[1]孙维民,秦红杰,张志勇,等.双氧水协同凤眼莲去除富营养化水体中高浓度蓝藻的效果[J].江苏农业学报,2023,(01):97-105.[doi:doi:10.3969/j.issn.1000-4440.2023.01.012]
 SUN Wei-min,QIN Hong-jie,ZHANG Zhi-yong,et al.Effect of hydrogen peroxide combined with Eichhornia crassipes on removal of high concentration cyanobacteria in eutrophic water[J].,2023,(01):97-105.[doi:doi:10.3969/j.issn.1000-4440.2023.01.012]
点击复制

双氧水协同凤眼莲去除富营养化水体中高浓度蓝藻的效果()
分享到:

江苏农业学报[ISSN:1006-6977/CN:61-1281/TN]

卷:
期数:
2023年01期
页码:
97-105
栏目:
耕作栽培·资源环境
出版日期:
2023-02-28

文章信息/Info

Title:
Effect of hydrogen peroxide combined with Eichhornia crassipes on removal of high concentration cyanobacteria in eutrophic water
作者:
孙维民123秦红杰45张志勇23张迎颖23陈金峰4姜智绘23宋雪飞23
(1.江苏大学环境与安全工程学院,江苏镇江212013;2.江苏省农业科学院农业资源与环境研究所/农业农村部长江下游平原农业环境重点实验室,江苏南京210014;3.国家农业环境六合观测实验站,江苏南京210014;4.广东省农业科学院环境园艺研究所/广东省园林花卉种质创新综合利用重点实验室,广东广州510640;5.岭南现代农业科学与技术广东省实验室肇庆分中心,广东肇庆526000)
Author(s):
SUN Wei-min123QIN Hong-jie45ZHANG Zhi-yong23ZHANG Ying-ying23CHEN Jin-feng4JIANG Zhi-hui23SONG Xue-fei23
(1.School of Environmental and Safety Engineering, Jiangsu University, Zhenjiang 212013, China;2.Key Laboratory of Agricultural Environment of Lower Yangtze River Plain, Ministry of Agriculture and Rural Affairs, Institute of Agricultural Resources and Environment, Jiangsu Academy of Agricultural Sciences, Nanjing 210014, China;3.National Agricultural Environment Liuhe Observation Experimental Station, Nanjing 210014, China;4.Environmental Horticulture Research Institute, Guangdong Academy of Agricultural Sciences/Guangdong Provincial Key Lab of Ornamental Plant Germplasm Innovation and Utilization, Guangzhou 510640, China;5.Zhaoqing Branch Center of Guangdong Laboratory for Lingnan Modern Agricultural Science and Technology, Zhaoqing 526000, China)
关键词:
双氧水凤眼莲蓝藻水华富营养化水体修复
Keywords:
hydrogen peroxideEichhornia crassipescyanobacterial bloomeutrophicationwater restoration
分类号:
X522
DOI:
doi:10.3969/j.issn.1000-4440.2023.01.012
文献标志码:
A
摘要:
为了实现蓝藻治理与富营养化水体氮、磷等污染物高效削减的双重目标,以暴发蓝藻的城市富营养化河道水体为分析对象,通过模拟试验,研究H2O2与凤眼莲协同去除水体中高质量浓度蓝藻的效果。H2O2除藻质量浓度阈值探索试验结果显示,15 mg/L H2O2处理4 h后,蓝藻的光合活性下降了75%,24 h内其活性无明显恢复。H2O2与凤眼莲协同试验结果表明,在处理后的前72 h,单一H2O2处理的除藻效果最好,在处理后72 h至处理后96 h,H2O2+凤眼莲处理的除藻效果最好,单一凤眼莲处理在试验后96 h内无明显除藻效果。研究还发现,单一H2O2处理的水体NO-2-N、NH+4-N、PO3-4-P质量浓度较对照组显著升高,可能存在藻华再次暴发的风险。试验后96 h,H2O2+凤眼莲处理对藻生物量的去除率为74.58%,对总氮(TN)、总磷(TP)的去除率分别为54%、36%。此外,微生物群落分析结果表明,H2O2+凤眼莲处理对水体中蓝藻的去除效果较显著,微生物群落多样性较对照显著提高,由此可见,H2O2协同凤眼莲处理可有效控制蓝藻水华并改善水质。
Abstract:
To achieve the dual objectives of cyanobacteria treatment and efficient reduction of pollutants such as nitrogen and phosphorus in eutrophic water, the urban eutrophic river water with cyanobacteria outbreak was taken as the object, and the synergistic removal effect of H2O2 and Eichhornia crassipes on high concentration cyanobacteria in water was studied through simulation experiment. The experimental results showed that the photosynthetic activity of cyanobacteria decreased by 75% after treatment with 15 mg/L H2O2 for four hours, and there was no obvious recovery of its activity within 24 hours. The synergistic experiment of H2O2 and E. crassipes showed that the algae removal effect of single H2O2 treatment was the best in the first 72 hours, from 72 hours to 96 hours, the algae removal effect of H2O2+E. crassipes treatment was the best, and the single E. crassipes treatment had no obvious algae removal effect in 96 hours. It was found that the concentrations of NO-2-N, NH+4-N, PO34-P in the water treated with single H2O2 were significantly higher than those in the control group, and there may be a risk of algal blooms again. At 96 h after the experiment, the removal rate of algae biomass by H2O2+E. crassipes treatment was 74.58%, and the removal rates of total nitrogen (TN) and total phosphorus (TP) were 54% and 36%, respectively. In addition, the results of microbial community analysis showed that H2O2+E. crassipes had a significant removal effect on cyanobacteria in water, and the diversity of microbial community was significantly improved. Therefore, H2O2 combined with E. crassipes can effectively control cyanobacteria bloom and improve water quality.

