Hg~(2+)、Cd~(2+)及其复合胁迫对苦草的毒害

利用微宇宙系统研究了不同浓度的Hg2+、Cd2+单一及复合处理下,苦草对这三种胁迫的响应。三种胁迫下,3d内苦草现存量增加百分比与金属离子浓度间显著负相关,其中在[Hg2+]或[Hg2++Cd2+]([Hg2+]/[Cd2+]=1)>5μmol/L时,2～3d可致死;总生产力、净生产力、呼吸强度以及叶绿素含量均随着金属离子浓度的增加而下降,同时叶绿素含量还随着胁迫时间的延长而降低,但上述四个指标在低浓度胁迫时常略有升高;可溶性蛋白含量在[Hg2+]或[Hg2++Cd2+]≤2.5μmol/L、以及[Cd2

Cd~(2+)和Cu~(2+)对美人蕉的氧化胁迫及抗性机理研究

通过测定植物的丙二醛(MDA)含量、酸溶性SH含量以及两种抗氧化酶(超氧化物歧化酶SOD和愈创木酚过氧化物酶GPX)的酶活,研究了重金属镉(Cd)和铜(Cu)对美人蕉(Cannaindica Linn.)的氧化胁迫。结果表明,20μmol·L~(-1)和100μmol·L~(-1)的Cd~(2+)和Cu~(2+)均使其根部MDA含量显著增加,但除了100μmol·L~(-1)的Cd~(2+),叶部MDA含量无明显变化。与Cu~(2+)相比,Cd~(2+)能引起植物根部GSH的明显提高,并能诱导PCs的产生

Cd~(2+)对绿球藻生长及生理特性的影响研究

863计划资助(2002AA601021); 973计划(2002CB412309)资助

重金属Cd~(2+)、Pb~(2+)和Zn~(2+)对泥鳅DNA损伤的研究

采用单细胞凝胶电泳技术(SCGE),研究重金属Cd2+、Pb2+、Zn2+在不同暴露时间(1—35d)、单一重金属离子不同暴露浓度(0.05mg/L、0.5mg/L、5.0mg/L)或混合重金属离子(Cd2++Pb2+、Cd2++Zn2+、Pb2++Zn2+、Cd2++Pb2++Zn2+)相同浓度(0.5mg/L)条件下对泥鳅肝胰脏细胞核DNA的损伤作用。以带彗尾核DNA百分率和彗尾长度(TL)与核直径(D)比值为指标,探讨DNA损伤级别与处理浓度间的相关性。结果显示,随着处理时间的延长,带彗尾核DNA百

Hg~(2+)、Cd~(2+)及其联合胁迫对伊乐藻的生长及POD和SOD活性的影响

利用水族箱实验研究了伊乐藻的现存量以及POD和SOD活性在Hg2+、Cd2+及其联合胁迫下的响应特点.结果表明:Hg2+和Cd2+对伊乐藻的联合毒性大于单一的毒性;在Hg2+20μmol.L-1,或Cd2+80μmol.L-1,或Hg2++Cd2+50μmol.L-1([Hg2+]/[Cd2+]=1/4)时,植物现存量增加的百分比与金属离子浓度负相关;高于上述浓度时,植物现存量减少的速率明显降低.POD和SOD活性的变化趋势相似,在6 h时,其活性在低于40μmol.L-1的Hg2+、或160μmol.L

Hg~(2+)、Cd~(2+)及其复合胁迫对伊乐藻的毒害

利用水生微宇宙系统研究了不同浓度的Hg2+、Cd2+单一及复合处理对伊乐藻可溶性蛋白质浓度、叶绿素含量、叶绿素a/b比值,以及生产力和呼吸作用的影响.可溶性蛋白质和叶绿素含量在低浓度胁迫时(Hg2+≤2.5μmol/L,Cd2+≤10μmol/L,Hg2++Cd2+≤1.25μmol/LHg2++5μmol/LCd2+)略有升高,之后随胁迫的增强而持续下降,两者呈负相关;叶绿素a/b比值、净生产力、呼吸强度随离子浓度增加不断下降,除呼吸强度外,两者也呈负相关.Hg2+对伊乐藻的毒性是Cd2+的4倍左右(以

