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1.
采用盆栽实验,研究了海泡石、酸改性海泡石以及二者与磷酸盐联合使用对镉铅复合污染稻田土壤的钝化修复效果,并通过培养实验和重金属形态分析探讨了不同钝化剂处理的作用机理。结果表明:添加海泡石可以显著提高污染土壤pH值,而磷酸盐和改性海泡石则对土壤pH值无显著影响。钝化处理能显著降低土壤TCLP提取态Cd、Pb的质量分数,最大降低率分别可达23.3%和47.2%,钝化剂复配处理对土壤TCLP提取态重金属的抑制效果优于单一处理。施用海泡石和磷酸盐,通过提高土壤pH值、物理化学吸附以及生成矿物沉淀等作用,可以促进污染土壤中的Cd、Pb由活性高的交换态向活性低的残渣态转化,从而显著降低Cd、Pb的生物有效性和迁移能力。添加钝化剂可以显著提高水稻各部位的产量,稻谷和稻草的最大增产率分别为34.3%和26.6%;钝化剂复配处理对水稻的增产作用明显优于单一处理。施用钝化剂可以显著降低水稻各部位的Cd、Pb质量分数,最大可使精米的Cd、Pb质量分数分别降低35.8%和40.9%,钝化剂复配处理对水稻吸收Cd、Pb的抑制作用明显优于单一处理,海泡石和磷酸盐复配处理中精米的Cd、Pb质量分数符合国家食品卫生标准要求。综合分析不同钝化处理的增产作用、降低作物Cd、Pb吸收以及土壤Cd、Pb可迁移性的作用可知,海泡石与磷酸盐复配处理对稻田土壤Cd、Pb复合污染的钝化修复效果最佳。  相似文献   

2.
A pot experiment was conducted to evaluate the effectiveness of sepiolite-induced immobilisation remediation of Cd contaminated soil. The results demonstrated that adding sepiolite significantly increased the soil pH and resulted in 35.1–66.0%, 30.3–48.9%, and 31.6–51.6% reduction in toxicity characteristic leaching procedure of Cd (TCLP-Cd), respectively, for the Cd levels of 1.25, 2.5, and 5?mg/kg compared with the no-sepiolite controls. These decreases in TCLP-Cd were associated with reductions in plant phyotoxicity and Cd absorption, and sepiolite-treated soils resulted in increases of 3.2–38.0%, 34.2–52.3%, and 8.4–51.5% in shoot biomass, respectively, and in decreases of 26.7–39.6%, 17.3–28.5%, and 6.1–21.8% in shoot Cd contents, respectively, under soil Cd concentration of 1.25, 2.5 and 5?mg/kg compared to the unamended soils. The greater microbial biomass and catalase and urease activities after applying sepiolite implied a certain degree of recovery in metabolic function recovery during soil remediation. These results demonstrated that the application of sepiolite not only was effective at reducing Cd bioavailability and the rate of Cd accumulation in plants, but also improved soil environmental quality.  相似文献   

3.
Concentrations of heavy metals (Pb, Zn, Cd, Cu) were determined in soils and vegetables (chrysanthemum, spinach and four cultivars of Chinese cabbage from the area adjacent to a Pb/Zn mine in Shaoxing, Zhejiang province, China, and compared with the Chinese National Standards for Soil Environmental Quality. The accumulation of heavy metals in cabbage cv. Siyuegreen was investigated at different distances from the center of the mine. The vegetable plantation soils were polluted with Pb, Cd, Cu and Zn, especially by Pb and Cd. The levels of Pb and Cd were 20 and 30 times higher than the permitted standards, indicating that this Pb/Zn mining area is unsuitable for agricultural use. Chinese cabbage, chrysanthemum and spinach had different enrichment coefficients. The enrichment coefficient of Cd from soil to roots of chrysanthemum was >80% and from roots to leaves of cabbage cv. Shanghaigreen was >120%. These vegetables were polluted by heavy metals and could not be regarded as safe for human consumption. Environmental accumulation of heavy metals in the vegetable plantation soils was proportional to heavy metal accumulation in vegetables and both were inversely proportional to the distance from the lead/zinc mine.  相似文献   

