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Impact of zinc oxide nanoparticles on green pea plant and seed quality and effects on physiological traits of green peas, corn, and zucchini by silver nanoparticles.

机译:纳米银颗粒对氧化锌纳米颗粒对豌豆植物和种子品质的影响以及对豌豆,玉米和西葫芦的生理特性的影响。

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摘要

This project was completed in four phases. In Phase I, the green pea plants (P. sativum L.) were exposed to 0, 125, 250, and 500 mg kg--1 of 10 nm bare ZnO NPs and bulk ZnO for 25 days in organic matter enriched soil (native soil: potting soil= 1:1) in a growth chamber. Toxicological effects were investigated in terms of plant growth, chlorophyll production, zinc accumulation in different tissues, reactive oxygen species/ROS (H2O2) generation, stress enzyme activity (catalase/CAT and ascorbate peroxidase/APOX), and lipid peroxidation. Root elongation reduction (48-52%) was observed in all ZnO NP concentrations ( p ≤ 0.05); however, stem lengths were unaffected compared to control. Chlorophyll in leaves decreased, compared to the control, by 61%, 67%, and 77% in plants treated with 125, 250, and 500 mg kg--1 ZnO NPs, respectively. Bulk ZnO treatments also showed similar results. In roots and leaves, APOX activity decreased in both nano and bulk treatments. However, in leaves, CAT activity decreased in NP treatments but remained unaltered with addition of bulk ZnO. In leaves, there was a 61% increase in H2 O2 production with a twofold increase in lipid peroxidation. From this study, it may be concluded that the nano form of ZnO is more toxic than the bulk form under the growth conditions of this study. Phase II was designed to evaluate the toxicological effects of 10% Fe ZnO NPs on green peas at 0, 125, 250, and 500 mg kg--1 concentrations for 25 days in similar soil type and similar growth conditions. Results were compared with that of Phase I. At 500 mg kg--1, zinc bioaccumulation was increased in both root (200%) and stem (31-48%), compared to control, without affecting the iron uptake (p ≤ 0.05). Chlorophyll content and H2O2 production decreased by 27% and ∼50%, respectively (p<0.05), compared to control. Fe ZnO showed less toxicity than that of bare-ZnO NPs under the applied growth conditions as indicated by zinc bioaccumulation, chlorophyll production, and H2O2 production. Therefore, iron doping can be considered as a safer approach to reduce toxicity of ZnO NPs in terrestrial plants. Phase III was focused on phyto-toxicological studies of bare-ZnO NPs, alumina ZnO NPs, and ZnO KH550 NPs on green pea plant, its life-cycle, and seeds. The plants were grown in a greenhouse with continuous supply of nutrients (fertilizer) in the similar 1:1 organic matter enriched soil for 65 days. Upon harvest, different physiological and biochemical parameters, e.g., fresh and dry weights, leaf chlorophyll a, b, leaf carotenoids, zinc bioaccumulation, protein and carbohydrate profiles were measured in different parts of the plant, as applicable. No change in plant fresh and dry weights with treatments were observed, except with ZnO KH550 at 1000 mg kg--1 treatment, which showed about one fold (95%) increase in plant fresh weight compared to control. Plant roots showed a significant increase in Zn accumulation of 5.7x, 5.7x, and 8x treated with 250 mg kg--1 bulk ZnO, bare ZnO NP, and Al2O3 ZnO NP respectively, compared to controls. Similarly, at 1000 mg kg --1, bare ZnO NP and Al2O3 