pollution, drawing on data from the Global Burden of Disease Study 2021.
The influence of air pollution on diabetes burden was analyzed at global, regional, and national levels. The study considered variations across age groups and genders and explored the relationship between disease impact and the Socio-Demographic Index (SDI). Additionally, an ARIMA model was employed to predict the future incidence of diabetes burden related to air pollution until 2050.
In 2021, approximately 281.91 thousand fatalities and 12.90 million disability-adjusted life years were attributed to diabetes burden due to air pollution, featuring an age-standardized mortality rate (ASMR) of 3.3234 (95% UI, 1.9549–4.6634) and an age-standardized DALY rate (ASDR) of 148.9167 (95% UI, 86.5013–224.9116) per 100,000 individuals. There was a noticeable escalation in the disease burden over the period studied. The most severe effects were noted in individuals aged 60 and above. The data also revealed a higher disease burden among males. Forecasting suggests that while low SDI regions might see a decrease in death rates, lower-middle SDI areas could face an increase in standardized mortality rates. On a national scale, Russia, Mexico, and several African nations are predicted to experience rising diabetes burden attributable to air pollution mortality rates and age-standardized mortality rates from now to 2050. South Asia and Africa are anticipated to witness substantial growth in age-standardized death rates compared to other areas.
The results provide essential insights for developing preventive strategies for diabetes burden and measures to mitigate air pollution.
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Diabetes, a persistent medical condition, interferes with how the body processes food into energy. It often emerges in individuals with obesity, which impairs glucose management and heightens insulin resistance, elevating diabetes risk (
Environmental hazards, particularly fine particulate matter (PM2.5), pose significant global health risks. Research indicates that PM2.5 exposure correlates with higher risks of both obesity (
While well-established risk factors like obesity, lack of physical activity, and hereditary traits are recognized (
However, previous studies didn’t analyze the overall disease burden of diabetes burden attributable to air pollution. Thus, this study assesses how air pollution affects the global burden of diabetes burden by analyzing mortality and disability-adjusted life years (DALYs) trends across various demographics and socio-economic indicators from 1990 to 2021. Future trends are also projected using the autoregressive integrated moving average (ARIMA) model, supported by earlier studies (
Our research utilized data from the Global Burden of Disease Study (GBD) 2021, available at
The methodologies adopted to evaluate the diabetes burden are described in external references (
Age-standardized rates (ASR) were employed to adjust mortality and DALY figures for countries with diverse age structures and demographic profiles. We applied a linear regression to the natural logarithm of these rates, expressed as y = α+βx+ϵ, where x denotes the year, and y is the natural log of the rate. The estimated annual percentage change (EAPC) was calculated using the formula 100 * (e^β − 1), accompanied by a 95% confidence interval (95% CI). An upward trend in ASR was determined if both the EAPC and the lower limit of the 95% CI were positive, whereas a decline was noted if the EAPC and the upper limit of the 95% CI were negative. Stability in ASR was inferred if neither condition was met (
Moreover, the ARIMA (Autoregressive Integrated Moving Average) model was utilized to examine the effects of air pollution on diabetes mellitus trends and to project these trends globally, regionally, and nationally from 2020 to 2050. In the ARIMA model configuration (p, d, q), ‘AR’ indicates the autoregressive part with p representing the number of lag observations included in the model; ‘MA’ denotes the moving average segment with q indicating the number of lag forecast errors; and d specifies the degree of differencing required for data stabilization (
Uncertainty intervals (UI) of 95% were determined for all calculated figures (
In 2021, air pollution was responsible for roughly 281.91 thousand deaths and 12.90 million disability-adjusted life years (DALYs) related to diabetes mellitus, featuring an age-standardized mortality rate (ASMR) of 3.3234 (95% UI, 1.9549–4.6634) and an age-standardized DALY rate (ASDR) of 148.9167 (95% UI, 86.5013–224.9116) per 100,000 individuals. Over the past three decades, there has been a marked rise in the diabetes burden attributable to air pollution (
In terms of the Socio-demographic Index (SDI), while high SDI and high-middle SDI regions have experienced a decrease in the diabetes burden due to air pollution, other regions have observed an increase. Additionally, an increase in the overall burden was noted across all SDI regions (
Global and regional deaths and DALYs of diabetes mellitus attributable to air pollution in 1990 and 2021 in 27 global regions.