4.
The current study investigated the effects of nano-silicon (Si) and common Si on lead (Pb) toxicity, uptake, translocation, and accumulation in the rice cultivars Yangdao 6 and Yu 44 grown in soil containing two different Pb levels (500 mg·kg−1 and 1000 mg·kg−1). The results showed that Si application alleviated the toxic effects of Pb on rice growth. Under soil Pb treatments of 500 and 1000 mg·kg−1, the biomasses of plants supplied with common Si and nano-Si were 1.8%–5.2% and 3.3%–11.8% higher, respectively, than those of plants with no Si supply (control). Compared to the control, Pb concentrations in rice shoots supplied with common Si and nano-Si were reduced by 14.3%–31.4% and 27.6%–54.0%, respectively. Pb concentrations in rice grains treated with common Si and nano-Si decreased by 21.3%–40.9% and 38.6%–64.8%, respectively. Pb translocation factors (TFs) from roots to shoots decreased by 15.0%–29.3% and 25.6%–50.8%, respectively. The TFs from shoots to grains reduced by 8.3%–13.7% and 15.3%–21.1%, respectively, after Si application. The magnitudes of the effects observed on plants decreased in the following order: nano-Si treatment>common Si treatment and high-grain-Pb-accumulating cultivar (Yangdao 6)>low-grain-Pb-accumulating cultivar (Yu 44) and heavy Pb stress (1000 mg·kg−1)>moderate Pb stress (500 mg·kg−1)>no Pb treatment. The results of the study indicate that nano-Si is more efficient than common Si in ameliorating the toxic effects of Pb on rice growth, preventing Pb transfer from rice roots to aboveground parts, and blocking Pb accumulation in rice grains, especially in high-Pb-accumulating rice cultivars and in heavily Pb-polluted soils.  相似文献   

5.
矿冶区周边水稻对不同来源重金属污染的指示作用   总被引:4,自引:1,他引:4  
有色金属开采与冶炼可对周边环境造成严重的重金属污染,查明重金属污染来源对于矿冶周边重金属污染管理与控制具有重要意义.为探索利用矿冶周边水稻对As、Cd、Pb、Zn和Cu的富集与水稻体内元素的含量平衡特征指示重金属污染来源的可行性,选择了我国著名的水口山Pb-Zn矿山开采与冶炼周边区,根据重金属污染排放和迁移扩散特征,结合当地气象和地貌条件,确定了3个典型采样区,其中两个采样区分别邻近冶炼厂和尾砂库,另一处为位于两者之间的过渡区.采用蛇形采样法在稻田内采集33个成熟水稻及土壤样品,分析水稻不同部位(包括根、茎叶、籽粒)及土壤中As、Cd、Pb、Zn、Cu5种重金属和其他16种元素的含量.结果表明,3个采样区之间土壤中的As、Cd、Pb、Zn和Cu含量均存在显著性差异;各采样区水稻中除根际和籽粒中Cd含量外,各部位重金属含量也均有显著差异.靠近冶炼厂的水稻茎叶中As、Pb含量高于离冶炼厂较远的采样区水稻茎叶.尽管As、Pb在靠近尾砂库采样区土壤中含量最高,但在该区水稻茎叶中的含量却最低;在除As、Cd、Pb、Zn、Cu5种重金属以外的其他16种元素中,水稻根部仅有5种元素含量在各采样区之间存在差异,指示相同的土地利用类型及土壤母质条件;而在茎叶和籽粒中则分别有多达11和10种元素含量出现采样区差异,指示重金属污染来源影响水稻茎叶及籽粒中元素的含量平衡.多元统计分析结果显示,3个采样区水稻茎叶中元素含量平衡存在显著的分异,显示出明显的采样区属性.结合采样区域空间位置、污染物来源、水稻对重金属的富集与转运特征分析,3个采样区重金属主要污染特征可分别确定为水-气混合来源型、大气来源型和尾砂来源型.论文结果证明利用水稻茎叶指示矿冶周边重金属污染来源是可行的.  相似文献   

