三种农作物中镉积累与全硫含量的关系

采用田间试验方法,研究了土壤中镉浓度分别为2和5 mg·kg^-1时,向日葵(Helianthus annuus)、玉米(Zea mays)和大豆(Glycine max)从苗期至成熟期各生长阶段茎叶中镉积累与全硫含量的关系。结果表明,玉米和向日葵各生长时期茎中镉含量与其全硫含量呈极显著相关,叶片中镉含量与硫含量没有相关性,说明硫在植物镉的运输过程中发挥着重要的作用。土壤中镉浓度为2 mg·kg^-1时,籽实中镉含量从高到低的顺序是：向日葵＞大豆＞玉米;土壤中镉浓度为5 mg·kg^-1时,籽实中镉含量从高到低的顺序是：大豆＞向日葵＞玉米,与籽实中硫含量的高低顺序一致;玉米籽实中镉含量最低,在2个镉浓度处理下平均值仅为0.01和0.03 mg·kg^-1,低于国家标准食品中镉限量值。     

镧对镉胁迫下大蒜幼苗生长及镉积累的影响

采用土培实验研究了镧(La²⁺)对镉(Cd)胁迫下大蒜幼苗生长及Cd积累的影响。结果表明：低浓度Cd（＜5 mg·kg^-1）对大蒜生长有微弱的促进作用而高浓度Cd对其有明显抑制作用。外施系列浓度La²⁺对高浓度Cd胁迫下大蒜幼苗生长具有明显的缓解效应,单株鲜重、干重、根长及地上部分高度均具有明显或不同程度的增加。测定结果表明,Cd主要积累在大蒜根部而向地上部分转运的较少,外施系列浓度La²⁺对高浓度Cd胁迫下大蒜幼苗根系对Cd积累具有显著的抑制效应,同时也抑制Cd向地上部分转运。从外施La²⁺对高浓度Cd胁迫下大蒜幼苗生长及大蒜对Cd积累情况来看,La²⁺的适宜缓解效应浓度是在Cd浓度为20 mg·kg^-1时,La²⁺浓度为10～15 mg·kg^-1;在Cd浓度为40 mg·kg^-1,La²⁺浓度为5 mg·kg^-1。     

不同能源柳无性系对土壤镉污染的抗性研究

运为了比较不同能源柳无性系对土壤镉抗性的差异,采用盆栽方法,设置土壤镉含量5个梯度(0、10、20、40、80 mg·kg^-1),以乡土旱柳为对照,对能柳1、能柳2、能柳E、能柳C的扦插幼苗对土壤镉污染的生理生态反应进行了系统测定,分析了不同无性系的抗性。结果显示,低浓度处理（≤20 mg·kg^-1）促进苗木生长,其中能柳2在10 mg·kg^-1处理下根和单株生物量增幅最大,可达到对照的132.0%和120.0%;随着镉浓度的增加,生长量下降,在最高浓度处理下,能柳C生长量降低最少,根、枝、叶和单株生物量分别为对照的86.1%、85.3%、82.9%、84.9%,旱柳的枝、叶生物量降低最多,为对照（无镉）的43.8%、45.0%,而能柳1的根、单株生物量降低最多,仅为对照的36.1%、44.4%;随着镉浓度的增加,不同能源柳无性系叶片的SOD、POD、CAT活性和根系活力基本呈现先升后降的趋势,其中,CAT活性变化较为平缓;关于SOD活性和根系活力,能柳1、能柳2在20 mg·kg^-1时已显著下降,旱柳在40 mg·kg^-1时显著下降,而能柳E、能柳C在40 mg·kg^-1时才显著下降。采用隶属函数对5个无性系在镉胁迫条件下的生长和酶指标进行综合分析,不同无性系对土壤镉污染的抗性顺序为能柳C>能柳2>能柳1>旱柳>能柳E。不同无性系对镉均有抗性,都可在镉污染区推广种植,栽培中,应根据土壤污染和绿化目标,做出适当选择。     

