紫茎泽兰(Eupatorium adenophorum Spreng)致病型链格孢菌毒素(Tenuazonic Acid)作用靶标与杀草机理的研究
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摘要
紫茎泽兰(Eupatorium adenophorum Spreng)是一种世界性的外来入侵恶性杂草,目前仍没有找到有效的方法来控制它。令人振奋的是强胜等在1999年从紫茎泽兰致病型链格孢菌(Alternaria alternata(Fr.) Keissler)中分离得到了一种毒素(命名为AAC-toxin),这种毒素能够引起包括紫茎泽兰在内的许多杂草的褐斑病。这为紫茎泽兰的防除提供了巨大的新的希望.后来证明AAC-toxin就是细交链格孢菌酮酸(Tenuazonic acid,TeA)。自从1957年首次从链格孢菌菌株上分离以来,已经先后在橄榄、向日葵、柑橘、胡椒、高梁、烟草、水稻和紫茎泽兰上发现了这种TeA毒素。长期以来,关于TeA的研究主要集中在来源和动物毒性方面,关于植物活性方面研究十分少见,更没有关于除草活性方面的报道.我们的前期研究表明TeA对广泛的寄主表现出很高的生物活性,能够迅速杀死许多单双子叶植物,这些寄主植物既有杂草也有作物。本论文主要研究TeA的作用靶标和它引起叶片坏死的机理,目的是为利用TeA开发生物源除草剂提供理论依据。
     首先,我们利用TeA的粗毒素研究了TeA和光合作用之间的关系。结果表明在叶片出现明显的外观伤害之前,TeA处理使叶片的光合放氧速率和表观量子效率明显降低。进一步研究发现TeA主要作用于光合作用光反应的光系统Ⅱ(PSⅡ),能够完全抑制PSⅡ电子传递活性,对光Ⅰ(PSⅠ)活性影响不大。而且,TeA对光合作用暗反应关键酶RuBPcase、叶绿素含量和叶片总可溶性蛋白含量则没有明显的影响。叶绿素荧光试验结果表明TeA抑制了PSⅡ受体侧电子的传递从而导致PSⅡ光化学效率的降低,但对PSⅡ供体侧的天线色素分子和放氧复合体没有明显的影响。另外,TeA能够强烈的降低叶绿体Mg~(2+)-ATPase活性,对线粒体并没有影响。因此,可以推断PSⅡ受体侧和叶绿体ATPase可能是TeA的2个最重要的作用靶标。这也意味着TeA可能是一个PSⅡ抑制剂。
     为了进一步研究TeA在PSⅡ上的精确作用靶标,我们应用了快速叶绿素荧光动力学和同位素标记光亲合技术。纯TeA毒素能够完全抑制紫茎泽兰类囊体PSⅡ电子传递活性,半抑制浓度是238μM。来自不同植物的快速叶绿素动力学结果表明TeA在PSⅡ上有几个作用位点.首先,TeA处理导致OJIP曲线发生的最大变化在于TeA加速了J点的快速上升,这一点和传统的PSⅡ除草剂敌草隆作用方式是相同的。这说明TeA最关键和最重要的作用是阻断PSⅡ受体侧电子向QA以后的位置传递。而且进一步证实了TeA对PSⅡ供体侧的天线色素分子和放氧复合体没有影响。与经典的PSⅡ除草剂不同的是TeA处理导致了热反应中心的上升。另外,TeA也可能对FNR活性产生抑制作用。此外,来自碳14标记阿特拉津的竞争结合试验证据表明:TeA和阿特拉津在Q_B绑定区域上作用的方式是不同的,虽然它们有着共同的作用靶标-Q_B绑定区域。这说明TeA可能是一种新的天然的PSⅡ抑制剂。除了最主要的位点Q_B绑定区域外,TeA也可能对叶绿体ATPase和FNR的活性产生一定的抑制作用。
     十分有意思的是,在链格孢菌引起寄主植物发病过程中为什么它产生的是TeA而不是其它的TeA类似物呢?在植物体内有20多种氨基酸可供选择去合成TeA的吡咯环,然而链格孢菌却利用异亮氨酸合成了这个在5位是异丁基长链的物质—TeA。这个问题要得到解决,我们必须先弄清除TeA在PSⅡ上精确靶标的分子基础。因此我们选择了莱茵藻(包括野生型和5个psbA突变体)这种除草剂靶标研究和光合作用研究的模式材料来探讨TeA同Q_B绑定区域相互作用的分子基础。叶绿素荧光试验显示TeA抑制了光合电子在PSⅡ受体侧Q_A到Q_B之间的传递。来自莱茵藻D1蛋白突变体的证据表明在TeA和Q_B位点相互作用过程中D1蛋白上的256位氨基酸起着关键的作用。从碳14标记阿特拉津的竞争结合实验、JIP-test分析和D1系列突变体实验结果可以看出:在同Q_B绑定位点相互作用的过程中,TeA与其它已知的PSⅡ抑制剂有着不同的绑定行为,进一步证明了TeA可能是一种新型的PSⅡ抑制剂。TeA和它的类似物生物活性试验表明3-酰基-5-烷基吡咯烷酮甚至四氨酸或许提供了一种新型光合抑制剂的结构骨架。
     在植物病害和许多非生物胁迫中细胞死亡总是伴随着活性氧(ROS)的产生而发生。为了进一步阐明TeA引起叶片坏死的机理,我们进行了一系列试验来探究在TeA致病过程中TeA、活性氧产生和细胞死亡的关系。我们的结果表明在TeA引起紫茎泽兰叶片发病的过程中的确产生了活性氧。激光共聚焦的试验结果表明TeA诱导叶肉细胞活性氧产生的最初位点在叶绿体,这个结果在细胞化学染色(CeCl_3染色)试验中得了到进一步证实。电子自旋共振(EPR)和活性氧清除剂试验结果表明TeA激发的叶绿体活性氧的最初种类是羟自由基(OH)、单线态氧(~1O_2)、超氧自由基(O_2~(.~-))和过氧化氢(H2O_2)。最初产生的活性氧首先对叶绿体结构造成伤害,但没有对细胞中其他细胞器造成氧化伤害。随着ROS弥散到细胞,高浓度的活性氧能够与细胞中许多重要的生物分子象膜脂、色素、蛋白质和氨基酸等发生反应,接着一系列氧化伤害如膜脂过氧化、叶绿素降解、染色质浓缩、细胞结构和功能丧失等相继发生,最终导致细胞坏死。象经典的光合作用除草剂一样,TeA所引起的光氧化伤害是细胞死亡和叶片坏死的主要原因。
     总之,TeA是一种新型的天然的光合作用抑制剂。TeA能够通过与Q_B位点结合而诱发叶绿体活性氧的爆发,进而直接导致叶片快速坏死,这个过程主要是一个光氧化损伤的过程。TeA对叶绿体ATPase和FNR活性的影响可能也参入了这个过程。相对于敌草隆和百草枯等单一位点的传统光合作用除草剂而言,一旦TeA进入叶肉细胞后,它的这种多位点作用机制也许能够导致细胞在短时间内产生更多种类和更高水平的活性氧,从而迅速毁坏细胞而杀死杂草。