6.
It is unclear whether certain plant species and plant diversity could reduce the impacts of multiple heavy metal pollution on soil microbial structure and soil enzyme activities. Random amplified polymorphic DNA (RAPD) was used to analyze the genetic diversity and microbial similarity in planted and unplanted soil under combined cadmium (Cd) and lead (Pb) pollution. A metal hyperaccumulator, Brassica juncea, and a common plant, Festuca arundinacea Schreb, were used in this research. The results showed that microorganism quantity in planted soil significantly increased, compared with that in unplanted soil with Cd and Pb pollution. The order of microbial community sensitivity in response to Cd and Pb stress was as follows: actinomycetes>bacteria>fungi. Respiration, phosphatase, urease and dehydrogenase activity were significantly inhibited due to Cd and Pb stress. Compared with unplanted soil, planted soils have frequently been reported to have higher rates of microbial activity due to the presence of additional surfaces for microbial colonization and organic compounds released by the plant roots. Two coexisting plants could increase microbe population and the activity of phosphatases, dehydrogenases and, in particular, ureases. Soil enzyme activity was higher in B. juncea phytoremediated soil than in F. arundinacea planted soil in this study. Heavy metal pollution decreased the richness of the soil microbial community, but plant diversity increased DNA sequence diversity and maintained DNA sequence diversity at high levels. The genetic polymorphism under heavy metal stress was higher in B. juncea phytoremediated soil than in F. arundinacea planted soil.  相似文献   

7.
This study was focused on determining Arsenic (As), Lead (Pb), Cadmium (Cd) and Zinc (Zn) in 33 indigenous plants and 12 soil in-situ plant samples in Thai Nguyen Province, Vietnam. The results showed that the soils of surveyed mining areas contained 181.2- 6754.3 mg kg(-1) As, 235.5-4337.2 mg kg(-1) Pb, 0.8- 419 mg kg(-1) Cd and 361.8-17565.1 mg kg(-1) Zn depending on the characteristics of each mining site. These values are much higher than those typical for normal soil. The heavy metal uptake into shoots and roots of 33 indigenous plant species was also determined. Two species of the plants investigated, Pteris vittata L. and Pityrogramma calomelanos L. were As hyperaccumulators, containing more than 0.1% heavy metals in their shoots. Eleusine indica L., Cynodon dactylon L., Cyperus rotundus L. and Equisetum ramosissimum (Vauch) accumulate very high Pb (0.15-0.65%) and Zn (0.22-1.56%) concentration in their roots. Additional experiments to clarify the potential of six these plants as good candidates for phytoremediation of heavy metal pollution soil are being carried out in our laboratory.  相似文献   

8.
This paper studied the relationship between heavy metal concentrations of herbaceous plants and soils at four Pb-Zn mining sites in Yunnan, China. 50 herbaceous plant samples of 9 plant species from 4 families and 50 soil samples were collected and then ana1yzed for the tota1 concentrations of Pb, Cd, and Zn. The results showed that the average concentrations of Pb, Cd, and Zn in soil samples were 3772.83, 168.81, and 5385.65 mg/kg, respectively. The average concentrations of Pb, Cd, and Zn were 395.68, 28.14, and 1664.20 mg/kg in the shoots, and 924.12, 57.25, and 1778.75 mg/kg in the roots, respectively. Heterospecific plants at the same site and conspecific plants at various sites had different average levels of Pb, Cd, and Zn, both in the shoots and the roots. Enrichment coefficients of Pb, Cd, and Zn were greater than 1 in 2, 3, and 9 herbaceous plant samples, respectively. Translocation factors of Pb, Cd, and Zn were greater than 1 in 10, 17, and 25 herbaceous plant samples, respectively. In all 50 samples, the concentrations of Pb, Cd, and Zn between the shoots and the roots, the shoots, and the soils, and the roots and the soils had significant positive relationships.  相似文献   

