土壤铅胁迫对地被竹出笋成竹的影响研究
|
摘要
以6种地被竹(菲黄竹、菲白竹、铺地竹、美丽箬竹、白纹椎谷笹和狭叶倭竹)为材料,设计3个土壤铅浓度处理(0、300、1 500 mg·kg~(-1)),研究土壤铅胁迫对地被竹出笋成竹数量和新竹抗逆生理特性的影响,并采用隶属函数法对地被竹出笋成竹期的土壤铅耐受性进行综合评价。结果表明:(1)土壤铅胁迫对地被竹笋期节律的影响主要出现在出笋盛期(4～5月),发笋数的降低会导致多数竹种退笋率下降,以稳定新竹数量,只有菲白竹、白纹椎谷笹、狭叶倭竹的新竹数在高浓度土壤铅胁迫下显著低于CK,降幅分别为15.87%、23.64%和31.25%。(2)土壤铅胁迫会普遍引起地被竹新竹超氧阴离子和丙二醛含量的增加,在高浓度铅胁迫下铺地竹中二者含量最低(9.96μg·g~(-1)、0.016μmol·g~(-1)),狭叶倭竹的超氧阴离子含量最高(15.99μg·g~(-1)),菲黄竹的丙二醛含量最高(0.021μmol·g~(-1))。(3)与其余4个竹种不同,在土壤铅胁迫下白纹椎谷笹和狭叶倭竹不能显著积累游离脯氨酸,细胞渗透调节作用弱。(4)6种地被竹在出笋成竹期对高浓度土壤铅的耐受性排序为:美丽箬竹(0.79)>铺地竹(0.75)>菲白竹(0.70)>狭叶倭竹(0.49)>白纹椎谷笹(0.39)>菲黄竹(0.38),其中美丽箬竹、铺地竹和菲白竹出笋成竹数量正常,且具有较强的抗逆生理特性,具有在高浓度土壤铅污染地区应用的潜力。
The objective was to examine the shoot-emergence of dwarf bamboos in Pb-contained soil. In this regard, we selceted six kinds of dwarf bamboo [namely, Sasa auricoma(Mitford) E.G.Camus, Sasa fortunei(Van Houtte) Fiori, Sasa argenteostriata(Regel) E.G.Camus, Indocalamus decorus Q. H. Dai, Sasaella glabra(Nakai) f. albo-striata Muroi, Shibataea lanceifolia C. H. Hu] and treated with three doses Pb concentrations(0, 300, 1 500 mg·kg~(-1)) to investigate the quantity of shoot emergence and physiological stress resistance characteristics when exposed to soil Pb stress. Results showed that:(1) the effects of soil Pb stress on the shoot period rhythm of dwarf bamboo mainly in the shoot-emergence period(April to May). The shoot emergence numbers of most bamboo species decreased accompany with degenerated shoot rate, so that to make it possible to stabilize the numbers of new bamboo shoot. Only that in Sasa fortunei, Sasaella glabra and Shibataea lanceifolia emerged a significantly lower tendency on numbers of new shoot under high concentration soil Pb stress when compared with CK, which decreases by 15.87%, 23.64% and 31.25%, respectively.(2) Soil Pb stress induced a surge in contents of ■ and MDA of generally in new shoots. Both of them were presented with the lowest-contained in Sasa argenteostriata(9.96 μg·g~(-1), 0.016 μmol·g~(-1)), while the highest-contained of ■ and MDA appeared in Shibataea lanceifolia(15.99 μg·g~(-1)) and Sasa auricoma(0.021 μmol·g~(-1)), respectively.(3) As a result of being not capable of accumulating enormous free proline, which caused a weak osmotic regulation in Sasaella glabra and Shibataea lanceifolia, when compared with the other 4 species.(4) The tolerance of six dwarf bamboos to high concentration Pb soil during shoot-emergence period was ranked as follows: Indocalamus decorus(0.79)> Sasa argenteostriata(0.75)>Sasa fortunei(0.70)>Shibataea lanceifolia(0.49)>Sasaella glabra(0.39) >Sasa auricoma(0.38). Above all, Indocalamus decorus, Sasa argenteostriata and Sasa fortunei innately possessed a better physiological characteristics of stress resistance, along with a common regular quantity of new shoots, was considered to retain the superiority of remediation in high concentration of Pb-contained soil.
