不同浓度镉胁迫下6种草本植物的耐性及富集特征的比较

doi:10.11733/j.issn.1007-0435.2021.06.017

草地学报 ›› 2021, Vol. 29 ›› Issue (6): 1265-1276.DOI: 10.11733/j.issn.1007-0435.2021.06.017

不同浓度镉胁迫下6种草本植物的耐性及富集特征的比较

张杨杨¹, 李希铭¹, 高鹏², 宋桂龙¹

1. 北京林业大学草坪研究所, 北京 100083;
2. 北京林业大学林木育种国家工程实验室, 北京 100083

收稿日期:2020-11-19 修回日期:2021-01-14 出版日期:2021-06-15 发布日期:2021-07-05
通讯作者: 宋桂龙,E-mail:syihan@163.com
作者简介:张杨杨(1993-)，女，山东聊城人，硕士研究生，主要从事重金属植物修复研究，E-mail：15501090703@163.com
基金资助:
裸露创面植被快速修复喷播基材改良技术研究与集成（2019YFF0303202-01）；中央高校基本科研业务费专项资金（PTYX202150）资助

Comparison of Tolerance and Enrichment Characteristic for Six Herbaceous Plant under Different Levels Cd Stress

ZHANG Yang-yang¹, LI Xi-ming¹, GAO Peng², SONG Gui-long¹

1. Institute of Turfgrass Science, Beijing Forestry University, Beijing 100083, China;
2. National Engineering Laboratory for Tree Breeding, Beijing Forestry University, Beijing 100083, China

Received:2020-11-19 Revised:2021-01-14 Online:2021-06-15 Published:2021-07-05

摘要/Abstract

摘要： 为了筛选并评价耐镉（Cadmium，Cd）性较高的优势植物物种，本研究以紫花苜蓿（Medicago sativa）、百脉根（Lotus corniculatus）、多变小冠花（Coronilla varia）、披碱草（Elymus dahuricum）、细茎冰草（Agropyron trachycaulum）和野牛草（Buchloe dactyloides）为试验材料，采用盆栽模拟试验进行不同浓度Cd胁迫处理，以0 mg·kg^-1Cd处理浓度为对照（CK），探究多梯度Cd胁迫对植物的富集特征及根系形态变化的影响，并评估其Cd耐性阈值。结果表明：不同浓度Cd胁迫下6种草本植物的生物量及根系形态均表现出“低促高抑”现象；不同物种对Cd的耐受能力不同，紫花苜蓿和多变小冠花对Cd的耐性阈值在50 mg·kg^-1到100 mg·kg^-1之间，百脉根、披碱草、细茎冰草和野牛草对Cd的耐性阈值在100 mg·kg^-1以上；在100 mg·kg^-1Cd胁迫下百脉根、披碱草和野牛草，可通过植物萃取的方式应用于重金属污染土壤的治理修复；细茎冰草在100 mg·kg^-1Cd胁迫下，根系富集系数仍然大于1，且根系生物量、耐性系数具有随着Cd胁迫加重不断上升的趋势，是较理想的修复重金属污染土壤的高耐高抗型草本植物材料。

关键词: 镉胁迫, 富集特征, 根形态特征, 耐性阈值

Abstract: In order to screen and evaluate plant species with higher cadmium (Cd) tolerance,in this study,Medicago sativa,Lotus corniculatus,Coronilla varia,Elymus dahuricum,Agropyron trachycaulum,and Buchloe dactyloides,six common herbaceous plant species were selected. We set 0 mg·kg^-1 Cd treatment concentration as control (CK),and potted simulation experiments of different concentrations of cadmium were used to explore the effects of Cd stress on plant enrichment characteristics and root morphological changes,and to evaluate their Cd tolerance threshold. The main findings were as follows:the biomass and root morphology of the six herbaceous plants under different concentrations of Cd showed a phenomenon of "promotion at low Cd concentration and suppression at high Cd concentration". Different species had different tolerance to Cd. The tolerance threshold of Cd was between 50 mg·kg^-1 and 100 mg·kg^-1 for Medicago sativa and Coronilla varia,and the tolerance threshold of Lotus corniculatus,Elymus dahuricum,Agropyron trachycaulum and Buchloe dactyloides to Cd was above 100 mg·kg^-1. Under the stress of 100 mg·kg^-1 Cd,Lotus corniculatus,Elymus dahuricum and Buchloe dactyloides could be used for restoration of heavy metal contaminated soil by means of plant extraction. When Agropyron trachycaulum was treated at 100 mg·kg^-1 Cd,the root enrichment coefficient was still greater than1,and the root biomass and tolerance coefficient had a trend of increasing with the increasd of Cd stress. Agropyron trachycaulum is an ideal herb material with high Cd tolerance and high resistance for repairing heavy metal contaminated soil.

