908 resultados para heavy metal ion absorption


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Aspartate aminotransferase (E.C. 2.6.1.1.) from the skeletal muscle of fresh water fish Cirrhina mrigala has been purified 40 fold by ammonium sulphate fractionation, adsorption on alumina Csub(8) gel and chromatography using DEAE-cellulose column and the properties of the purified enzyme studied. The pH optimum of the enzyme is 7.8. The Km value of aspartic acid and 2-oxoglutaric acid are found to be 2.8 x 10sub(-3) M and 1.0 x 10sub(-4) M respectively. The activity of enzyme is inhibited by p-chloromercurybenzoate, hydroxylamine hydrochloride and sodium cyanide. The inhibition by pchloromercurybenzoate is reversed by reduced glutathione, B-mercaptoethanol and cysteine. Dicarboxylic acids such as maleic acid, malic acid and succinic acid inhibit the enzyme activity. The enzyme is not activated by any of the metal ions tested and heavy metal ions such as mercury and silver strongly inhibit the enzyme activity.

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Ecological risk assessment is determination of the probability of an adverse effect occurring to an ecological system. This investigation was carried out to assess the ecological risk of sediment in coast of Bandar Abbass in 9 stations including Shilat Jetty, Hotel Amin, Poshte-Shahr, Souro, Bahonar Jetty, Powerhouse, Refinery and Rajaee Jetty from autumn 2013 to summer 2014. Results showed that Polychaete with 1177 , 1109 , 414 , 573 , ind.m2 in autumn 91 , winter 91 , spring 92 and summer 92 were the most abundant in frequency respectively. Among ecological indices, the Margalof that ranged from 4 to 7 was in a good situation while Shanoon and Berger – Parker with 1.2 (at most) and 0.32 (at least) respectively indicated an environment with probable stress. Heavy metal distribution obtained as Cd>Pb>Cu>Zn in sediment. In tissue, the distribution of heavy metals were as Crab>polychaete>Bivalve>gastropod for Pb, Gastropod>Bivalve>Polychaete>Crab for Cd, Gastropod>Crab>Polychaete>Bivalve for Cu and Gastropod>Bivalve>Crab>Polychaete for Zn. Maximum and Minimum of TOM obtained 10.16 and 1.96 percent in Posht-e-Shahr and shilat Jetty respectively and clay was the dominant grain in most area. Bioaccumulation coefficient of Zn and Cu was high in all stations. Igeo as a single index was high for Cd indicating a high risk in all stations. Potential Ecological Risk was high for Cu and Zn and goes increasingly from shilat Jetty to Rajee Jetty but goes down for Pb. Pollution index for Cu and Pb was nearly the same as Potential Ecological Risk but for Zn goes constantly. Among PAH, 5-ring and 6-ring PAhs were more concentrate comparison to other compounds in sediment. 2-ring and 3-ring, 3-ring, 4-ring and 5-ring and 5-ring PAHs were more concentrate in Gastropod, Bivalve, Crab and Polychaete respectively. HI as an index of PAH obtained 1. Ecological Risk Indices showed that the heavy metals are a serious risk for invertebrate in sediment but PAHs are not a risk for benthic community.

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Stabilisation, using a wide range of binders including wastes, is most effective for heavy metal soil contamination. Bioremediation techniques, including bioaugmentation to enhance soil microbial population, are most effective for organic contaminants in the soil. For mixed contaminant scenarios a combination of these two techniques is currently being investigated. An essential issue in this combined remediation system is the effect of microbial processes on the leachability of the heavy metals. This paper considers the use of zeolite and compost as binder additives combined with bioaugmentation treatments and their effect on copper leachability in a model contaminated soil. Different leaching test conditions are considered including both NRA and TCLP batch leaching tests as well as flow-through column tests. Two flow rates are applied in the flow-through tests and the two leaching tests are compared. Recommendations are given as to the effectiveness of this combined remediation technique in the immobilisation of copper. © 2005 Taylor & Francis Group.

