沉水植物对逆境胁迫的响应研究进展
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摘要
沉水植物在水生生态系统中发挥着重要作用,尤其是在污染水体中的恢复与重建已成为水环境生态修复研究的重点,重金属、有机物和高营养盐等是影响沉水植物生长的主要环境污染胁迫因子,探索沉水植物在逆境胁迫条件下的适应能力是当前研究需要解决的关键问题之一。综述了沉水植物在重金属、有机物和高营养盐逆境胁迫下生理形态和抗氧化系统变化的研究情况,旨在深入了解沉水植物对逆境胁迫的耐受机制,为生态环境修复中沉水植物的筛选与重建提供理论依据。
Submerged macrophytes play an important role in aquatic ecosystems, especially in the recovery and reconstruction of polluted water bodies, which have become the focus of ecological research on water environment. Heavy metals, organic matter and high nutrients are the main environmental pollution stress factors affecting the growth of submerged macrophytes. Exploring the adaptability of submerged macrophytes under adverse stress conditions is one of the key issues that need to be solved in current research. The research on the physiological morphology and antioxidant system of submerged macrophytes under the stress of heavy metals, organic matter and high nutrients was reviewed. The aim is to understand the tolerance mechanism of submerged macrophytes to stress, and provide a theoretical basis for the screening and reconstruction of submerged macrophytes in ecological restoration.
Submerged macrophytes play an important role in aquatic ecosystems, especially in the recovery and reconstruction of polluted water bodies, which have become the focus of ecological research on water environment. Heavy metals, organic matter and high nutrients are the main environmental pollution stress factors affecting the growth of submerged macrophytes. Exploring the adaptability of submerged macrophytes under adverse stress conditions is one of the key issues that need to be solved in current research. The research on the physiological morphology and antioxidant system of submerged macrophytes under the stress of heavy metals, organic matter and high nutrients was reviewed. The aim is to understand the tolerance mechanism of submerged macrophytes to stress, and provide a theoretical basis for the screening and reconstruction of submerged macrophytes in ecological restoration.
引文
[1]甘新华,林清.沉水植物对受污染水体的修复机理及应用前景研究[J].环境科技,2008,21(6):72-75.
[2]黄峰,李勇,潘继征,等.冬春季富营养化滆湖中沉水植被重建及净化效果[J].环境科技,2010.23(4):13-16.
[3]王宝山.逆境植物生物学[M].北京:高等教育出版社,2010:4-10.
[4]吴寒.活性氧在植物体内的作用及其清除体制[J].广东蚕业,2018,52(3):18-20.
[5]胡韧,林秋奇,张小兰,等.Cr3+,Cr6+及其复合污染对狐尾藻的毒害作用[J].生态科学,2003,22(4):327-331.
[6]简敏菲,汪斯琛,余厚平,等.Cd2+,Cu2+胁迫对黑藻(Hydrilla verticillata)的生长及光合荧光特性的影响[J].生态学报,2016(3):1 719-1 727.
[7]施国新,解凯彬,杜开和,等.Cr6+,As3+污染对黑藻叶细胞伤害的超微结构研究[J].南京师大学报(自然科学版),2001,24(4):93-97.
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[9]张嘉桐,关颖慧,司莉青,等.Pb2+、Cd2+复合胁迫对桑树光合作用的影响[J].北京林业大学学报,2018,40(4):16-23.
[10]潘秋红,施国新,徐勤松,等.Cu2+对菱叶片生理指标及超微结构的毒理学效应分析[J].植物科学学报,2009,27(5):527-532.
[11]吕念泽,高桂青,吕顺华,等.Cu2+胁迫对马来眼子菜光合荧光特性的影响[J].南昌工程学院学报,2018,37(4):31-34.
[12]ASSCHE F V H.Clijsters,Effects of metals on enzyme activity in plants[J].Plant cell&environment,2010,13(3):195-206.
[13]崔静,袁旭音,刘泉,等.环境水体中纳米氧化铜对金鱼藻的毒性效应研究[J].农业环境科学学报,2013(5):910-915.
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[15]MISHRA S,SRIVASTAVA S,TRIPATHI R D,et al.Lead detoxification by coontail(Ceratophyllum demersum L)involves induction of phytochelatins and antioxidant system in response to its accumulation[J].Chemosphere,2006,65(6):1 027-1 039.
[16]程飞,张颖,方元平,等.金鱼藻抗氧化系统对镉胁迫的响应[J].安徽农业科学,2012,40(23):11 791-11 793.
