Published online Jun 21, 2023. doi: 10.3748/wjg.v29.i23.3688
Peer-review started: February 7, 2023
First decision: March 20, 2023
Revised: March 31, 2023
Accepted: April 23, 2023
Article in press: April 23, 2023
Published online: June 21, 2023
Processing time: 128 Days and 14.8 Hours
Geospatial patterning has been observed in inflammatory bowel disease (IBD) incidence and linked to environmental determinants of disease. However, knowledge of North American IBD spatial patterns is limited, and unknown in pediatric IBD (PIBD). A further understanding of geospatial patterns of IBD will help guide distribution of healthcare services and aid in identifying potential environmental risk and protective factors and populations at risk.
There is a lack of knowledge of the spatial distribution and environmental exposures relevant to PIBD in Canada and specifically in the Canadian province of British Columbia (BC).
The main objectives of this study were (1) To determine spatial patterning of PIBD and identify location of disease hot and cold spots in the Canadian province of BC during the period of 2001–2016; and (2) to model the association between IBD case counts and population-level ethnicity, average income, rural residence, and known as well as novel environmental determinants. Both objectives were addressed using the methods described below.
The Moran’s I statistic was used as a Local Indicator of Spatial Association to measure the degree, location, and type of geographic clustering of PIBD incidence, a method which improves on visual analysis of mapped incidence by empirically quantifying clustering. Statistical significance of observed clusters was approximated using Monte Carlo simulation. Case counts of IBD, Crohn’s disease (CD), and ulcerative colitis (UC) were modeled in Poisson rate models as a function of average population characteristics and average population environmental exposures to assess associations between IBD and rurality, ethnicity, income, family size, and air pollution, green space, ultraviolet (UV) light, and pesticide exposures. Data sources included a BCCH clinical registry of patients diagnosed with IBD ≤ age 16.9, high-quality national environmental exposure datasets developed for health research, and Canadian census data.
No high incidence hot spots were detected in the densest urban areas, suggesting unexplored urban protective factors. Rurality was negatively associated with UC. Novel risk factors for PIBD and specifically CD included fine particulate matter (PM2.5) pollution and agricultural applications of petroleum oil to orchards and grapes. Spatial distribution was partially explained by rurality, population ethnicity, family size, pesticide applications, air pollution, UV exposure, and residential greenness.
Pesticide and PM2.5 exposure are linked to the development of PIBD. Suburban and low-density urban areas of BC appear to lack protective exposures conferred by rural and dense urban areas.
Exploring geographic patterns of PIBD facilitated the identification of novel environmental determinants, which has prompted followup studies of environmental exposures and IBD onset.