不同区域松蓝根、叶(板蓝根、大青叶)有效成分含量差异

以靛蓝、靛玉红为指标性成分,采用HPLC法对不同生长环境(产地)的板蓝根和大青叶中有效成分进行测定.结果表明,不同产地的板蓝根、大青叶中有效成分含量存在显著差异.板蓝根的有效成分总含量以陕西汉阴为最高(16.27 mg·kg^-1),其次为宁夏隆德(15.67 mg·kg^-1)、安徽亳州（14.90 mg·kg^-1)和安徽临泉(14.23 mg·kg^-1),黑龙江佳木斯最低(13.97 mg·kg^-1 );大青叶中有效成分总含量以陕西汉阴为最高(698.32 mg·kg^-1),其次为宁夏隆德(683.68 mg·kg^-1)、安徽亳州(680.11 mg·kg^-1)和安徽临泉(654.19 mg·kg^-1),黑龙江佳木斯最低(642.73 mg·kg^-1);各产地大青叶HPLC图谱有所差异,不仅表现在指标性成分的峰面积所占比例不同,其成分的种类也存在较大差异.结合产品外观质量和内在品质等因素可以认为,菘蓝地道产区仍需进一步调查分析和确定.     

长柔毛委陵菜对锌的吸收动力学特性

采用水培方法研究了不同Zn处理水平和处理时间下长柔毛委陵菜对锌的吸收动力学特性. 结果表明,在10 mg·L^-1 Zn处理下,植株地上部和根系的Zn含量均在第8天达到最高值,分别为2.49×10³ mg·kg^-1和2.21×10³ mg·kg^-1;在100 mg·L^-1 Zn处理下,植株地上部的Zn含量在第16天达最高值1.23×10³ mg·kg^-1,而根系Zn含量不存在饱和现象. 在0～160 mg·L^-1 Zn处理下,植株叶片和叶柄Zn含量随Zn处理水平的提高显著增加,Zn浓度大于160 mg·L^-1后, 植株叶片和叶柄Zn含量不再随介质中Zn浓度的提高而增加（甚至减少）, 根系含Zn含量与介质中的Zn浓度和培养时间呈正相关,且根系Zn吸收动力学曲线具有二型性,即开始为快速的线性吸收,随后是较缓慢的饱和吸收,两者分界点约在1～2 h,这可能分别与根细胞壁吸附Zn和Zn跨根细胞膜运输有关.     

一种新发现的铜积累植物——密毛蕨

对铜尾矿上生长的密毛蕨(Petridium revolutum)进行了野外调查分析和温室营养液砂培实验.结果表明,密毛蕨所生长的废铜矿土壤中Cu含量平均为2 432 mg·kg^-1 DW,最高达7 554 mg·kg^-1 DW;地上部生物量平均为18.33 g·plant^-1 DW,最高达40.05 g·plant^-1 DW;地上部Cu含量平均为201 mg·kg^-1 DW,最高达567 mg·kg^-1 DW;地下部Cu含量平均为346 mg·kg^-1 DW,最高达1 723 mg kg^-1 DW;密毛蕨对Cu的转移系数平均为0.81,最高达3.88.在营养液砂培的条件下,Cu 7 mg·L^-1处理没有抑制密毛蕨地上部的生长;密毛蕨体内的Cu含量随着介质中Cu浓度的增加而显著增加,但是大部分的Cu积累在地下部.密毛蕨对Cu具有较强的忍耐和较高的积累能力,可作为修复Cu污染土壤的新材料.     

稻鸭共作对甲烷排放的影响

利用密闭箱技术,于2006和2007年研究了稻鸭复合系统CH₄的排放规律及影响因素.结果表明：与常规淹水稻田（CK）相比,由于鸭子的活动,养鸭稻田（RD）的田面水溶解氧浓度(DO)增加,CH₄的排放显著减少.2006年RD的平均CH₄排放通量为（6.84±1.49） mg·m^-2·h^-1,比CK的（10.17±1.25）mg·m^-2·h^-1降低32.7%,CH₄排放总量为（19.34±1.15） g·m^-2,比CK的（26.25±2.17） g·m^-2减少26.3%; 2007年RD的平均CH₄排放通量为(7.68±0.74) mg·m^-2·h^-1,比CK的（9.53±0.40）mg·m^-2·h^-1降低19.0%, CH₄排放总量为（18.41±1.05）g·m^-2,比CK的（22.81±0.75） g·m^-2减少19.3%.在水稻全生育期,各处理CH₄的排放通量分别在分蘖期和抽穗期出现2个排放高峰;CH₄排放通量的季节变化与土壤温度和土壤水溶性有机碳含量呈显著正相关,但与土壤总有机碳含量相关不显著.     