[17]高艳.重金属Pb2+胁迫对轮叶黑藻毒性效应研究[D].重庆:西南大学,2017.
[18]李佳华,慕君玲,郭红岩,等.邻苯二甲酸二丁酯污染对苦草生理生化指标的影响[J].环境化学,2005.24(1):32-36.
[19]宋志慧,张元园,柳宁,等.有机农药百草枯对金鱼藻的生理生化参数的毒性作用[J].环保科技,2016,22(1):10-13.
[20]赵秀侠,侯冠军,李静,等.磺胺对苦草(Vallisneria natans(Lour.)Hara)生理生长及细胞超微结构的影响[J].安徽大学学报(自科版),2017,41(2):92-99.
[21]高海荣,林清,陆延婷,等.有机溶剂胁迫下苦草生理指标的变化[J].广西师范学院学报(自然科学版),2006,23(4):40-44.
[22]肖能文,张宇,李卫兵,等.1,2,4-三氯苯对金鱼藻氧化压力及生理特性的影响[J].环境科学与技术,2017(1):49-54.
[23]胡一鸿,王梦龙,袁盛建,等.戊二醛胁迫对黑藻光合作用及抗氧化酶活性的影响[J].农业环境科学学报,2013,32(6):1 143-1 149.
[24]高亚岳,周俊,陈志宁,等.滆湖富营养化进程中沉水植被的演替及重建设想[J].环境科技,2008.21(4):21-24.
[25]王珺,顾宇飞,纪东成,等.富营养条件下不同形态氮对轮叶黑藻(Hydrilla verticillata)的生理影响[J].环境科学研究,2006,19(1):71-74.
[26]朱增银,陈灿,贾海霞,等.不同氮源对苦草(Vallisneria natans)生长及生理指标的影响[J].植物资源与环境学报,2006,15(4):48-51.
[27]高镜清,燕启社,黄五星,等.富营养化水体中铵态氮对金鱼藻生长的影响[J].长江流域资源与环境,2011,20(5):611-616.
[28]马剑敏,靳同霞,李今,等.伊乐藻、苦草和菹草对磷急性胁迫的响应[J].水生生物学报,2008,32(3):408-412.
[29]金相灿,郭俊秀,许秋瑾,等.不同质量浓度氨氮对轮叶黑藻和穗花狐尾藻抗氧化酶系统的影响[J].生态环境学报,2008,17(1):1-5.
[30]NIMPTSCH J,PFLUGMACHER S.Ammonia triggers the promotion of oxidative stress in the aquatic macrophyte Myriophyllum mattogrossense[J].Chemosphere,2007,66(4):708-714.
[31]WANG C,ZHANG S H,WANG P F,et al.Effects of ammonium on the antioxidative response in Hydrilla verticillata(L.f.)Royle plants[J].Ecotoxicology&environmental safety,2010,73(2):189-195.
[32]WANG C,ZHANG S H,WANG P F,et al.Metabolic adaptations to ammonia-induced oxidative stress in leaves of the submerged macrophyte vallisneria natans(lour)hara[J].Aquatic toxicology,2008,87(2):88-98.
[33]李迪,赵温,谭启玲,等.伊乐藻对水体磷浓度的生理响应[J].环境科学与技术,2018,41(S1):24-30.
[2]黄峰,李勇,潘继征,等.冬春季富营养化滆湖中沉水植被重建及净化效果[J].环境科技,2010.23(4):13-16.
[3]王宝山.逆境植物生物学[M].北京:高等教育出版社,2010:4-10.
[4]吴寒.活性氧在植物体内的作用及其清除体制[J].广东蚕业,2018,52(3):18-20.
[5]胡韧,林秋奇,张小兰,等.Cr3+,Cr6+及其复合污染对狐尾藻的毒害作用[J].生态科学,2003,22(4):327-331.
[6]简敏菲,汪斯琛,余厚平,等.Cd2+,Cu2+胁迫对黑藻(Hydrilla verticillata)的生长及光合荧光特性的影响[J].生态学报,2016(3):1 719-1 727.
[7]施国新,解凯彬,杜开和,等.Cr6+,As3+污染对黑藻叶细胞伤害的超微结构研究[J].南京师大学报(自然科学版),2001,24(4):93-97.
[8]陈辉,施国新,徐勤松,等.Cr6+对菹草叶绿素荧光参数、抗氧化系统和超微结构的胁迫影响[J].植物研究,2009,29(5):559-564.
[9]张嘉桐,关颖慧,司莉青,等.Pb2+、Cd2+复合胁迫对桑树光合作用的影响[J].北京林业大学学报,2018,40(4):16-23.
