焦化废水中硫氰化物的生物降解及其与苯酚、氨氮的交互影响
Biodegradation of thiocyanate and inhibitory interaction with phenol, ammonia in coking wastewater
查看参考文献18篇
文摘
|
硫氰化物(SCN~-)在焦化废水中的普遍出现,对COD、色度及NH~+_4~-N等指标构成贡献,且生物降解过程中还与其他污染物产生交互作用,影响工程工艺的选择和达标的控制.本研究采用实际工程不同单元工艺的活性污泥,在研究SCN~-的基本降解特性与动力学基础上,重点考察苯酚对SCN~-降解及SCN~-对氨氮硝化过程的影响,评价SCN~-在焦化废水实际降解过程中与其他污染物的交互作用.研究发现,在特征活性污泥培养条件下,SCN~-的降解速率达20.15 mg SCN~-·(g MLSS)~(~-1)·h~(~-1),污泥活性不受SCN~-底物浓度抑制,降解过程符合Michaelis~-Menten动力学模型;苯酚对SCN~-的降解表现为毒性抑制且存在浓度阈值,高浓度苯酚可严重抑制SCN~-的降解,738 mg·L~(~-1)苯酚使108 mg·L~(~-1) SCN~-完全降解时间从1.5 h延长至20 h;SCN~-对硝化过程有抑制作用,可同时影响NH~+_4的去除和NO_2~-的转化,导致硝化系统中NO_2~-浓度的积累.结果表明,生物过程中SCN~-与酚类、NH~+_4之间的交互影响使焦化废水的处理变得复杂且难以控制,针对实际工程,需要明确各核心组分之间的相互作用,从共基质效应或毒性效应方面考虑污泥活性与浓度区间的适配,才能构建出各项污染指标得到优化控制的高效工艺. |
其他语种文摘
|
Thiocyanate (SCN~-) is one of the main contaminants in coking wastewater and has non-neglectable contribution to COD, chroma and NH_4~+-N value. The interactive inhibitory reaction of SCN~-with other pollutants would affect the selection of treatment technology and the draining water quality control. In this study, the SCN~- degradation kinetics was investigated using activated sludge of coking wastewater. Effects of phenol on SCN~- degradation and SCN~- on nitrification were also studied in order to assess the interaction of SCN~- with other pollutants. Under specified culture condition, the degradation rate of SCN~- reached up to 20.15 mg SCN~- · (g MLSS)~(-1) · H~(-1) and the sludge activity was not significantly affected by the initial concentration of SCN~-. The SCN~- degradation process follows the Michaelis-Menten model. Experiment results indicated that phenol has toxic inhibition on SCN~-degradation, with 738 mg · L~(-1) phenol, the complete degradation time of 108 mg · L~(-1) SCN~- was delayed from 1. 5 h to 20 h. On the other hand, SCN~- also inhibits the nitrification of NH_4~+ , especially for the conversion of nitrite to nitrate, which resulted in the accumulation of NO_2~-. Hence, the inhibitory interactions of thiocyanate with phenol and ammonia make the treatment of coking wastewater more complicated and difficult. Thus, for the pollution control of coking wastewater, it should identify the interaction effects among main contaminants, consider the adaptation of sludge activity with pollutants concentrations from the point of co-substrate effect or poisonous effect, which would give help in establishing an optimized biological treatment technology. |
来源
|
化工学报
,2009,60(12):3089-3096 【核心库】
|
关键词
|
焦化废水
;
硫氰化物
;
生物降解
;
交互干扰
|
地址
|
华南理工大学环境科学与工程学院, 广东, 广州, 510006
|
语种
|
中文 |
文献类型
|
研究性论文 |
ISSN
|
0438-1157 |
学科
|
环境污染及其防治 |
基金
|
国家科技支撑计划重点项目
;
国家863计划
;
国家自然科学基金
|
文献收藏号
|
CSCD:3724954
|
参考文献 共
18
共1页
|
1.
Kaviraj A. Toxic effects of quinine factory efluents on tilapia Oreochromis mossambicus and aquatic ecosystem.
Philippine Journal of Science,1997,126(1):87-106
|
被引
1
次
|
|
|
|
2.
Bhunia F. Toxicity of thiocyanate to fish,plankton worm and aquatic ecosystem.
Bulletin of Environmental Contamination and Toxicology,2000,64(2):197-204
|
被引
2
次
|
|
|
|
3.
Sharma Virender K. Iron(Ⅵ)and iron(Ⅴ)oxidation of thiocyanate.
Environmental Science and Technology,2002,36(19):4182-4186
|
被引
1
次
|
|
|
|
4.
Changa E E. The chemical and biological characteristics of coke-oven wastewater by ozonation.
Journal of Hazardous Materials,2008,156(1/2/3):560-567
|
被引
1
次
|
|
|
|
5.
冯海兵. 硫氰根的γ射线辐照降解研究.
环境科学,2008,29(6):1578-1581
|
被引
3
次
|
|
|
|
6.
韦朝海. 焦化废水污染特征及其控制过程与策略分析.
环境科学学报,2007,27(7):1083-1093
|
被引
46
次
|
|
|
|
7.
Happold F C. The isolation and characteristics of an organism oxidizing thiocyanate.
Journal of General Microbiology,1954,10(3):261-266
|
被引
1
次
|
|
|
|
8.
Boucabeille C. Degradation of thiocyanate by a bacterial cocultue.
Biotechnology Letters,1994,16(4):425-430
|
被引
4
次
|
|
|
|
9.
Kwon Hyouk K. Thiocyanate degradation by Acremonium strictum and inhibition by secondary toxicants.
Biotechnology Letters,2002,24(16):1347-1351
|
被引
1
次
|
|
|
|
10.
Hung Chien-Ho. Aerobic biodegradation of thiocyanate.
Water Research,1997,31(11):2761-2770
|
被引
1
次
|
|
|
|
11.
国家环境保护总局.
水和废水监测分析方法.4th ed,2002:88-664
|
被引
1
次
|
|
|
|
12.
American Water Works Association.
Standard Methods for the Examination of Water and Wastewater 22nd ed,1999:4500-CN-M
|
被引
1
次
|
|
|
|
13.
Plessis C A du. Empirical model for the autotrophic biodegradation of thiocyanate in an activated sludge reactor.
Letters in Applied Microbiology,2001,32(2):103-107
|
被引
1
次
|
|
|
|
14.
Jeong Y S. Biodegradation of thiocyanate in biofilm reactor using fluidized-carriers.
Process Biochemistry,2006,41(3):701-707
|
被引
5
次
|
|
|
|
15.
Staib Cameron. Thiocyanate degradation during activated sludge treatment of coke-ovens wastewater.
Biochemical Engineering Journal,2007,34(2):122-130
|
被引
17
次
|
|
|
|
16.
Meiling Lay-Son. New approach to optimize operational conditions for the biological treatment of a high-strength thiocyanate and ammonium waste:pH as key factor.
Water Research,2008,42(3):774-780
|
被引
1
次
|
|
|
|
17.
Yamagishi T. Simultaneous removal of phenol and ammonia by activated sludge process with cross-flow filtration.
Water Research,2001,35(13):3089-3096
|
被引
8
次
|
|
|
|
18.
Kim Young Mo. Inhibitory effects of toxic compounds on nitrification process for cokes wastewater treatment.
Journal of Hazardous Materials,2008,152(3):915-921
|
被引
37
次
|
|
|
|
|