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双语推荐:铜绿微囊藻

铜绿微囊藻为试验材料,应用正交试验法,在培养温度(25℃)及接种量相同的情况下,研究光限制胁迫协同pH与氮磷比对铜绿微囊藻生长的影响.影响铜绿微囊藻生长的因素顺序为:pH光限制胁迫天数氮磷比,pH为铜绿微囊藻生长的显著性影响因素(F=63.111 5),且在pH 10.5、氮磷比15∶1及光限制胁迫5 d的条件下正常光照培养4 d后细胞数量最大.
The synergistic effects of pH value , ratio of N/P, and light limitation on the growth of Microcystis aeruginosa were investigated by orthogonal tests .Results of orthogonal test for the selective preference of the growth condition for M .aeruginosa showed that pH can significantly affect the growth of M .aeruginosa, and the optimal factor combination is pH 10.5, stress of 5 days and 15/1 for N/P.Under 25℃, the order of effect on the M .aeruginosa is pH>stress of light limitation >N/P, detected after cultured under normal light intensity for 4 days.

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通过观察暴露于不同浓度有毒铜绿微囊藻( Micorcystis aerug niosa)下的三角帆蚌( Hyriopsis cumingii)的胃、前肠、中肠以及晶杆体等消化系统的扫描电镜切片,了解有毒铜绿微囊藻对三角帆蚌消化系统超显结构的影响。结果显示,当三角帆蚌在浓度为1×107 cell/L的有毒铜绿微囊藻环境下,其晶杆体随时间推移而逐渐溶解。在低浓度的铜绿微囊藻环境下,尽管其会继续滤食,但有毒铜绿微囊藻会对其消化系统造成破坏,随着接触时间的增长,造成其肠道内绒毛、纤毛数量减少,长度降低,从而降低其消化效率,对其生长造成影响。
The ultrastructural changes in the digestive system such as stomach , foregut, midgut, and crystalline style of the Hyriopsis cumingii cultured in different concentrations of toxic Microcystis aeruginosa were observed during the whole experimental period .The results revealed that H.cuminigi′s crystal rod was dissolved due to starvation , when the concentration of microcystis was more than 1 ×107cell/L.Toxic M.eruginosa showed negative effects on the fluff and cilia of the intestine .The figures illustrated that fluff and cil-ia became fewer and less .Hereby, toxic M. eruginosa might decrease the digestive efficiency of H.cumingii′s and have negative effects on its growth .

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对分离自山东黄岛和江苏太湖两处富营养化池塘中的2株溶细菌的培养条件进行了优化,探究了2菌株对铜绿微囊藻生长的抑制作用。实验结果显示,2菌株可通过凝聚体细胞、裂解微藻细胞体以及胞外分泌活性物质产生生物降解作用,对铜绿微囊藻产生杀灭效果,且分泌的胞外活性物质对铜绿微囊藻的杀灭作用具有特异性。
The culture conditions of two strains of algicidal bacteria, which isolated from two eutrophic ponds in Shandong Huangdao and Jiangsu Taihu, are optimized. The inhibitory effect of the two strains on the growth of Mi-crocystis aeruginosa are explored. The experimental results show that the two strains can produce biological degrada-tion by coagulation algae cells, cleavage of microalgae cells and extracellular secretion of active substances to kill the algae cells. Besides, the killing effect of extracellular substances of two strains on Microcystis aeruginosa are specificity.