The objective was to examine the shoot-emergence of dwarf bamboos in Pb-contained soil. In this regard, we selceted six kinds of dwarf bamboo [namely, Sasa auricoma(Mitford) E.G.Camus, Sasa fortunei(Van Houtte) Fiori, Sasa argenteostriata(Regel) E.G.Camus, Indocalamus decorus Q. H. Dai, Sasaella glabra(Nakai) f. albo-striata Muroi, Shibataea lanceifolia C. H. Hu] and treated with three doses Pb concentrations(0, 300, 1 500 mg·kg~(-1)) to investigate the quantity of shoot emergence and physiological stress resistance characteristics when exposed to soil Pb stress. Results showed that:(1) the effects of soil Pb stress on the shoot period rhythm of dwarf bamboo mainly in the shoot-emergence period(April to May). The shoot emergence numbers of most bamboo species decreased accompany with degenerated shoot rate, so that to make it possible to stabilize the numbers of new bamboo shoot. Only that in Sasa fortunei, Sasaella glabra and Shibataea lanceifolia emerged a significantly lower tendency on numbers of new shoot under high concentration soil Pb stress when compared with CK, which decreases by 15.87%, 23.64% and 31.25%, respectively.(2) Soil Pb stress induced a surge in contents of ■ and MDA of generally in new shoots. Both of them were presented with the lowest-contained in Sasa argenteostriata(9.96 μg·g~(-1), 0.016 μmol·g~(-1)), while the highest-contained of ■ and MDA appeared in Shibataea lanceifolia(15.99 μg·g~(-1)) and Sasa auricoma(0.021 μmol·g~(-1)), respectively.(3) As a result of being not capable of accumulating enormous free proline, which caused a weak osmotic regulation in Sasaella glabra and Shibataea lanceifolia, when compared with the other 4 species.(4) The tolerance of six dwarf bamboos to high concentration Pb soil during shoot-emergence period was ranked as follows: Indocalamus decorus(0.79)> Sasa argenteostriata(0.75)>Sasa fortunei(0.70)>Shibataea lanceifolia(0.49)>Sasaella glabra(0.39) >Sasa auricoma(0.38). Above all, Indocalamus decorus, Sasa argenteostriata and Sasa fortunei innately possessed a better physiological characteristics of stress resistance, along with a common regular quantity of new shoots, was considered to retain the superiority of remediation in high concentration of Pb-contained soil.
引文
[1] 段德超,于明革,施积炎.植物对铅的吸收、转运、累积和解毒机制研究进展[J].应用生态学报,2014,25(1):287-296.DUAN D C,YU M G,SHI J Y.Research advances in uptake,translocation,accumulation and detoxification of Pb in plants[J].Chinese Journal of Applied Ecology,2014,25(1):287-296.
[2] 黄迪,杨燕群,肖选虎,等.土壤重金属污染治理修复剂技术[J].现代化工,2018,38(11):39-43.HUANG D,YANG Y Q,XIAO X H,et al.Advances of remediation agents in repairing heavy metals contaminated soil[J].Modern Chemical Industry,2018,38(11):39-43.
[3] 任海彦,胡健,胡毅飞.重金属污染土壤植物修复研究现状与展望[J].江苏农业科学,2019,(1):5-11.REN H Y,HU J,HU Y F.Research progress and prospect of phytoremediation of heavy metal contaminated soils[J].Jiangsu Agricultural Sciences,2019,(1):5-11.
[4] OZYIGIT I I,DOGAN I.Plant-Microbe interactions in phytoremediation soil remediation and plants-chapter9[J].Soil Remediation & Plants,2015,54(7):255-285.
[5] 邢艳帅,乔冬梅,朱桂芬,等.土壤重金属污染及植物修复技术研究进展[J].中国农学通报,2014,30(17):208-214.XING Y S,QIAO D M,ZHU G F,et al.Research progress of heavy pollution in soil and phytoremediation technology[J].Chinese Agricultural Science Bulletin,2014,30(17):208-214.
[6] 黄化刚,李廷轩,杨肖娥,等.植物对铅胁迫的耐性及其解毒机制研究进展[J].应用生态学报,2009,20(3):696-704.HUANG H G,LI T X,YANG X E,et al.Research advances in plant lead tolerance and detoxification mechanism[J].Chinese Journal of Applied Ecology,2009,20(3):696-704.
[7] 杜俊杰,周启星,李娜,等.超积累植物修复重金属污染土壤的研究进展[J].贵州农业科学,2018,46(5):64-72.DU J J,ZHOU Q X,LI N,et al.Progress in remediation of heavy metal contaminated soil by hyperaccumulator[J].Guizhou Agricultural Sciences,2018,46(5):64-72.
[8] REEVES R D,BAKER A J M.Studies on metal uptake by plants from serpentine and non-serpentine populations of Thlaspi geosingense Halacsy[J].New Phtol,1984,(98):191-204.
[9] BAKER A J M,BROOKS R R.Terrestrial higher plants which hyperaccumulate metallic elements—a review of their distribution[J].Ecology and Phytochemistry Biorecovery,1989,1:81-126.
[10] 马建玲,黄金龙,朱雪梅,等.普陀山苔草对铅锌的富集特性及生理响应研究[J].四川农业大学学报,2018,36(4):463-471.MA J L,HUANG J L,ZHU X M,et al.Lead and zinc accumulation characteristics and physiological responses of Carex putuoshanensis sp.[J].Journal of Sichuan Agricultural University,2018,36(4):463-471.
