菰和菖蒲对重金属的胁迫反应及其富集能力

通过盆栽实验研究了Cu—Zn—Ph-Cd复合污染条件下,菰和菖蒲的生长状况、生理特性及吸收和富集重金属的能力。结果表明,高浓度污染下菰和菖蒲不能存活;低、中浓度中菖蒲的生长受到抑制,菰各生长指标与对照相比差异不显著,表明菰对低、中浓度重金属的耐性强于菖蒲。随着污染浓度的增加,菰和菖蒲叶片叶绿索含量显著降低;菰叶绿素a／b值略有降低,菖蒲叶绿素a／b值显著降低;菰和菖蒲叶片脯氨酸含量、相对电导率显著升高,超氧化物歧化酶（SOD）、过氧化物酶（POD）活性在低浓度时升高,中浓度时降低。菰体内重金属含量为Zn〉Cu〉Pb〉Cd,菖蒲体内的含量为Cu〉Zn〉Pb〉Cd,且二者体内的重金属含量都随着污染浓度的增加而升高。菰和菖蒲对Cd的富集系数较大,地上部分（茎与叶）和地下部分（根与根状茎）均大于1;对Pb的富集系数较小,地上部分和地下部分均小于1。菰和菖蒲地下部分重金属含量均高于地上部分含量,二者根系对4种重金属都有较强的滞留效应,平均滞留率均大于50％。各处理中菰对重金属的吸收量均高于菖蒲。综合分析菰和菖蒲的生长、生理及富集重金属的能力,菰比菖蒲更适用于低、中浓度重金属污染水体的生态修复。     

镉在黑藻叶细胞中的亚显微定位分布及毒害效应分析

水生植物被认为能积累和浓缩重金属,本文以不同浓度Cd培养7天的黑藻为材料,研究了Cd的积累,亚细胞分布,亚显微定位,存在形态及对矿质营养吸收,光合速率和呼吸速率的影响,以揭示Cd的植物毒害机理.研究结果表明,随培养液中Cd浓度的增加,植株体内的Cd含量显著上升,富集系数为193-307;不同亚细胞组份中的Cd含量也都呈上升趋势,但分布显著不均,分配顺序依次为细胞壁＞可溶性部分＞细胞器,其中,积累在细胞壁中的含量所占比例呈下降趋势(61.66%-52.00%),而可溶性部分中则递增,细胞器部分结合的Cd含量所占比例相对恒定;硫化物-银法定位结果直观显示出Cd分布在细胞壁、叶绿体、细胞核和液泡中;逐步提取法分析表明受Cd毒害的黑藻体内Cd以不同化学形态存在,其中NaCl提取态占比例最大(55.05%),其他则较少,依次为FNaCl＞FHAc＞FWater＞FEthanol＞FHCl＞FResidue;Cd对黑藻的营养元素吸收也产生影响,主要是促进对Ca,Mn,Cu,Fe的吸收,降低对大量元素P,K的吸收;Cd对黑藻的光合速率和呼吸速率都有较强的抑制作用.结果表明Cd毒害与处理浓度间存在显著的剂量-效应关系;亚细胞分布与对细胞超微结构的损伤关系密切;Cd破坏了黑藻正常生理活动的结构基础和离子平衡,并造成功能紊乱.这些都是Cd对植物产生毒害的重要原因.     

硼在梨树苗不同部位的分布及与其他元素分配的关系

以‘翠冠'梨树苗为试验材料,采用微波消解提取灰分结合等离子发射光谱仪测定法,研究硼(B)添加对梨不同部位B分布及对P、K、Ca、Mg、Fe、Zn、Mn和Cu 8种元素吸收分配的影响.结果表明:‘翠冠'梨不同器官B浓度大小为叶片>根系>茎,随营养液B浓度增加,‘翠冠'梨根、茎、叶B浓度呈增加的趋势,营养液B浓度越高根系B浓度增加幅度越大,不同处理间差异显著.高B处理明显影响‘翠冠'梨苗8种矿质元素在根、茎、叶中的分配.根中P、K、Mg、Zn、Mn和cu浓度随营养液B浓度增加而提高,Ca和Fe浓度随营养液B浓度增加而降低,而转运系数均随B浓度增加而增大;茎中P、Ca、Mg、Zn、Mn和Cu浓度随营养液B浓度增加而提高,K和Fe随营养液B浓度增加而降低,P和K转运系数随B浓度增加而增大,Fe无明显变化,其他元素的转运系数随营养液B浓度增加而降低;叶中P、K、Mn和Cu浓度随营养液B浓度增加而提高,Fe和Zn则相反,而Ca和Mg则先升高后降低,除Zn与Mn外,其他元素的转运系数随营养液B浓度增加而增大.     