Location | Deaths Number in 1990 | Deaths Number in 2021 | ASMR in 2021 | DALY Number in 1990 | DALY Number in 2021 | ASDR in 2021 |
---|---|---|---|---|---|---|
|
117055.1981 (165962.1725, 69992.0516) | 281908.8380 (395527.8182, 165678.1738) | 3.3234 (4.6634, 1.9549) | 4568390.0872 (6604453.5510, 2676365.0738) | 12904493.5493 (19485253.9069, 7501414.2293) | 148.9167 (224.9116, 86.5013) |
|
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East Asia | 14727.5217 (20911.7647, 8881.8319) | 37751.9552 (55167.0425, 23300.1518) | 1.8276 (2.6631, 1.1295) | 824439.0782 (1245827.7639, 479151.7348) | 2387936.4267 (3684560.5727, 1386920.5967) | 112.2851 (172.9835, 64.9136) |
Southeast Asia | 12791.3861 (18293.7769, 7899.1202) | 36436.1704 (51043.5376, 22147.5947) | 6.1075 (8.5699, 3.7109) | 459576.2404 (668999.6680, 277287.7965) | 1476712.3687 (2172697.5502, 874644.3192) | 220.6117 (324.8253, 130.7635) |
Oceania | 492.4595 (745.7360, 291.5631) | 1286.6016 (1966.6874, 706.3905) | 19.0845 (29.0002, 10.4003) | 17177.2223 (25830.7760, 10427.4353) | 52693.2245 (79851.8979, 30148.2945) | 621.3560 (945.7589, 355.1970) |
Central Asia | 746.4653 (1117.9430, 418.5825) | 2488.6182 (3591.7984, 1462.0006) | 3.0928 (4.4446, 1.8212) | 35798.5655 (56922.9462, 19624.6453) | 138518.8492 (207337.2660, 81459.3424) | 155.8100 (233.2900, 91.5154) |
Central Europe | 3489.8882 (4995.3647, 2124.1619) | 5438.4075 (7873.7798, 3135.5907) | 2.3089 (3.3464, 1.3302) | 159701.0535 (240033.3917, 87915.7510) | 255097.4515 (395129.1260, 143860.4285) | 120.2278 (186.5299, 67.3995) |
Eastern Europe | 1897.4284 (2748.8987, 1052.1553) | 5028.5939 (8058.7657, 2530.9493) | 1.3850 (2.2185, 0.6970) | 125712.8564 (195719.1721, 67706.9107) | 227548.2176 (365162.8899, 112777.5481) | 66.4575 (106.6777, 32.5307) |
High-income Asia Pacific | 2581.6019 (4063.8218, 892.7968) | 3441.3828 (4974.9071, 1989.7310) | 0.6391 (0.9257, 0.3723) | 135720.6213 (235118.5005, 44485.9463) | 352888.8077 (571645.6177, 186920.1218) | 96.6851 (157.4390, 50.3967) |
Australasia | 162.9260 (411.7248, 6.3782) | 436.2037 (721.2144, 217.3460) | 0.7295 (1.2000, 0.3631) | 5404.8024 (14309.8875, 184.7536) | 18748.2949 (32384.6249, 8877.3381) | 36.7258 (63.6792, 17.2853) |
Western Europe | 14159.5754 (21006.8980, 7611.4867) | 9966.1210 (14953.0625, 5532.3714) | 0.8670 (1.3018, 0.4886) | 394566.4027 (594536.6140, 212282.0242) | 413144.0819 (671273.1168, 213306.2754) | 49.8410 (82.8157, 25.3066) |
Southern Latin America | 1550.7860 (2406.7956, 829.1138) | 1912.1466 (2911.1477, 1041.4349) | 2.1255 (3.2410, 1.1598) | 49491.6721 (77674.6896, 25784.0562) | 93484.2589 (152262.4287, 50637.3706) | 108.9616 (177.1198, 58.9048) |
High-income North America | 6881.3038 (11016.2108, 2741.3070) | 4475.0174 (8056.9680, 1817.8266) | 0.6633 (1.1933, 0.2694) | 246151.2045 (402247.6676, 96027.9795) | 301055.3128 (562699.8736, 117266.5579) | 49.3951 (92.3140, 19.2403) |
