Department of Forestry and Environmental Conservation, Clemson University , Clemson, South Carolina 29634, United States.
Department of Environmental Engineering and Earth Sciences, Clemson University , Anderson, South Carolina 29625, United States.
Environ Sci Technol. 2016 Aug 2;50(15):7991-8000. doi: 10.1021/acs.est.6b01578. Epub 2016 Jul 13.
Previous studies demonstrated that wildfires alter spectroscopic characteristics of terrestrial dissolved organic matter (DOM) and increase specific disinfection byproduct formation potential (SDBP-FP). However, it is unclear whether characteristics of thermally altered DOM (TA-DOM) are altered by biogeochemical processes (e.g., transformed by growing algae) before entering water treatment facilities. The freshwater green algae Pseudokirchneriella subcapitata and blue-green algae Microcystis aeruginosa were separately incubated in the mixture of cultural medium and pine (Pinus palustris) litter-derived TA-DOMs (50 °C, 250 °C, and 400 °C) over 7 days to demonstrate the effects of algal growth on alterations in SDBP-FP. TA-DOM optical characteristics and SDBP-FP were quantified by absorption and fluorescence spectroscopy and chlorination-based DBP-FP experiments. After the inoculation with P. subcapitata, TA-DOM aromaticity (indicated by SUVA254) increased from 1.19 to 1.90 L/mg/m for 50 °C-extract but decreased from 4.95 to 3.75 L/mg/m for 400 °C-extract. The fraction of tyrosine-like components decreased from 25.9 to 9.3% for 50 °C-extract but increased from 0.9 to 1.3% for 400 °C-extract. Same patterns were also observed for M. aeruginosa. Growing algae generally increased chlorine reactivities and formations of trihalomethanes, haloacetonitriles, chloral hydrate, and haloketones. Our data suggest that the biodegradable dissolved organic carbon in TA-DOM decreases as fire intensity (i.e., temperature) increases. Postfire algal blooms can increase chlorine reactivity of fire-affected terrestrial DOM for DBP formation.
先前的研究表明,野火会改变陆地溶解有机物(DOM)的光谱特征,并增加特定消毒副产物生成潜能(SDBP-FP)。然而,在进入水处理设施之前,DOM 热转化产物(TA-DOM)的特征是否会被生物地球化学过程(如被藻类转化)改变尚不清楚。淡水绿藻斜生栅藻和蓝藻铜绿微囊藻分别在培养基和松(Pinus palustris)落叶衍生的 TA-DOM 混合物中(50°C、250°C 和 400°C)培养 7 天,以证明藻类生长对 SDBP-FP 变化的影响。TA-DOM 的光学特性和 SDBP-FP 通过吸收和荧光光谱以及氯化衍生的 DBP-FP 实验进行量化。接种斜生栅藻后,50°C 提取物的 TA-DOM 芳香度(以 SUVA254 表示)从 1.19 增加到 1.90 L/mg/m,而 400°C 提取物则从 4.95 降低至 3.75 L/mg/m。50°C 提取物中酪氨酸样成分的比例从 25.9%降低到 9.3%,而 400°C 提取物则从 0.9%增加到 1.3%。铜绿微囊藻也出现了相同的模式。藻类生长通常会增加氯的反应性和三卤甲烷、卤代乙腈、氯仿和卤代酮的形成。我们的数据表明,随着火灾强度(即温度)的增加,TA-DOM 中可生物降解的溶解有机碳减少。野火后藻类大量繁殖会增加受火灾影响的陆地 DOM 的氯反应性,从而形成消毒副产物。