参考文献/References:

[1]刘旻慧,闻学政,张志勇,等. 生物浮岛与漂浮植物对开放池塘水质净化效果[J]. 水生生物学报, 2017, 41(6): 1318-1326.
[2]HO J C, MICHALAK A M, PAHLEVAN N. Widespread global increase in intense lake phytoplankton blooms since the 1980s[J]. Nature, 2019, 574(7780):667-670.
[3]张振华,高岩,郭俊尧,等. 富营养化水体治理的实践与思考——以滇池水生植物生态修复实践为例[J]. 生态与农村环境学报, 2014, 30(1): 129-135.
[4]童克难. “十年治太”成效与流域氮磷污染变化特征解析[N]. 中国环境报, 2020-07-09(04).
[5]张民,史小丽,阳 振,等. 太湖和巢湖中微囊藻(Microcystis)与长孢藻(Dolichospermum)的长时序变化及其驱动因子[J]. 湖泊科学, 2021, 33(4): 1051-1061.
[6]邓莎,周键. 蓝藻水华的危害及主要控制技术研究进展[J]. 安徽农学通报, 2020, 26(18): 150-151, 198.
[7]赵芳. 基于海绵城市理念的公园建设研究——以武汉韵湖公园为例[C]//《工业建筑》杂志社有限公司.《环境工程》2019年全国学术年会论文集(下册), 2019: 41-43, 71.
[8]李宝磊,刘舒,曾乐,等. 我国污染河流治理与修复技术现状[J]. 科技创新与应用, 2020(1): 137-138.
[9]洪喻,胡洪营. 水生植物化感抑藻作用研究与应用[J]. 科学通报, 2009, 54(3): 287-293.
[10]BARRINGTON D J, GHADOUANI A. Application of hydrogen peroxide for the removal of toxic cyanobacteria and other phytoplankton from wastewater[J]. Environmental Science & Technology, 2008, 42(23): 8916-8921.
[11]DRBKOV M, ADMIRAAL W, MARSLEK B. Combined exposure to hydrogen peroxide and light-selective effects on cyanobacteria, green algae, and diatoms[J]. Environmental Science & Technology, 2007, 41(1):309-314.
[12]MATTHIJS H C P, VISSER P M, REEZE B, et al. Selective suppression of harmful cyanobacteria in an entire lake with hydrogen peroxide[J]. Water Research, 2012, 46(5):1460-1472.
[13]陈志超,张志勇,刘海琴,等. 4种水生植物除磷效果及系统磷迁移规律研究[J]. 南京农业大学学报, 2015, 38(1): 107-112.
[14]HASIBUAN A A, YUNIATI R, WARDHANA W, et al. The growth rate and chlorophyll content of water hyacinth under different type of water sources[J]. Iop Conference Series: Materials Science and Engineering, 2020, 902(1):012064.
[15]洪昌红,曾烨翀,邱静,等. 不同覆盖度水葫芦对藻类水华的抑制效应研究[J]. 广东水利水电, 2020, 297(11): 25-29.
[16]杨小杰,韩士群,唐婉莹,等. 凤眼莲对铜绿微囊藻生理、细胞结构及藻毒素释放与削减的影响[J]. 江苏农业学报, 2016, 32(2): 376-382.
[17]秦红杰,张志勇,刘海琴,等. 两种漂浮植物的生长特性及其水质净化作用[J]. 中国环境科学, 2016, 36(8): 2470-2479.
[18]徐黎,路荣昭,施定基. 蓝藻叶绿素a提取方法的比较[J]. 植物学通报, 1988(4): 246-249.
[19]李合生. 植物生理生化实验原理和技术[M]. 北京:高等教育出版社,2000.
[20]WANG B L, SONG Q Y, LONG J J, et al. Optimization method for Microcystis bloom mitigation by hydrogen[J]. Chemosphere, 2019, 228: 503-512.
[21]陈宇炜,陈开宁,胡耀辉. 浮游植物叶绿素a测定的“热乙醇法”及其测定误差的探讨[J]. 湖泊科学, 2006(5): 550-552.
[22]王应军,全皓,李娟. 过氧化氢除藻及相关环境条件优化[J]. 安全与环境学报, 2016, 16(5): 247-252.
[23]RODRGUEZ E, MAJADO M E, MERILUOTO J, et al. Oxidation of microcystins by permanganate: reaction kinetics and implications for water treatment[J]. Water Research, 2007, 41(1): 102-110.
[24]QIAN H F, YU S Q, SUN Z Q, et al. Effects of copper sulfate, hydrogen peroxide and N-phenyl-2-naphthylamine on oxidative stress and the expression of genes involved photosynthesis and microcystin disposition in Microcystis aeruginos[J]. Aquatic Toxicology, 2010, 99(3): 405-412.
[25]BURSON A, MATTHIJS H C P, DE BRUIJNE W, et al. Termination of a toxic Alexandrium bloom with hydrogen peroxide[J]. Harmful Algae, 2014, 31: 125-135.
[26]景江,周明,汪星,等. H2O2与UV-C灭藻的协同效果研究及工程实验[J]. 环境科学研究, 2006(6): 59-63.
[27]陈超,范帆,史小丽,等. 化学氧化剂对水华蓝藻的控制研究[J]. 中国环境科学, 2018, 38(11): 4307-4313.
[28]KIM Y, KIM W J. Roles of water hyacinths and their roots for reducing algal concentration in the effluent from waste stabilization ponds[J]. Water Research, 2000, 34(13): 3285-3294.
[29]JESPERSEN A, CHRISTOFFERSEN K J. Measurements of chlorophyll-a from phytoplankton using ethanol as extraction solvent[J]. Archiv Fur Hydrobiologie, 1987, 109(3): 445-454.
[30]吴馨婷,祁闯,许晓光,等. 蓝藻腐解对水中营养盐影响的模拟研究[J]. 环境科学学报, 2017, 37(8): 2846-2853.
[31]彭小云. 亚硝酸盐在水产养殖中的危害[J]. 渔业致富指南, 2015(12): 63-64.
[32]RAMSEIER M K, VON GUNTEN U, FREIHOFER P, et al. Kinetics of membrane damage to high (HNA) and low (LNA) nucleic acid bacterial clusters in drinking water by ozone, chlorine, chlorine dioxide, monochloramine, ferrate(Ⅵ), and permanganate[J]. Water Research, 2011, 45(3): 1490-1500.
[33]高岩,易能,张志勇,等. 凤眼莲对富营养化水体硝化、反硝化脱氮释放N2O的影响[J]. 环境科学学报, 2012, 32(2): 349-359.
[34]QIN H J, ZHANG Z Y, LIU M H, et al. Efficient assimilation of cyanobacterial nitrogen by water hyacinth[J]. Bioresource Technology, 2017, 241: 1197-1200.
[35]张迎颖,严少华,刘海琴,等. 富营养化水体生态修复技术中凤眼莲与磷素的互作机制[J]. 生态环境学报, 2017, 26(4): 721-728.

