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                  <mods:namePart>Jiménez, Tamara</mods:namePart>
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                  <mods:namePart>García-Pérez, Javier</mods:namePart>
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                  <mods:dateAccessioned encoding="iso8601">2025-10-22T13:35:28Z</mods:dateAccessioned>
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               <mods:identifier type="citation">Jiménez T, Domínguez-Castillo A, Fernández de Larrea-Baz N, Lucas P, Sierra MÁ, Salas-Trejo D, Llobet R, Martínez I, Pino MN, Martínez-Cortés M, Pérez-Gómez B, Pollán M, Lope V, García-Pérez J. Residential exposure to traffic pollution and mammographic density in premenopausal women. Sci Total Environ. 2024 Jun 10;928:172463. doi: 10.1016/j.scitotenv.2024.172463. Epub 2024 Apr 12. PMID: 38615764.</mods:identifier>
               <mods:identifier type="doi">10.1016/j.scitotenv.2024.172463</mods:identifier>
               <mods:identifier type="journal">Science of The Total Environment</mods:identifier>
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               <mods:abstract>Background: Mammographic density (MD) is the most important breast cancer biomarker. Ambient pollution is a carcinogen, and its relationship with MD is unclear. This study aims to explore the association between exposure to traffic pollution and MD in premenopausal women. Methodology: This Spanish cross-sectional study involved 769 women attending gynecological examinations in Madrid. Annual Average Daily Traffic (AADT), extracted from 1944 measurement road points provided by the City Council of Madrid, was weighted by distances (d) between road points and women's addresses to develop a Weighted Traffic Exposure Index (WTEI). Three methods were employed: method-1 (1dAADT), method-2 (1dAADT), and method-3 (eAADT). Multiple linear regression models, considering both log-transformed percentage of MD and untransformed MD, were used to estimate MD differences by WTEI quartiles, through two strategies: "exposed (exposure buffers between 50 and 200 m) vs. not exposed (>200 m)"; and "degree of traffic exposure". Results: Results showed no association between MD and traffic pollution according to buffers of exposure to the WTEI (first strategy) for the three methods. The highest reductions in MD, although not statistically significant, were detected in the quartile with the highest traffic exposure. For instance, method-3 revealed a suggestive inverse trend (e = 1.23, e = 0.96, e = 0.85, e = 0.85, p-trend = 0.099) in the case of 75 m buffer. Similar non-statistically significant trends were observed with Methods-1 and -2. When we examined the effect of traffic exposure considering all the 1944 measurement road points in every participant (second strategy), results showed no association for any of the three methods. A slightly decreased MD, although not significant, was observed only in the quartile with the highest traffic exposure: e = 0.98 (method-1), and e = 0.95 (methods-2 and -3). Conclusions: Our results showed no association between exposure to traffic pollution and MD in premenopausal women. Further research is needed to validate these findings.</mods:abstract>
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                  <mods:topic>Air pollution</mods:topic>
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               <mods:subject>
                  <mods:topic>Breast cancer</mods:topic>
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               <mods:subject>
                  <mods:topic>Breast density</mods:topic>
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                  <mods:topic>DDM-Madrid</mods:topic>
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                  <mods:topic>Premenopausal</mods:topic>
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               <mods:subject>
                  <mods:topic>Traffic exposure</mods:topic>
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                  <mods:title>Residential exposure to traffic pollution and mammographic density in premenopausal women</mods:title>
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