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研究壳聚糖、沸石单独絮凝除以及壳聚糖-沸石复合体对铜绿微囊藻去除效果。结果表明:单独使用壳聚糖,质量浓度在0.6~1.1mg/L时,对铜绿微囊藻的去除率超过90%;单独使用沸石,沸石质量浓度小于500 mg/L时,对铜绿微囊藻的去除率低于40%。经壳聚糖包覆改性后,壳聚糖-沸石复合体对铜绿微囊藻絮凝去除能力大幅提高。当壳聚糖质量浓度为0.5 mg/L,沸石质量浓度为6~14 mg/L时,壳聚糖-沸石复合体对铜绿微囊藻的去除率达90%以上。壳聚糖-沸石复合体适用的pH值范围在5~7之间。
The removal of Microcystis aeruginosa by chitosan , zeolite, and chitosan-zeolite composite was studied. The results show that with a dosage of 0.6 to 1.1 mg/L, chitosan can remove more than 90% of Microcystis aeruginosa, and with a dosage of less than 500 mg/L, zeolite can remove less than 40%of Microcystis aeruginosa. After the modification of zeolite, the chitosan-zeolite composite greatly improved the algal removal efficiency .The chitosan-zeolite composite could remove more than 90%of algae when the dosage of chitosan was 0.5 mg/L and the dosage of zeolite was between 6 mg/L and 14 mg/L.The optimal pH value ranged from 5 to 7 for the chitosan-zeolite composite.

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为认知星肋小环(硅)春季活动、滇池铜绿微囊藻(蓝)春夏大规模暴发的活动规律,通过确定生长温区后进行变温实验,分析低温对2种实验的生长影响,其结果为:小环的生长温度为9.5~15.0℃,微囊藻生长温度为15.0~31.0℃,生长高温将抑制2种的生长;15.5℃以上、9.0℃以下时小环停止生长,31.0℃以上、15.0℃以下时微囊藻停止生长;在15.5~17.5℃停止生长后用7.0~9.0℃处理一天后放回生长温度培养,小环恢复生长,在31.0~33.0℃停止生长后用7.0~14.0℃处理一天后放回生长温度培养,微囊藻恢复生长,表明特定低温可使处于高温休眠的恢复生长,即低温具有解除高温休眠的作用;诱导低温7.5~9.5℃、10.0~14.0℃时,星肋小环铜绿微囊藻的生长与低温诱导强度反相关,与诱导时间正相关;低温可解除高温休眠作用诱导生长,同样,高温也可解除的低温诱导作用。分析认为:星肋小环铜绿微囊藻的低温诱导作用与植物春化作用一致,因此实验具有春化作用,其年活动规律为:经冬季低温诱导,处于休眠的实验春季恢复生长,夏季生长高温抑制铜绿微囊藻生长,秋季无诱导低温过程,铜绿微囊藻华可发生但不如春夏。
To study the activities of the Cyclotella asterocostata in spring and Microcystis aeruginosa in Dianchi Lake in spring and summer, on the basis of the experiment to determine the growth temperature, Analyses the low temperature impact on two experimental algae growth. The results show that:the Cyclotella asterocostata growth temperature was 9.5~15.0 ℃, the Microcystis aeruginosa growth temperature was 15.0~31.0 ℃, growth high temperature would restrain the growth of the two kinds of experimental algae. The Cyclotella asterocostata stopped growing when the temperature was more than 15.5 ℃, 9.0 ℃ below, it was the same to Microcystis aeruginosa(more than 31.0 ℃, 15.0 ℃ below). The stop growing Cyclotella asterocostata will recovery growth after treated with 7.0~9.0 ℃ for a day and back on the growth temperature, it was the same to Microcystis aeruginosa which was treated with 7.0~14.0 ℃. This showed that specific low temperature could make experimental algae recovery gr

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铜绿微囊藻以其毒素和产生的嗅味威胁人类健康和安全,且因大量生长和难去除性给水处理带来困难。本文以电子加速器产生的电子束对铜绿微囊藻培养液(对数生长期)分别进行1、2、3、4和5kGy剂量的辐射,通过考察细胞蛋白质、抗氧化体系酶活性及光合速率的变化,研究辐射对铜绿微囊藻生命特征及机能产生的影响。结果表明:1kGy的辐射对细胞可溶性蛋白质及POD、SOD活性的影响较小;而2~5kGy的辐射明显降低了蛋白质含量,并破坏了细胞的抗氧化系统,光合速率也因辐射明显降低,使铜绿微囊藻短时间内失活。表明一定剂量的电子束辐射能有效控制细胞生长,并影响其重要生命特征。
Microcystis aeruginosa often threatens human health and safety for its micro-cystin and bad smell .Its large number and hardness of removal are difficulty for water treatment .In this study ,electron beam generated by an accelerator was applied to irra-diate Microcystis aeruginosa by dose of 1 ,2 ,3 ,4 and 5 kGy .The effect of irradiation on Microcystis aeruginosa characteristic and mechanism was studied by surveying the changing of protein ,enzyme activity and photosynthesis rate .The data show that irradi-ation of 1 kGy has little effect on dissoluble protein ,POD and SOD activity .Irradiation of 2-5 kGy can decrease protein content and destroy the antioxidant system ,also the photosynthesis rate decreases obviously ,which makes Microcystis aeruginosa lose activ-ity in short time .The result proves that a certain dose of electron beam irradiation can control algae grow th and affect its life characteristic efficiently .