9.
壳聚糖辅助下玉米修复铅污染土壤能力的研究   总被引:3,自引:0,他引:3  
为了研究壳聚糖辅助下玉米(ZeamaysL.)对铅污染土壤的修复能力,采用L9(34)正交试验进行研究,考虑了4因素3水平,4因素为土壤铅含量、壳聚糖含量、壳聚糖溶液pH值以及加入壳聚糖后的提取时间.研究结果表明,加入壳聚糖会造成玉米生长停滞,甚至死苗,原因在于壳聚糖属于天然高分子有机物,会造成土壤板结,阻碍植物吸收水分,同时壳聚糖将土壤中的大量重金属溶出,造成玉米重金属中毒.加入壳聚糖后,玉米对铅的吸收较对照结果有很大提高,壳聚糖能够促进铅元素从土壤向植物体内转移,但壳聚糖促进铅元素从玉米地下部分向地上部分转移的能力较弱;综合壳聚糖的促进效果,在土壤铅含量为1.8g·kg-1,壳聚糖含量为5mmol·kg-1(土),壳聚糖溶液pH值为4.5,提取时间为7天的条件下,有利于促进铅在玉米地上部分的吸收.  相似文献   

10.
Heavy metals and soil microbes   总被引:1,自引:0,他引:1  
Heavy metal pollution is a global issue due to health risks associated with metal contamination. Although many metals are essential for life, they can be harmful to man, animal, plant and microorganisms at toxic levels. Occurrence of heavy metals in soil is mainly attributed to natural weathering of metal-rich parent material and anthropogenic activities such as industrial, mining, agricultural activities. Here we review the effect of soil microbes on the biosorption and bioavailability of heavy metals; the mechanisms of heavy metals sequestration by plant and microbes; and the effects of pollution on soil microbial diversity and activities. The major points are: anthropogenic activities constitute the major source of heavy metals in the environment. Soil chemistry is the major determinant of metal solubility, movement and availability in the soil. High levels of heavy metals in living tissues cause severe organ impairment, neurological disorders and eventual death. Elevated levels of heavy metals in soils decrease microbial population, diversity and activities. Nonetheless, certain soil microbes tolerate and use heavy metals in their systems; as such they are used for bioremediation of polluted soils. Soil microbes can be used for remediation of contaminated soils either directly or by making heavy metals bioavailable in the rhizosphere of plants. Such plants can accumulate 100 mg g?1 Cd and As; 1000 mg g?1 Co, Cu, Cr, Ni and 10,000 mg g?1 Pb, Mn and Ni; and translocate metals to harvestable parts. Microbial activity changes soil physical properties such as soil structure and biochemical properties such as pH, soil redox state, soil enzymes that influence the solubility and bioavailability of heavy metals. The concept of ecological dose (ED50) and lethal concentration (LC50) was developed in response to the need to easily quantify the influence of pollutants on microbial-mediated ecological processes in various ecosystems.  相似文献   

11.
Changes in soil pH, soil heavy metal forms, and the metabolic diversity of microbial communities were examined in soil samples collected in 1-mm increments from barley roots in soil contaminated with cadmium (Cd) and zinc (Zn) using a rhizobox system. Concentrations of exchangeable Cd and Zn increased near the roots owing to a decrease in soil pH. Conversely, the concentration of inorganically bound Cd and Zn decreased near the roots. Despite having the highest concentration of the most toxic exchangeable metals, the rhizosphere also had the highest bacterial and fungal metabolic activity and diversity when assessed using BIOLOG plates. Therefore, the promoting effects of root exudates on microbial activity could outweigh the adverse effects of Cd and Zn on microorganisms in the rhizosphere.  相似文献   

