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1.
稀土元素的植物生理效应   总被引:97,自引:3,他引:97  
国内外大量研究资料表明,在适宜条件下,稀土对植物的许多生理功能都有积极影响,是植物的有益元素,但尚不能证明它是植物的必需营养元素。本文综合介绍了稀土元素在植物体内的含量、分布,以及对植物萌发、生长、营养代谢、光合作用和抗逆、抗病等生理方面的影响效应,并对其作用机制作了些讨论,以资参考。  相似文献   

2.
稀土元素在植物中的生理效应   总被引:10,自引:0,他引:10  
江玲 《生物学通报》1997,32(2):9-11
稀土元素是元素周期表中57-71的15个镧系元素及与其性质十分相似的抗钇共17种元素的统称,本文概述了稀土元素对改善植物矿质营养、促进植物光合作用,增强植物抗逆性方面的生理效应,还讨论了稀土元素与植物激素间关系。  相似文献   

3.
稀土元素对生物机体剂量效应机理的研究   总被引:3,自引:0,他引:3  
综述了稀土元素对生物机体剂量效应的机理,从稀土对细胞质膜、细胞周期及细胞凋亡、CaM水平调节的作用到对蛋白质、DNA的影响等不同层次和水平进行了探讨,以期为稀土在生物学领域的进一步广泛应用奠定理论基础.  相似文献   

4.
稀土元素生物效应中的Hormesis现象   总被引:20,自引:0,他引:20  
综述了稀土元素在动物、植物和微生物生理、生化过程中的Hormesis现象,并就其机理进行了讨论,以期为进一步弄清稀土元素的生物效应机制提供参考。  相似文献   

5.
稀土元素的生物安全性探讨   总被引:11,自引:0,他引:11  
采用微核检测、单细胞凝胶电泳、同工酶等技术研究了稀土元素遗传毒理效应的有关结果。大量试验表明,稀土元素断裂DNA的能力,因而在一定浓度范围内,稀土元素确有致突变性。稀土元素在土壤中可专性吸附、不可降解,在动植物和人体皆有累积效应,因此稀土元素的生物安全性值得深入探讨。  相似文献   

6.
植物空间诱变的生物效应及其育种研究进展   总被引:34,自引:0,他引:34  
薛淮  刘敏 《生物学通报》2002,37(11):7-9
概述了空间环境对植物的诱变效应及植物空间诱变育种的研究进展,并提出了目前植物空间诱变研究存在的问题及今后的研究方向。  相似文献   

7.
低强度激光生物效应机理研究   总被引:11,自引:0,他引:11  
结合低强度激光生物效应研究的现状,对低强度激光生物效应机理研究的各种观点进行了归纳分析,提出了对低强度激光生物效应机理研究的一些初步思考,把低强度激光生物效应的一般过程归纳为:激光(辐射)→初始光受体→信号传导与放大→生物效应。并指出探讨低强度激光生物效应机理,应着重于寻找并研究初始光受体与激光的相互作用,以及随后的信号传导与放大过程。  相似文献   

8.
酸雨(Acid rain)是当代重大环境污染问题之一。中国已成为继西欧和北美之后的全球第三大酸雨区,酸雨发生面积约120万平方千米,重酸雨发生面积约6万平方千米[1]。同时,中国也是稀土(Rare earth,RE)资源大国,RE对作物具有优质增产的生物学效应且农业经济效益显著[2],一度作为政府行为得到广泛应用。仅2006年,农用稀土达4 800吨(以  相似文献   

9.
稀土元素对生物机体剂量效应的研究   总被引:3,自引:0,他引:3  
综述了稀土元素对生物机体的剂量效应,包括稀土对生物体生长发育、内分泌系统、体内分布及其引发的疾病、细胞毒性及抗诱变、抗癌等影响,以期为稀土在生物学领域的进一步应用提供参考.  相似文献   

