Table 1.
Study | Outcome | Exposure | ||||||||||
---|---|---|---|---|---|---|---|---|---|---|---|---|
Study (year) [citation] | Location | Design | Time Period | Number of Participants | Male (%) | Age (average (SD) or range, years) | UCa Type | Outcome | Number of Outcomes | Air Pollutants | Concentration (Average (SD) or range, μg/m3) | Assessment method |
For systematic review and meta-analysis | ||||||||||||
Felici (2024)47 | UK | Case-control | 2006~ |
Cases: 53,270 Controls: 302,645 |
Cases: 46.6 Controls: 46.8 |
Cases: 63.76 Controls: 55.63 |
PCa BCa KCa |
Incidence |
PCa: 12,838 BCa: 1516 KCa: 1700 |
PM2.5 NO2 NOX PM10 |
NA | LUR |
Fan (2023)29 | China/Jiangsu | Ecological | 2015–2020 |
PCa: 43,000,000 KCa/BCa: 84,700,000 |
50.8 | NA |
PCa BCa KCa |
Mortality |
PCa: 13,618 BCa:11,392 KCa: 5,820 |
PM2.5 | 60.3 (7.0) | Hybrid machine-learning prediction models & |
Yu (2022) (2)27 | Brazil | Ecological | 2010–2016 |
KCa/BCa: 199,997,499 PCa/TCa:65,496,608 |
48 | NA |
PCa BCa KCa TCa |
Mortality |
PCa: 96,501 BCa:25,019 KCa: 21,018 TCa: 2054 |
Wildfire PM2.5 | 2.38 (1.62) | CTM |
Hvidtfeldt (2022)45 | Europe (Denmark, Sweden, Netherland, France, Austria) | Cohort | 1985–2015 | 302,493 | 0-50 * | 48.2 (13.4) | KCa | Incidence | 847 |
PM2.5 NO2 O3 BC |
PM2.5: 15.3 (8.6–19.2) NO2: 24.1 (12.8–39.2) O3: 87.0 (70.3–97.4) BC: 0.88 (0.385–1.155) # |
LUR |
Yu (2022)28 | Brazil | Ecological | 2010–2018 | KCa/BCa: 147,514,042 | NA | NA |
PCa BCa KCa TCa |
Mortality |
PCa: 127,499 BCa:33,787 KCa: 28,625 TCa: 2802 |
PM2.5 | 7.63 (3.32) | CTM |
Youogo (2022)44 | Canada | Case-control | 1975–1997 | 2844 | 100 |
cases: 66.7 (5.6) controls: 65.5 (6.4) |
PCa | Incidence | 1420 |
PM2.5 NO2 |
PM2.5: 11.9 (3.0) NO2: 29.14 (16.72) |
Satellite |
Taj (2022)41 | Denmark | Case-control | 1989–2014 | 25,387 | 100 | ≤40 (65%) ^ | TCa | Incidence | 6390 |
PM2.5 BC NO2 NO3 O3 SO2 SO4 |
PM2.5: 18.2 BC: 0.85 NO2: 21.75 NO3: 3.71 O3: 58.99 SO2: 13.63 SO4: 3.11 |
DEHM/UBM/AirGIS |
Shin (2022)30 | South Korea | Cohort | 2005–2015 |
PCa: 47,159 BCa: 87,608 KCa: 87,608 |
53.8 | 46.58 (11.01) |
PCa BCa KCa |
Mortality |
PCa: 36 BCa: 27 KCa: 38 |
PM2.5 PM10 |
NA | Kriging |
Huang (2022)31 | Taiwan | Cohort | 2000–2015 | 189,549 | 100 | 39.5 (12.8) | PCa | Incidence | 732 | PM2.5 | 20.81 | Satellite |
Chen (2022)32 | Europe (Sweden, Denmark, Netherland, France, Austria) | Cohort | 1985–2015 | 302,493 | 0–50 * | 41.7–72.5 | BCa | Incidence | 967 |
PM2.5 NO2 BC O3 |
PM2.5: 14.94 NO2: 24.86 BC: 1.672 O3: 85.44 |
LUR |
Coleman (2020)34 | USA | Cohort | 1987–2014 |
PCa: 282,815 BCa: 635,539 KCa: 635,539 |
44.5 | 45.3 |
PCa BCa KCa |
Mortality |
PCa: 1215 BCa:589 KCa: 603 |
PM2.5 | 10.7 (2.4) | LUR |
Coleman (2020) (2)46 | USA | Ecological | 1992–2016 | 35.4 million Δ | 49.7 | NA |
PCa BCa KCa |
Incidence |
PCa: 1,151,454 BCa: 346,681 KCa: 254,706 |
PM2.5 | 11.5 (2.6) | LUR |
Turner (2019)43 | Spain | Case-control | 1998–2001 | 1911 |
Cases: 88 Controls: 87 |
cases: 65.8 (9.7) controls: 64.7 (9.8) |
BCa | Incidence | 938 |
PM2.5 NO2 |