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This scoping study proposes using mixed nitride fuel in Pu-based high conversion LWR designs in order to increase the breeding ratio. The higher density fuel reduces the hydrogen-to-heavy metal ratio in the reactor which results in a harder spectrum in which breeding is more effective. A Resource-renewable Boiling Water Reactor (RBWR) assembly was modeled in MCNP to demonstrate this effect in a typical high conversion LWR design. It was determined that changing the fuel from (U,TRU)O2 to (U,TRU)N in the assembly can increase its fissile inventory ratio (fissile Pu mass divided by initial fissile Pu mass) from 1.04 to up to 1.17. © 2011 Elsevier Ltd. All rights reserved.

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The effects of cadmium (Cd2+) on growth status, chlorophyll (Chl) content, photochemical efficiency, and photosynthetic intensity were studied on Canna indica Linn. Plant specimens that were produced from a constructed wetland and precultivated hydroponically in 20 L of 1/10 Hoagland solution under greenhouse conditions for I week were exposed to cadmium in concentrations of 0, 0.4, 0.8, 1.6 and 3.2 mg L- Cd2+, respectively. The results show that leaves were injured in the Cd2+ solution by the third day of exposure and the injury became more serious with an increase in the applied heavy metal. Under 3.2 mg L-1 Cd2+ treatment, growth retardation, the decrease of chlorophyll content from 0.70 to 0.43 mg g(-1) FW, and a decrease in Chl a/b ratio from 2.0 to 1.2 were observed. Chl a was more sensitive than Chl b to Cd2+ stress. The decrease was the same with photochemical efficiency. Photosynthetic intensity decreased by 13.3% from 1.5X10(4) mumol m(-2)s(-1) CO2 in control to 1.3x10(4) mumol m(2)s(-1) CO2 in the treatment of 3.2 mg L-1. Because Canna species are used in heavy metal phytoremediation, these results show that C. indica can tolerate 0.4 to 0.8 mg L-1 Cd2+. Therefore, it is a potential species for phytoremediation of cadmium with some limitations only at higher concentrations.

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The release of heavy metals from the combustion of hazardous wastes is an environmental issue of increasing concern. The species transformation characteristics of toxic heavy metals and their distribution are considered to be a complex problem of mechanism. The behavior of hazardous dyestuff residue is investigated in a tubular furnace under the general condition of hazardous waste pyrolysis and gasfication. Data interpretation has been aided by parallel theoretical study based on a thermodynamic equilibrium model based on the principle of Gibbs free energy minimization. The results show that Ni, Zn, Mn, and Cr are more enriched in dyestuff residue incineration than other heavy metals (Hg, As, and Se) subjected to volatilization. The thermodynamic model calculation is used for explaining the experiment data at 800 degrees C and analyzing species transformation of heavy metals. These results of species transformation are used to predict the distribution and emission characteristics of trace elements. Although most trace element predictions are validated by the measurements, cautions are in order due to the complexity of incineration systems.

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用不同浓度Hg处理两种基因型小麦种子,较低浓度的Hg对小麦种子萌发影响比较小,对抗旱品种的小麦种子(陕合)的萌发有略微的刺激作用。小剂量、短时间的重金属处理可以提高POD的活性,发芽后受到Hg胁迫的陕合对Hg的耐受性低于发芽前就受到Hg胁迫的陕合,也低于同样胁迫处理的小麦品种(郑引)。发芽后进行Hg胁迫处理情况下,陕合对于Hg胁迫比较敏感,POD活性随着Hg浓度的升高而下降;而郑引,低浓度Hg对其POD活性有促进作用。在小麦发芽前就受到Hg胁迫的情况下,陕合和郑引的POD活性都随着Hg浓度增加表现为先上升而后下降趋势。