Caribbean | 1695.2934 (2534.4880, 890.8865) | 3069.0994 (4680.7284, 1750.6287) | 5.6684 (8.6432, 3.2373) | 58820.3235 (90973.0032, 30474.7866) | 140828.8269 (218925.6747, 77559.0644) | 262.9395 (409.4020, 144.7345) |
Andean Latin America | 782.2747 (1112.6003, 466.7733) | 2565.3712 (3724.1001, 1459.6133) | 4.4561 (6.4632, 2.5362) | 28148.1111 (40902.9454, 16680.9748) | 105561.3220 (158662.8863, 59919.8403) | 176.2803 (264.6323, 100.1207) |
Central Latin America | 7081.5374 (10037.6700, 4398.2229) | 18235.8409 (27256.0315, 10856.8972) | 7.4408 (11.1154, 4.4297) | 270263.3370 (395222.0916, 160774.5611) | 719122.7417 (1087740.2597, 413501.1583) | 280.3022 (423.2255, 161.6501) |
Tropical Latin America | 4139.9958 (6413.2387, 1915.8542) | 8304.6454 (13268.1751, 4179.8888) | 3.3167 (5.3095, 1.6702) | 158441.0346 (250641.1484, 76699.0603) | 338172.2017 (567838.6979, 173090.7017) | 130.2282 (218.3913, 66.6377) |
North Africa and Middle East | 6552.4805 (9291.4332, 3949.1182) | 22388.3259 (31732.6698, 13338.5734) | 5.7063 (8.0298, 3.3953) | 254835.1041 (372106.4090, 152680.9399) | 1230289.9345 (1852439.9446, 720894.9538) | 255.6159 (383.5728, 150.0744) |
South Asia | 22522.9288 (31817.3960, 13753.1357) | 82661.2192 (117963.7517, 48643.2485) | 6.4430 (9.1718, 3.8023) | 874625.7825 (1270423.1982, 521885.8734) | 3346802.8601 (4919034.9482, 1987992.7285) | 220.4004 (321.6524, 130.8132) |
Central Sub-Saharan Africa | 1929.6030 (2815.4227, 1174.9889) | 4639.7403 (6893.6914, 2693.5834) | 10.2495 (14.9176, 6.0600) | 64505.7477 (93396.5765, 39294.4031) | 188123.2643 (280297.8027, 108997.9301) | 313.9963 (463.5407, 181.9338) |
Eastern Sub-Saharan Africa | 6022.3026 (8679.7887, 3625.4875) | 11640.4778 (16705.6779, 6745.2431) | 8.2715 (11.7470, 4.7620) | 185740.6114 (268457.1093, 109893.0197) | 400931.7369 (578903.7322, 234032.2020) | 226.2891 (324.8920, 131.4685) |
Southern Sub-Saharan Africa | 1997.5890 (2844.1628, 1217.2715) | 7016.5256 (10225.8838, 4254.8601) | 13.7259 (19.9942, 8.2911) | 62084.9723 (89645.7421, 37454.4042) | 221361.0138 (320787.4753, 134034.4476) | 379.2860 (548.2145, 229.6119) |
Western Sub-Saharan Africa | 4849.8507 (6998.6712, 2934.7707) | 12726.3741 (18335.8386, 7562.4411) | 7.9127 (11.4000, 4.7694) | 157185.3437 (229960.0314, 92654.1773) | 495472.3529 (721787.9051, 291548.7828) | 239.8894 (345.9861, 142.4705) |
|
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High-middle SDI | 20173.3690 (28802.9125, 12103.6235) | 38951.2947 (56060.0623, 23560.4730) | 1.9804 (2.8529, 1.1989) | 871726.0750 (1311374.9800, 510336.5721) | 2080648.5439 (3196593.9305, 1180843.7641) | 108.4117 (167.7089, 61.6624) |
High SDI | 21821.4335 (32583.3718, 11950.2465) | 21695.3443 (32950.6270, 12189.9508) | 0.9546 (1.4458, 0.5400) | 776220.5040 (1194573.3961, 411469.9721) | 1339270.3990 (2192458.4179, 698466.1025) | 72.6476 (119.2426, 37.7252) |