12.
广西刁江流域Cd和Pb复合污染稻田土壤的钝化修复   总被引:12,自引:0,他引:12  
采用田间小区试验,研究施用海泡石、石灰和磷酸盐对广西刁江流域Cd和Pb复合污染稻田土壤的钝化修复效应,并通过土壤重金属形态分析探讨不同钝化剂的作用机理。结果表明,添加钝化剂可显著提高稻谷和秸秆产量,最大增产率分别可达25.4%和28.3%,其中海泡石与磷酸盐复配处理增产效果最佳。施用钝化剂可以有效降低水稻各部位重金属含量,水稻糙米Cd和Pb含量最大降幅可达65.12%和61.86%;钝化剂复配处理对水稻地上部Cd和Pb含量的降低效果明显优于单一处理,其中海泡石和磷酸盐或石灰复配处理糙米cd含量符合GB2762--2005《食品中污染物限量》。不同钝化处理均能显著降低土壤TCLP(毒性特性浸出程序)提取态cd和Pb含量,最大降幅分别为28.86%和45.60%,其中钝化剂复配处理对土壤TCLP提取态重金属的抑制效果优于单一钝化处理。总体而言,海泡石与磷酸盐复配处理对广西刁江流域重金属复合污染稻田土壤的钝化修复作用最佳。  相似文献   

13.
滩涂围垦土壤是重金属等难降解污染物的主要最终归宿场所之一,其重金属的解吸将影响重金属的迁移性、生物有效性和潜在毒性,研究重金属的解吸对土壤污染评价、修复及环境容量预测至关重要.研究了烟气脱硫石膏对广州市南沙滩涂围垦土壤重金属的解吸效果,并分析了烟气脱硫石膏对重金属形态的影响.在离心管中称取20.0 g过0.25mm筛土样,加入20 mL水和不同量的烟气脱硫石膏,在室温下于恒温振荡器振荡,风干研碎后用原子吸收分光光度法测定重金属全量,并用Tessier连续提取法研究了处理前后重金属形态变化.研究结果表明,随着脱硫石膏施用量的增加,经过振荡离心后的滩涂围垦土壤中重金属质量分数先急剧下降,之后变化趋于平缓.与原土相比各重金属最大解吸率分别为:Cd 30.38%,Cu17.73%,Ni 15.00%,Zn 14.19%,Pb 9.46%,Cr 8.89%.比较处理前后重金属的形态变化,发现各重金属的可交换态解吸率均达50%以上,并且重金属碳酸盐结合态质量分数也有减少.说明烟气脱硫石膏能降低土壤对重金属的吸附,经振荡离心后能降低土壤中重金属的毒性和生物可利用性.  相似文献   

14.
The immobilisation of heavy metals in the soil of a 25-year-old active firing range using durian (Durio zibethinus L.) tree sawdust (DTS), coconut coir (CC) and oil palm empty fruit bunch (EFB) was investigated. The immobilisation effects were evaluated in terms of metal accumulation in water spinach (Ipomoea aquatica) and soil metal bioavailability. A pot experiment was conducted by amending the firing range soil with DTS, CC and EFB at application rates of 0%, 1% and 3% (w/w), respectively. All amendments increased the biomass yield and reduced the uptake of heavy metals in the plant tissue. Zn had the highest values of Bioconcentration Factor (BCF: 0.301–0.865) and Translocation Factor (TF: 1.056–1.883). Pb was the least-accumulated and transported metal in the plant tissues, with the BCF and TF values of 0.019–0.048 and 0.038–0.116, respectively. The bioavailable fraction of heavy metals in the firing range soil decreased following the application of the three agricultural wastes studied. DTS, CC and EFB did not cause toxicity symptoms in the water spinach over the pot experiment. Therefore, DTS, CC and EFB are considered promising immobilising agents for the remediation of metal-contaminated land.  相似文献   