[11] 罗于洋,赵磊,王树森.铅超富集植物密毛白莲蒿对铅的富集特性研究[J].西北林学院学报,2010,25(5):37-40.LUO Y Y,ZHAO L,WANG S S.Absorption characteristics of Artemisia sacrorum var.messerschmidtiana to lead[J].Journal of Northwest Forestry University,2010,25(5):37-40.
[12] 吴双桃,吴晓芙,胡曰利,等.铅锌冶炼厂土壤污染及重金属富集植物的研究[J].生态环境,2004,(2):156-157,160.WU S T,WU X F,HU Y L,et al.Study on soil pollution and heavy metal-enriched plants in lead and zinc smelters[J].Ecological and Environment,2004,(2):156-157,160.
[13] 侯晓龙,陈加松,刘爱琴,等.Pb胁迫对金丝草和柳叶箬生长及富Pb特征的影响[J].福建农林大学学报(自然科学版),2012,41(3):286-290.HOU X L,CHEN J S,LIU A Q,et al.Growth response and accumulation characteristics of Pogonatherum crinitum and Lsache globosa under the stress of lead[J].Journal of Fujian Agriculture and Forestry University (Natural Science Edition) ,2012,41(3):286-290.
[14] 胡鹏杰,李柱,钟道旭,等.我国土壤重金属污染植物吸取修复研究进展[J].植物生理学报,2014,50(5):577-584.HU P J,LI Z,ZHONG D X,et al.Research progress on the phytoextraction of heavy metal contaminated soils in China[J].Plant Physiology Journal,2014,50(5):577-584.
[15] 郑钧,吴仁武,史琰,等.竹类植物的主要环境效应研究进展[J].浙江农林大学学报,2017,34(2):374-380.ZHENG J,WU R W,SHI Y,et al.Research progress on environmental effects of bamboo:a review[J].Journal of Zhejiang A & F University,2017,34(2):374-380.
[16] 陈俊任,柳丹,吴家森,等.重金属胁迫对毛竹种子萌发及其富集效应的影响[J].生态学报,2014,34(22):6 501-6 509.CHEN J R,LIU D,WU J S,et al.Seed germination and metal accumulation of Moso bamboo (Phyllostachys pubescens) under heavy metal exposure[J].Acta Ecologica Sinica,2014,34(22):6 501-6 509.
[17] 李松,柳丹,吴家森,等.雷竹对铅胁迫的生理响应及其修复效率研究[J].水土保持学报,2014,28(2):175-179.LI S,LIU D,WU J S,et al.Effects of lead stress on physiological response and phytoremediation efficiency of Phyllostachys praecox[J].Journal of Soil and Water Conservation,2014,28(2):175-179.
[18] 李娟,高健.黄条金刚竹、阔叶箬竹和菲白竹在干旱、冻害和重金属Pb胁迫下光合生理响应研究[J].竹子研究汇刊,2016,35(1):22-29.LI J,GAO J.Photosynthetic and physiological responses to drought,cold and Pb Stresses in Pleioblastus kongosanensi,Indocalamus latifolius and Sasa fortunei[J].Journal of Bamboo Research,2016,35(1):22-29.
[19] 张志坚,高健,蔡春菊,等.铅胁迫下菲白竹的矿质营养吸收和分配[J].林业科学,2011,47(1):153-157.ZHANG Z J,GAO J,CAI C J,et al.Absorption and distribution of mineral nutrients in Pleioblastus fortunei under lead stress[J].Scientia Silvae Sinicae,2011,47(1):153-157.
[20] 王兵,曹帮华,蔡春菊.重金属胁迫对2种地被竹抗氧化酶与脂质过氧化的影响[J].世界竹藤通讯,2010,8(4):15-19.WANG B,CAO B H,CAI C J.Effect of heavy metal stress on antioxidative enzymes and lipid peroxidation in two dwarf bamboos (Sasa auricoma and Arundinaria fortunei) [J].World Bamboo and Rattan,2010,8(4):15-19.
[21] JIANG M Y,LIU S L,LI Y F,et al.EDTA-facilitated toxic tolerance,absorption and translocation and phytoremediation of lead by dwarf bamboos[J].Ecotoxicology and Environmental Safety,2019,170:502-512.
[22] 李娟,高健,牟少华.不同Pb浓度胁迫下4种地被竹的叶绿素荧光响应和转运积累研究[J].世界竹藤通讯,2014,12(3):5-11.LI J,GAO J,MOU S H.A study of chlorophyll fluorescence response and its mechanism of transportation and accumulation in four dwarf bamboo species under Pb (NO3)2 stress at different concentrations[J].World Bamboo and Rattan,2014,12(3):5-11.
[23] 史军义,易同培,马丽莎,等.园林地被竹及其开发利用[J].四川林业科技,2006,(6):95-100.SHI J Y,YI T P,MA L S,et al.Study on dwarf bamboos and their application in gardening[J].Journal of Sichuan Forestry Science and Technology,2006,(6):95-100.
[24] 熊庆娥.植物生理学实验教程[M].成都:四川科学技术出版社,2003.
[25] 李合生.植物生理生化实验原理和技术[M].北京:高等教出版社,2003.