Low-middle SDI | 26232.9461 (37438.1812, 15932.0077) | 84425.6851 (118940.2042, 50251.1953) | 6.6191 (9.3593, 3.9587) | 972904.8319 (1418692.0810, 589820.0050) | 3433414.7602 (5056634.7496, 2033882.2760) | 231.3510 (338.4636, 136.3710) |
Low SDI | 13613.2478 (19515.6433, 8247.1861) | 31013.1188 (44159.4322, 18332.8679) | 7.2531 (10.2497, 4.2973) | 465812.1450 (673243.1667, 281964.2837) | 1263109.0667 (1828692.8957, 753685.6540) | 234.4284 (342.1238, 139.5443) |
Middle SDI | 35031.1495 (49607.8278, 20775.8184) | 105491.6752 (149953.5829, 62747.3338) | 4.1866 (5.9240, 2.4868) | 1474810.6300 (2128310.7871, 883136.3560) | 4773270.5045 (7165713.8618, 2774297.9443) | 173.7644 (260.5925, 101.1816) |
Region-wise, East Asia, Southeast Asia, and South Asia registered the highest impact with the most deaths and DALYs, whereas Oceania, Central Asia, and Australasia recorded the lowest. Conversely, in terms of ASMR and ASDR, Oceania, Central Sub-Saharan Africa, and Southern Sub-Saharan Africa demonstrated the highest burden (
At the national level, in 2021, there was significant variability in ASMR across countries, with populous nations like China and India showing the highest rates, reflecting major health challenges linked to environmental and public health issues (
Age–specific rates of global deaths
Correlations between ASMR
Projections for mortality rates, DALY rates, ASMR, and ASDR related to CVDs due to air pollution are detailed in
Estimated Trends of Mortality Rate
Estimated Trends of Mortality Rate
Estimated Trends of DALYs Rate
On a national scale, the patterns are expected to stay stable in both 2030 and 2050. However, the projected death rates and ASMR from diabetes mellitus due to air pollution are notably higher in Russia, Mexico, and most African countries compared to others for both 2030 and 2050. In terms of ASDR, nations in South Asia and Africa are expected to witness more significant increases than other countries (
This study examined the diabetes burden worldwide resulting from air pollution between 1990 and 2021, identifying a significant upward trend during this timeframe. The most impacted demographic included individuals over the age of 60, with males showing higher rates. Projections indicate that while mortality rates might decrease in regions with a low Social Development Index (SDI), standardized mortality rates are expected to rise in lower-middle SDI areas. Moreover, diabetes mortality and age-standardized death rates associated with air pollution are projected to remain elevated in Russia, Mexico, and many African nations, with a notably sharper increase in age-standardized mortality rates expected in South Asia and Africa compared to other regions. To our knowledge, this research is the first to thoroughly assess diabetes burden from air pollution.