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铜绿微囊藻(Microsystis aeruginosa)作为生物模型,通过测定细胞氧化损伤程度与细胞内外毒素LR(microcystin-LR,MC-LR)的含量,研究除草剂禾草灵的生态毒性。结果表明,禾草灵在实验室处理质量浓度1,2,5mg/L下,能诱导铜绿微囊藻细胞活性氧(reactive oxygen species,ROS)的产生,引起细胞脂质过氧化水平丙二醛(malondialdehyde,MDA)的提高和超氧化物歧化酶(superoxide dismutase,SOD)的活性增强。说明禾草灵对铜绿微囊藻产生了氧化胁迫。5mg/L禾草灵使铜绿微囊藻释放到细胞外的微囊藻毒素MC-LR显著增加,为空白对照的68.5,2.11,2.50,123.67倍(第2,3,4,5天);细胞内MC-LR含量与空白对照相比有一定的降低,为空白对照的0.34,0.82,2.76,0.11倍(第2,3,4,5天)。说明禾草灵在一定质量浓度下能对铜绿微囊藻产生氧化胁迫,引起细胞脂质过氧化,从而引起细胞膜损伤,导致微囊藻毒素MC-LR更多的释放到水体中,对水环境造成一定的影响。实验结果可对禾草灵的环境安全评价提供一定的参考。
Summary Diclofop-methyl is a postemergence herbicide introduced in the 1 960s.It is widely used on wheat, barley,and golf courses (turf) all over the world.Residues of diclofop-methyl may pollute the water system and affect the physiological processes in cyanobacteria.Causative cyanobacteria can often cause serious environmental, aesthetic,and economic problems;besides,it can produce microcystins(MCs)which are toxic to domestic livestock and wildlife.Certain environmental factors such as pH,temperature,and the amount of nitrogen and phosphorus in the water have been found to affect the production of MCs.But other factors,such as the concentration of environmental pollutants including pesticide residues which may be prevalent in aquatic ecosystems,have not been studied in sufficient detail. In the current study,oxidative damage and toxin release from Microsystis aeruginosa caused by diclofop-methyl were investigated.Diclofop-methyl was proposed to induce oxidative stress in susceptible

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铜绿微囊藻(Microcystis aeruginosa)16S rRNA基因片段为靶序列设计一对特异性引物,采用Real-time PCR法,对铜绿微囊藻进行定性、定量检测。试验表明,仅含铜绿微囊藻DNA模板的样品有特异性扩增,扩增产物熔解曲线平稳,峰尖且窄,熔解温度为(87±1)℃。以重组质粒pMD-18T-16S为标准品,检测区间为1.1×102copies/mL~1.1×108copies/mL,所得标准曲线符合制备实时定量PCR标准曲线的要求,对标准品进行测定,方法检出限为11 copies/mL。用该标准曲线对实验室培养获得的铜绿微囊藻DNA样品进行定量检测,与显镜计数结果基本一致。
A real-time polymerase chain reaction ( PCR) assay was designed and evaluated for rapid detec-tion and quantification of the algae Microcystis aeruginosa.A pair of specific primers was designed from the se-quence of 16S region,of which the PCR pecificity was examined compared with Chlorella sp.and Nitzschia sp.. PCR amplifications were detected only from samples which contained Microcystis cells and specific signals were not detected from Chlorella sp..Melting curve was stationary and peak was narrow .Melting temperature was (87 ±1)℃.Based on recombinant plasmid pMD -18T-16S for the standard,the standard curve we got has high linearity and correlation coeficient .Moreover,this assay was in accordance with preparative real-time PCR. Using the developed standard curves ,Microcystis aeruginosa could be quantified in agreement with the quantifica-tion by optical microscopy .