镉、铜和锌胁迫下黑藻活性氧的产生及抗氧化酶活性的变化研究

研究了不同Cd、Cu、Zn处理浓度对黑藻体内活性氧()产生及对抗氧化酶(SOD、POD、CAT)活性的分子毒理学效应以探讨高等水生植物抗氧化酶对重金属胁迫的反应。结果表明,三种重金属都不同程度地加快了产生速率;Cu使SOD、POD、CAT活性下降;Cd也都减弱了SOD和POD活性,而CAT活性在0.5—5mg/L处理浓度时增加;Zn对SOD活性也为抑制作用,当浓度为0.5—5mg/L时POD和CAT活性都上升。关联度分析发现Cd、Cu和Zn胁迫下黑藻起主要保护作用的分别为SOD、POD和CAT,而SOD最易受到影响。Cd、Cu处理下的叶绿素含量也都呈下降趋势,而0.5—5mg/L的Zn浓度刺激了叶绿素合成。所有Zn处理、0.5mg/L的Cu处理和0.5—1mg/L的Cd处理的叶绿素a/b值都大于对照值。除了Cu使可溶性蛋白含量减少外,0.5—5mg/L的Zn和0.5—1mg/L的Cd都使其含量增加。综合起来,Cu的毒性最强,其次为Cd,Zn最弱。致死阈浓度分别为:Cu:0.5—1mg/L;Cd:1—2mg/L;Zn:5—6mg/L。SOD是评价重金属对沉水植物毒性效应的灵敏指标。黑藻对水环境Cu污染反应敏感。       

泉州湾河口红树林湿地重金属的分布与迁移

通过测定泉州湾河口湿地2种红树植物(桐花树和秋茄)不同部位(根、枝和叶)及其根际沉积物中重金属酸可提取态含量,探讨该区域重金属元素的分布、在植物不同部位富集和迁移的情况。结果表明:2种红树植物根际沉积物中酸可提取态重金属含量顺序均为FeMnZnPbCuCrNi;秋茄根际沉积物中Cu、Zn、Pb、Ni和Cr两两之间呈正相关,桐花树根际沉积物中Cu与Zn呈正相关,Pb与其他重金属的相关性不显著;2种红树植物根中大多数重金属含量与根际沉积物中重金属酸可提取态含量之间呈正相关,而枝中的相关性不显著;2种红树植物重金属富集的情况较接近,Mn富集系数最大,其次是Cu和Zn;Mn、Cu、Zn、Cr主要富集在叶中,而Pb、Fe、Ni主要富集在根部;2种植物中Mn的迁移能力最强,易于从根部运输到叶中。     

珍稀濒危植物矮牡丹体内矿质元素的研究

采用原子吸收分光光度法测定了矮牡丹体内的10种矿质元素,即K、Mg、Mn、Fe、Ni、Zn、Cu、Cd、Cr、Pb。分析了矿质元素在矮牡丹体内的分布规律及矮牡丹对各种元素的富集能力。结果表明:在不同器官中的矿质元素含量有显著差异, K、Mg、Mn、Ni、Cd、Cr、Pb以叶中为高, Fe、Zn、Cu分别以根、茎、叶柄中含量最高;大多数元素在叶柄中含量最低。矮牡丹对K、Mg、Mn、Fe、Zn有较强的吸收富集能力,一般叶的富集系数较其它器官为高。元素间相关分析表明:Zn、Cd、Cr、Pb、Mn、Fe、Ni、Cu之间有显著的相关性, K、Mg之间的相关性显著。此外,土壤与植物体内元素含量表现出显著的相关性。     