ZnO NP treatments showed significant increases in zinc uptake up to 16x and 36x times compared to controls. Green pea stems showed higher level of Zn accumulation, except with the ionic zinc treatment. The Zn accumulation was in this order: [at 250 mg kg--1 : bulk (5x), bare (7x), doped (4.7x) and coted (7x); at 1000 mg kg --1: bulk (9x), bare (11x), doped (20x) and coted (9x)] compared to control. In leaves, all the treatments (bulk and coated) showed significant increase in zinc uptake (4.6x to 5.3x) except at 250 mg kg--1 and 500 mg kg--1 treatments. The1000 mg kg --1 treatments (bulk, bare, and doped) also showed significant increase in zinc uptake (5.5x to 11x) except for coated and ionic treatments. The aluminum and silicon uptake did not change with one exception at 1000 mg kg--1. Amount of chlorophyll-a (Chl-a) was significantly increased at 250 mg kg--1 alimina doped treatment (4.5x) and in all the treatments at 1000 mg kg--1 [bulk (3.2x), bare (2.7x), doped (3.6x), coted (2.5x), and ionic (2.4x)] compared to control. However, there was no difference in the amount of chlorophyll-b (Chl-b) was observed. The total carotenoid was increased significantly at 250 mg kg --1 to 10x in doped and 7x times in ionic treatment. The increase was 7.6x in bulk and 8.6x in case of doped NPs at 1000 mg kg--1 treatments. (Abstract shortened by UMI.).
机译:该项目分四个阶段完成。在阶段I中,将豌豆植物(P. sativum L.)在富含有机物的土壤中(原生)暴露于0、125、250和500 mg kg--1的10 nm裸露ZnO NPs和大量ZnO中25天。土壤:在生长室中盆栽土壤= 1:1)。从植物生长,叶绿素生成,锌在不同组织中的积累,活性氧/ ROS(H2O2)的产生,胁迫酶活性(过氧化氢酶/ CAT和抗坏血酸过氧化物酶/ APOX)和脂质过氧化方面研究了毒理学效应。在所有ZnO NP浓度下均观察到根伸长降低(48-52%)(p≤0.05);然而,与对照相比,茎长不受影响。与对照相比,用125、250和500 mg kg--1 ZnO NP处理的植物叶片中的叶绿素分别降低61%,67%和77%。批量ZnO处理也显示出相似的结果。在根和叶中,APOX活性在纳米和批量处理中均下降。但是,在叶片中,CAT活性在NP处理中下降,但在添加大量ZnO时保持不变。在叶片中,H2 O2产生增加了61%,脂质过氧化增加了两倍。从这项研究可以得出结论,在本研究的生长条件下,纳米形式的ZnO比整体形式的毒性更大。 II期旨在评估在相似的土壤类型和相似的生长条件下,浓度为0、125、250和500 mg kg--1的豌豆中10%Fe ZnO NPs在25天的毒理作用。将结果与第一阶段的结果进行了比较。与对照相比,在500 mg kg--1时,根部(200%)和茎部(31-48%)锌的生物蓄积均增加,但不影响铁的吸收(p≤0.05) )。与对照相比,叶绿素含量和H2O2产量分别降低了27%和〜50%(p <0.05)。 Fe ZnO在所应用的生长条件下的毒性低于裸露的ZnO NPs,如锌的生物累积,叶绿素生成和H2O2生成所表明的。因此,铁掺杂可以被认为是减少陆地植物中ZnO NPs毒性的更安全方法。第三阶段的重点是对豌豆植物上裸露的ZnO NP,氧化铝ZnO NP和ZnO KH550 NP的植物毒理学研究,生命周期和种子。这些植物在温室中生长,并在相似的1:1有机质富集土壤中连续供应养分(肥料)65天。收获后,在适用的情况下,在植物的不同部位测量了不同的生理和生化参数,例如鲜重和干重,叶绿素a,b,叶类胡萝卜素,锌的生物积累,蛋白质和碳水化合物分布。除用1000 mg kg--1的ZnO KH550处理外,未观察到处理的植物鲜重和干重变化,与对照相比,植物鲜重增加了约一倍(95%)。与对照相比,用250 mg kg--1体积的ZnO,裸露的ZnO NP和Al2O3 ZnO NP处理后,植物根系的锌积累量分别显着增加5.7x,5.7x和8x。同样,在1000 mg kg-1的条件下,与对照组相比,裸露的ZnO NP和Al2O3 ZnO NP处理显示锌吸收显着增加,分别高达16倍和36倍。除离子锌处理外,绿豌豆茎显示出较高的锌积累水平。锌的累积顺序如下:[在250 mg kg--1时:大块(5x),裸露(7x),掺杂(4.7x)和有色(7x);剂量为1000 mg kg -1时:与对照相比为大块(9x),裸露(11x),掺杂(20x)和有色(9x)]。在叶片中,除250 mg kg--1和500 mg kg--1处理外,所有处理(散装和包膜处理)的锌吸收量均显着增加(4.6倍至5.3倍)。除包膜和离子处理外,1000 mg kg -1处理(散装,裸装和掺杂)还显示锌吸收显着增加(5.5倍至11倍)。铝和硅的吸收量没有变化,只有一个例外:1000 mg kg--1。在250 mg kg--1掺杂alimina的处理中,叶绿素a(Chl-a)的量显着增加(4.5x),在所有处理中,在1000 mg kg-1 -1的情况下,[散装(3.2x),裸露(2.7x ),掺杂(3.6倍),带色(2.5倍)和离子(2.4倍)]。但是,没有观察到叶绿素b(Chl-b)的量的差异。总类胡萝卜素在250 mg kg -1时显着增加,在掺杂中为10倍,在离子处理中为7倍。在1000 mg kg--1处理下,掺杂量增加7.6倍,而掺杂NP则增加8.6倍。 (摘要由UMI缩短。)。

著录项

  • 作者

    Mukherjee, Arnab.;

  • 作者单位

    The University of Texas at El Paso.;

  • 授予单位 The University of Texas at El Paso.;
  • 学科 Environmental Sciences.;Chemistry Analytical.;Health Sciences Toxicology.
  • 学位 Ph.D.
  • 年度 2014
  • 页码 141 p.
  • 总页数 141
  • 原文格式 PDF
  • 正文语种 eng
  • 中图分类 语言学;
  • 关键词

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