Key words: Cadmium stress, Enrichment Characteristic, Accumulation Characteristic, Tolerance threshold

中图分类号:

S618.81

张杨杨, 李希铭, 高鹏, 宋桂龙. 不同浓度镉胁迫下6种草本植物的耐性及富集特征的比较[J]. 草地学报, 2021, 29(6): 1265-1276.

ZHANG Yang-yang, LI Xi-ming, GAO Peng, SONG Gui-long. Comparison of Tolerance and Enrichment Characteristic for Six Herbaceous Plant under Different Levels Cd Stress[J]. Acta Agrestia Sinica, 2021, 29(6): 1265-1276.

0
/ / 推荐

导出引用管理器 EndNote|Ris|BibTeX

链接本文: https://manu40.magtech.com.cn/Jweb_cdxb/CN/10.11733/j.issn.1007-0435.2021.06.017

https://manu40.magtech.com.cn/Jweb_cdxb/CN/Y2021/V29/I6/1265

参考文献

[1] Yang Q Q,Li Z Y,Lu X N,et al. A review of soil heavy metal pollution from industrial and agricultural regions in China:Pollution and risk assessment[J]. Science of The Total Environment,2018,642:690-700
[2] 陈能场,郑煜基,何晓峰,等.《全国土壤污染状况调查公报》探析[J]. 农业环境科学学报,2017,36(9):1689-1692
[3] 陈树兰,许晨阳,耿增超,等. 不同配比复合材料对农田镉污染土壤的修复效果[J]. 环境科学,2019,40(12):5531-5539
[4] 邓新,温璐璐,迟鑫姝. 镉对人体健康危害及防治研究进展[J]. 中国医疗前沿,2010,5(10):4-5
[5] 赵首萍,叶雪珠,张棋,等. 重金属污染土壤几种生物修复方式比较[J]. 中国农学通报,2020,36(20):83-91
[6] 曾键尧,李娜,王妍,等. 植物修复治理镉污染及其镉富集分子机制研究[J]. 资源节约与环保,2019(11):102-103
[7] Fu J T,Yu D M,Chen X,et al. Recent research progress in geochemical properties and restoration of heavy metals in contaminated soil by phytoremediation[J]. Journal of Mountain Science,2019,16(9):2079-2095
[8] Afsheen Z,Zulfiqar A S,Tong W B,et al. Assessment of sunflower germplasm for phytoremediation of lead-polluted soil and production of seed oil and seed meal for human and animal consumption[J]. Journal of Environmental Sciences,2020,87(1):24-38
[9] 张云霞,宋波,宾娟,等. 超富集植物藿香蓟(Ageratum conyzoides L.)对镉污染农田的修复潜力[J]. 环境科学,2019,40(5):2453-2459
[10] Hazrat A,Ezzat K,Muhammad A S. Phytoremediation of heavy metals-Concepts and applications[J]. Chemosphere,2013,91(7):869-881
[11] 李希铭,李金波,宋桂龙,等. 35份草本植物镉吸收与富集特征比较[J]. 草业科学,2018,35(4):760-770
[12] 王洪斌,张煜坤,张大才. 青藏苔草形态特征及生物量分配沿水分梯度的变化[J]. 草地学报,2021,29(3):522-530
[13] 薛博晗,李娜,宋桂龙,等. 外源柠檬酸、苹果酸和草酸对披碱草镉耐受及富集的影响[J]. 草业学报,2018,27(6):128-136
[14] 王沛琦,高梅,刘旭云,等. 5个蓖麻品种对土壤中镉富集的差异[J]. 核农学报,2021,35(6):1433-1439
[15] 李金波,李诗刚,宋桂龙,等. 砷胁迫对黑麦草根系形态及养分吸收的影响[J]. 草业科学,2018,35(6):1385-1392
[16] María L F,Sabrine H,Sarra H,et al. Specific mechanisms of tolerance to copper and cadmium are compromised by a limited concentration of glutathione in alfalfa plants[J]. Plant Science,2015,233:165-173
[17] Wang X J,Song Y,Ma Y H,et al. Screening of Cd tolerant genotypes and isolation of metallothionein genes in alfalfa (Medicago sativa L.)[J]. Environmental Pollution,2011,159(12):3627-3633
[18] 彭昌琴. 尾穗苋对镉胁迫的生理生化响应及镉富集规律的探究[D]. 贵阳:贵州大学,2019,12-24
[19] 丁晓辉,任丽萍,张春荣,等. Cd²⁺胁迫对紫花苜蓿叶绿素和可溶性糖含量的影响[J]. 华北农学报,2007(S1):64-66
[20] 龙应霞,刘荣鹏,刘洋. 镉胁迫对水稻幼苗生长的影响[J]. 农业与技术,2020,40(18):15-17
[21] 秦世玉,郭文英,程锦,等. 不同浓度镉胁迫对冬小麦根系生长的影响[J]. 河南农业大学学报,2019,53(4):519-524,530