利用微量热法研究Cd~(2+)和Cu~(2+)对嗜热四膜虫(Tetrahymena thermophila)的毒性效应

利用微量热法研究Cd2 + 和Cu2 + 对嗜热四膜虫BF5(TetrahymenathermophilaBF5)生长代谢毒性效应 ,结果表明 :①低浓度的Cd2 + (0～ 0 .4mgL-1)和Cu2 + (0～ 10mgL-1)对四膜虫的生长有促进作用 ,而高浓度的Cd2 + (0 .8～ 3.2mgL-1)和Cu2 + (2 0～ 2 0 0mgL-1)则产生抑制作用 ;②Cd2 + 和Cu2 + 的半抑制浓度IC50 分别为 2 .0 4mg/L和15 5 .5mg/L ;③联合毒性为协同作用

伯胺N_(1923)与其它试剂对金属离子(Zn~(2+).Cd~(2+).RE~(3+))的萃取及协同萃取

胺类萃取剂具有其独特优点，特别是伯胺，因含有活泼氢，既能作为“阴离子交换剂”，又能与被萃的含氧金属络阴离了形成氢键而溶剂化，同时伯胺为一路易斯碱，可作为配体与某些金属离子形成配位键等，因而已广泛地用于金属离子的提纯与分离工业中。然而，1）为了寻找新的、更有效的萃取及协同萃取体系，以适应分析分离各种金属离子，改善金属离子的分离工艺；2）研究萃取和协同萃取的一般规律，探寻其内在规律性，充实完善萃取化学原理的内容；3）研究多元配合物的组成、结构和机理；4）系统地研究和比较不同结构胺类萃取剂与其它萃取剂对金属离子的萃取及协同萃取的相互作用，探讨多元配合物的形成条件等，因此，研究伯胺N_(1923)与其它萃取剂在不同酸度、不同条件，不同体系中对Zn(II)、Cd(II)、Re(III)的萃取及协同萃取具有一定意义。本文分别研究了伯胺N_(1923)与中性磷试剂对ZnCl_2、CdCl_2、Zn(SCN)_2的协同萃取；伯胺N_(1923)与HPMBP对RE（III）的协同萃取以及伯胺N_(1923)在不同介质中对Sc(III)的萃取机理等，并用得到了一些有意义的结果与结论。一、伯胺N_(1923)与中性磷萃取剂(TBP, DBBP)对Zn(II)、Cd(II)的协同萃取1. 伯胺N_(1923)与TBP、DBBP对ZnCl_2的协萃取 研究了伯胺N_(1923)与TBP、DBBP的正庚烷溶液从盐酸介质中对ZnCl_2的萃取机理，用斜率法、等摩尔系列法确定了协萃配合物组成为：(RNH_3Cl)_3·ZnCl_2·B、(RNH_3Cl)_2·ZnCl_2·B (B = TBP·DBBP)协萃反应为：ZnCl_2 + (RNH_3Cl)_3_((o)) + TBP_((o)) →~(K_(12)(TBP) (RNH_3Cl)_3·ZnCl_3·ZnCl_2·TBP_((o)) ZnCl_2+Z/3(RNH_3Cl)_(3(o)) + DBBP_((o)) → (RNH_3Cl)_2 · ZnCl_2·DBBP_((o))协萃配合物生成反应为：(RNH_3Cl)_3·ZnCl_(2(o)) + TBP_((o))→~(B_(12)(TBP) (RNH_3Cl)_3·ZnCl_2·TBP_((o)) (RNH_3Cl)_3·ZnCl_(2(o)) + DBBP_((o)) →~(B_(12)(DBBP) (RNH_3Cl)_2·ZnCl_2·DBBP_((o)) + RNH_3Cl_((o))同时发现，中性磷试剂对Zn(II)的协萃效应大小影响有下列关系：DBBP>TBP。并求得了协萃反应平衡常数和协萃配合物生成反应平衡常数。在研究溶剂对协同效应影响时发现，对芳香烃及其衍生物，分配比（D）与溶剂介电常数（ε）的关系为D_∝1/ε，而对芳香烃及其衍生物，分配比（D）与介电常数（ε）的关系为D_∝ε。讨论了温度对协萃反应的影响，对协萃配合物的IR、NMR谱也进行了研究。2.