[26] 康芙蓉,赵丽丽,徐凯璐,等.钙盐胁迫对6个燕麦品种种子萌发特性的影响[J].黑龙江畜牧兽医,2018,(1):163-167.KANG F R,ZHAO L L,XU K L,et al.The effect of calcium salt stress on seed germination characteristics of six oat varieties[J].Heilongjiang Animal Science and Veterinary Medicine,2018,(1):163-167.
[27] 刘建新,欧晓彬,刘秀丽,等.过氧化氢缓解裸燕麦幼苗低温胁迫的主成分和隶属函数分析[J].植物研究,2018,38(5):748-756.LIU J X,OU X B,LIU X L,et al.Principal component and subordinate function of the alleviating effects of hydrogen peroxide (H2O2) on low-temperature stress in naked Oat (Avena nuda) seedlings[J].Bulletin of Botanical Research,2018,38(5):748-756.
[28] 韩航,陈雪娇,陈顺钰,等.类芦对铅胁迫的生理响应[J].森林与环境学报,2017,37(4):398-404.HAN H,CHEN X J,CHEN S Y,et al.Physiology response of Neyraudia reynaudiana under Pb stress[J].Journal of Forest and Environment,2017,37(4):398-404.
[29] 郭晖,郭孝茹,柴光东,等.重金属短期胁迫下5种观赏植物积累特性与生理抗性研究[J].西南林业大学学报(自然科学),2017,37(4):28-34.GUO H,GUO X R,CAI G D,et al.Soil heavy metals stress on the accumulation characteristics and physiological resistance of 5 ornamental plants in the short-term conditions[J].Journal of Southwest Forestry University (Natural Sciences),2017,37(4):28-34.
[30] 金亚荣,王国娟,黄晓光,等.铅污染对山皂角生长生理的影响[J].安徽农业科学,2010,38(16):8 775-8 776,8 803.JIN Y R,WANG G J,HUANG X G,et al.Effect of lead contamination on the growth and physiology of Japanese Honeylocust[J].Journal of Anhui Agricultural Sciences,2010,38(16):8 775-8 776,8 803.
[31] 肖志华,张义贤,张喜文,等.外源铅、铜胁迫对不同基因型谷子幼苗生理生态特性的影响[J].生态学报,2012,32(3):889-897.XIAO Z H,ZHANG Y X,ZHANG X W,et al.Effects of exogenous Pb and cu stress on eco-physiological characteristics on foxtail millet seedlings of different genotypes[J].Acta Ecologica Sinica,2012,32(3):889-897.
[32] 张大鹏,蔡春菊,范少辉,等.重金属Pb2+和Cd2+对毛竹种子萌发及幼苗早期生长的影响[J].林业科学研究,2012,25(4):500-504.ZHANG D P,CAI C J,FAN S H,et al.Effects of Pb2+,Cd2+ on germination and seeding early growth of Moso bamboo (Phyllostachys edulis) seed[J].Forest Research,2012,25(4):500-504.
[33] 陶贵耘,傅鹰,周明兵.竹类植物快速生长的机理研究进展[J].农业生物技术学报,2018,26(5):871-887.TAO G Y,FU Y,ZHOU M B.Advances in studies on molecular mechanisms of rapid growth of bamboo species[J].Journal of Agricultural Biotechnology,2018,26(5):871-887.
[34] 刘爱荣,张远兵,张雪平,等.铅污染对高羊茅生长、无机离子分布和铅积累量的影响[J].核农学报,2009,23(1):128-133,144.LIU A R,ZHANG Y B,ZHANG X P,et al.Effect of lead pollution on growth,inorganicion distribution and Pb2+ accumulationn in Festuca arundinacea[J].Journal of Nuclear Agricultural Sciences,2009,23(1):128-133,144.
[35] 林树燕,丁雨龙,王吉子.4种地被观赏竹的笋期生长特性比较[J].林业科技开发,2007,(1):51-53.LIN S Y,DING Y L,WANG J Z.Comparasion on the growth characteristics of four ornamental bamboo species[J].China Forestry Science and Technology,2007,(1):51-53.
[36] 方伟,林新春,洪平,等.苦竹生长发育规律研究[J].浙江农林大学学报,2005,22(1):1-5.FANG W,LIN X C,HONG P,et al.Study on the growth and development law of Pleioblastus amarus[J].Journal of Zhejiang Forestry College,2005,22(1):1-5.
[37] 曲良谱.金明竹在泰州地区发笋退笋规律研究[J].竹子学报,2017,36(4):37-40.QU L P.The shooting and decay of Phyllostachys bambusoides f.castillonis in Taizhou area[J].Journal of Bamboo Research,2017,36(4):37-40.
[38] 郑绍鑫,蒋林,滕维超,等.刨花润楠对硝酸铅胁迫的生长和生理响应机制[J].林业科技开发,2015,29(3):25-30.ZHENG S X,JIANG L,TENG W C,et al.Growth and physiological mechanism of Machilus pauhoi seedlings in response to lead nitrate stress[J].China Forestry Science and Technology,2015,29(3):25-30.