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对水芹、美人蕉、黄菖蒲、菹草4种水生植物对铜绿微囊藻的化感特征进行了研究。不同的植物组织器官及不同的植物处理方式下,抑效果不同,最具抑潜力的植物为黄菖蒲和美人蕉。经黄菖蒲和美人蕉种植水培养5d后,铜绿微囊藻的抑制率达70.12%~77.25%。质量分数为0.53%的黄菖蒲叶提取物,经11 d的培养后,对铜绿微囊藻的抑制率为65.30%。抑机理可能在于化感物质的胁迫使微囊藻细胞内活性氧自由基过量堆积,进而引起对细胞的伤害和影响类正常的光合作用。SOD酶活性与的比增长率均呈现较好的负相关关系。
The allelopathic effects of four aquatic macrophytes (Iris pseudacorus,Canna indica,OenantheJavani-ca,and Potamogeton)on the growth of Microcystis aeruginosa were investigated.The allelopathic effects were dif-ferent by different organs and various pretreatment.Iris pseudacorus and Canna indica were found to have the most potentialities of controlling algae.The water after culturing Iris pseudacorus and Canna indica were used to culture algae.The inhibition rate of algae could reach 70.12% to 77.25% five days later.The liquid extracted from the leaves of Iris pseudacorus with 0.53 percentage of mass fraction was applied to culture algae for 1 1 days.The inhibi-tion rate was 65.30%.The allelopathic mechanism could be explained by the stress fromthe allelopathic materials that damaged and hindered the photosynthesis of algae through improving the accumulation of active oxygen radicals in the cells of algae.In addition,the activity of superoxide dismutase (SOD)showed a good nega

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铜绿微囊藻(Microcystis aeruginosa)为溶解对象,利用液体感染分离技术从浙江大学华家池校区湖水样品中分离到1株溶菌N10,对其生长及溶相关特性进行了研究.结果表明:经过16SrDNA核苷酸序列分析,该菌株属于柠檬酸杆菌属(Citrobacter sp.);当N10无细胞培养物(cell-free culture filtrate,CCF)与铜绿微囊藻液按照体积比为1∶5混合后,在24h内N10CCF对铜绿微囊藻的溶率可达到86.55%,并且溶率随着溶时间的延长而增强,在72h内溶率可达到97.08%;对N10生长量影响最大的是pH值,其次是NaCl质量分数,最后是温度,但N10菌株对铜绿微囊藻的溶率受培养温度和培养基中NaCl质量分数的影响很小;N10菌株通过分泌一种对高温(115℃)敏感但却能抗蛋白酶K的物质来溶解铜绿微囊藻;透射电子显镜观察表明,经过N10CCF处理后的细胞出现了细胞膜、细胞壁破裂,伪空胞结构、细胞质中磷酸颗粒以及蓝色体等颗粒性物质消失,细胞中的光合片层排列趋于松散且混乱的现象.
Summary In recent decades,harmful algal blooms(HABs),which are natural phenomena that occur across all the world, have posed threats to decrease dissolved oxygen and have had a negative effect on fisheries, aquaculture,drinking water,tourism and human health.It is increasingly urgent to develop useful strategies for predicting and reducing the negative impacts of HABs.Actually,many methods have been devoted to controlling HABs,including copper sulfate,hydrogen peroxide,ozonization,ultrasonication,collection of algae from water surface using nets,iron powder and magnets,centrifugal separation,or ultraviolet radiation.As an effective and environment friendly strategy to control harmful algal bloom outbreaks,biologic control methods such as using algicidal bacteria against M.aeruginosa have been more and more attractive.It has been demonstrated that algicidal bacteria could serve as potential ways in reducing the impacts of HABs. In this study,a Citrobacter sp.N10 with algicidal activity

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