浸种对镉胁迫下油菜种子萌发及幼苗生长的影响

通过水培实验研究了La(NO₃)₃浸种对镉胁迫下油菜（Brassica napus）种子萌发及幼苗生长的影响。结果表明,当镉浓度≤10 mg·L^-1时,La(NO₃)₃浸种（0～50 mg·L^-1）能提高油菜种子的活力,促进油菜幼苗的生长,并提高脂肪酶的活性和幼苗根细胞有丝分裂指数。其中以10 mg·L^-1 La(NO₃)₃浸种处理效果最佳,与对照相比,种子活力指数及油菜幼苗各生长指标显著提高,脂肪酶活性增加40.41%～65.09%,幼苗根细胞有丝分裂指数增加62.76%～77.02%。当镉浓度>10 mg·L^-1时,La(NO₃)₃浸种对镉胁迫的缓解效用明显减 弱,与对照相比,仅脂肪酶活性显著提高,其它指标无明显变化。     

野葛叶片和茎段高频再生体系的建立

探讨几种因子对野葛叶片和茎段高频再生体系建立的影响。采用植物组织培养、正交实验和单因子实验的方法。野葛叶片和茎段的最佳消毒方式为70%酒精处理30 s后再用0.1%HgCl₂处理15 min;野葛叶片愈伤组织诱导的最佳培养基为MS+NAA 1.0 mg·L^-1+2,4-D 2 mg·L^-1,野葛茎段愈伤组织诱导的最佳培养基为MS+NAA 0.5 mg·L^-1+6-BA 1.0 mg·L^-1+2,4-D 2 mg·L^-1;暗培养更有利于野葛愈伤组织的诱导;野葛叶片和茎段愈伤组织诱导的最佳蔗糖浓度均为30 g·L^-1;野葛叶片愈伤组织的最佳出芽培养基为MS+NAA 1.0 mg·L^-1+6-BA 3.0 mg·L^-1,而野葛茎段愈伤组织的最佳出芽培养基为MS+ NAA 0.5 mg·L^-1+KT 2 mg·L^-1;光照培养更有利于野葛叶片和茎段愈伤组织芽的再分化;野葛叶片愈伤组织再生芽生根的最佳培养基为MS+NAA 0.5 mg·L^-1+PP₃₃₃ 0.5 mg·L^-1,而野葛茎段愈伤组织再生芽生根的最佳培养基为MS+NAA 0.5 mg·L^-1+PP₃₃₃ 3.0 mg·L^-1;野葛叶片和茎段愈伤组织再生芽生根的最佳蔗糖浓度均为30 g·L^-1;叶片再生苗移栽的最佳PP₃₃₃浓度为1.0 mg·L^-1,茎段再生苗移栽的最佳PP₃₃₃浓度为3.0 mg·L^-1;叶片和茎段再生苗的最佳移栽基质均为蛭石:珍珠岩（2:1）。     

Cu胁迫对狭叶香蒲体内元素吸收分配的影响

采用水培法,研究了不同浓度Cu²⁺胁迫下狭叶香蒲（Typha angustifolia）体内Cu及其他元素吸收分配的变化。结果表明：狭叶香蒲地上部和根系累积的Cu量均随Cu²⁺浓度升高显著增加;在同一浓度Cu²⁺胁迫下,根中Cu的累积量明显高于地上部。根系同一组织中的Cu百分含量随Cu²⁺浓度的升高均显著增加;同一Cu²⁺浓度下,根系各组织中Cu含量均表现为：中柱>皮层>表皮。低浓度（1和5 mg·L^-1）Cu²⁺对地上部及根中Ca、Mg含量及地上部Mn含量均无显著影响,但高浓度（80和100 mg·L^-1）Cu²⁺可促进植株对Ca的吸收,显著降低对Mg﹑Mn和Zn的吸收。较高浓度（55～100 mg·L^-1）Cu²⁺胁迫后,根系各组织对Ca的吸收增加,对Zn的吸收降低;55～80 mg·L^-1 Cu²⁺胁迫下根系不同组织对Cl和K的吸收增加,但高浓度（100 mg·L^-1）Cu²⁺胁迫下则显著降低。根系累积的Ca、Zn和K主要分配到中柱中,Cl主要分配到皮层中.     

