不同胁迫条件下入侵植物土荆芥(Chenopodium ambrosioides L.)与藜(Chenopodium album L.)的生长及生理比较研究
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摘要
土荆芥(Chenopodium ambrosioides L.)为藜科藜属一年生或多年生草本植物。有强烈芳香味,通常生长在河岸、公路边、荒地及农田边,是一种入侵植物,常与一年蓬、黄花蒿等植物混生在一起形成杂草群落。目前全国各地均有分布。但各地其情况又有不同,有些地方(如长江流域一带)土荆芥已入侵成为优势种,阻碍了本土植物的生长繁殖,并给当地农业造成了一定危害。彻底根除土荆芥,控制其危害和扩散蔓延已成为这些地方的农业要求。目前对入侵植物土荆芥的研究仅限于其化学成分、药用价值、种子贮藏与萌发特性等方面;对其入侵机理方面的研究基本还是一片空白。因此,以同属本土近缘种藜作对比,研究其在逆境条件下的生理适应机制对于了解入侵机理、提出有效的防治对策等具有重要的理论与实践价值,也能为其它入侵植物的研究和防除提供参考。
     藜(Chenopodium album L.)是跟土荆芥亲缘关系较近的一种难以除掉的本土杂草,为藜科藜属一年生草本植物,常见于路旁、荒地及田间。本文以藜作为实验对照,在盐、人工模拟酸雨、重金属镉等胁迫因子以及模拟不同程度光照强度的条件下,从形态、生物量分配、抗氧化酶活性、渗透调节物质(脯氨酸、可溶性糖)等方面研究了土荆芥的生长和生理适应机制,以期为入侵植物入侵机制的认识、防治对策的制定等提供一定的理论与实践依据。研究结果表明:
     1)人工模拟盐胁迫和碱胁迫下,土荆芥的生长受到了抑制,且处理浓度越高抑制作用越明显。随NaCl盐胁迫程度增加,土荆芥各形态指标数据呈明显下降趋势,根长表现出先增后降的趋势,根重比、根冠比在各处理水平均高于对照;丙二醛含量在低浓度NaCl处理时变化较为平缓,高浓度处理时呈上升趋势,抗氧化酶除SOD活性变化较小,CAT、POD的活性均呈现出先增后降的趋势。Na2C03碱胁迫时,土荆芥各形态指标的变化趋势和抗氧化酶的活性变化趋势与NaCl处理时相似,但根重比和根冠比低于对照,丙二醛含量呈上升趋势,SOD、CAT和POD均具有不同的酶活最高点。两种盐处理对比表明Na2C03胁迫对土荆芥造成的危害更大,土荆芥耐受NaCl胁迫能力强于Na2C03胁迫。近缘植物藜的生长也同样受到了抑制,且SOD、CAT、POD分别具有与土荆芥不同的活性变化以及酶活最高点,但其根重比、根冠比、抗氧化酶活性的变化程度均低于土荆芥,说明土荆芥可能比藜更能耐受盐、碱胁迫。另外,土荆芥脯氨酸在NaCl处理时得到了积累,而藜脯氨酸在低浓度Na2C03处理时有所积累,且仅低浓度的盐、碱胁迫能提高土荆芥和藜可溶性糖的含量,表明脯氨酸和可溶性糖的渗透调节作用具有一定的局限性。
     2)人工模拟酸雨胁迫下,土荆芥的形态变化较小,各酸雨处理水平除根长、叶片数、分枝数存在显著性差异,其它形态指标变化不大。土荆芥根受到的影响较为明显,pH3.5-4.59水平酸雨均促进了土荆芥根的生长,但根重比和根冠比随模拟酸雨pH值的减小显著下降,叶重比有上升趋势。随模拟酸雨胁迫程度的加深,土荆芥丙二醛含量增加,SOD活性呈小幅度上升趋势,CAT活性呈下降趋势,POD活性则表现为先升后降呈单峰曲线型变化。酸雨对藜的形态变化影响也较小,除pH2.0酸雨外,其它水平酸雨均促进了藜根的生长。与土荆芥不同的是,pH2.0处理组藜的根重比和根冠比高于对照,其原因不明。除SOD活性变化与土荆芥一致,藜CAT和POD活性分别具有与土荆芥不同的变化趋势,且在酸雨pH4.59时,三种酶的活性均高于对照,表明藜对当地pH4.59的酸雨已具有一定的适应性,但强酸雨条件下土荆芥SOD、CAT、POD活性变化仍高于藜,说明土荆芥比藜具有更高的抗逆能力。酸雨处理下土荆芥脯氨酸含量变化不大,酸度较小的模拟酸雨能有效促进藜脯氨酸的积累,但二者可溶性糖的合成均受到了抑制。