10.
叶有华  彭少麟 《生态学报》2011,31(11):3190-3196
概述了国内外露水对植物作用效应争议的两个方面,一是露水有利于促进植物生长,二是露水对植物生长具有负效应。前者主要包括干旱胁迫下植物生长重要的水资源、调节植物体内水分、改善土壤水分平衡、调节森林植物生长环境、有利于农作物管理及其病虫害防治等生态效益;后者包括导致植物发病、降低植物产量和质量等。文章还指出了露水对植物作用效应研究存在的问题,并提出了今后研究的方向:(1)露水对植物作用效应的机理研究;(2)干扰条件下露水对植物作用效应研究包括酸露对植物作用效应研究和城市热岛条件下露水对植物作用效应研究;(3)露水对植物多样性的影响研究;(4)露水在生物防治中的应用研究。  相似文献   

11.
Distribution pattern of rare earth elements in fern   总被引:1,自引:0,他引:1  
All the lanthanide elements (REE) in fern (Matteuccia) and in soil were determined with inductively coupled plasma mass spectrometer (ICP-MS) in order to discuss REE behavior in fern. The fern sample was divided into three parts: root, stem, and leaf; the soil of the same site was also sampled and the soil sample was divided into two parts: HCl and HNO3 soluble part (soil[HCl]) and HF soluble part (soil[HF]). REE in each part was determined by ICP-MS after solvent extraction separation. The overall variation of the REE pattern of the root does not resemble that of the whole soil, but that of the HF soluble part. A tetrad effect variation (W-type) was found in the REE patterns of root, stem and leaf; more conspicuous tetrad effect variation was observed in HREE region than in LREE region, and was so in stem and leaf than in root. Negative anomalies of Ce were observed in the REE patterns of root, stem and leaf, with bigger anomalies in stem and leaf than in root. The results of this study suggest that REE in fern has come from silicates of soil and has once been in dissolved state.  相似文献   

12.
稀土对蚯蚓体内氨基酸含量的影响   总被引:4,自引:1,他引:4  
采用滤纸接触染毒法,分别进行了氯化稀土、氯化镧与土居动物蚯蚓接触染毒不同时间和不同浓度的试验。研究其对蚯蚓体内氨基酸含量的影响变化。结果表明。Re、La对蚯蚓体内的氨基酸含量影响较显著,在低浓度时总体表现为促进蚯蚓体内氨基酸的形成,而在高浓度状态下则使蚯蚓体内氨基酸含量下降,产生抑制作用,两种稀土在400mg·L^-1浓度时,蚯蚓体内氨基酸含量除脯氨酸外开始上升,随着作用时间延长,氨基酸含量逐渐下降,在100~1200mg·L^-1浓度范围,两种稀土均引起蚯蚓体内脯氨酸含量的下降,产生抑制作用。  相似文献   

13.
The concentrations of rare earth elements (REs) in atmospheric particles, soil, soil water, surface runoff, and different parts of corn in an experimental plot in the suburb of Beijing, China were measured and the flux of REs was estimated. The concentration of REs in air particles with diameter less than 10 μm is 36 ng/m3 and, by ratio analysis, the origin of REs in the atmosphere was likely local soil. The concentration of soluble REs is 0.69 μg/L in rainwater, 5–7 μg/L in surface runoff, as well as 1–4 μg/L in soil water and the application of RE mixture has no observed influences on their concentrations. The concentration of soluble REs in surface runoff and soil water was dominated by aqueous-solid-phase partitioning. By estimation of the flux, most of the REs applied will remain in the soil phase and continued application of REs will cause an accumulation of REs in agricultural soil.  相似文献   

14.
稀土元素对土栖动物群落结构的影响及对蛴螬的生态毒性   总被引:4,自引:0,他引:4  
采用土施法和OECD推荐的滤纸接触法研究了稀土(ReCl3·6H2O)对豆田土栖动物群落结构的影响以及稀土对蛴螬的生态毒性.结果表明,对照与各处理之间动物种类数、主要动物种群数量、多样性指数差异均不显著;急性和慢性毒性试验表明,对照与各处理间的死亡率差异不显著.在稀土有效施用范围内,稀土对蛴螬的生态毒性很小,不会明显改变蛴螬种群结构.  相似文献   