PM2.5: 15.8 (3.89) NO2: 28.6 (10.02) |
LUR |
Shekarrizfard (2018)40 | Canada/Montreal | Case-control | 2005–2009 | 1722 | 100 | Cases: 65.0 (7.0) | PCa | Incidence | 803 | NO2 | 28.2 | LUR |
Gandini (2018)36 | Italy | Cohort | 1999–2008 | 74,989 | 47.3 | 35–65 (70.2%) |
BCa KCa |
Incidence |
BCa: 501 KCa: 196 |
PM2.5 NO2 |
10-30 (NO2: 76.3%, PM2.5: 79.1%) |
CTM |
Pedersen (2018)37 | Europe (Sweden, Norway, Denmark, Netherlands, England, Austria, Italy, Spain) | Cohort | 1985– ~ 2010 |
NO2 /NOX: 303,431 Others: 263,634 |
21-55 * | 48 (43–57) * | BCa | Incidence |
NO2/NOX: 943 Others: 827 |
PM2.5 BC NO2 NOX PM10 PM2.5-10 |
PM2.5: 7.1-30.1 BC: 0.66–3.41 NO2: 5.2–53.2 NOX: 8.7–96.4 PM10: 13.5-46.4 PM2.5-10: 4.0–16.7 * |
LUR |
Datzmann (2018)35 | German/Saxony | Cohort | 2007–2014 | 1,918,449 | 46.8 | 49.33 (25.33) | PCa | Incidence | 9611 |
PM10 NO2 |
PM2.5: 20.89 NO2: 20.44 |
LUR |
Cohen (2018)33 | Israel | Cohort | 2004–2015 |
BCa: 9,816 PCa:7,509 |
44.7 | 68.2 (12.1) |
BCa, PCa |
Incidence |
BCa: 74 PCa:122 |
NOX | 37.24 | LUR |
Turner (2017)42 | USA | Cohort | 1982–2004 |
PCa: 278,455 BCa: 623,048 KCa: 623,048 |
40-69 (85%) |
PCa BCa KCa |
Mortality |
PCa: 1068 BCa:1324 KCa: 927 |
PM2.5 NO2 O3 |
PM2.5: 12.6 (2.8) NO2: 21.62 (9.59) O3: 76.4 (8.0) |
hybrid LUR and BME | |
Raaschou-Nielsen (2017)39 | Europe (Sweden, Norway, Denmark, Netherlands, England, Austria, Italy, Spain) | Cohort | 1985- ~ 2010 |
NO2 /NOX: 289,002 Others: 249,521 |
21-55 * | 48 (43-57) * | KCa | Incidence |
NO2 /NOX: 697 Others: 603 |
PM2.5 BC NO2 NOX PM10 PM2.5-10 |
PM2.5: 7.1–30.1 BC: 0.66–3.41 NO2: 5.2–53.2 NOX: 8.7–96.4 PM10: 13.5-46.4 PM2.5-10: 4.0–16.5 * |
LUR |
Raaschou-Nielsen (2011)38 | Denmark | Cohort | 1993–2006 |
PCa: 25,803 BCa: 53,234 KCa: 46,259 |
47.6 | 56.7 |
PCa BCa KCa |
Incidence |
PCa: 673 BCa:221 KCa: 95 |
NOX | 28.4 | DEHM/UBM/AirGIS |
For systematic review only ¶ | ||||||||||||
Lim (2023)62 | Australia | Cohort | 1996–2018 | 11,627 | 100 | 72.1 (4.4) | BCa | Incidence | 224 |
PM2.5 BC NO2 |
PM2.5: 5.06 (1.68) BC: 1.07 (0.30) NO2: 13.42 (4.09) |
LUR |
Park (2023)61 | Korea | Cohort | 2005–2018 | 231,997 | 77.3 | ≥65 (49.5%) |
PCa KCa UTCa UCa |
Incidence |
PCa: 28,440 KCa: 9,736 UTCa: 12,501 UCa: 50,677 |
PM10 | 56.24 | Monitoring stations |
Dummer (2023)63 | Canada | Case-control | 2005–2011 | 1022 | NA | >20 | UCa | Incidence | 219 |
NO2 SO2 PM1.0 PM2.5 |
NO2: 10.90 (3.95) SO2:0.79 (0.79) PM1.0: 2.7 (0.2) PM2.5: 3.1 (0.3) |
Monitoring stations/LUR |
Wei (2023)60 | USA | Cohort | 2000–2016 | 2,161,156 | 100 | 75–84 (88.8%) | PCa | Incidence | 80,615 |
NO2 PM2.5 |
NO2: 32.52 (0-239.89) PM2.5:9.8 (0–30.9) |
GWR† |
Wang (2019)55 | China | Ecological | 2000–2011 | 44.4 million | 100 | NA | PCa | Incidence & Mortality | NA | PM2.5 | 36–60 (91%) <35 (9%) | Satellite |
Collarile (2017) @53 | Italy | Ecological | 1995–2009 | NA | NA | NA | BCa | Incidence | 650 |
PM10 NO2 SO2 |
PM10: 19.6–107.1 NO2: 10.8–25.5 SO2: 27.5–85.0 |
SPRAY v3 |
Weichenthal (2017)57 | Canada/Montreal | Case-control | 2005–2009 | 2486 | 100 | NA | PCa | Incidence | 1240 | ultrafine particles | 24,263/m3 | LUR |