伯胺N_(1923)与TBP对Zn_(SCN)_2的协同萃取研究了伯胺N_(1923)与TBP的庚烷溶液从硝酸底液中对Zn(SCN)_2的萃取机理，用等摩尔系列法、斜率法确定了TBP和Zn(SCN)_2以及伯胺N_(1923)与TBP对Zn(SCN)_2的协萃配合物组成分别为：Zn(SCN)_2·3TBP. (RNH_3)_2Zn(SCN)_4·TBP,协谇反应为：Zn(SCN)_4~(2-) + (RNH_3NO_3)_(2(o)) + TBP_((o)) → (RNH_3)_2Zn(SCN)_4·TBP_((o)) + 2NO_3~-协萃配合物三种可能生成反应为(RNH_3)_2Zn(SCN)_(4(o)) + TBP_((o)) → ~(B'12) (RNH_3)_2Zn(SCN)_4·TBP_((o)) (a) (RNH_3NO_3)_(2(o)) + Zn(SCN)_2·3TBP_((o)) + 2SCN~-→~(β"12)→(RNH_3)Zn(SCN)_4βTBP_((o))+2TBP_((o))+2NO_3~- (b) (RNH_3NO_3)_(2(o)) + (RNH_3)_2Zn(SCN)_(4(o)) + 2SCN~- + Zn(SCN)_2.3TBP_((o)) →~(β"12)→R(RNH_3)_2Zn(SCN)_4.TBP_((o)) + 2NO_3~- + TBP_((o)) (c) 求得了协萃反应及生成反应的平衡常数，并由生成反应常数可知：β"'_(12) > β'_(12) > β"_(12)，即反应（c）对协萃配合物的生成贡献最大，其次反应（a），最小的是反应（b），同时还发现，不同阴离子对协萃效应影响有下列关系：SCN~- > Cl~_。并对协萃配合物的IR谱进行了研究，讨论了温度对协萃反应的影响。3. 伯胺N_(1923)与TBP、DBBP对Cd（II）的协同萃取研究了伯胺N_(1923)与TBP、DBBP的正庚烷溶液从盐酸介质中对Cd(II)的协同萃取，用等摩尔系列法、斜率法确定了协萃配合物组成为(RNH_3Cl)_2·CdCl_2·B，协萃反应及协萃配合物生成的反应分别为：CdCl_2 + 2/3 (RNH_3Cl)_(3(o)) + B_((o)) →~(K_(12)) → (RNH_3Cl)_2·CdCl_2·B_((o)) (RNH_3Cl_3)·CdCl_2_((o)) + B_((o)) →~(BR)(RNH_3Cl)_2·CdCl_2·B_((o)) + RNH_3Cl_((o))求得了协萃反应及生成反应平衡常数，计算了协萃反应的热力学函数值，结果还发现与Zn(II)协同萃取比较，协同效应大小有下列关系：Zn(II) > Cd(II)，由实验结果证实了“萃取效应大，则协萃效应小，反之，萃取效应小，则协同效应大”这一结论。并对协萃配合物的IR、NMR谱进行了研究。二. 伯胺N_(1923)与HPMBP对RE（III）的协同萃取研究了伯胺N_(1923)与HPMBP的二甲苯溶液在盐酸介质中对RE（III）的协萃机理（RE~(3+ = La~(3+), Pr~(3+), Eu~(3+), Gd~(3+), Tb~(3+), Er~(3+), Yb~(3+)和Y~(3+)）用斜率法及等摩尔系列法确定了协萃配合物组成为RNH_3Ln(PMBP)_4。求得了关于Pr(III)的协萃反应及生成反应的平衡常数值，协萃反应及生成反应分别为：Ln~(3+) + 4HPMBP_((o)) + RNH_3Cl_((o)) → RNH_3LN(PMBP)_(4(o)) + 4H~+ + Cl~- Ln(PMBP)_(3(o)) + RNH_3Cl_((o)) → RNH_3Ln(PMBP)_(4(o)) + H~+ + Cl~- 结果还发现协萃系数（R）随稀土元素的原子序数（Z）递变而出现“双峰效应”（未见文献报道），而且随RNH_3Cl浓度增加到某一一出现反协同效应。同时研究了关于Pr(III)协萃配合物的IR、NMR谱。三、伯胺N_(1923)在硝酸盐及硫氰酸盐混合介质中对Sc(III)的萃取研究了RNH_3NO_3在硝酸盐和硫氰酸盐混合介质中萃取Sc(III)的机理，结果发现，钪是以Sc(OH)_2~+形式萃入有机相的，且SCN~-, NO_3~-对RNH_3nO_3萃取Sc(III)具有协同效应，并且斜率法、连续变化法及PH值测定确定了萃取反应为：Sc(OH)_2~+ + SCN~- + 2(RNH_3NO_3)_(2((o)) → (RNH_3nO_3)_4.Sc(OH)_2SCN_((o)) Sc(OH)_2~+ + SCN~- + NO_3~- + (RNH_3NO_3)_(2(o)) → (RNH_3NO_3)_2.Sc(OH)(SCN)NO_3 + OH~-求得了反应的平衡常数及热力学函数值。