Tissue metallothionein, apoptosis and cell proliferation responses in Atlantic salmon (Salmo salar L.) parr fed elevated dietary cadmium

Atlantic salmon parr were reared for 4 months on experimental diets supplemented with 0 (control), 0.5, 5, 25, 125, or 250 mg Cd x kg(-1) feed to establish a threshold concentration for dietary cadmium exposure by assessing early adaptive cellular responses. At the end of the experiment, the lowest dietary Cd concentration that caused significant accumulation in the gut, kidney and muscle was 5 mg Cd x kg(-1) compared to the control group. Over time, dietary Cd accumulated first in the gut (after 1 month), followed by the kidney (2 months), and later by muscle (4 months). Highest Cd accumulation (100-fold) was found in the gut. A significant increase in regulated cell death and proliferation in salmon fed 125 mg Cd x kg(-1) compared to control fish appeared efficient in preventing gross histopathological damage in the intestine. The highest increase in metallothionein levels was found in the kidney, and metallothionein (MT) levels increased disproportionally to Cd accumulation at increased exposure concentrations. It was concluded that MT was not directly associated with long-term Cd accumulation. Atlantic salmon showed increased metallothionein levels in the kidney at a median effective concentration (concentration of dietary Cd giving 50% of the maximum increase in metallothionein, EC50) of 7 mg Cd x kg(-1), indicating toxic exposure at this concentration.     

Effect of exposure of pregnant rats to cadmium on prenatal and postnatal development of the young

Cadmium chloride in doses of 2, 12 and 40 mg Cd/kg was administered per os to pregnant rats from the 7th to 16th day of pregnancy. In another experiment female rats were exposed to cadmium oxide at a concentration of 0.02 mg Cd/m3 or 0.16 mg Cd/m3 for 5 hours a day and 5 days weekly for a period of 5 months or 1 mg Cd/m3 for 4 months. The exposure was then continued during mating and from the 1st to 20th day of pregnancy. A decrease in fertility was only observed in females exposed by inhalation to cadmium oxide at a concentration of 1 mg Cd/m3, at which concentration cadmium exhibits a considerable toxic effect on the whole organism. The young of females orally treated with CdCl2 in a dose of 40 mg Cd/kg displayed congenital defects in the form of sirenomelia or amelia, as well as raised cadmium levels in tissues. A retardation of intrauterine development manifested by lower body weight and slowed down osteogenesis was observed in the other groups. A cadmium concentration increase was not found in the tissues of the young in these groups. Inhalation exposure to 0.16 mg Cd/m3 of females prior to and during pregnancy induced in their young a decrease in viability, lower body weight gain, prolongation of latency in the negative-geotaxis test, lower locomotor activity and deteriorated development of the conditioned-reflex response. The offspring of females exposed to 0.02 mg Cd/m3 displayed lowered locomotor activity and worsened consolidation of the conditioned-reflex response.     

中华绒螯蟹对Pb和Cd的富集与释放特性

应用生物富集双箱动力学模型模拟了中华绒螯蟹(Eriocheir sinensis)分别在Pb浓度为0.25、0.50、0.75mg/L,Cd浓度为0.025、0.050、0.075mg/L的单一水环境中暴露时,蟹鳃、肝胰腺、肌肉和血淋巴对Pb和Cd的生物富集与释放实验,并通过非线性拟合得到中华绒螯蟹对Pb和Cd的富集速率常数k1、排出速率常数k2、生物富集系数BCF、生物半衰期B1/2、富集平衡时生物体内Pb和Cd含量CAmax等动力学参数。结果表明:(1)中华绒螯蟹对Pb和Cd具有明显的富集,蟹鳃、肝胰腺和肌肉中Pb和Cd的含量与富集时间和水环境中Pb和Cd暴露浓度表现出了很好的正相关,血淋巴在富集阶段没有明显的规律。理论平衡状态下鳃、肝胰腺和肌肉中Pb和Cd含量CAmax随着暴露浓度的增大而增大,且成正相关。(2)Pb和Cd在中华绒螯蟹组织器官中的富集具有选择性,开始实验前,Pb在中华绒螯蟹体内的的分布规律为:肝胰腺>鳃>肌肉>血淋巴;Cd的分布规律为:鳃>肝胰腺>血淋巴>肌肉。在实验浓度的Pb和Cd水环境中暴露16d后,Pb的分布规律为:鳃>肝胰腺>肌肉>血淋巴;Cd的分布规律为:肝胰腺>鳃>肌肉>血淋巴。(3)中华绒螯蟹对Pb和Cd的生物富集和释放都较缓慢。经过16d的生物富集,各组织器官中Pb和Cd的含量均未达到稳态平衡。Pb和Cd在组织器官中的生物富集系数(BCF)范围分别为5-51和6-3148,中华绒螯蟹对Cd的富集能力明显高于Pb(P1/2)范围分别为4-9d和8-57d,中华绒螯蟹对Cd的排出能力明显低于Pb。       