Cohen (2017) §52 | Israel | Cohort | 1992–2013 | 1393 | 81 | 54 (8) | UCa | Incidence & Mortality |
Incidence:262 Mortality:105 $ |
NOx | 45.9 (17.2, 160.7) | LUR |
Yeh (2017)51 | Taiwan | Ecological | 2000–2012 | NA | NA | NA | BCa | Mortality | NA | PM2.5 | NA | Kriging |
Wong (2016)49 | Hong Kong | Cohort | 1998–2001 | 66,820 | 35 | ≥65 | UCa | Mortality | 155 | PM2.5 | PM2.5: 33.7 (3.2) | Satellite |
Ancona (2015) @48 | Italy/Rome | Cohort | 2001–2010 | 85,559 | 48.4 | 5–106 |
KCa BCa |
Incidence & Mortality |
KCa: 164 (I), 54 (M) BCa: 477 (I), 73 (M) |
SOx PM10 |
SOx:1.67 PM10: 2*10−5 |
SPRAY v5 |
Shekarrizfard (2015)56 | Canada/Montreal | Case-control | 2005–2008 | 1722 | 100 | Cases: 65.0 (7.0) | PCa | Incidence | 803 |
NO2 NOx |
NO2: 14.87 NOX: 788.84 g |
LUR |
Parent (2013)58 | Canada/Montreal | Case-control | 2005–2008 | 1772 | 100 | Cases: 65.0 (7.0) | PCa | Incidence | 803 | NO2 |
controls: 22.20 (5.08) cases: 22.75 (5.25) |
LUR |
AI-Ahmadi (2013)50 | Saudi Arabia | Ecological | 1998–2004 | NA | NA | NA |
BCa PCa |
Incidence | NA | NO2 | NA | Satellite |
Yanagi (2012)59 | Brazil | Ecological | 1997–2005 | NA | NA | NA | BCa | Incidence & Mortality | NA | PM10 | NA | Monitoring stations |
Liu (2009)54 | Taiwan | Case-control | 1995–2005 | 1360 | Cases/controls: 67.8 | 50–69 | BCa | Mortality | 680 |
PM10 NO2 O3 CO SO2 |
PM10: ≤90.29 NO2: ≤84.32 O3: ≤71.4 CO: ≤3.42 SO2: ≤46.82 |
Monitoring stations |
&This model integrates ground measurement data, satellite remote sensing products, and atmospheric reanalysis data.
*Range across cohorts.
#median (5-95% percentile).
^65% of participants in the study were younger than 40 years old.
ΔBased on the Surveillance, Epidemiology, and End Results (SEER)website (https://seer.cancer.gov/registries/data.html), the SEER 12 data covers roughly 12.2% of the US population. In 2016, the US population was 323.1 million, and in 1992, the US population was 256.9 million. Here, the average population between 1992-2016 is applied.
¶Included in the systematic review, but did not provide association estimates that could be included in the meta-analysis (i.e., spatial analysis, combined estimates for various cancer types with no specific estimates by UCa type, air pollution from special pollution sources).
@The environmental air pollutants included the source of nearby incinerators or coal-fired and oil-thermal power plants.
§The study population focused on survivors of myocardial infarction.
$These are numbers of all cancer types.
†Geographically weighted regressions that ensembled predictions from random forests, gradient boosting, and neural network
BCa bladder cancer; BME Bayesian maximum entropy interpolation model, CTM chemical transport model, DEHM Danish Eulerian Hemispheric Model, KCa kidney cancer, LUR land use regression, NA not available, PCa prostate cancer, SD standard deviation, TCa testicular cancer, UTCa urothelial cancer, UCa urological cancer, UBM Urban Background Model, GWR geographically weighted regression.