     3)人工模拟重金属镉胁迫下,土荆芥和藜生长受到了严重的抑制,形态和生物量的分配发生了较大变化。土荆芥的茎高、叶片数、分枝数存在明显下降趋势,根长、根重比、根冠比表现出先增后降的趋势。藜除叶长外,各形态指标均存在显著性差异,其根长也有先升后降的趋势,但其根重比、根冠比变化不大。随镉胁迫程度的增加,土荆芥和藜MDA含量呈现先增后降的趋势,高浓度镉处理下MDA含量降低说明镉胁迫已超出细胞抵御的最大能力。土荆芥和藜SOD、POD活性变化不稳定,CAT活性呈下降趋势,表明酶系统的功能已失调或无法再激活。低浓度镉胁迫能有效促进二者脯氨酸的积累,土荆芥更为明显:二者可溶性糖含量随镉浓度增加显著升高,此时藜可溶性糖的积累更为明显。镉浓度为10mg·mL-1时,土荆芥的根长、根重比、根冠比、脯氨酸增加幅度达到最大,对镉胁迫表现出了一定的抗性。
     4)在人工模拟不同光照强度(遮阴)条件下,土荆芥和藜生长受到了严重的影响,三层遮阴处理的植株其生长已完全受到抑制。二者各形态指标数据随光照强度的降低均呈下降趋势。土荆芥根重比和根冠比有先增后降的趋势,在一层遮阴处其根重比和根冠比达到最大,二层遮阴处即低于对照。藜根重比、根冠比随光照强度降低而减小。二层遮阴时,土荆芥和藜MDA含量开始下降,表明二者受到严重伤害,已超出细胞抵御的最大能力。除对SOD活性影响较小,弱光抑制了土荆芥和藜CAT、POD的活性。光照强度的降低促进了土荆芥脯氨酸和可溶性糖的积累,但藜渗透调节物质积累具有一定的局限性,藜脯氨酸含量呈现出先降后升的趋势,可溶性糖含量呈现出先增后降的趋势,前者在光照强度极低的情况下才大量积累有可能是脯氨酸生成失调。一层遮阴处理时土荆芥根重比和根冠比达到最大,对光照强度降低仍作出了一些反应,表现出了一定的抗性。
     综上结果表明,土荆芥具有一定的表型可塑性,会改变自身的形态和生理特征来响应环境的变化;对逆境具有较强的抵抗能力,比藜具有更高的生理调节水平,证明了入侵植物的优势在于其本身具有较强的适应性和忍耐性,使其能快速适应新环境。在逆境条件下,土荆芥各指标的变化并不同步,其抗性很难用单一的指标来衡量,在某个时期某个指标占了主导地位。鉴于土荆芥具有抗低浓度的盐、镉能力,将其用作盐化草甸建群草种以及镉污染土壤的修复具有重要的现实意义。
Chenopodium ambrosioides L. is the annual or perennial plant of Chenopod. It is an invasive plant, having strong aroma and usually growing on the riverside, road, badlands or cropland, and always forms ruderal community with Erigeron annuus L.and Artemisia annua L.It can be seen all the country, but in some places (like drainage area of the Changjiang River), it has become preponderant species, disturbing growth and propagation of the native plants, and bringing harms to native agriculture. Eradicating C.ambrosioides L.thoroughly and controlling its damage and spread has turned into these places'agricultural requests. At present, the research of C.ambrosioides L. is still nothingness, only having researches in its chemic components and officinal value, and starting pilot study on the seed storage and germination. So for managing this invasive plant effectively, it's meaning to investigate the adaptability of growth and physiology in adversity, and the result also can provide new theoretical method and practical experience for mechanism of biological invasion.