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Natural surface coatings sampled (NSCSs) from the surface of shingles and surficial sediments (SSs) in the Songhua River, China were employed to investigate the similarities and difference in fractions of heavy metals (Fe, Mn, Zn, Cu, Pb, and Cd) between NSCSs and SSs using the modified sequential extraction procedure (MSEP). The results show that the differences between NSCSs and SSs in Fe fractions were insignificant and Fe was dominantly present as residual phase (76.22% for NSCSs and 80.88% for SSs) and Fe-oxides phase (20.33% for NSCSs and 16.15% for SSs). Significant variation of Mn distribution patterns between NSCSs and SSs was observed with Mn in NSCSs mainly present in Mn-oxides phase (48.27%) and that in SSs present as residual phase (45.44%). Zn, Cu, Pb and Cd were found dominantly in residual fractions (>48%), and next in solid oxides/hydroxides for Zn, Pb and Cd and in easily oxidizable solids/compounds form for Cu, respectively. The heavy metal distribution pattern implied that Fe/Mn oxides both in NSCSs and SSs were more important sinks for binding and adsorption of Zn, Pb and Cd than organic matter (OM), and inversely, higher affinity of Cu to OM than Fe/Mn oxides in NSCSs and SSs was obtained. Meanwhile, it was found that the distributions of heavy metals in NSCSs and SSs were similar to each other and the pseudo-total concentrations of Zn, Cu, Pb and Cd in NSCSs were greater than those in SSs, highlighting the more importance for NSCSs than SSs in controlling behaviours of heavy metals in aquatic environments.

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本论文以沈阳张士污灌区土壤为例,首次采用传统微生物生态学与现代微生物分子生态学相结合的研究方法系统地研究了污灌区长期重金属污染胁迫下原位农田土壤微生物特征。结果表明,虽然已经停止污灌十多年,张士灌区土壤耕作层(0~30 cm)仍然存在普遍的Cd污染,灌区土壤Cd含量高达1.75~3.89 mg kg-1。部分区域土壤Cd呈现向下迁移的趋势,且同时伴随有Cu、Zn复合污染。灌区土壤Cd含量较高时清水灌溉能降低土壤表层Cd含量,灌区土壤Cd含量下降到一定程度(约2 mg kg-1)后,清水灌溉对消除土壤表层Cd污染的作用消失。重金属元素中Cd对土壤微生物的影响最突出,在三个不同季节中土壤Cd与土壤微生物生物量(MBC)和微生物商(qM)呈显著负相关,与土壤微生物代谢商(qCO2)呈显著正相关。所检测的微生物指标中qM和qCO2与多种重金属元素呈显著相关性,可作为评价一定程度重金属污染的微生物指标。土壤营养元素(除P外)与微生物特征呈显著正相关性,土壤营养元素对微生物的刺激作用有可能在某种程度上掩盖了重金属对土壤微生物的负面影响。 用16S rDNA-PCR-DGGE方法,研究了不同浓度Cd胁迫下土壤Cd抗性细菌群落结构的动态变化,结果表明在Cd的胁迫下Cd抗性细菌多样性显著增加,不同土壤样品中Cd抗性细菌群落结构向相似的方向偏移,群落结构最终将可能趋向一致。Cd胁迫使敏感菌Pontibacter消失,而伯克氏菌(Burkholderia)、罗尔斯通氏菌(Ralstonia)、芽孢杆菌(Bacillus)和节杆菌(Arthrobacter)则富集成为优势菌。 从张士灌区Cd污染土壤中分离出32株Cd抗性细菌,研究了Cd抗性细菌和Cd抗性基因cadA的分布特征。这32株Cd抗性细菌分别归属于拟杆菌门(Bacteroidetes)(37.5%)、变形菌门(Proteobacteria) (37.5%)、放线菌门(Actinobacteria)(9.4%) 和厚壁菌门(Firmicutes)(15.6%)。在液体LB培养基中对Cd的抗性浓度都大于2 mmol L-1,对Zn抗性浓度介于5~13 mmol L-1。首次从Cetobacillus属的Cd抗性菌株S1基因组DNA中扩增出cadA基因的部分片断。在芽孢杆菌属(Bacillus)的4株菌N7,N9,N10和N11的基因组DNA中扩增出cadA基因的部分片断。序列分析结果表明这5株菌的cadA基因序列相似性为99%~93%,它们与坚强芽孢杆菌(Bacillus firmus) cadA 基因序列(M90750)相似性为94%~92%。系统发育分析结果表明这5株菌的cadA都与Bacillus firmus cadA 基因有着较近的亲缘关系。不同属的Cd抗性细菌间cadA基因的高度相似性揭示了cadA基因能在不同种属间转移的特性。

