Soil and Water Science Department, University of Florida, Gainesville, FL 32611, USA.
Sci Total Environ. 2010 Jun 1;408(13):2726-32. doi: 10.1016/j.scitotenv.2010.01.005. Epub 2010 Apr 2.
Triclocarban (TCC) is an antibacterial compound commonly detected in biosolids at parts-per-million concentrations. Approximately half of the biosolids produced in the United States are land-applied, resulting in a systematic release of TCC into the soil environment. The extent of biosolids-borne TCC environmental transport and potential human/ecological exposures will be greatly affected by its bioavailability and the rate of degradation in amended soils. To investigate these factors, radiolabeled TCC ((14)C-TCC) was incorporated into anaerobically digested biosolids, amended to two soils, and incubated under aerobic conditions. The evolution of (14)CO2 (biodegradation) and changes in chemical extractability (bioavailability) was measured over time. Water extractable TCC over the study period was low and significantly decreased over the first 3 weeks of the study (from 14% to 4% in a fine sand soil and from 3 to <1% in a silty clay loam soil). Mineralization (i.e. ultimate degradation), as measured by evolution of (14)CO(2), was <4% over 7.5 months. Methanol extracts of the amended soils were analyzed by radiolabel thin-layer chromatography (RAD-TLC), but no intermediate degradation products were detected. Approximately 20% and 50% of the radioactivity in the amended fine sand and silty clay loam soils, respectively, was converted to bound residue as measured by solids combustion. These results indicate that biosolids-borne TCC becomes less bioavailable over time and biodegrades at a very slow rate.
三氯卡班(TCC)是一种常见的抗菌化合物,在生物固体中以百万分之几的浓度被检测到。大约一半的美国生物固体被土地应用,导致 TCC 系统地释放到土壤环境中。生物固体携带的 TCC 对环境的迁移以及人类/生态的潜在暴露程度将受到其生物利用度和在改良土壤中的降解速率的极大影响。为了研究这些因素,放射性标记的 TCC(14C-TCC)被掺入厌氧消化的生物固体中,添加到两种土壤中,并在有氧条件下培养。随着时间的推移,测量了 14CO2 的演变(生物降解)和化学可提取性(生物利用度)的变化。在研究期间,水可提取的 TCC 较低,并且在研究的前 3 周内显著下降(在细砂土壤中从 14%下降到 4%,在粉质粘壤土中从 3%下降到<1%)。通过 14CO2 的演化来衡量的矿化(即最终降解),在 7.5 个月内<4%。用放射性标记薄层层析法(RAD-TLC)分析了添加土壤的甲醇提取物,但未检测到中间降解产物。在添加的细砂和粉质粘壤土土壤中,放射性的约 20%和 50%分别转化为固相燃烧法测量的结合残留。这些结果表明,生物固体携带的 TCC 随着时间的推移变得生物利用度降低,并且生物降解速度非常缓慢。