School of Environmental Resources and Development, Asian Institute of Technology, Klong Luang, Pathumthani, Thailand.
J Environ Sci Health A Tox Hazard Subst Environ Eng. 2010;45(3):263-74. doi: 10.1080/10934520903468012.
This study evaluated the application of nanoscale metallic particles (nanoscale zero-valent iron (nZVI) particles) in the remediation of TNT in contaminated water and soil samples. The effects of treatment dosages of synthesized nZVI particles and reaction time on degradation rate of TNT were determined. The synthesized nZVI particles (99.99% pure) size distribution was between 20-100 nm (average particle size 80 nm), with a surface area of 21.63 +/- 0.24 m(2)/g. The optimum dosage of nZVI for degradation of 10 mg/L TNT in the contaminated water was 2000 mg/L (w/v) at a reaction time 20 min. However, trace level of TNT remained since the BOD(5) and COD levels at the optimum nZVI treatment dosage were 834 +/- 8 mg/L and 1280 +/- 900 mg/L, respectively. The BOD(5)/COD ratio was 0.65, which was higher than the BOD(5)/COD ratios for the other nZVI dosages which supports the beneficial effect of using nZVI particles for enhancing degradation of TNT. The observed first-order degradation rate of TNT at 25 degrees C was 0.137 min(-1) corresponding to a degradation rate of 0.156 L/m(2) h. In experiments using sandy clay loam soil containing 20 mg/kg TNT in slurry form (1:2 soil to solution ratio, the optimum nZVI treatment dosage that resulted in 99.88% TNT removal was 5000 mg/kg soil. Less toxic intermediate products and their concentrations following degradation were 2-ADNT and 4-ADNT at 0.90 and 0.10 mg/kg, respectively. Results of this study indicate it is feasible to use nZVI for the remediation of TNT-contaminated water and soil samples as a pre-treatment step however secondary treatments such as phyto-remediation or other biological processes may be needed to remove any residue or intermediate products of TNT degradation.
本研究评估了纳米级金属颗粒(纳米零价铁(nZVI)颗粒)在受污染水和土壤样品中 TNT 修复中的应用。确定了合成 nZVI 颗粒的处理剂量和反应时间对 TNT 降解速率的影响。合成的 nZVI 颗粒(99.99%纯)的粒径分布在 20-100nm 之间(平均粒径 80nm),表面积为 21.63±0.24m²/g。在污染水中,降解 10mg/L TNT 的最佳 nZVI 用量为 2000mg/L(w/v),反应时间为 20min。然而,由于最佳 nZVI 处理剂量下的 BOD(5)和 COD 值分别为 834±8mg/L 和 1280±900mg/L,因此仍残留痕量 TNT。BOD(5)/COD 比值为 0.65,高于其他 nZVI 剂量的 BOD(5)/COD 比值,这支持了使用 nZVI 颗粒增强 TNT 降解的有益效果。在 25°C 下,TNT 的观察到的一级降解速率为 0.137min⁻¹,相应的降解速率为 0.156L/m²h。在含有 20mg/kg TNT 的沙壤土泥浆形式的实验中(土壤与溶液比为 1:2),导致 99.88%TNT 去除的最佳 nZVI 处理剂量为 5000mg/kg 土壤。降解后较少毒性的中间产物及其浓度分别为 2-ADNT 和 4-ADNT,浓度分别为 0.90 和 0.10mg/kg。本研究结果表明,使用 nZVI 作为 TNT 污染水和土壤样品的修复前处理步骤是可行的,然而,可能需要进行植物修复或其他生物过程等二次处理,以去除 TNT 降解的任何残留或中间产物。