芦竹修复镉汞污染湿地的研究

以湿土盆栽方法研究了芦竹在Cd和Hg污染模拟湿地中的富集能力及其在植株中的分布.结果表明,芦竹在101mg·kg^-1Hg污染环境中生长8个月后,对Hg的富集量是根系>茎>叶片,植物地上部分对Hg富集量为200±20mg·kg^-1DW;而在115mg·kg^-1Cd污染环境中生长8个月后,其对Cd的富集量是叶片>根系>茎,芦竹叶片对Cd的富集量在160±26mg·kg^-1DW.重金属在芦竹各器官内的含量随种植时间的延长而增加,8个月生长期富集量比4个月生长期富集量高30%～50%.芦竹生物富集系数(Bio concentrationfactorBCF)随土壤中重金属含量增加而减小.在污染土壤中,芦竹叶、茎对Hg的BCF为1.9和2.1、对Cd为1.5和0.3;在未受污染的空白对照湿土中(含Hg6.8mg·kg^-1,Cd8.5mg·kg^-1),芦竹叶、茎对Hg的BCF为6.8和12.2,对Cd为7.0和2.7,表明芦竹具有生物量大、根系发达、适应性强等特点,对Cd、Hg有较大富集量和较好的耐受性.     

重金属离子对凡纳滨对虾肝胰脏、鳃丝和血液SOD活力的影响

研究了3种重金属离子(Cu²⁺、Zn²⁺、Cd²⁺)在96 h内对凡纳滨对虾(Litopenaeus vannamei)对肝胰脏、鳃丝和血液超氧化物歧化酶(SOD)活力的影响.结果表明,凡纳滨对虾SOD活力在3种重金属离子作用下随取样时间变化显著(P＜0.0),Cu²⁺在实验浓度范围内(0.1～1 mg·L^-1),肝胰脏、鳃丝和血液的SOD活力随时间延长呈一峰值变化,Zn²⁺在10 mg·L^-1时对肝胰脏表现为显著抑制作用,Cd²⁺在0. mg·L^-1时对肝胰脏和鳃丝起显著抑制作用,0.2 mg·L^-1对鳃丝SOD活力无显著变化(P＞0.0),其他浓度Zn²⁺(＜10 mg·L^-1)、Cd²⁺(＜0.2 mg·L^-1)对各组织器官SOD活力的影响随时间延长均呈现先升高后下降的趋势.3种重金属离子对凡纳滨对虾肝胰脏、鳃丝、血液SOD活力的影响呈现明显的剂量-时间效应关系.其SOD活力大小顺序为肝胰脏＞鳃丝＞血液,3种重金属离子对凡纳滨对虾伤害大小顺序为Cd²⁺＞Cu²⁺＞Zn²⁺.     

Energetics in Atlantic salmon (Salmo salar L.) parr fed elevated dietary cadmium

Atlantic salmon (Salmo salar L.) parr were reared for 4 months on experimental diets supplemented with Cd (0.5, 5, 25, 125, or 250 mg Cd x kg(-1)) to assess the long-term energetic changes based on the digestibility and biochemical deposition of the major dietary nutrients and to evaluate a maximum tolerable dietary toxicant concentration. Growth did not differ significantly (P>0.05) from the control groups. The biochemical composition of the carcass, but not the viscera, was negatively affected by dietary Cd exposure. The significant decreases in protein, lipid, and glycogen concentrations in the carcass (P<0.05, 25 mg x kg(-1) compared to control groups) caused a reduction in calculated whole-body energy content in fish fed 125 mg x kg(-1)compared to control groups. This reduction in calculated whole-body energy content was explained by a concurrent significant disturbance to the gastrointestinal function (measured as reduced digestibility). Only at the highest dietary Cd exposure (250 mg x kg(-1)), increased metabolic costs to cope with Cd toxicity was thought to contribute significantly to the reduction in carcass energy content. The most important factor effecting calculated total energetics was nutrient digestibility. Based on the logarithmic effective median concentration for reduced calculated energy digestibility (dietary Cd concentration corresponding to 50% reduction, EC50), the maximum tolerable dietary Cd concentration is 11 mg x kg(-1) diet.     