四种重金属胁迫下朝天委陵菜的生长特性及富集能力

通过砂基培养,研究了朝天委陵菜(Potentilla supina)在不同浓度Cd2 、Cu2 、Pb2 、Zn2 胁迫下的生长特性及富集能力.结果表明,朝天委陵菜对Cu2 、Zn2 、Pb2 、Cd2 的耐受性较强,在≤130 mg/L的胁迫下未出现死亡,仅随浓度增大而植株生长减慢;Cu2 的富集量及富集系数为50 mg/L组最大,分别达1 422.91 mg/kg和28.46;Pb2 的富集量及富集系数为70 mg/L组最大,分别达1 148.92 mg/kg和16.41;Zn2 的富集能力较弱,富集系数在1.48～6.33之间;Cd2 的富集量最少,各浓度组富集系数均小于0.1.在砂培条件下,朝天委陵菜对四种重金属的富集能力,各浓度组均为Cu2 ＞Pb2 ＞Zn2 ＞Cd2 ;当Cu2 、Pb2 污染物浓度≤90 mg/L时,朝天委陵菜对Pb2 和Cu2 的富集达到超富集植物的富集水平,可选作Cu2 、Pb2 污染土壤的修复植物;Cu2 、Pb2 污染土壤上生长的朝天委陵菜,因Cu2 、Pb2 含量超标不宜采食或药用.     

镉在水生植物中的富集与亚细胞分布及其化学形态特征

以7种水生植物(长苞香蒲、水生美人蕉、黑藻、粉绿狐尾藻、花叶芦竹、香根鸢尾、水葫芦)为研究材料,构建生物塘系统,通过差速离心法和五步提取法,提取植物各亚细胞组分和不同化学形态的镉,并用原子吸收分光光度法测定镉含量,分析镉在水生植物体中富集特征,揭示植物对镉的耐性机制。结果表明:(1)水生植物根中镉富集量大于茎和叶;3种类型水生植物富集镉能力表现为沉水植物(粉绿狐尾藻、黑藻)浮水植物(水葫芦)挺水植物(长苞香蒲、水生美人蕉、花叶芦竹、香根鸢尾)。(2)镉在黑藻、水葫芦和花叶芦竹中的亚细胞分布量均呈现为细胞壁可溶组分原生质体线粒体,所占比例分别为37.16%~50.86%、20.69%~31.21%、10.81%~23.83%、8.15%~19.83%。(3)赋存化学形态表现为以氯化钠提取态、醋酸提取态为主,所占比例分别为29.37%~56.27%和15.06%~36.19%。研究发现,粉绿狐尾藻、水葫芦、水生美人蕉和花叶芦竹4种植物为富集镉较好的植物,而黑藻、香根鸢尾和长苞香蒲3种植物的镉富集能力相对较弱;镉主要以果胶酸盐、蛋白质结合态或吸附态存在于植物根的细胞壁和液泡中,以减弱镉对根细胞器和植物地上部分的毒害。     

某冶炼厂周围8种植物对重金属的吸收与富集作用

采用野外采样系统分析法,研究了沈阳冶炼厂的8种植物对重金属(Pb、Zn、Cu和Cd)的吸收与富集作用以及可能的耐性机制.结果表明,植物对重金属的吸收和富集,因植物种类、部位及重金属种类而不同.茼麻(Abutilon theophrasti)对Pb的吸收和富集能力较强,小白酒花(Conyza canadensis)、三裂叶豚草(Ambrosia trifida)、酸模叶蓼(Polygonum lapathifolium)、茼麻、龙葵(Solanum nigrum)、绿珠藜(Chenopodium acuminatum)和菊芋(Helianthus tuberosus)对Zn的吸收和富集效果较好,绿珠藜和茼麻对Cu的吸收和富集能力较强,龙葵、绿珠藜、茼麻、酸模叶蓼和小白酒花对Cd的吸收和富集能力较强.这些植物向地上部转移某些重金属的能力很强,转移系数大于1,可用于植物提取方式的污染土壤修复.其他转移系数小于1的植物,适合于重金属污染土壤的植物稳定.     

曼陀罗和苍耳对污染土壤中镉的吸收与富集

目的:研究曼陀罗和苍耳对重金属镉的吸收与富集特征.方法:室外盆栽试验和室内原子吸收测定曼陀罗和苍耳体内的镉含量.结果:土壤中的镉刺激了植物的生长,曼陀罗和苍耳的生物量都比对照有所增加;曼陀罗和苍耳体内的镉含量随土壤中镉浓度的增加而增加;当土壤中镉浓度为100mg·kg-1时,曼陀罗地上部分富集系数为1.15,大于1,而在其它测试浓度下均小于1;苍耳地上部分的富集系数在所有测试浓度下都小于1.结论:曼陀罗和苍耳都不属于镉的超富集植物.     