[39] 黄亚萍,俎丽红,沈广爽,等.铅胁迫对蜀葵重金属积累及抗氧化酶活性的影响[J].农业环境科学学报,2017,36(9):1 746-1 752.HUANG Y P,ZU L H,SHEN G S,et al.Effects of lead stress on accumulation ability and antioxidant enzyme activities of Althaea rosea Cavan.[J].Journal of Agro-Environment Science,2017,36(9):1 746-1 752.
[40] 黄化刚,李廷轩,杨肖娥,等.植物对铅胁迫的耐性及其解毒机制研究进展[J].应用生态学报,2009,20(3):696-704.HUANG H G,LI T X,YANG X E,et al.Research advances in plant lead tolerance and detoxification mechanism[J].Chinese Journal of Applied Ecology,2009,20(3):696-704.
[41] 毕诗畦,穆立蔷.‘鲁赫’刺蔷薇对铅、镉及其混合胁迫的生理响应[J].西北林学院学报,2018,33(6):47-55.BI S Q,MU L Q.Physiological response of Rosa acicularis ‘Luhe’to lead,cadmium and mixed stresses[J].Journal of Northwest Forestry University,2018,33(6):47-55.
[42] 方志红,董宽虎.NaCl胁迫对碱蒿可溶性糖和可溶性蛋白含量的影响[J].中国农学通报,2010,26(16):147-149.FANG Z H,DONG K H.Effects of NaCl stress on soluble protein contents and soluble carbohydrate contents of Artemisia cnethifolia[J].Chinese Agricultural Science Bulletin,2010,26(16):147-149.
[43] 张家洋.重金属铅镉短期胁迫对蓬莱蕉生理生化指标的影响[J].水土保持学报,2016,30(2):340-345.ZHANG J Y.The effect of Pb and Cd on physiological and biochemical indexes of Monstera deliciosa Liebm.in the short-term conditions[J].Journal of Soil and Water Conservation,2016,30(2):340-345.
[44] 高飞霞,邹天森,张金良,等.中国城市土壤环境铅含量分析[J].城市环境与城市生态,2015,28(2):1-5.GAO F X,ZOU T S,ZHANG J L,et al.Lead concentration in urban soils of China[J].Urban Environment & Urban Ecology,2015,28(2):1-5.
[45] 张园,耿春女,蔡超.铅暴露对人体健康风险评价的模型综述[J].环境化学,2013,32(6):943-951.ZHANG Y,GENG C N,CAI C.Review on models for lead exposure on human health risk assessment[J].Environmental Chemistry,2013,32(6):943-951.
[46] 吴迪,杨秀珍,李存雄,等.贵州典型铅锌矿区水稻土壤和水稻中重金属含量及健康风险评价[J].农业环境科学学报,2013,32(10):1 992-1 998.WU D,YANG X Z,LI C X,et al.Concentrations and health risk assessments of heavy metals in soil and rice in zinc-lead mining area in Guizhou Province,China[J].Journal of Agro-Environment Science,2013,32(10):1 992-1 998.
[47] 苏耀明,陈志良,雷国建,等.多金属矿区土壤重金属垂向污染特征及风险评估[J].生态环境学报,2016,25(1):130-134.SU Y M,CHEN Z L,LEI G J,et al.Vertical pollution characteristic and ecological risk assessment of heavy metal of soil profiles in polymetallic ore mine[J].Ecology and Environmental Sciences,2016,25(1):130-134.
[2] 黄迪,杨燕群,肖选虎,等.土壤重金属污染治理修复剂技术[J].现代化工,2018,38(11):39-43.HUANG D,YANG Y Q,XIAO X H,et al.Advances of remediation agents in repairing heavy metals contaminated soil[J].Modern Chemical Industry,2018,38(11):39-43.
[3] 任海彦,胡健,胡毅飞.重金属污染土壤植物修复研究现状与展望[J].江苏农业科学,2019,(1):5-11.REN H Y,HU J,HU Y F.Research progress and prospect of phytoremediation of heavy metal contaminated soils[J].Jiangsu Agricultural Sciences,2019,(1):5-11.
[4] OZYIGIT I I,DOGAN I.Plant-Microbe interactions in phytoremediation soil remediation and plants-chapter9[J].Soil Remediation & Plants,2015,54(7):255-285.
[5] 邢艳帅,乔冬梅,朱桂芬,等.土壤重金属污染及植物修复技术研究进展[J].中国农学通报,2014,30(17):208-214.XING Y S,QIAO D M,ZHU G F,et al.Research progress of heavy pollution in soil and phytoremediation technology[J].Chinese Agricultural Science Bulletin,2014,30(17):208-214.
[6] 黄化刚,李廷轩,杨肖娥,等.植物对铅胁迫的耐性及其解毒机制研究进展[J].应用生态学报,2009,20(3):696-704.HUANG H G,LI T X,YANG X E,et al.Research advances in plant lead tolerance and detoxification mechanism[J].Chinese Journal of Applied Ecology,2009,20(3):696-704.