     Chenopodium album L. is a sort of weed which is difficult to dispose of, and is the relatives plant to C.ambrosioides L..It is the annual plant of Chenopod, always growing on the roadside, badlands or field. The experiment is taken to research adaptability of growth and physiology of C. ambrosioides L. in comparison with C.album L.n the way of morphological indicators, biomass allocation, antioxidant enzymes activity, and osmotic adjustment substances (proline and soluble sugar), under simulating the salt and alkali stress, acid rain, heavy metal-Cadmium stress, and different light intensity (overshadowing). The results of researches showed that:
     Under the simulated salt and alkali stress, the growth of C.ambrosioides L.was inhibited, and this restraining effection was obvious along with extent of intimidation. Under NaCl stress, morphology indicators datas of C.ambrosioides L.decreased, root length increased at first and then decreased, root weight ratio and crown-root ratio were higher than comparison; malondialdehyde content changed gently in low concentrations and gained in high concentrations; SOD activity had changed little, POD and CAT activity had increased firstly and then decreased. Under Na2CO3 stress, trend of morphology indicators and antioxidant enzymes activity of C.ambrosioides L. was similar to that under NaCl stress, but root weight ratio and crown-root ratio were lower than comparison, malondialdehyde content increased all through, and SOD、CAT and POD activity also had different changes. A result between the two stresses showed Na2CO3 stress did more harm to C. ambrosioides L. than NaCl stress. The growth of C.album L.was also inhibited, and its'SOD、CAT and POD activity had different diversifications with C. ambrosioides L. The root weight ratio、crown-root ratio and antioxidant enzymes activity of C.album L. was lower than that of C.ambrosioides L., indicating that C.ambrosioides L. had stronger tolerance to the salt and alkaline stress than C.album L..In addition, the proline of C. ambrosioides L. accumulated under NaCl stress, proline of C.album L.got together in low concentrations of Na2CO3 stress, and soluble sugar of these two species all gained in low concentrations of salt and alkali stress, indicating that the osmotic adjustment function of proline and soluble sugar had definite limitation.
     Under simulated acid rain, it had small influence on morphology of C. ambrosioides L.,except root length and the number of laminae and ramification had markedly otherness, other morphology indicators changed little. It seriously affected C. ambrosioides L.'s root, promoted its growth from pH 3.5 to 4.59,but root weight ratio and crown-root ratio decreased clearly as simulated acid rain's pH values declined, besides leaves ratio increased slightly. As stress of acid rain increased, malondialdehyde content increased, SOD activity gained a little, CAT activity declined, and POD activity increased at first and then decreased. Acid rain also had little effect on morphology of C.album L..Except acidity of pH 2.0, other acidity promoted its root growth. Root weight ratio and crown-root ratio of C.album L. were higher than comparison at pH 2.0, but the reason was unaware. In addition, activity of CAT and POD had different trends with C. ambrosioides L., but SOD activity was accordant with it. At pH 4.59, antioxidant enzymes activity was higher than comparison, indicating that C.album L. had been adapted to the local acid rain, whereas, under strong acid rain, the antioxidant enzymes activity of C. ambrosioides L. was higher than that of C. album L., showing C. ambrosioides L. was more tolerant than C.album L. under adversity. Proline of C. ambrosioides L. was influenced a little, but that of C. album L. was gained under weak acid rain, and soluble sugar synthesization of these two species was all restrained.