[22] Huang B,Xin J,Dai H,et al. Root morphological responses of three hot pepper cultivars to Cd exposure and their correlations with Cd accumulation[J]. Environmental Science and Pollution Research,2014,22(2):1151-1159
[23] 贾月慧,韩莹琰,刘杰,等. 生菜对镉胁迫的生理响应及体内镉的累积分布[J]. 农业环境科学学报,2018,37(8):1610-1618
[24] Umed Ali. 不同pH对水稻幼苗镉积累的影响[D]. 北京:中国农业科学院,2019,54-67
[25] 王宝媛,濮阳雪华,宋桂龙,等. 20个高羊茅品种镉耐性评价及富集特征[J]. 草地学报,2017,25(1):107-114
[26] 云娜,石凤翎,王晓龙,等. EMS诱变对蒙农红豆草出苗和幼苗生长的影响[J]. 草地学报,2014,36(3):5-9
[27] Zhuang P,McBride Murray B,Xia H P,et al. Health risk from heavy metals via consumption of food crops in the vicinity of Dabaoshan mine,South China[J]. The Science of the total environment,2009,407(5):1551-1561
[28] Liu H W,Wang H Y,Zhang Y,et al. Comparison of heavy metal accumulation and cadmium phytoextraction rates among ten leading tobacco (Nicotiana tabacum L.) cultivars in China[J]. International Journal of Phytoremediation,2019,21(7):699-706
[29] 贾茵,刘才磊,兰晓悦,等. 外源水杨酸对镉胁迫下小报春幼苗生长及生理特性的影响[J]. 草地学报,2020,28(5):1346-1354
[30] Laporte M A,Sterckeman T,Dauguet S,et al. Variability in cadmium and zinc shoot concentration in 14 cultivars of sunflower (Helianthus annuus L.) as related to metal uptake and partitioning[J]. Environmental & Experimental Botany,2015,10:45-53
[31] 刘霄霏,李惠英,陈良,等. 外源硒对镉胁迫下黑麦草生长和生理的影响[J]. 草地学报,2020,28(01):72-79
[32] Gonzalez A,Gil-Díaz M,Lobo M C. Response of Two Barley Cultivars to Increasing Concentrations of Cadmium or Chromium in Soil During the Growing Period[J]. Science Letter,2015,163(1-2):235-243
[33] 史静,潘根兴,夏运生,等. 镉胁迫对两品种水稻生长及抗氧化酶系统的影响[J]. 生态环境学报,2013,22(5):832-837
[34] Xiong J,Lu H,Lu K,et al. Cadmium decreases crown root number by decreasing endogenous nitric oxide,which is indispensable for crown root primordia initiation in rice seedlings[J]. Planta,2009,230(4):599-610
[35] Lux A,Martinka M,Vaculík,et al. Root responses to cadmium in the rhizosphere:a review[J]. Journal of Experimental Botany,2011,62(1):21-37
[36] 邵小杰,杨洪强. 氯化钙对镉胁迫下葡萄根系细胞质膜ATPase和自由基的影响[C]//中国植物学会.2009中国植物学会植物细胞生物学学术年会论文集.成都:中国植物学会,2009:1441-1447
[37] 于永昂,王润豪,胡海燕,等. 小麦对镉胁迫的生理响应及体内镉的积累分布[J]. 贵州农业科学,2019,47(9):14-19
[38] Huang B F,Xin J L,Dai H W,et al. Root morphological responses of three hot pepper cultivars to Cd exposure and their correlations with Cd accumulation[J]. Environmental Science and Pollution Research,2015,22(2):1151-1159
[39] 聂胜委,黄绍敏,张水清,等. 重金属胁迫对小麦生长的影响及阈值研究[J]. 华北农学报,2012,27(6):118-124
[40] Laporte M A,Sterckeman T,Dauguet S,et al. Variability in cadmium and zinc shoot concentration in 14 cultivars of sunflower (Helianthus annuus L.) as related to metal uptake and partitioning[J]. Environmental & Experimental Botany,2015,10:45-53
[41] Laporte M A,Denaix L,Pagès L,et al. Longitudinal variation in cadmium influx in intact first order lateral roots of sunflower (Helianthus annuus. L)[J]. Plant & Soil,2013,372(1-2):581-595