镉在黑藻叶细胞中的亚显微定位分布及毒害效应分析

Aquatic plants are known to accumulate and bioconcentrate heavy metals. In this study, aquatic vascular plant Hydrilla verticillata (L.f.) Royle was cultivated in water containing elevated concentrations of cadmium (up to 10 mg/L) for 7 d, the accumulation, subcellular distribution, ultrastructural localization, chemical form, toxic effects on mineral nutrient absorption of cadmium, photosynthesis rate and respiration rate were studied. It was found that H. verticillata fronds was able to accumulate cadmium, the bioconcentration factor was 193-307; subcellular fraction analysis revealed that cadmium major accumulated in cell wall (61.66%-52.00%) with decrease trends, the content of Cd enhanced in soluble fraction and remained stable in organelles, with the augment of pollutant concentration. The Cd levels occurred in different parts of leaf cell with the following sequence: cell wall > soluble fraction > organelles. Ultrastructural localization of cadmium with sulfide-silver method showed that Cd appeared in cell wall, chloroplast, nucleus and vacuole. Sequential extraction indicated that the ratio of different cadmium chemical form was different markedly, of which NaCl extractable Cd was predominated as compared with the other 5 forms; which could be seen in the following order: F(NaCl) > F(HAc) >F(Water) > F(Ethanol) > F(HCl) > F(Residue). The mineral nutrient absorption was also affected by cadmium stress, it increased the absorption of Ca, Mn, Cu, and Fe; but reduced that of P and K. Cd had a strong inhibitive effect on photosynthesis rate and respiration rate. The results suggested that the toxic symptoms of plant showed an evident correlation between dose and effect; the ultrastructural damage was closely related to the distribution of Cd. The conclusion could be reached that the death of plant was resulted from destruction of structure foundation of physiological function, unbalance of ion equilibrium and disorder of physiological metabolism.     

Effects of soil acidification on the chemical extractability of Fe,Mn, Zn and Cu and the growth and micronutrient uptake of highbush blueberry plants

Summary The effects of soil acidification and micronutrient addition on levels of extractable Fe, Mn, Zn and Cu in a soil, and on the growth and micronutrient uptake of young highbush blueberry plants (Vaccinium corymbosum L. cv. Blueray) was investigated in a greenhouse study.Levels of 0.05M CaCl₂-extractable Fe, Mn, Zn and Cu increased as the pH was lowered from 7.0 to 3.8. However, the solubility (CaCl₂-extractability) of Fe and Cu was considerably less pH-dependent than that of Mn and Zn. With the exception of HCl-and DTPA-extractable Mn, micronutrients extractable with 0.1M HCl, 0.005M DTPA and 0.04M EDTA were unaffected or raised only slightly as the pH was lowered from 6.0 to 3.8. Quantities of Mn and Zn extractable with CaCl₂ were similar in magnitude to those extractable with HCl, DTPA and EDTA whilst, in contrast, the latter reagents extracted considerably more Cu and Fe than did CaCl₂. A fractionation of soil Zn and Cu revealed that soil acidification resulted in an increase in the CaCl₂- and pyrophosphate-extractable fractions and a smaller decrease in the oxalate-extractable fraction.Plant dry matter production increased consistently when the soil pH was lowered from 7.0 to 4.6 but there was a slight decline in dry matter as the pH was lowered to 3.8. Micronutrient additions had no influence on plant biomass although plant uptake was increased. As the pH was lowered, concentrations of plant Fe first decreased and then increased whilst those of Mn, and to a lesser extent Zn and Cu, increased markedly.     

Effects of liming on the extractability of Fe,Mn, Zn and Cu from a peat medium and the growth and micronutrient uptake of highbush blueberry plants

Summary Levels of extractable micronutrients in a peat and the growth and nutrient uptake of young highbush blueberry plants (Vaccinium corymbosum L cv. Blueray) were studied in a greenhouse experiment in response to liming and two rates of addition of Fe, Mn, Zn and Cu.Levels of extractable micronutrients showed different trends with liming depending upon the extractant used and the element being considered. Levels of 0.05M CaCl₂-extractable Fe, Mn and Zn decreased as the pH was raised whilst those of Cu first decreased and then increased again. There was a general decline in 0.1M HCl-extractable Fe, Mn and Cu with increasing pH but levels of Zn were not greatly affected. Levels of 0.005M DTPA extractable Fe, Mn Zn and Cu generally declined but those extractable with 0.04M EDTA were either unaffected or increased as the pH was raised. Levels of CaCl₂-extractable Mn and Zn were the same order of magnitude as those extractable with HCl, DTPA and EDTA. In contrast, the latter reagents extracted considerably more Fe and Cu than did CaCl₂.Dry matter yields of plants were increased as the pH was raised from 3.9 to 4.3 but then decreased markedly as the pH was raised further to 6.7. With increasing pH, concentrations of plant Fe generally increased those of Mn were decreased and those of Zn and Cu were not greatly affected except for a marked decline in plant Cu at pH 6.7.     

