The capability of anaerobic bacterial consortia from different environmental sources including soils, sewage sludges, and sediment of the river Saale (Germany) to dehalogenate chlorinated dioxins was compared using 1,2,3,4-tetrachlorodibenzo-p-dioxin (1,2,3,4-TCDD) as the model compound. The inocula were amended with mineral medium and organic acids and spiked with a high concentration (50 µM) of 1,2,3,4-TCDD to stimulate microbial dehalogenating activity. Reductive dechlorination was observed to 1,3dichlorodibenzo-p-dioxin (1,3-DCDD) as the main product and to minor amounts of the 1,2,4-and 1,2,3-trichlorodibenzop-dioxins (TrCDD) using incubations with Saale River sediment. No reaction was observed in the controls and in incubations with soils or sewage sludges. The dechlorination of 1,2,4-and 1,2,3-TrCDD was analyzed in separate subcultures. Reductive dechlorination of 1,2,4-TrCDD was a relative fast process (about 6 µM converted within 58 days) and yielded only one product (1,3-DCDD). 1,2,3-TrCDD was slowly dechlorinated to equal amounts of 1,3-and 2,3-DCDD. These observations suggest that the main dechlorination route of 1,2,3,4-TCDD to 1,3-DCDD proceeds primarily via the removal of a lateral chlorine atom with 1,2,4-TrCDD as the intermediate.