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沉积物中的重金属,与无机、有机胶体通过吸附、配位体交换、络合、共沉淀等作用与沉积物中不同组分结合,由于污染来源、环境条件、赋存时间的不同,重金属可以有不同的化学形态。不同赋存形态的重金属具有不同的生物环境地球化学过程及生物有效性规律。 5种氧化物矿物吸附态Cd的富集实验表明,芦苇对吸附在含铝矿物表面的Cd吸收最多,其次为铁锰矿物。比表面积较大、等电点较低的矿物与Cd的吸附强度和稳定性较强,进而造成Cd的植物有效性较低。可能对Cd的吸附解吸产生影响的是植物根系分泌的有机酸,有机酸对不同矿物吸附Cd的解吸规律与芦苇对Cd的吸收规律一致。有机酸本身性质,如羧基数量、电离常数等影响Cd解吸量。 环境中与水合氧化物结合(吸附和共沉淀)的Cd生物有效性研究表明,两种结合形式的Cd均被芦苇富集,不同处理体系中富集强度不同,根中富集量9.1 ~ 37.8 mg/kg;地上部分富集量为0 ~ 10.0 mg/kg。由于共沉淀处理增加了矿物的比表面积和吸附位点密度,并且在预先混合的过程中Cd进入氧化物内部使结合了Cd的水合氧化物更加稳定,因此吸附态Cd的植物有效性大于共沉淀。老化处理可使Cd向水合氧化物晶格内部扩散,因而显著地降低吸附态Cd的富集。由于Fe(OH)3的等电点较低、阳离子交换容量较大,因此与Fe(OH)3 结合的Cd有效性较低。采用2种低分子量有机酸对Cd进行解吸,Cd的解吸规律与芦苇对镉的富集规律一致。 与无定形铁氧化物结合(吸附和共沉淀)的多金属富集实验表明,芦苇对不同金属的富集强度不同。金属离子与铁氧化物的亲合力由金属阳离子水合半径和水化数决定,本研究中金属与铁矿物结合亲合力遵循:Pb > Cd > Cu > Ni,因此芦苇对金属的富集规律大致为Ni > Cu > Cd > Pb。在多金属处理体系中,金属之间往往竞争相同的吸附位点,形成相似络合物,从而改变吸附强度和稳定性。Ni和Cd在根中富集量较少,可能是体系中Pb的投加产生了竞争作用。此外,植物对金属的选择性吸收也影响金属的植物有效性。解吸实验表明,吸附处理的金属解吸量大于共沉淀,单一金属投加体系中,重金属的解吸量:Ni > Cu > Cd > Pb;多种金属投加体系中,Pb的解吸量增加,Cd的解吸量下降。根系分泌的低分子量有机酸对沉积物中的重金属有重要的活化作用,这可能是植物吸收污染沉积物或土壤中重金属的重要因素之一。 针铁矿和不溶性腐殖酸吸附态Cd的富集实验表明,水溶态金属的有效性最大,其次为针铁矿吸附态,最难被植物吸收的是腐殖酸吸附态金属。由于腐殖酸结构复杂、表面多官能团和吸附位点,因此与金属的亲合力较大,结合牢固,不易被芦苇吸收富集。解吸实验验证了相同条件下,柠檬酸对腐殖酸吸附态金属的解吸量小于针铁矿结合态。pH值是影响金属与沉积物中活性组分结合强度和稳定性的重要因素。较低的pH值,水相中H+浓度较高,与金属离子竞争吸附位点,降低针铁矿或腐殖酸对金属离子的吸附容量和稳定性。另外,环境pH值较低(低于矿物等电点)时,矿物表面趋于带正电,增加了金属离子吸附的难度。 水体-沉积物体系中,可溶性腐殖酸影响重金属的迁移和生物有效性。不同的腐殖酸浓度和投加顺序对金属的生物有效性影响研究表明,单一金属投加体系中,金属在芦苇体内的富集规律为:Cu > Cd > Ni > Pb,金属在植物不同部位的分布遵循:根 > 叶 > 茎 > DCB,腐殖酸浓度的增加降低了金属的富集(除Ni外)。混合金属投加体系中,金属的富集遵循:Ni > Cu > Cd > Pb(HA 5 ppm);Cd > Ni > Cu > Pb(HA 20 ppm)。与单一金属投加相比,金属的富集量降低,DCB提取态金属含量增加。腐殖酸浓度的增加降低了金属的生物有效性。腐殖酸加入顺序显著影响的金属与针铁矿的吸附,进而影响金属的生物有效性。