     Under simulated heavy metal-Cadmium stress, the growth of C. ambrosioides L. and C.album L.were inhibited seriously, and their morphology and biomass allocation had obvious changes. Stem height and the number of laminae and ramification of C. ambrosioides L. had dropped, and its root length, root weight ratio and crown-root ratio had increased at first and then decreased. Except leaf length, other morphology indicators of C.album L. also had markedly otherness, the root length also had the trend like C. ambrosioides L., but root weight ratio and crown-root ratio changed little. Their malondialdehyde content still increased firstly and then decreased, reducement of malondialdehyde content under high concentrations of Cd treatment showing Cd stress had exceeded cells'resist capability farthest. Their SOD and POD activity was unstable, CAT activity was degressive, indicating the functiong of enzyme system was maladjusted or unactivated. Low concentrations of Cd can effectively promoted accumulation of proline, specially for C. ambrosioides L., and also availably added soluble sugar, yet specially for C.album L.. At the 10 mg-L'concentration of Cd, root length, root weight ratio, crown-root ratio and proline of C. ambrosioides L. had come to the most, figuring that C. ambrosioides L.had put up some resistance for Cd stress.
     Under the simulated different light intensity (overshadowing), the growth of C. ambrosioides L. and C.album L. were inhibited seriously, at the overshadowing of three layers stress, their growth had been completely repressive. Their morphology indicators datas decreased. Root weight ratio and crown-root ratio of C. ambrosioides L. were increased firstly and then decreased, higher than comparison at one layer's overshadowing, but lower than comparison at two layers'overshadowing. By contraries, root weight ratio and crown-root ratio of C.album L. dropped all through. At the overshadowing of two layers stress, their malondialdehyde content declined, showing stress had exceeded cells'resist capability farthest. Low light restrained CAT and POD activity, except SOD activity. Low light intensity promoted proline and soluble sugar's accumulation of C. ambrosioides L., but accumulation of osmotic adjustment substance of C.album L. had some limitation, its proline content had decreased at first and then increased, soluble sugar content had the opposite trend, guessing synthesization of proline had been maladjusted. At the overshadowing of one layer, root weight ratio and crown-root ratio of C. ambrosioides L. had come to the most, showing certain resistance to the decrease of light intensity.
     According to these results above, C. ambrosioides L. has some phenotypic plasticity,and can change configuration and physiology in answer to variety of environment; has stronger resistance to adversity and higher physiological adjustment level than C.album L., testifying that invasive plant can quickly adapt to new environment due to its predominances of adaptability and endurance. In adversity, indexes of C. ambrosioides L. are nonsynchronous, the resistance can't measure with single index, and some index is more principal than others in some phase. Since C. ambrosioides L. has the ability of resisting salt and Cd in low concentrations, it's meaning that making use of it as grass of saline and restoration of Cd-contaminative soil.
引文
[1]达良俊,田志慧,王晨曦,王娟.从生态学角度对生物入侵的思考[J].自然杂志,2007,29(3):152-158
    [2]顾忠盈,吴新华,杨光,陈建东.我国外来生物入侵现状及防范对策[J].江苏农业科学,2006,6:418-422
    [3]李梅,聂呈荣,李锐,陈碧云.外来植物入侵机制研究进展[J].广东农业科学,2005,(2):93-97
    [4]王金亭,杨敏一.我国入侵植物的研究概况[J].聊城大学学报(自然科学版),2008,21(1):70-74
    [5]王真辉.外来植物入侵群落理论假说[J].热带农业科学,2007,27(1):67-73
    [6]Hierro Jose L,Maron John L, Callaway Ragan M. A biogeographical approach to plant invasions:the importance of studying exotics in their introduced and native range. Journal of Ecology,2005,93(1):5-15
    [7]吴锦荣,彭少麟.化感-外来入侵植物的“Novel Weapons”[J].生态学报,2005,25(11):3093-3098
    [8]Rice E L. Allelopathy. New York:Academic Press,1984
    [9]朱世新,覃海宁,陈艺林.中国菊科植物外来种概述[J].广西植物,2005,25(1):69-76
    [10]钟永德,李迈和,Norbert Kraeuchi.地球暖化促进植物迁移与入侵[J].地理研究,2004,23(3):347-357
    [11]李博,徐炳声,陈家宽.从上海外来杂草区系剖析植物入侵的一般特征[J].生物多样性,2001,9(4):446-457
    [12]张乃群,庞振凌,庞发虎,杜敏华,李运贤.中国外来植物的入侵、危害及防除研究[J].南阳师范学院学报,2006,5(3):59-63
    [13]陈元胜.外来物种入侵对生物多样性的影响及对策[J].安徽农业科学,2007,35(5):1445-1446
    [14]屈冉,李俊生.外来物种入侵的负面生态效应及防治策略[J].生态安全,2007,7:31-33
    [15]江贵波,曾任森.外来入侵植物的危害及防治[J].安徽农业科学,2006,34(2):273-274,280
    [16]张晓梅.从薇甘菊入侵德宏浅析对外来物种侵入的防范[J].云南农业科技,2007,1:56-57
    [17]王振华,朱子平,徐家文.我国生物入侵之现状及对策[J].湖北植保,2004,3:29-30
    [18]严玉平,王晓鸿.生物入侵对中国农业的危害及对策[J].江西农业学报,2007,19(2):90-94
    [19]徐海根,强胜,韩正敏,等.中国外来入侵物种的分布与传入途径分析[J].生物多样性,2004,12(6):626-638.