[7] 杜俊杰,周启星,李娜,等.超积累植物修复重金属污染土壤的研究进展[J].贵州农业科学,2018,46(5):64-72.DU J J,ZHOU Q X,LI N,et al.Progress in remediation of heavy metal contaminated soil by hyperaccumulator[J].Guizhou Agricultural Sciences,2018,46(5):64-72.
[8] REEVES R D,BAKER A J M.Studies on metal uptake by plants from serpentine and non-serpentine populations of Thlaspi geosingense Halacsy[J].New Phtol,1984,(98):191-204.
[9] BAKER A J M,BROOKS R R.Terrestrial higher plants which hyperaccumulate metallic elements—a review of their distribution[J].Ecology and Phytochemistry Biorecovery,1989,1:81-126.
[10] 马建玲,黄金龙,朱雪梅,等.普陀山苔草对铅锌的富集特性及生理响应研究[J].四川农业大学学报,2018,36(4):463-471.MA J L,HUANG J L,ZHU X M,et al.Lead and zinc accumulation characteristics and physiological responses of Carex putuoshanensis sp.[J].Journal of Sichuan Agricultural University,2018,36(4):463-471.
[11] 罗于洋,赵磊,王树森.铅超富集植物密毛白莲蒿对铅的富集特性研究[J].西北林学院学报,2010,25(5):37-40.LUO Y Y,ZHAO L,WANG S S.Absorption characteristics of Artemisia sacrorum var.messerschmidtiana to lead[J].Journal of Northwest Forestry University,2010,25(5):37-40.
[12] 吴双桃,吴晓芙,胡曰利,等.铅锌冶炼厂土壤污染及重金属富集植物的研究[J].生态环境,2004,(2):156-157,160.WU S T,WU X F,HU Y L,et al.Study on soil pollution and heavy metal-enriched plants in lead and zinc smelters[J].Ecological and Environment,2004,(2):156-157,160.
[13] 侯晓龙,陈加松,刘爱琴,等.Pb胁迫对金丝草和柳叶箬生长及富Pb特征的影响[J].福建农林大学学报(自然科学版),2012,41(3):286-290.HOU X L,CHEN J S,LIU A Q,et al.Growth response and accumulation characteristics of Pogonatherum crinitum and Lsache globosa under the stress of lead[J].Journal of Fujian Agriculture and Forestry University (Natural Science Edition) ,2012,41(3):286-290.
[14] 胡鹏杰,李柱,钟道旭,等.我国土壤重金属污染植物吸取修复研究进展[J].植物生理学报,2014,50(5):577-584.HU P J,LI Z,ZHONG D X,et al.Research progress on the phytoextraction of heavy metal contaminated soils in China[J].Plant Physiology Journal,2014,50(5):577-584.
[15] 郑钧,吴仁武,史琰,等.竹类植物的主要环境效应研究进展[J].浙江农林大学学报,2017,34(2):374-380.ZHENG J,WU R W,SHI Y,et al.Research progress on environmental effects of bamboo:a review[J].Journal of Zhejiang A & F University,2017,34(2):374-380.
[16] 陈俊任,柳丹,吴家森,等.重金属胁迫对毛竹种子萌发及其富集效应的影响[J].生态学报,2014,34(22):6 501-6 509.CHEN J R,LIU D,WU J S,et al.Seed germination and metal accumulation of Moso bamboo (Phyllostachys pubescens) under heavy metal exposure[J].Acta Ecologica Sinica,2014,34(22):6 501-6 509.
[17] 李松,柳丹,吴家森,等.雷竹对铅胁迫的生理响应及其修复效率研究[J].水土保持学报,2014,28(2):175-179.LI S,LIU D,WU J S,et al.Effects of lead stress on physiological response and phytoremediation efficiency of Phyllostachys praecox[J].Journal of Soil and Water Conservation,2014,28(2):175-179.
[18] 李娟,高健.黄条金刚竹、阔叶箬竹和菲白竹在干旱、冻害和重金属Pb胁迫下光合生理响应研究[J].竹子研究汇刊,2016,35(1):22-29.LI J,GAO J.Photosynthetic and physiological responses to drought,cold and Pb Stresses in Pleioblastus kongosanensi,Indocalamus latifolius and Sasa fortunei[J].Journal of Bamboo Research,2016,35(1):22-29.
[19] 张志坚,高健,蔡春菊,等.铅胁迫下菲白竹的矿质营养吸收和分配[J].林业科学,2011,47(1):153-157.ZHANG Z J,GAO J,CAI C J,et al.Absorption and distribution of mineral nutrients in Pleioblastus fortunei under lead stress[J].Scientia Silvae Sinicae,2011,47(1):153-157.