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随着工农业的快速发展,土壤重金属尤其Cd和Pb污染日益严重。筛选和培育具有重金属低积累特性的农作物排异品种被认为是当前应对土壤重金属污染最为合理和有效的途径之一。本文通过盆栽试验、大田试验和砂培试验,研究了大白菜品种对Cd和Pb的吸收和积累的品种差异、对Cd、Pb胁迫的响应以及大白菜安全生产的调控技术,得出以下结论: 1) 盆栽梯度试验中,80种大白菜地上部对Cd的吸收存在显著差异(p < 0.05)。在3种Cd处理下(1.0, 2.5和5.0 mg/kg),80种大白菜Cd含量浓度范围分别为(mg/kg) 0.22–2.46, 0.90–14.10和2.03–18.01, 其平均值分别为 0.79, 3.76 和6.79 mg/kg DW。大白菜对Cd胁迫具有较强的耐性。大田试验中,15种大白菜的富集系数和转运系数与盆栽梯度试验的结果基本一致。排异植物的筛选和鉴定标准包括:(1)该植物的地上部和根部的Cd含量都很低或者可食部位低于有关标准;(2) 富集系数(BF) < 1.0;(3) 转运系数(TF) < 1.0;(4)该植物具有较高的Cd耐性,在较高的Cd污染下能够正常生长且生物量无显著下降。采用此标准,结合盆栽梯度试验和大田试验结果,北京新3号、绿星70和丰源新3号可鉴定为Cd排异品种。秋傲和赛新5号具有排异Cd特性,但其对Cd的耐性较差。 2) 盆栽梯度试验中,在Pb投加浓度为500和1500 mg/kg处理下,30种大白菜地上部对Pb的吸收存在显著差异 (p < 0.05),其Pb浓度的范围分别为:0.52–8.68 和1.86–16.20 mg/kg, 其平均值分别为3.01 和6.87 mg/kg DW。并且,随着Pb浓度的增加,白菜地上部Pb含量有随之增加的趋势。大白菜对Pb具有较强的耐性。低浓度的Pb处理对大白菜的生物具有一定的促进作用。结合盆栽试验和大田试验的结果,秋傲、世博秋抗和福星80可鉴定为Pb排异大白菜品种。 3) 砂培试验中,在Cd和Pb胁迫下,大白菜地上部的丙二醛(MDA)含量增加,随着Cd处理浓度的增加,超氧化物歧化酶(SOD)活性呈现先下降后上升接着下降的趋势,酸菜王的SOD活性要高于北京新3号SOD的活性。随着Pb处理浓度的增加,福星80地上部的SOD活性随之增加,而绿星大棵菜地上部的SOD活性先下降后增加。在不同梯度的Cd处理下,大白菜地上部的可溶性蛋白(SP)含量未见显著降低,甚至有所增加,而在不同梯度的Pb处理下,大白菜地上部的SP含量有所降低。 4) 施用改良剂可升高土壤的pH值和降低土壤中的有效态Cd,从而对大白菜的生长具有促进作用。施用改良剂可显著降低大白菜对Cd和Pb的吸收和累积。