15.
长期受到重金属铅(Pb)和镉(Cd)污染的土壤生态危害指数较高,土壤微生物群落结构容易受到重金属的影响,重金属对土壤微生物的毒性与重金属的生物利用度直接相关。以白银市重金属污染土壤为样本,分析了土壤的理化性质、重金属Pb和Cd的污染状况及土壤微生物群落结构,探究它们之间的关联性。样本采自距离污染中心由近及远的4个位置(分别命名为S1、S2、S3和S4)。采用Hakanson指数法来评估该地重金属生态风险;选用改进的BCR顺序提取法分析Pb与Cd的组分分布情况;利用SPSS和Canoco 4.5对土壤性质、重金属和细菌群落进行相关性分析和冗余分析,探究微生物群落结构与土壤性质和重金属污染之间的相关性。结果表明:白银市该处重金属污染场地3 km以内的土壤均受到严重的Pb、Cd污染。Pb主要以弱酸可提取态和可还原态的形式存在于土壤中,Cd则以弱酸可提取态为主;土壤重金属的危害生态指数均已经达到极高污染风险程度,且危害程度S1>S3>S2>S4;微生物丰度和多样性可能受到土壤性质及重金属的共同影响,与Pb、Cd的污染程度大致呈负相关(S2相似文献   

16.
水库疏浚底泥农用对芥菜生长和品质的影响   总被引:1,自引:0,他引:1  
疏浚底泥重金属污染是限制底泥农用的主要因素。采用土培盆栽试验,研究了底泥与土壤按不同质量比混合,对芥菜生物量、重金属、硝酸盐、维生素C(Vc)、以及可溶性糖含量的影响;并研究了m(底泥):m(土壤)=2:1时,施加20mg·kg-1的碳酸钙对土壤有效态重金属含量影响,以及对芥菜生物量和品质的影响。结果表明:加入水库底泥可以显著促进芥菜的生长,随着底泥加入比例的增加,芥菜地上部生物量表现出先上升后降低的趋势,以m(底泥):m(土壤)=2:1芥菜地上部生物量最高,是对照的1.71倍。底泥处理均能显著地增加芥菜地上部重金属含量,其中以全底泥处理芥菜地上部鲜质量Zn、Cd质量分数最高,分别是53.3、0.595mg·kg-1,是食品卫生标准的2.67、2.98倍。施用底泥可以提高芥菜地上部Vc、降低其硝酸盐含量。在m(底泥):m(土壤)=2:1的土壤上,施入20mg·kg-1的碳酸钙处理可以显著降低土壤有效态重金属质量分数,有效态Cu、Zn、Pb、Cd质量分数分别下降到对照的58.7%、75.4%、59.8%、44.0%,从而有效地降低了芥菜对重金属的吸收积累,施加碳酸钙处理后,芥菜地上部Cu、Zn、Pb、Cd分别下降66.1%、83.2%、70.5%、53.1%。施加碳酸钙处理不仅可以促进芥菜生长还可以提高芥菜品质,与对照相比施加20mg·kg-1的碳酸钙处理后,芥菜生物量、可溶性糖质量分数、Vc质量分数分别增加了3.2%、6.0%、27.5%,而地上部硝酸盐质量分数降低了24.4%。  相似文献   

17.
利用不同浓度的Cd、Pb溶液模拟污水农用,淋浇于蔬菜盆栽土壤上,研究其土壤生物活性的变化。结果显示,在试验所设置的浓度范围内.重金属Cd、Pb对土壤微生物三大菌和土壤酶中的蔗糖酶、脲酶等都有一定的抑制作用,三大菌对它们的敏感程度:Cd为细菌>放线菌>真菌,Pb为放线菌>细菌>真菌;而它们对土壤酶的抑制程度则都为蔗糖酶>脲酶。研究还表明,土壤微生物总量的变化与重金属浓度有一定的相关性。  相似文献   