不同浓度镉胁迫下6种草本植物的耐性及富集特征的比较

Comparison of Tolerance and Enrichment Characteristic for Six Herbaceous Plant under Different Levels Cd Stress

PDF

可视化

摘要/Abstract

引用本文

使用本文

参考文献

相关文章 11

编辑推荐

Metrics

本文评价

[1]	朱瑞婷, 牛奎举, 张娣君, 杨阳, 宋云, 马晖玲. 外源2,4-表油菜素内酯对镉胁迫下草地早熟禾叶绿素代谢的影响[J]. 草地学报, 2021, 29(4): 635-643.
[2]	孔海明, 李开源, 高双红, 孙娈姿. 根瘤菌对紫花苜蓿生物修复镉污染功能的影响[J]. 草地学报, 2021, 29(12): 2763-2768.
[3]	刘霄霏, 李惠英, 陈良, 徐倩, 胡龙兴, 王慧彬, 马向明. 外源硒对镉胁迫下黑麦草生长和生理的影响[J]. 草地学报, 2020, 28(1): 72-79.
[4]	鲜靖苹, 王勇, 马晖玲. 外源NO缓解草地早熟禾镉胁迫的转录组分析[J]. 草地学报, 2019, 27(6): 1467-1476.
[5]	鲜靖苹, 王勇, 马晖玲. 一氧化氮信号途径参与草地早熟禾耐镉机制的研究[J]. 草地学报, 2019, 27(6): 1577-1586.
[6]	邵将, 陈瑶, 刘大林, 陈鸣晖, 吴亚, 黄玉婷. 硅对镉胁迫下不同狼尾草属牧草生理代谢的影响[J]. 草地学报, 2018, 26(5): 1223-1228.
[7]	见妮, 刘璐, 屈佳欣, 李凯, 王佺珍. 超声波对镉胁迫鸭茅和冰草种子萌发的影响[J]. 草地学报, 2018, 26(2): 427-434.
[8]	王宝媛, 濮阳雪华, 宋桂龙, 周述琼, 赵克奇, 蒋凯. 20个高羊茅品种镉耐性评价及富集特征[J]. 草地学报, 2017, 25(1): 107-114.
[9]	施宠, 王纯利, 黄长福, 安沙舟. 镉胁迫对野燕麦幼苗生长及其生理特性的影响[J]. 草地学报, 2015, 23(3): 526-532.
[10]	黄耿磊, 黄冬芬, 刘国道, 郇恒福. 镉胁迫对3种柱花草生长及植株镉积累和分配的影响[J]. , 2011, 19(1): 97-101.
[11]	陈平, 余土元, 叶丽敏. 镉胁迫对弯叶画眉草幼苗生长和生理特性的影响[J]. , 2002, 10(3): 212-216.