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综合运用环境地球化学、土壤学、生态学和统计学的方法开展了矿山废弃物尾矿石的堆置对土壤造成的污染以及矿区土壤重金属污染对白菜(Brassica Chinensis)的卫生品质和营养品质的影响研究。静态培养试验和动力学淋溶试验证明:在环境因素(如降水)的作用下,尾矿石的堆置将对下伏土壤的重金属含量产生长久影响,随着降水量以及酸度的增加,土壤中Cu、Cd、Pb、Zn的全量和有效态含量都有所升高并且土层间的差异减小。有机酸能不同程度地促进土壤中的重金属转化为有效态,增强重金属的生物有效性;多元梭酸比一元梭酸的转化率高。另外,有机酸对重金属的转化作用随其浓度的增大而增强,在低温范围内,随温度的升高而增加。通过网室盆栽试验,研究了土壤受Cu、Cd、Pb,Zn单一重金属污染后对大白菜吸收Cu、Cd、Pb、Zn以及植物体内粗纤维和维生素C含量的影响;同时还进一步对Cd-P交互作用影响大白菜吸收Cd、P以及植物体内粗纤维和维生素C含量的情况进行了研究,结果表明大白菜从污染的土壤吸收重金属与土壤中目标元素的含量呈极显著正相关,对非目标重金属的吸收情况复杂,因不同元素间的相互作用机制而异;白菜体内粗纤维和抗坏血酸含量随土壤重金属浓度的增加而降低,它们之间呈极显著的负相关关系。在采用大白菜进行高等植物毒性试验的基础上,首次运用典型相关分析方法对Cu、Cd、Pb、Zn复合污染土壤的生态毒性进行了评价,分别建立了由4元素共同组成的复合污染土壤毒性的线性组合函数和由芽生物量抑制率和根伸长抑制率组成的植物学表征的线性组合函数,并计算了其第一典型变量Toxl(土壤毒性)和BloL(植物学表征)之间的相关系数为0.94(p<0.01)。典型相关分析是介质毒性评价的有效方法之一。

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超积累植物是植物提取修复的核心,同时也是污染环境修复领域研究的热点与前沿。针对目前已发现的超积累植物数量与对重金属提取种类较少的现状,并根据修复实践的需求,本研究确立了以超积累植物的筛选为主要研究内容并就一些强化措施进行了初步探索,同时根据已报道的植物修复研究的阶段性成果,对污染土壤植物修复的基本概念、原理、方式、强化机制等相关的修复过程进行了系统总结,结果如下:(1)超积累植物应同时具有四个基本特征,即临界含量特征、转移特征、耐性特征和富集系数特征。(2)龙葵和球果掉菜是Cd超积累植物,在Cd投加浓度为259/kg条件下,其茎和叶中Cd含量分别为103.80mg/kg和124.57mg/kg及107.7Omg/kg和150.10mg/kg。植物体内积累的Cd主要分布在茎和叶中。这2种植物不具有同时超积累Pb、Cu或Zn的能力。(3)施加鸡粪后植物对Cd的提取率提高了35.7%~97.0%;采用开花期收获超积累植物的复种方式,植物提取率可以提高到1.43倍和1.75倍。(4)以杂草为筛选对象,将成为筛选超积累植物的一个突破口。(5)盆栽筛选试验具有可操作性强、易于实施等优点,是筛选超积累植物值得尝试的一种方法。(6)现发现的超积累植物几乎均来源于污染区,本研究表明,未污染区也可能存在超积累植物。(7)栽培措施对植物修复效果有较大影响,与现代农业高新技术相结合是植物修复技术成功应用于修复实践的一条捷径。