Nowdays,there is no quite efficacious methods to be used to Crofton weed (Eupatorium adenophorum Spreng) control,which is one of the most troublesome invasive weed with worldwide distribution.Excitingly,Qiang et al.(1999) found a phytotoxin (named AAC-toxin) produced by Alternaria alternata(Fr.) Keissler Crofton weed pathotype,which can cause brown leaf spot disease in many weeds,especially host Crofton weed,which supplies a big new opportunity to Crofton weed control.AAC-toxin is later proven to be tenuazonic acid(TeA) through isolation and identification.Since its first isolation in 1957 from the culture filtrates of Alternaria tenuis,TeA has been found in olives,sunflower seeds,tangerines,peppers,sorghum,tobacco,rice and Crofton weed.So far,interest in TeA is mainly focused on its source and its toxicity to animals.However, only few studies have addressed the bioactivity of TeA to plants with few purposes for weed control.From our previous studies,TeA shows high bioactivity to a wide range of plants,from weeds to crops,and then quickly kills the seedlings of mono- and dicotyledonous weeds.However,mechanism of killing weeds has not been known before. Here,action target of TeA and the mechanism of leaf necrosis induced by TeA are investigated in order to supply the theory basis for development of bio-based herbicides using TeA.
     Firstly,we studied the relationship between TeA(crude toxin) and photosynthesis.The results show that TeA greatly inhibited their oxygen evolution rate and declines evidently quantum efficiency before any distinct change in leaf appearance was observed.The effect of TeA on the electron transfer reaction of chloroplasts shows that the activity of photosystemⅡ(PSⅡ),but not photosystemⅠ(PSI),was completely inhibited by TeA.This inhibition mainly focuses on the light reaction not the dark reaction of photosynthesis.No evident difference of the key enzyme RuBPcase of dark reaction and chlorophyll content was found under TeA treatment.Evidences from chlorophyll fluorescence further indicate that TeA decreased the efficiency of photochemistry of whole PSⅡattributed to inhibit electron transport in PSⅡacceptor side,but had no effect on the donor side of PSⅡsuch as antenna pigment molecule and Oxygen Evolving Complex(OEC).In the addition,TeA led to a distinct decrease of Mg~(2+)-ATPase activity of chloroplast,whereas,had no influence on mitochondria.Thus,it is concluded that the acceptor side of PSⅡand ATPase of chloroplast are possible two most important action target of TeA until now.These results mean that TeA may be a PSⅡinhibitor.