15.
在试验生态小区的土壤中 ,模拟长期使用稀土 ,以探讨稀土积累与油菜菌核病发生发展的关系 .结果表明 ,0 .5 %、1%、3%、5 %、7%、10 %吸附容量和 0 6kg·hm-2 的稀土以及土壤中 30kg·hm-2 和 0 6kg·hm-2 的稀土复合肥添加剂对油菜菌核病自然发生的病情指数和病株率影响无显著差异 ;对人工接种发病后的病斑绕茎度、病斑扩展速率、单株平均产量和千粒重的影响也无显著差异  相似文献   

16.
稀土元素对谷氨酸发酵的影响   总被引:1,自引:0,他引:1  
通过对谷氨酸发酵培养基中添加稀土元素的研究,确定了几种能对发酵产酸有提高作用的稀土元素及其浓度,其中La^3 、Ce^4 、Nd^3 离子浓度分别为100mg/L、10mg/L、1mg/L时能提高产酸水平,而Sm^3 、Y^3 离子对发酵基本上没有影响。  相似文献   

17.
Fractionations of rare earth elements (REEs) and their mechanisms in soybean were studied through application of exogenous mixed REEs under hydroponic conditions. Significant enrichment of middle REEs (MREEs) and heavy REEs (HREEs) was observed in plant roots and leaves respectively, with slight fractionation between light REEs (LREEs) and HREEs in stems. Moreover, the tetrad effect was observed in these organs. Investigations into REE speciation in roots and in the xylem sap using X-ray absorption spectroscopy (XAS) and nanometer-sized TiO2 adsorption techniques, associated with other controlled experiments, demonstrated that REE fractionations should be dominated by fixation mechanism in roots caused by cell wall absorption and phosphate precipitation, and by the combined effects of fixation mechanism and transport mechanism in aboveground parts caused by solution complexation by intrinsic organic ligands. A conceptive model was established for REE fractionations in plants based on the above studies.  相似文献   

18.
Fractionations of rare earth elements (REEs) and their mechanisms in soybean were studied through application of exogenous mixed REEs under hydroponic conditions. Significant enrichment of middle REEs (MREEs) and heavy REEs (HREEs) was observed in plant roots and leaves respectively, with slight fractionation between light REEs (LREEs) and HREEs in stems. Moreover, the tetrad effect was observed in these organs. Investigations into REE speciation in roots and in the xylem sap using X-ray absorption spectroscopy (XAS) and nanometer-sized TiO2 adsorption techniques, associated with other controlled experiments, demonstrated that REE fractionations should be dominated by fixation mechanism in roots caused by cell wall absorption and phosphate precipitation, and by the combined effects of fixation mechanism and transport mechanism in aboveground parts caused by solution complexation by intrinsic organic ligands. A conceptive model was established for REE fractionations in plants based on the above studies.  相似文献   

19.
在我国施用稀土时间最长的黑龙江省花园农场,研究比较了施用稀土12 a和不施稀土的对照处理上小麦和土壤中的稀土元素的分布、累积及运移.结果表明,长期叶面喷施稀土并未造成耕层土壤和下部土层的稀土元素的累积.成熟期小麦植株各部位的稀土元素含量顺序为根>叶>茎、壳;稀土元素主要累积在根部,其次是叶,茎和壳累积较少.喷施处理小麦根部的稀土元素累积量高于对照,叶部也有此趋势,而茎、壳等部位差异不大.根、茎、叶、壳稀土元素分布模式与土壤中相似,与施用的常乐稀土差别较大;长期喷施稀土未曾造成籽粒中稀土元素的明显累积.  相似文献   

20.
混合稀土对作物出苗率的影响   总被引:15,自引:0,他引:15  
用OECD方法,在红壤、黄潮土、黄褐土上进行了混合稀土对水稻、油菜、大豆相对出苗率影响的试验,从LC50(半致死浓度)值看,在供试条件下,稀土对水稻的毒性最小,稀土在黄褐土上对作物的毒性也较小,而稀土对黄潮土上的大豆以及红壤上的油菜的毒性则较大。  相似文献   

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