[20] 王兵,曹帮华,蔡春菊.重金属胁迫对2种地被竹抗氧化酶与脂质过氧化的影响[J].世界竹藤通讯,2010,8(4):15-19.WANG B,CAO B H,CAI C J.Effect of heavy metal stress on antioxidative enzymes and lipid peroxidation in two dwarf bamboos (Sasa auricoma and Arundinaria fortunei) [J].World Bamboo and Rattan,2010,8(4):15-19.
[21] JIANG M Y,LIU S L,LI Y F,et al.EDTA-facilitated toxic tolerance,absorption and translocation and phytoremediation of lead by dwarf bamboos[J].Ecotoxicology and Environmental Safety,2019,170:502-512.
[22] 李娟,高健,牟少华.不同Pb浓度胁迫下4种地被竹的叶绿素荧光响应和转运积累研究[J].世界竹藤通讯,2014,12(3):5-11.LI J,GAO J,MOU S H.A study of chlorophyll fluorescence response and its mechanism of transportation and accumulation in four dwarf bamboo species under Pb (NO3)2 stress at different concentrations[J].World Bamboo and Rattan,2014,12(3):5-11.
[23] 史军义,易同培,马丽莎,等.园林地被竹及其开发利用[J].四川林业科技,2006,(6):95-100.SHI J Y,YI T P,MA L S,et al.Study on dwarf bamboos and their application in gardening[J].Journal of Sichuan Forestry Science and Technology,2006,(6):95-100.
[24] 熊庆娥.植物生理学实验教程[M].成都:四川科学技术出版社,2003.
[25] 李合生.植物生理生化实验原理和技术[M].北京:高等教出版社,2003.
[26] 康芙蓉,赵丽丽,徐凯璐,等.钙盐胁迫对6个燕麦品种种子萌发特性的影响[J].黑龙江畜牧兽医,2018,(1):163-167.KANG F R,ZHAO L L,XU K L,et al.The effect of calcium salt stress on seed germination characteristics of six oat varieties[J].Heilongjiang Animal Science and Veterinary Medicine,2018,(1):163-167.
[27] 刘建新,欧晓彬,刘秀丽,等.过氧化氢缓解裸燕麦幼苗低温胁迫的主成分和隶属函数分析[J].植物研究,2018,38(5):748-756.LIU J X,OU X B,LIU X L,et al.Principal component and subordinate function of the alleviating effects of hydrogen peroxide (H2O2) on low-temperature stress in naked Oat (Avena nuda) seedlings[J].Bulletin of Botanical Research,2018,38(5):748-756.
[28] 韩航,陈雪娇,陈顺钰,等.类芦对铅胁迫的生理响应[J].森林与环境学报,2017,37(4):398-404.HAN H,CHEN X J,CHEN S Y,et al.Physiology response of Neyraudia reynaudiana under Pb stress[J].Journal of Forest and Environment,2017,37(4):398-404.
[29] 郭晖,郭孝茹,柴光东,等.重金属短期胁迫下5种观赏植物积累特性与生理抗性研究[J].西南林业大学学报(自然科学),2017,37(4):28-34.GUO H,GUO X R,CAI G D,et al.Soil heavy metals stress on the accumulation characteristics and physiological resistance of 5 ornamental plants in the short-term conditions[J].Journal of Southwest Forestry University (Natural Sciences),2017,37(4):28-34.
[30] 金亚荣,王国娟,黄晓光,等.铅污染对山皂角生长生理的影响[J].安徽农业科学,2010,38(16):8 775-8 776,8 803.JIN Y R,WANG G J,HUANG X G,et al.Effect of lead contamination on the growth and physiology of Japanese Honeylocust[J].Journal of Anhui Agricultural Sciences,2010,38(16):8 775-8 776,8 803.
[31] 肖志华,张义贤,张喜文,等.外源铅、铜胁迫对不同基因型谷子幼苗生理生态特性的影响[J].生态学报,2012,32(3):889-897.XIAO Z H,ZHANG Y X,ZHANG X W,et al.Effects of exogenous Pb and cu stress on eco-physiological characteristics on foxtail millet seedlings of different genotypes[J].Acta Ecologica Sinica,2012,32(3):889-897.
[32] 张大鹏,蔡春菊,范少辉,等.重金属Pb2+和Cd2+对毛竹种子萌发及幼苗早期生长的影响[J].林业科学研究,2012,25(4):500-504.ZHANG D P,CAI C J,FAN S H,et al.Effects of Pb2+,Cd2+ on germination and seeding early growth of Moso bamboo (Phyllostachys edulis) seed[J].Forest Research,2012,25(4):500-504.
[33] 陶贵耘,傅鹰,周明兵.竹类植物快速生长的机理研究进展[J].农业生物技术学报,2018,26(5):871-887.TAO G Y,FU Y,ZHOU M B.Advances in studies on molecular mechanisms of rapid growth of bamboo species[J].Journal of Agricultural Biotechnology,2018,26(5):871-887.