    [20]傅俊范.中国外来有害生物入侵现状及控制对策[J].沈阳农业大学学报,2005-06,36(4):387-391.
    [21]迟德富,严善春.关于外来植物的几点思考[J].世界林业研究.2007,20(4):12-19
    [22]吴晓雯,罗晶,陈家宽,李博.中国外来入侵植物的分布格局及其与环境因子和人类活动的关系[J].植物生态学报,2006,30(4):576-584
    [23]重庆缙云山植物志[M].重庆:西南师范大学出版社
    [24]中国植物志编辑委员会[M].中国植物志.北京:科学出版社
    [25]王云,唐书国,陈巧敏,周国庆,周国峰,王文龙,彭友林.土荆芥种子贮藏与萌发特性的研究[J].草业科学,2008,25(2):103-107
    [26]杨丽,邓洪平,韩敏,崔亚琼.入侵植物对重庆生态环境的风险分析评价[J].西南师范大学学报(自然科学版),2008,33(1):72-77
    [27]史冬燕.模拟酸雨对藜种子萌发过程的影响[J].安徽农业科学,2008,36(16):6651-6652
    [28]孙存华,李扬,杜伟,金会丽,王东升,陈湘玲,徐新娜.干旱胁迫下藜的光合特性研究[J].植物研究,2007,27(6):715-720
    [29]潘瑞炽.植物生理学[M].北京:高等教育出版社.2004
    [30]吕金印,赵晖,冯万健.NaCl胁迫对甜高粱幼苗保护酶活性等生理特性的影响[J].干旱地区农业研究,2008,26(6):133-137
    [31]Floyd RA,Nagy I.Formation of long-lived hydroxyl free radical adducts of proline and hydroxyproline in a Fenton reaction [J].Biochim Biophys Acta,1984,790(1):94
    [32]赵江涛,李晓峰,李航,徐睿忞.可溶性糖在高等植物代谢调节中的生理作用[J].安徽农业科学,2006,34(24):6423-6425,6427
    [33]刘凤荣,陈火英,刘杨,卫志明.盐胁迫下不同基因型番茄可溶性物质含量的变化[J].植物生理与分子生物学学报,2004,30(1):99-104
    [34]颜宏,赵伟,尹尚军,石德成,周道玮.羊草对不同盐碱胁迫的生理响应[J].草业科学,2006,15(6):49-55
    [35]Bazzaz FA, Grace J. Plant Resource Allocation. SanDi2ego:Academic Press.Chap in FS (?), Schulze ED,1997.