     To further study the precise action site of TeA on PSⅡ,the modern techniques of fast chlorophyll fluorescence kinetics and photoaffinity labeling with radioactive technique were utilized.Results demonstrate that TeA(pure toxin) inhibited completely the activity of PSⅡelectron transport of Crofton weed;the pI_(50)-value was 240μM.Evidences from chlorophyll fluorescence transients OJIP curves of the various species plants show that TeA has several sites of action.As the classical PSⅡherbicides(eg.diuron and atrazine),the biggest change of OJIP curves of all plants is a fast rise of step-J after TeA treatment.It is concluded that the most key and important action site of TeA is that it interrupts electron transport beyond Q_A on the acceptor side of PSⅡ.Moreover,TeA has no affect on the antenna pigments,OEC at the donor side of PSⅡ.On the other hand,TeA treatment causes the increase of heat sink centers and inactivation of the FNR system and the reduction of NADP~+,which is different from a classical inhibitor.Evidence from the competitive displacement with[~(14)C]atrazine shows that TeA does not share the same binding environment with atrazine despite they possess a common action target:the Q_B site.It is showed that TeA is possible a novel natural PSⅡinhibitor.Moreover,TeA maybe also effect on FNR and ATPase of chloroplast besides the most main Q_B site.
     Interestingly,why does A.alternata only synthesize TeA with pyrrole ring as phytotoxin against the resistance of host plant during its infection? The fungi easily use all 20 kinds of natural amino acid available as materials to synthesize pyrrole ring as phytotoxin.However,A.alternata only selectively use isoleucine,having butyl side chain, to synthesize into TeA with long side chain at 5-position.To answer the question,we must clarify the precise molecular target of TeA in PSⅡ.Chlamydononas reinhardtti,a typical model organism used in the field of herbicide target and photosynthesis research,is utilized to confirm the molecule basis of TeA binding to the Q_B site.Results from chlorophyll fluorescence of C.reinhardtti further prove that TeA blocks electron flow from Q_A to Q_B at PSⅡacceptor side.On the basis of studies with D1-mutants of C.reinhardtii,the No.256 amino acid plays a key role in TeA binding to the Q_B-niche.The results of competitive replacement with[~(14)C]atrazine combined with JIP-test and D1-mutant show that TeA should be considered as a new type of PSⅡinhibitor because it has a different binding behavior within Q_B site from other known PSⅡinhibitors.Bioassay of TeA and its analogues indicates 3-acyl-5-alkyltetramic and even tetramic acid compounds may present a new structural framework with pyrrole ring for photosynthetic inhibitors.
     Cell death,along with the production of ROS,occurs during plant-pathogen and many abiotic stresses.In order to further elucidate the mechanism of TeA-induced leaf necrosis, we carried out a series of experiments to investigate the relationship between TeA,ROS generation and cell death.Our studies show that TeA induces ROS burst in leaves during TeA-induced brown leaf spot disease of E.adenophorum.According to the data of laser scanning confocal microscope,it is suggested the primary site of TeA-induced ROS generation in mesophyll cells is chloroplasts.This result is further proved by the evidence from the experiments of CeCl_3 staining.The results of EPR and ROS scavenger experiments suggest that the original sources of TeA-induced ROS production in chloroplasts are hydroxyl radicals(OH),singlet oxygen(~1O_2),superoxide radical(O_2~-) and hydrogen peroxide(H_2O_2).The initial generation of ROS firstly results in damage in the structure of chloroplasts.Latter production of ROS is dispersed into cells and reacts with many important biomolecules such as pigments,lipids,proteins and nucleic acids,causing lipid peroxidation,chlorophyll breakdown,chromatin condensation,the loss of structure and function of cells,and resulting in cell destruction.Like classical photosynthetic herbicides,this injury triggered by TeA is a result of the directly oxidative damage of high ROS level in cell.
     In conclusion,TeA is a novel natural photosynthetic inhibitor.It induces oxidative burst in chloroplasts by acting with the Q_B site,resulting in leaf necrosis.In addition,the inhibition of the activity of ATPase and FNR of chloroplasts possible play some role in this process.Photo-oxidative damage is responsible for the process of TeA-induced leaf necrosis.Compared with the general photosynthetic inhibitor herbicides such as DCMU and paraquat,such action mode of TeA makes possibly cells generate more reactive oxygen species with a faster rate and higher level and kill quickly many weeds once mesophyll cells touch directly TeA.
引文
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