[34] 刘爱荣,张远兵,张雪平,等.铅污染对高羊茅生长、无机离子分布和铅积累量的影响[J].核农学报,2009,23(1):128-133,144.LIU A R,ZHANG Y B,ZHANG X P,et al.Effect of lead pollution on growth,inorganicion distribution and Pb2+ accumulationn in Festuca arundinacea[J].Journal of Nuclear Agricultural Sciences,2009,23(1):128-133,144.
[35] 林树燕,丁雨龙,王吉子.4种地被观赏竹的笋期生长特性比较[J].林业科技开发,2007,(1):51-53.LIN S Y,DING Y L,WANG J Z.Comparasion on the growth characteristics of four ornamental bamboo species[J].China Forestry Science and Technology,2007,(1):51-53.
[36] 方伟,林新春,洪平,等.苦竹生长发育规律研究[J].浙江农林大学学报,2005,22(1):1-5.FANG W,LIN X C,HONG P,et al.Study on the growth and development law of Pleioblastus amarus[J].Journal of Zhejiang Forestry College,2005,22(1):1-5.
[37] 曲良谱.金明竹在泰州地区发笋退笋规律研究[J].竹子学报,2017,36(4):37-40.QU L P.The shooting and decay of Phyllostachys bambusoides f.castillonis in Taizhou area[J].Journal of Bamboo Research,2017,36(4):37-40.
[38] 郑绍鑫,蒋林,滕维超,等.刨花润楠对硝酸铅胁迫的生长和生理响应机制[J].林业科技开发,2015,29(3):25-30.ZHENG S X,JIANG L,TENG W C,et al.Growth and physiological mechanism of Machilus pauhoi seedlings in response to lead nitrate stress[J].China Forestry Science and Technology,2015,29(3):25-30.
[39] 黄亚萍,俎丽红,沈广爽,等.铅胁迫对蜀葵重金属积累及抗氧化酶活性的影响[J].农业环境科学学报,2017,36(9):1 746-1 752.HUANG Y P,ZU L H,SHEN G S,et al.Effects of lead stress on accumulation ability and antioxidant enzyme activities of Althaea rosea Cavan.[J].Journal of Agro-Environment Science,2017,36(9):1 746-1 752.
[40] 黄化刚,李廷轩,杨肖娥,等.植物对铅胁迫的耐性及其解毒机制研究进展[J].应用生态学报,2009,20(3):696-704.HUANG H G,LI T X,YANG X E,et al.Research advances in plant lead tolerance and detoxification mechanism[J].Chinese Journal of Applied Ecology,2009,20(3):696-704.
[41] 毕诗畦,穆立蔷.‘鲁赫’刺蔷薇对铅、镉及其混合胁迫的生理响应[J].西北林学院学报,2018,33(6):47-55.BI S Q,MU L Q.Physiological response of Rosa acicularis ‘Luhe’to lead,cadmium and mixed stresses[J].Journal of Northwest Forestry University,2018,33(6):47-55.
[42] 方志红,董宽虎.NaCl胁迫对碱蒿可溶性糖和可溶性蛋白含量的影响[J].中国农学通报,2010,26(16):147-149.FANG Z H,DONG K H.Effects of NaCl stress on soluble protein contents and soluble carbohydrate contents of Artemisia cnethifolia[J].Chinese Agricultural Science Bulletin,2010,26(16):147-149.
[43] 张家洋.重金属铅镉短期胁迫对蓬莱蕉生理生化指标的影响[J].水土保持学报,2016,30(2):340-345.ZHANG J Y.The effect of Pb and Cd on physiological and biochemical indexes of Monstera deliciosa Liebm.in the short-term conditions[J].Journal of Soil and Water Conservation,2016,30(2):340-345.
[44] 高飞霞,邹天森,张金良,等.中国城市土壤环境铅含量分析[J].城市环境与城市生态,2015,28(2):1-5.GAO F X,ZOU T S,ZHANG J L,et al.Lead concentration in urban soils of China[J].Urban Environment & Urban Ecology,2015,28(2):1-5.
[45] 张园,耿春女,蔡超.铅暴露对人体健康风险评价的模型综述[J].环境化学,2013,32(6):943-951.ZHANG Y,GENG C N,CAI C.Review on models for lead exposure on human health risk assessment[J].Environmental Chemistry,2013,32(6):943-951.
[46] 吴迪,杨秀珍,李存雄,等.贵州典型铅锌矿区水稻土壤和水稻中重金属含量及健康风险评价[J].农业环境科学学报,2013,32(10):1 992-1 998.WU D,YANG X Z,LI C X,et al.Concentrations and health risk assessments of heavy metals in soil and rice in zinc-lead mining area in Guizhou Province,China[J].Journal of Agro-Environment Science,2013,32(10):1 992-1 998.
[47] 苏耀明,陈志良,雷国建,等.多金属矿区土壤重金属垂向污染特征及风险评估[J].生态环境学报,2016,25(1):130-134.SU Y M,CHEN Z L,LEI G J,et al.Vertical pollution characteristic and ecological risk assessment of heavy metal of soil profiles in polymetallic ore mine[J].Ecology and Environmental Sciences,2016,25(1):130-134.