Objectives: To evaluate lifetime exposure to trihalomethanes (THM) through ingestion, inhalation, and dermal absorption in a hospital based case-control study of bladder cancer conducted between 1998 and 2001 in five areas of Spain. The study base was comprised of subjects living in the catchment areas of the participating hospitals. Methods: Individual information on water related habits was obtained from personal interviews of 1219 cases and 1271 controls: residential and occupational history, drinking water source at each residence and job, amount of water consumption, frequency and duration of showering, bathing, and swimming pool attendance. THM levels, water source history, and year when chlorination started in study areas were ascertained through measurements in drinking water samples and questionnaires to water companies and local authorities. Estimates of THM levels covered 79% of the subjects' person-years of exposure. Results: Current and historical average THM levels in water were correlated. Control subjects reported that drinking water source in the last residence was municipal for 63%, bottled for 22%, private well for 2%, and other sources for 13%. For the time window between age 15 and the time of interview, average residential THM level was 32.2 mg/l. THM exposure through ingestion was 23.7 mg/day on average, and was correlated with the ingestion THM level in the workplace. Overall, 79% usually took showers, 16% usually took baths, and 13% had ever attended a swimming pool. Between 21% and 45% of controls unexposed to THM through ingestion were evaluated as moderately or highly exposed through showering or bathing, and 5-10% were exposed through swimming in pools. Conclusion: The importance of evaluating different routes is underscored by findings from experimental studies showing substantial differences in THM uptake and internal distribution by route.D isinfection by-products (DBP) have been associated with elevated risk of several types of cancer, with evidence most consistent for the urinary bladder. This is particularly true among studies that incorporated a detailed evaluation of exposure to trihalomethanes (THM, the most prevalent group of chlorination by-products) as an index of exposure to DBP. [1][2][3][4] Relative risks in these studies were generally below 2.0, and despite the consistency of the evidence, concerns remain about the validity of these findings, particularly regarding the evaluation of exposure.DBP constitute a complex mixture of hundreds of compounds with heterogeneous physical and chemical properties, different mutagenic and carcinogenic potential, and with temporal and spatial variability. 5 6 Different exposure pathways (ingestion, inhalation, dermal absorption) depend on the type of DBP and the exposure setting, such as drinking the water or beverage made up with water, showering, bathing, swimming in pools, and to a lesser extent other water related activities such as washing dishes, cooking, and washing children. [7][8][9][10] Recent studies show that inhalation ...