相似文献/References:

[1]杨小杰,韩士群,唐婉莹,等.凤眼莲对铜绿微囊藻生理、细胞结构及藻毒素释放与削减的影响[J].江苏农业学报,2016,(02):376.[doi:10.3969/j.issn.1000-4440.2016.02.022]
 YANG Xiao-jie,HAN Shi-qun,TANG Wan-ying,et al.Physiological characteristics and cell structure of Microcystis aeruginosa and microcystin release and reduction in Eichhornia crassipes-grown water[J].,2016,(01):376.[doi:10.3969/j.issn.1000-4440.2016.02.022]
[2]闻学政,宋伟,张迎颖,等.凤眼莲深度净化污水处理厂尾水的效果[J].江苏农业学报,2018,(05):1072.[doi:doi:10.3969/j.issn.1000-4440.2018.05.015]
 WEN Xue-zheng,SONG Wei,ZHANG Ying-ying,et al.Effects of Eichhornia crassipes on advanced treatment of tail water in domestic sewage plant[J].,2018,(01):1072.[doi:doi:10.3969/j.issn.1000-4440.2018.05.015]
[3]周庆,王岩,宋伟,等.凤眼莲净化藻华养殖尾水过程中的潜在病原菌风险[J].江苏农业学报,2019,(02):340.[doi:doi:10.3969/j.issn.1000-4440.2019.02.014]
 ZHOU Qing,WANG Yan,SONG Wei,et al.Potential pathogen risk in cyanobacteria-blooming aquaculture wastewater after remediated by water hyacinth[J].,2019,(01):340.[doi:doi:10.3969/j.issn.1000-4440.2019.02.014]

备注/Memo

备注/Memo:
收稿日期:2022-04-02基金项目:江苏省治太专项资金项目(TH2018403);国家自然科学基金项目(41877510);广东省农业科学院创新基金产业专项(202136)作者简介:孙维民(1996-),男,山东临沂人,硕士研究生,主要从事水体治理研究。(E-mail)1902454339@qq.com通讯作者:张志勇,(E-mail)jaaszyzhang@126.com;秦红杰,(E-mail)hongjieqin111@126.com
更新日期/Last Update: 2023-03-21