缬氨酸杀虫菊酯的合成

缬氨酸杀虫菊酯是一类很有发展前景的杀虫杀螨剂,它的菊酸部分为Ｒ－构型,菊醇部分为Ｓ－构型,其合成是由相应的缬氨酸或者它的活性衍生物与相应的醇经酯化而制得。具体过程是Ｄ－缬氨酸经６ＮＨＢｒ／ＮａＮＯ２溴化制成（Ｒ）－α－溴代异戊酸,再与对三氟甲基苯胺反应合成（Ｒ）－Ｎ－［（４－三氟甲基）苯基］α－缬氨酸,后被Ｎ－氯代琥珀酰亚胺氯化制成（Ｒ）－Ｎ－［２－氯－４－（三氟甲基）苯基］α－缬氨酸,最后与（Ｓ）－α－氰基－３－苯氧苯基甲醇用ＤＣＣ脱水酯化合成缬氨酸杀虫菊酯Ｉ（Ｒ１＝Ｆ３Ｃ,Ｒ２＝Ｈ,ＣＬ,Ｒ３＝Ｈ）。还给出了两种菊酯２×４种异构体杀虫（烟草夜蛾和家蝇）活性数据。     

5种沉水植物无性繁殖和定居能力的比较研究

 竹叶眼子菜(Potamogeton malaianus)、微齿眼子菜(Potamogeton maackianus)、苦草(Vallisneria spiralis)、穗花狐尾藻(Myriophyllum spicatum)、黑藻(Hydrilla verticillata)是长江中下游湖泊主要的沉水植物。在栽培条件下,它们的无性繁殖速率(单位时间内新增个体数)大小顺序为黑藻>微齿眼子菜>竹叶眼子菜>苦草>穗花狐尾藻。同时采用抛掷实验的方法观察研究了这5种沉水植物及其无性繁殖体的存活和生根情况;完整植株存活率为黑藻>穗花狐尾藻>微齿眼子菜>竹叶眼子菜>苦草,无性繁殖体部分存活率为黑藻>苦草>穗花狐尾藻>微齿眼子菜>竹叶眼子菜。生根能力和其存活时间长短相关,而且生根能力与存活率大小基本一致。在实验中,只有穗花狐尾藻的断枝存活率和生根能力存在差异,故无性繁殖体生根能力为黑藻>苦草>微齿眼子菜>竹叶眼子菜>穗花狐尾藻。     

Effect of salinity on chlorophyll and proline contents in three aquatic macrophytes

The role of proline in imparting tolerance to salinity was investigated in Hydrilla verticillata, Najas indica and Najas gramenia. The plants were exposed to different concentrations of NaCl and artificial sea water (SWS) separately. The chlorophyll (Chl) a/b ratio decreased significantly in all the three plant species in both NaCl and SWS treatments, comparatively more in former than the latter. NaCl resulted in drastic decrease in this ratio in salt sensitive H. verticillata and N. indica, but in somewhat lesser decrease in salt resistant N. gramenia. Proline content increased at both NaCl and SWS treatments, especially at the latter. However, in H. verticillata proline content at 1.5 and 2.5 % NaCl decreased. It was concluded that proline cannot be used as a biochemical marker of salt tolerance in aquatic plants, however, the decrease in Chl a/b ratio in response to NaCl may be used as an index of salt sensitivity in this ecological group of plants. This revised version was published online in August 2006 with corrections to the Cover Date.     

农作物体内铅,镉,铜的化学形态研究

本文报道了农作物体内重金属存在的化学形态。用逐步提取法分析了生长在污染土壤上的水稻、小麦的根与叶。结果表明,在两种作物中,根部的铅以活性较低的醋酸可提取态与盐酸可提取态占优势,而叶中的铅以盐酸可提取态占优势。不论根部或叶部,在各种形态镉中,以氯化钠可提取镉所占比例较高,作用较重要。作物体内的铜活性较强,根部以乙醇可提取态占优势,叶中以水提取态占优势。各种结合形态的重金属迁移能力、毒性效应有显著差异。作物体内重金属化学形态特征与其表观毒性效应有密切联系。     