    [36]王迎春,杨持.物种生活史策略的研究现状[J].内蒙古大学学报(自然科学版),2001,32(1):112-118
    [37]吴小花.濒危植物金毛狗形态多样性分化的研究[J].江西化工,2007(2):24-26
    [38]江波,邓洪平,孙敏,肖璇,孙一铭.缙云山绞股蓝形态多样性分化研究[J].西南师范大学学报(自然科学版),2005,30(3):538-542
    [39]张桂萍,何平,邓洪平.濒危植物缙云卫矛的形态分化研究[J].西南师范大学学报(自然科学版),2001,26(6):703-708
    [40]何显静,李标,周利杰,虞泓.云南5种百合形态多样性研究[J].黑龙江农业科学,2003,(6):26-28
    [41]邓洪平,成明吴,陈亚飞,等.变叶海棠变异类型的形态多样性分化与陇东海棠关系的研究[J].西南师范大学学报(自然科学版),2002,27(1):79-82
    [42]周超,刘济明,蒙朝阳,陈美.不同喀斯特生境条件下小蓬竹构件生物量研究[J].安徽农业科学,2008,36(5):1835-1836
    [43]何玉惠,赵哈林,刘新平,张铜会,岳广阳.不同类型沙地狗尾草的生长特性及生物量分配[J].生态学杂志,2008,27(4):504-508
    [44]罗群,申平,黄春萍.干旱胁迫对附子各营养器官生物量的影响[J].西南农业学报,2008,21(3):633-635
    [45]吴成龙,周春霖,尹金来,刘兆普,徐阳春,沈其荣.碱胁迫对不同品种菊芋幼苗生物量分配和可溶性渗透物质含量的影响[J].中国农业科学,2008,41(3):901-909
    [46]贺海波,李彦.干旱、盐胁迫条件下两种盐生植物生物量分配对策的研究[J].干旱区研究,2008,25(2):242-246
    [47]张炜银,王伯荪,李鸣光,咎启杰,王勇军.不同光照强度对薇甘菊幼苗生长和形态的影响[J].中山大学学报论丛,2002,22(1):222-226
    [48]李合生.现代植物生理学[M].北京:高等教育出版社.2002
    [49]尹力初,张杨珠,周卫军.光照强度与氮肥施用水平对麦田杂草婆婆纳和离子草的生长及其竞争关系的影响[J].生态学杂志,2006,25(10):1285-1288
    [50]郝建军,康宗利.植物生理学[M].北京:化学工业出版社,2005
    [51]闫兴富,曹敏.不同光照梯度的遮阴处理对绒毛番龙眼幼苗生长的影响[J].热带亚热带植物学报,2007, 15(6):465-472
    [52]李志刚,侯扶江,安渊.不同光照强度对三种牧草生长发育的影响[J].中国草地学报,2009,31(3):55-60
    [53]黄睿,李炎林,章金盟,于晓英,吕长平,严潜.不同光照处理对吉祥草生理生化特性的影响[J].湖南农业科学,2009,(3):36-38
    [54]吉牛拉惹.不同光照强度对苦荞麦主要生物学性状的影响[J].安徽农业科学,2008,36(16):6638-6639,6641
    [55]杨毅,郭文源.不同光照强度对豚草生长发育的影响[J].湖北大学学报(自然科学版),13(2):175-178
    [56]杨梅娇.不同光照强度对一年生油樟苗生长的影响[J].浙江林业科技,2006,26(3):41-44
    [57]代莉,谢双喜.皂荚一年生幼苗对不同光照强度的生态适应性[J].贵州农业科学,2004,32(4):14-16
    [58]吴能表,谈锋.不同光照条件对少花桂幼苗生长的影响[J].西南师范大学学报(自然科学版),1999,24(2):214-218
    [59]李霞,曹昆,阎丽娜,王超,孙志伟,周月兰.盐碱胁迫对不同水稻材料苗期生长特性的影响[J].植物生理科学,2008,24(8):252-256
    [60]马勇.植物耐盐性研究进展综述[D].华中农业大学学士学位论文,2004
    [61]周建,杨立峰,张琳,袁德义,尤扬.碱胁迫对合欢种子萌发及幼苗生理指标的影响[J].浙江大学学报(农业与生命科学版),2008,34(4):401-408