[10]潘秋红,施国新,徐勤松,等.Cu2+对菱叶片生理指标及超微结构的毒理学效应分析[J].植物科学学报,2009,27(5):527-532.
[11]吕念泽,高桂青,吕顺华,等.Cu2+胁迫对马来眼子菜光合荧光特性的影响[J].南昌工程学院学报,2018,37(4):31-34.
[12]ASSCHE F V H.Clijsters,Effects of metals on enzyme activity in plants[J].Plant cell&environment,2010,13(3):195-206.
[13]崔静,袁旭音,刘泉,等.环境水体中纳米氧化铜对金鱼藻的毒性效应研究[J].农业环境科学学报,2013(5):910-915.
[14]NEL A,XIA T,LUTZ M,et al.Toxic potential of materials at the nanolevel[J].Science,2006,311(5 761):622-627.
[15]MISHRA S,SRIVASTAVA S,TRIPATHI R D,et al.Lead detoxification by coontail(Ceratophyllum demersum L)involves induction of phytochelatins and antioxidant system in response to its accumulation[J].Chemosphere,2006,65(6):1 027-1 039.
[16]程飞,张颖,方元平,等.金鱼藻抗氧化系统对镉胁迫的响应[J].安徽农业科学,2012,40(23):11 791-11 793.
[17]高艳.重金属Pb2+胁迫对轮叶黑藻毒性效应研究[D].重庆:西南大学,2017.
[18]李佳华,慕君玲,郭红岩,等.邻苯二甲酸二丁酯污染对苦草生理生化指标的影响[J].环境化学,2005.24(1):32-36.
[19]宋志慧,张元园,柳宁,等.有机农药百草枯对金鱼藻的生理生化参数的毒性作用[J].环保科技,2016,22(1):10-13.
[20]赵秀侠,侯冠军,李静,等.磺胺对苦草(Vallisneria natans(Lour.)Hara)生理生长及细胞超微结构的影响[J].安徽大学学报(自科版),2017,41(2):92-99.
[21]高海荣,林清,陆延婷,等.有机溶剂胁迫下苦草生理指标的变化[J].广西师范学院学报(自然科学版),2006,23(4):40-44.
[22]肖能文,张宇,李卫兵,等.1,2,4-三氯苯对金鱼藻氧化压力及生理特性的影响[J].环境科学与技术,2017(1):49-54.
[23]胡一鸿,王梦龙,袁盛建,等.戊二醛胁迫对黑藻光合作用及抗氧化酶活性的影响[J].农业环境科学学报,2013,32(6):1 143-1 149.
[24]高亚岳,周俊,陈志宁,等.滆湖富营养化进程中沉水植被的演替及重建设想[J].环境科技,2008.21(4):21-24.
[25]王珺,顾宇飞,纪东成,等.富营养条件下不同形态氮对轮叶黑藻(Hydrilla verticillata)的生理影响[J].环境科学研究,2006,19(1):71-74.
[26]朱增银,陈灿,贾海霞,等.不同氮源对苦草(Vallisneria natans)生长及生理指标的影响[J].植物资源与环境学报,2006,15(4):48-51.
[27]高镜清,燕启社,黄五星,等.富营养化水体中铵态氮对金鱼藻生长的影响[J].长江流域资源与环境,2011,20(5):611-616.
[28]马剑敏,靳同霞,李今,等.伊乐藻、苦草和菹草对磷急性胁迫的响应[J].水生生物学报,2008,32(3):408-412.
[29]金相灿,郭俊秀,许秋瑾,等.不同质量浓度氨氮对轮叶黑藻和穗花狐尾藻抗氧化酶系统的影响[J].生态环境学报,2008,17(1):1-5.
[30]NIMPTSCH J,PFLUGMACHER S.Ammonia triggers the promotion of oxidative stress in the aquatic macrophyte Myriophyllum mattogrossense[J].Chemosphere,2007,66(4):708-714.
[31]WANG C,ZHANG S H,WANG P F,et al.Effects of ammonium on the antioxidative response in Hydrilla verticillata(L.f.)Royle plants[J].Ecotoxicology&environmental safety,2010,73(2):189-195.
[32]WANG C,ZHANG S H,WANG P F,et al.Metabolic adaptations to ammonia-induced oxidative stress in leaves of the submerged macrophyte vallisneria natans(lour)hara[J].Aquatic toxicology,2008,87(2):88-98.
[33]李迪,赵温,谭启玲,等.伊乐藻对水体磷浓度的生理响应[J].环境科学与技术,2018,41(S1):24-30.
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