Soft-tissue accumulation of lead in the blue tilapia,Oreochromis aureus (steindachner), and the modifying effects of cadmium and mercury

The interaction of mercury and cadmium with lead was investigated by exposingOreochromis aureus to two heavy metals simulataneously. The chronic accumulation prolife of lead was determined by analyzing the liver, brain, gill filaments, intestine, caudal muscle, spleen, trunk kidney, and gonads following exposure to lead alone and in mixtures with mercury and cadmium. Nominal exposure concentrations of lead were 0.05, 0.10, 0.50, and 1.00 mg/L. Mixtures of lead (0.50 or 0.05 mg/L) with cadmium (0.05 mg/L) and lead (0.50 or 0.05 mg/L) with mercury (0.05 mg/L) were also used. Following 140 d of exposure to lead, the highest concentrations of lead consistently accumulated in the trunk kidney. The concentration of lead in the kidney was decreased by coexposure to mercury or cadmium, but increased in the muscle and liver. Under all exposure regimes, the median concentration of lead in the muscle exceeded safety levels recommended for human consumption. In a food fish, such asO. aureus, a knowledge of toxic metal accumulation patterns is of great importance.     

Effects of water chemistry variables on gill binding and acute toxicity of cadmium in rainbow trout (Oncorhynchus mykiss): A biotic ligand model (BLM) approach

This study investigated the short-term (3 h) cadmium binding characteristics of the gills, as well as the influence of various water chemistry variables [calcium, magnesium, sodium, pH, alkalinity and dissolved organic carbon (DOC)] on short-term gill accumulation and acute toxicity of cadmium in juvenile freshwater rainbow trout. The cadmium binding pattern revealed two types of cadmium binding sites in the gill: (i) saturable high affinity sites operating at a low range of waterborne cadmium concentration, and (ii) non-saturable low affinity sites operating at a higher range of cadmium concentration. Among the water chemistry variables tested, only calcium and DOC significantly reduced both gill accumulation and toxicity of cadmium. Interestingly, alkalinity (15-90 mg L(-1) as CaCO(3)) did not influence the gill cadmium accumulation but a significant increase in toxicity was recorded at a higher alkalinity level (90 mg L(-1)). Affinity constants (log K) for binding of competing cations (Cd(2+) and Ca(2+)) to the biotic ligand and for binding of Cd(2+) to DOC were derived separately from the 3 h gill binding tests and the 96 h toxicity tests. In general, the values agreed well, indicating that both tests targeted the same population of high affinity binding sites, which are likely Ca(2+) uptake sites on the gills. These parameters were then incorporated into a geochemical speciation model (MINEQL+) to develop a biotic ligand model for predicting acute toxicity of cadmium in trout. The model predictions exhibited a good fit with the measured toxicity data except for high alkalinity and pH.     

The influence of dietary microbial phytase and calcium on the accumulation of cadmium in different organs of pigs.

A total of 72 barrows (initial body weight 16.7 kg) was used, to evaluate the influence of microbial phytase supplementation alone or in combination with calcium to barley soybean meal diets on the accumulation of cadmium (Cd) in kidney, liver, muscle, brain and bone. The control group received the basal diet with 6 g Ca and a low native Cd concentration of 0.03 mg/kg dry matter (DM). In the experimental groups 2, 3, 4 and 5 dietary cadmium concentration was elevated to 0.78 mg/kg DM. The diet of group 3 was supplemented with 800 U microbial phytase/kg, the diet of group 4 with 6 g Ca/kg. The diet of group 5 contained both supplements. The addition of microbial phytase caused an increase of Cd retention in kidney and liver at 30 and 50 kg body weight. This effect was counteracted by the contemporary addition of calcium. A supplementation of Ca alone showed no effect on the Cd accumulation in kidney and liver. In muscle, brain and bone no effects of phytase and calcium on the accumuLation of Cd could be found.     

龙须草对镉的耐受性和富集特征

利用盆栽试验,研究了龙须草对Cd的耐受能力和富集特征.结果表明:低浓度Cd处理(5 mg·kg-1)能促进龙须草的生长,增强其生理活性,生物量、净光合速率等12个指标比对照提高1.0%～15.5%;高浓度Cd处理(>5 mg.kg-1)对龙须草的生长产生抑制作用,但当Cd浓度达到100 mg.kg-1时,龙须草仍能完成正常的生理周期,生物量、净光合速率仅比对照分别下降27.0%和25.6%.龙须草各器官的Cd含量随Cd污染程度的上升而大幅度增加,根的Cd含量为350～500 mg.kg-1,茎叶为15～35 mg·kg-1.在Cd浓度<50 mg·kg-1时,吸Cd量随添加浓度的增大而增大,茎叶吸Cd量占总吸Cd量的15.7%～38.4%,茎叶与根的吸Cd量比值最高可达0.62.龙须草对Cd污染的耐受性、富集和转运能力均较强,是一种潜在的Cd超富集植物.