    [62]周峰,华春.低浓度NaC1对菠菜生长的效应[J].西北农业学报,2008,17(6):127-129,142
    [63]周建,刘弘,尤扬,郝峰鸽,张琳.碱胁迫对紫荆幼苗生长与光合作用的影响[J].东北林业大学学报,2008,36(6):13-15
    [64]周峰,周泉澄,华春,陈全战.Na2C03和NaCl处理对盐角草生长和抗氧化酶活性的影响[J].安徽农业科学,2007,35(36):11748-11750
    [65]毛桂莲,许兴,杨涓.NaC1和Na2C03对枸杞的胁迫效应[J].干旱地区农业研究,2004,22(2):100-104
    [66]颜宏,赵伟,尹尚军,石德成,周道玮.羊草对不同盐碱胁迫的生理响应[J].草业科学,2006,15(6):49-55
    [67]王波,张金才,宋凤斌,赵敏,韩希英.燕麦对盐碱胁迫的生理响应[J].水土保持学报,2007,21(3):86-89
    [68]迟春明,王志春,李彬.混合盐碱胁迫对帚用高粱萌发及苗期生长的影响[J].干旱地区农业研究,2008,26(4):148-151
    [69]张玉霞,谭巍巍,王艳树,魏建慧.盐碱胁迫对芦笋抗氧化酶活性的影响[J].内蒙古民族大学学报(自然科学版),2006,21(2):165-168
    [70]刘爱荣,张远兵,陈登科.盐胁迫对盐芥生长和抗氧化酶活性的影响[J].植物研究,2006,26(2):216-222
    [71]张超强,杨颖丽,王莱,孙坤,范小峰,刘军梅,李科文.盐胁迫对小麦幼苗叶片H202产生和抗氧化酶活性的影响[J].西北师范大学学报(自然科学版),2007,43(1):71-76
    [72]李妍.盐胁迫对中华补血草生长和保护酶活性的影响[J].种子,2007,26(12):76-80
    [73]齐泽民,王玄德,宋光煜.酸雨对植物影响的研究进展[J].世界科技研究与发展,2004,26(2):36-41
    [74]付晓萍,田大伦.酸雨对植物的影响研究进展[J].西北林学院学报,2006,21(4):23-27
    [75]蔡燕微,江红英,陈中义.模拟酸雨对外来入侵植物空心莲子草的出苗及生长的影响[J].长江大学学报(自科版)农学卷,2007,4(4):73-76
    [76]廖周瑜,彭少麟.酸雨对外来植物入侵的影响[J].生态环境,2007,16(2):639-643
    [77]MANCHESTER S J, BULLOCK J M. The impacts of non-native species on UK biodiversity and the effectiveness of control[J].Journal of Applied Ecology,2000,37:845-864.
    [78]齐泽民,钟章成,邓君,刘素君.模拟酸雨对杜仲叶膜脂过氧化及氮代谢的影响[J].西南师范大学学报(自然科学版),2001,26(1):38-44
    [79]朱韦,魏虹等.模拟酸雨对四川大头茶幼苗的生理生态影响[J].西南师范大学学报(自然科学版),2006,31(2):147-150
    [80]田大伦,付晓萍,方晰,项文化.模拟酸雨对樟树幼苗光合特性的影响[J].林业科学,2007,43(8):29-35
    [81]刘昊,余树全,江洪,方江保.模拟酸雨对山核桃叶绿素荧光参数、叶绿素和生长的影响[J].浙江林学院学报,2009,26(1):32-37
    [82]陈学政,李永健,朱高浦,司瑞丽.模拟酸雨对花生生长和一些生理指标的影响[J].安徽农学通报,2007,13(5):105107
    [83]倪寿清,宋晓东,崔清洁,李建国,杨国栋.模拟酸雨胁迫下中国北方小麦生理特性研究[J].山东农业大学学报(自然科学版),2008,39(1):19-22
    [84]黄建昌,肖艳,张运新,李娟浓.模拟酸雨对芒果的生理伤害和生长的影响[J].热带作物学报,2003,24(1):28-30
    [85]赵丽娟,陈文德,彭培好.重庆都市经济圈土壤重金属的分布与评价[J].天津农业科学,2008,14(4):34-37