18.
In the present study, impact of tannery and other industrial effluents on the physico-chemical characteristics of loamy drain water and their consequent impact on soil and plants irrigated with effluent have been studied. The study reveals most of the parameter pH, BOD5 and COD at sampling station I was higher than station II. Waste water quality at both Stations I and II exceeded prescribed limits (BIS) for safe disposal of effluents into the surface water Samples of soil and vegetables from the land irrigated with loamy drain water has been collected and analyzed for Cu, Zn, Ni, Cr Pb and Cd. The different metals showed different enrichment factor for loamy drain water irrigated soil and are as follows: Cd 30% (max), Pb 26%, Zn 18%, Cr 5%, Cu 5%, Ni 2% (min). For plant samples collected at polluted sites are Ni 46% spinach (whole plant) (max), Zn 42% spinach (whole plant), Cr 39% spinach (whole plant), Cu 33% spinach (whole plant), Pb 20% potato tuber, Cd 20% potato tuber (min). The levels of Zn 145, Cu 5.25, and Ni 39.25 microg/ g in spinach, Pb 29.25, Cr 38. 25 and Cd 3.2 microg/g in potato tuber grown on polluted soil irrigated with contaminated drain water were found more than the reference value, which may create chronic health hazard problem to human and cattle through food chain in long run. Accumulation of toxic heavy metals may be build up in the agriculturally productive land where it is treated with contaminated effluent enrich with metals in turn bio-concentrated in the edible fodder/plants.  相似文献   

19.
腐殖酸存在下镉和铅对土壤脱氢酶活性的影响   总被引:9,自引:0,他引:9  
采用室内培养试验研究Cd和Pb污染红壤添加不同组分腐殖酸后,其脱氢酶活性的变化,结果表明,红壤遭受镉和铅污染后,脱氢酶活性显著降低,然而腐殖酸特别是胡敏酸的存在能够使脱氢酶活性得到显著回升,说明腐殖酸与重金属的相互作用对重金属污染土壤微生物活性的改善和修复功能,对土壤有一定的去污降毒作用.不同腐殖酸组分的效应大小为:灰色胡敏酸(GHA)>棕色胡敏酸(BHA)>富里酸(FA),表明分子量愈大、芳构化程度愈高的腐殖酸组分,其对重金属的钝化愈强,从而解除土壤重金属对生物毒害的能力愈强.  相似文献   

20.
通过铜陵矿集区土壤中重金属污染元素含量与土壤中微生物生物量之间的对应关系,研究其环境效应。采集深度为20cm的土样,分别制备不同微生物的培养基以期对土壤中的微生物进行分离计数,细菌和放线菌采用稀释平板涂布法计数,高铁还原菌采用最大或然数法计数。研究结果表明,铜陵矿集区土壤中As、Au、Cd、Zn、Cu、Pb元素含量与土壤中细菌、放线菌、高铁还原菌数量之间的相关关系为:As、Au、Zn、Cu与细菌和放线菌,Cd、Pb与放线菌的含量呈负相关关系,指示了土壤中高浓度污染元素对微生物的抑制作用;Cd、Pb与细菌,Cd、Zn与高铁还原菌的含量呈正相关关系,反映部分微生物受污染元素的胁迫已产生了耐受性;Au、Pb、As与高铁还原菌数量的关系不明显。通过实验数据发现,微生物在重金属含量高的区域和含量低的区域的数量下降了大约2~3个数量级,有些区域微生物数量下降了约50%。矿集区土壤中三种菌种对污染元素的敏感程度不同,其敏感程度依次是:放线菌〉细菌〉高铁还原菌。矿集区部分土壤中,细菌、高铁还原菌由于其本身的耐受性或由于受胁迫而产生了耐受性,对Cd、Zn、Pb等三种重金属污染元素的抗性水平较高,具有作为土壤重金属元素污染修复微生物菌种的潜力。  相似文献   

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