贵州兴仁煤矿区农田土壤重金属化学形态及风险评估

为了解煤矿区周边农田土壤重金属污染状况,采集了贵州省兴仁县某典型煤矿区农田土壤样品64份,测定了土样中重金属(As、Cr、Pb、Zn、Cd、Hg、Cu、Ni)总量及各形态含量,采用单因子指数法、潜在生态风险指数法(Hkanson法)和风险评估编码法(RAC)对研究区主要土壤利用类型(水稻土、薏米地、植烟土和菜园土)中重金属进行潜在生态风险评估和环境风险评价.结果表明： 不同利用类型土壤中重金属含量除Zn外,其他元素均明显超过贵州省背景值.单因子指数法评价结果表明,As、Pb、Hg和Cu污染较为严重,均属重度污染.形态分析表明,土壤中重金属形态构成差异明显,酸可提取态As、酸可提取态Cd所占比例较高;Cr、Zn、Cu、Ni主要以残渣态为主;Pb主要以可还原态和残渣态为主;而Hg的酸可提取态、可还原态、可氧化态均占有相当比例,三者之和大于55%.重金属可利用度大小顺序为:As(63.6%)>Hg(57.3%)>Cd(56.4%)>Pb(52.5%)>Cu(45.7%)>Zn(32.8%)>Ni(26.2%)>Cr(13.2%).潜在生态风险指数表明,各类型土壤潜在生态风险(RI)〖JP2〗为:菜园土(505.19)>薏米地(486.06)>植烟土(475.33)>水稻土(446.86),均处于较高风险.风险评估编码法结果显示,As在水稻土、薏米地及植烟土中均处于高风险,在菜园土中处于中等风险;Cd、Hg均处于中等风险,Cr、Pb、Zn、Cu和Ni均处于低风险.因此,对该区域农田土壤进行管控时应重点考虑As、Cd和Hg污染.     

铜锈环棱螺对沉积物中重金属的生物积累及其与重金属赋存形态的关系

以铜锈环棱螺（Bellamya aeruginosa）为测试生物,采用28 d沉积物生物积累试验研究铜锈环棱螺对污染河流沉积物中重金属的生物积累,并探讨其与重金属赋存形态的关系.结果表明：铜锈环棱螺肝胰脏对Cd、Pb、Cu、Cr、Zn和Mn均具有较强的积累作用.不同重金属的积累量存在较大差别,Zn的积累量最多,占重金属总积累量的84.32%±4.36%,其次为Cu,占7.67%±2.84%;Pb、Cr和Mn的比例相对较少,分别为3.62%±1.84%、2.22%±1.03%和1.33%±0.15%;Cd所占比例最少,为0.83%±0.53%.肝胰脏中重金属元素之间的相关性均不显著.肝胰脏金属污染指数与沉积物污染综合指数具有显著的正相关关系,铜锈环棱螺可以作为沉积物重金属污染的监测生物.不同沉积物Cd、Cr、Zn和Mn的生物-沉积物积累因子（BSAF）具有较大的差异,Cu和Pb的BSAF比较稳定.Cd的生物积累与沉积物中Cd的可交换的与酸可溶态及可氧化态显著相关;Pb的生物积累与Pb的可还原态显著相关;Cu的生物积累与Cu的可氧化态显著相关;Mn的生物积累与Mn的可交换的与酸可溶态和可还原态显著相关;Cr和Mn的生物积累与其不同形态和总量均不相关.BSAF不宜作为衡量铜锈环棱螺对沉积物中重金属生物积累能力的指标.     

Interaction of phosphorus and molybdenum and the availability of zinc,copper, manganese,molybdenum and phosphorus in waterlogged rice soil

Summary Laboratory incubation experiments were conducted with low-land rice soil to study the effect of applying three different levels of molybdenum (0, 2.5 and 5.0 ppm) and phosphorus (0, 100 and 200 ppm), in all possible combinations, on the changes in available Mo, P, Mn, Zn and Cu in soil. The results showed that application of Mo at both the levels increased the content of extractable Mo and P but decreased those of Cu and Mo in soil whereas application of Mo at higher level only increased the content of extractable Zn in soil. Application of P at both the levels decreased the content of extractable Mo, Mn and Cu but increased that of P whereas it showed an inconsistent effect on the extractable Zn content in soil. The P × Mo interaction effect was found to be beneficial for the content of P, Mo and Zn only. During the initial period of incubation all elements except Cu recorded an increase but with the progress of incubation period the content of all the elements except Mn gradually declined.