In 2017, PM2.5 exposure contributed to 4.58 million deaths and 142.52 million DALYs worldwide (
According to the World Health Organization, as economic conditions and sanitation improved, non-communicable diseases (NCDs) represented over 60% of the global disease burden and contributed to more than 70% of deaths in 2017 (
Studies have shown that economic growth has often led to substantial environmental pollution which adversely affects glucose metabolism, promoting insulin resistance and Type 2 Diabetes Mellitus (T2DM, 39). Meta-analyses have established a positive association between significant air pollutants (like PM2.5, PM10, NO2, and NOX) and T2DM (
Furthermore, our studies have shown that East Asia, Southeast Asia, and South Asia bear the greatest burden, with the highest numbers of deaths and DALYs, highlighting that densely populated and rapidly industrializing countries like India and China face disproportionately high disease burdens from PM2.5, exacerbated by significant rural-urban economic disparities and uneven public health resources. Between 2000 and 2010, health welfare costs and losses in labor productivity due to air pollution accounted for 6.5% of China’s GDP annually, and 8.5% of India’s GDP in 2013, while Bangladesh incurs around $6.5 billion annually in related costs. In response, the Chinese government implemented the Air Pollution Prevention and Control Action Plan, revised the Law on the Prevention and Control of Atmospheric Pollution, and took steps such as switching to natural gas for heating, regulating power plants, and limiting vehicle emissions (
Air pollution, especially PM2.5, ozone (O₃), and nitrogen oxides (NOx), can reduce vitamin D synthesis by blocking UVB radiation necessary for its production in the skin. This effect is particularly pronounced in highly polluted urban areas, where low UV exposure contributes to higher rates of vitamin D deficiency. Additionally, pollution–induced inflammation and oxidative stress can impair insulin sensitivity, increasing the risk of diabetes. Both reduced vitamin D levels and increased systemic inflammation from air pollutants may synergistically elevate the risk of type 2 diabetes, highlighting the need for effective environmental and health interventions (
Building on our findings, actionable policy recommendations are essential to mitigate the diabetes burden attributable to air pollution. Governments should prioritize stricter air quality regulations and promote cleaner energy alternatives to reduce particulate matter exposure, particularly in high–risk regions. Integrating air pollution mitigation strategies with existing public health programs targeting diabetes prevention could amplify their impact. Additionally, improving urban planning to decrease air pollution in densely populated areas and raising public awareness about the health risks associated with air pollution are critical. Future policies should also emphasize tailored interventions for vulnerable populations, such as the elderly and individuals in lower SDI regions.
In the context of our study findings, the recent public health measures and policy developments in countries like China and India provide insightful examples. China’s Air Pollution Prevention and Control Action Plan and India’s National Clean Air Program (NCAP) aim to significantly reduce PM2.5 and PM10 levels. These initiatives demonstrate a proactive approach to mitigating air pollution and its associated health impacts, including diabetes mellitus. By incorporating these national efforts into our discussion, we can better illustrate the potential for public health policies to influence and possibly reduce the burden of diseases exacerbated by environmental pollutants (
Our research encounters several notable constraints. Primarily, there is a deficiency of primary data from less developed areas, particularly in Sub–Saharan Africa, where assessments are predominantly based on mathematical modeling, leading to wide ranges of uncertainty. Additionally, air pollution comprises a complex mixture of various components, each possessing unique physicochemical properties and toxic effects that vary significantly across different regions and seasons.
This study offers an in–depth analysis of the global burden of diabetes mellitus attributed to air pollution from 1990 to 2021, observing a significant increase over the years. Individuals aged over 60 were the most impacted, with men facing a greater burden. Looking ahead, only regions with a low Socio–Demographic Index (SDI) are expected to see a decrease in mortality rates, whereas those in lower–middle SDI regions will likely witness an increase in standardized mortality rates. On a national scale, countries such as Russia, Mexico, and most of Africa are anticipated to continue experiencing elevated diabetes mortality rates and ASMR due to air pollution up to 2030 and 2050. Both South Asia and Africa are projected to encounter substantial rises in ASDR compared to other areas.
This underscores the urgent necessity for policymakers to devise and refine preventive measures tailored to specific populations to reduce the diabetes burden associated with air pollution in the future.
The raw data supporting the conclusions of this article will be made available by the authors, without undue reservation.
QM: Formal analysis, Writing – original draft. XioZ: Data curation, Investigation, Writing – original draft. XinZ: Visualization, Writing – original draft. YK: Conceptualization, Data curation, Formal analysis, Investigation, Methodology, Project administration, Resources, Software, Supervision, Validation, Visualization, Writing – original draft, Writing – review & editing.
The author(s) declare that no financial support was received for the research and/or publication of this article.
The authors declare that the research was conducted in the absence of any commercial or financial relationships that could be construed as a potential conflict of interest.
All claims expressed in this article are solely those of the authors and do not necessarily represent those of their affiliated organizations, or those of the publisher, the editors and the reviewers. Any product that may be evaluated in this article, or claim that may be made by its manufacturer, is not guaranteed or endorsed by the publisher.
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