    [86]李章平,陈玉成等.重庆市主城区土壤重金属的潜在生态危害评价[J].西南农业大学学报,2006,28(2):227-230
    [87]龚双姣,马陶武,姜业芳,陈军,刘应迪,李菁.镉胁迫下3种藓类植物抗氧化酶活性变化的比较研究[J].西北植物学报,2008,28(9):1765-1771
    [88]徐苏凌,方勇,邢承华.酸雨和Cd胁迫对紫花苜蓿生长和抗氧化酶系统的影响[J].浙江大学学报(农业与生命科学版),2008,34(4):467-472
    [89]郭燕梅,王昌全,李冰.重金属镉对植物的毒害研究进展[J].陕西农业科学,2008,(3):122-126
    [90]安建平,王廷夂,谢天柱,等.镉胁迫对亚麻种子萌发及幼苗生理特性的影响[J].中国麻业科学,2008,30(4):199-203
    [91]张兆金.土荆芥对铅胁迫的生理响应及其对铅污染土壤的修复.南京林业大学,2006
    [92]杨卫东,陈益泰.镉胁迫对旱柳细胞膜透性和抗氧化酶活性的影响[J].西北植物学报,2008,28(11):2263-2269
    [93]唐秀梅,龚春风,刘鹏,徐根姊,蔡妙珍,吴琼鸯.镉胁迫下龙葵叶中三种抗氧化酶的活性和抗坏血酸含量的变化[J].植物生理学通讯,2008,.44(6):1135-1136
    [94]袁祖丽,吴中红,刘秀敏.镉胁迫对烤烟叶片抗氧化酶系统的影响[J].河南农业科学,2008,(7):43-47
    [95]胡仲义,章建红.重金属镉对铁冬青幼苗的毒害效应[J].浙江农业科学,2008,(3):306-309
    [96]陶毅明,陈燕珍,梁士楚,梁杨琳.镉胁迫下红树植物木榄幼苗的生理生化特性[J].生态学杂志,2008,27(5):762-766
    [97]曾秀存,许耀照,王晓琴,张芬琴.镉胁迫对红果龙葵幼苗生理生化的影响[J].沈阳农业大学学报,2008,39(2): 240-242
    [98]于方明,仇荣亮,胡鹏杰,赵璇,吴妤都.不同Cd水平对小白菜叶片抗氧化酶系统的影响[J].农业环境科学学报,2007,26(3):950-954
    [99]郑世英,张秀玲,王丽燕,李研.Cd2+胁迫对蚕豆抗氧化酶活性及丙二醛含量的影响[J].河南农业科学,2007,(2):35-38
    [100]何俊瑜,任艳芳.镉胁迫对水稻种子萌发、幼苗生长和淀粉酶活性的影响[J].华北农学报,2008,23:131-134
    [101]崔永行,范仲学,杜瑞雪,蔡利娟.镉胁迫对甜高粱种子萌发的影响[J].华北农学报,2008,23:140-143
    [102]张玉霞,谭巍巍,王艳树,魏建慧.盐碱胁迫对芦笋抗氧化酶活性的影响[J].内蒙古民族大学学报(自然科学版),2006,21(2):165-168
    [103]廖柏寒,蒋青.我国酸雨中盐基离子的重要性[J].农业环境保护,2001,20(4):254-256
    [104]廖正军,唐亮.重庆市酸雨成因及控制对策[J].环境保护科学,2000,26(100):1-5
    [105]张志良,瞿伟菁.植物生理学实验指导[M].北京:高等教育出版社,2003
    [106]杨铁钊,殷全玉,丁永乐,张玉梅.烟草气孔特性、抗氧化酶活性与臭氧伤害的关系[J].植物生态学报,2004,28(5):672-679
    [107]赵世杰,许长成,邹琦,孟庆伟.植物组织中丙二醛测定方法的改进[J].植物生理学通讯,1991,30(3):207-210
    [108]张兆金.土荆芥对铅胁迫的生理响应及其对铅污染土壤的修复[D].南京林业大学研究生硕士学位论文,2006
    [109]关保华,蔡颖,等.底泥高磷浓度提高了喜旱莲子草的入侵性[J].植物生态学报,2007,31(4):665-672
    [110]耿宇鹏,张文驹,李博,陈家宽.表型可塑性与外来植物的入侵能力[J].生物多样性,2004,12(4):447-455
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