稀土及过渡金属离子Fe(III)、Zn(II)、Cd(II）的协同萃取研究

自从1956年Blake等研究HDEHP萃取铀时发现协同效应以来，由于协同萃取具有可以显著地提高萃取效率，改变萃取选择性等优点，所以对协同萃取进行了大量研究工作，目前已广泛应用于核燃料稀有金属湿法冶金分离分析。但协同萃取研究领域十分广阔，新协萃体系，协萃机理和协萃配合物结构等许多方面还有待进一步研究。Fe~(3+)、Zn~(2+)和Cd~(2+)等过渡金属离子常与稀土离子在一起，成为高纯稀土产品的重要杂质元素，因此寻找Fe(III)、Zn(II)和Cd(II)与RE（III）的新协同萃取分离体系，不但具有理论意义，也有实际意义。本文研究了萃取分离中广泛使用的四种萑取剂，甲基膦酸二（1-甲基庚基）酯（P_(350), 以B表示）、仲碳伯胺N_(1923)(以RNH_2表示）、1-苯基-3-甲基-4-苯甲酰基吡唑酮-5（PMBP，以HL表示）和2-乙基基膦酸单（2-乙基已基）酯（P_(507)，以HA表示）对盐酸介质中Fe(III)、Zn(II)、Cd(II)和Nd(III)等金属离子的协同萃取，得到了六个新协萃体系，并且对协萃机理和萃取平稀奇规律等进行了研究，得到了一些有意义的结果。

LITHIUM PASSIVATION OF ZN AND CD ACCEPTORS IN P-TYPE GAAS

We report lithium passivation of the shallow acceptors Zn and Cd in p-type GaAs which we attribute to the formation of neutral Li-Zn and Li-Cd complexes. Similar to hydrogen, another group-I element, lithium strongly reduces the concentration of free holes when introduced into p-type GaAs. The passivation is inferred from an increase of both the hole mobility and the resisitivity throughout the bulk of the sample. It is observed most clearly for Li concentrations comparable to the shallow-acceptor concentration. In addition, compensation of shallow acceptors by randomly distributed donors is present in varying degree in the Li-diffused samples. Unlike hydrogenation of n-type GaAs, Li doping shows no evidence of neutralizing shallow donors in GaAs.

Correlation of electrical and optical properties in dually Cd+ and N+ ion-implanted GaAs

Cd in GaAs is an acceptor atom and has the largest atomic diameter among the four commonly-used group-II shallow acceptor impurities (Be, Mg, Zn and Cd). The activation energy of Cd (34.7 meV) is also the largest one in the above four impurities, When Cd is doped by ion implantation, the effects of lattice distortion are expected to be apparently different from those samples ion-implanted by acceptor impurities with smaller atomic diameter. In order to compensate the lattice expansion and simultaneously to adjust the crystal stoichiometry, dual incorporation of Cd and nitrogen (N) was carried out into GaAs, Ion implantation of Cd was made at room temperature, using three energies (400 keV, 210 keV, 110 keV) to establish a flat distribution, The spatial profile of N atoms was adjusted so as to match that of Cd ones, The concentration of Cd and N atoms, [Cd] and [N] varied between 1 x 10(16) cm(-3) and 1 x 10(20) cm(-3). Two type of samples, i.e., solely Cd+ ion-implanted and dually (Cd+ + N+) ion-implanted with [Cd] = [N] were prepared, For characterization, Hall effects and photoluminescence (PL) measurements were performed at room temperature and 2 K, respectively. Hall effects measurements revealed that for dually ion-implanted samples, the highest activation efficiency was similar to 40% for [Cd] (= [N])= 1 x 10(18) cm(-3). PL measurements indicated that [g-g] and [g-g](i) (i = 2, 3, alpha, beta,...), the emissions due to the multiple energy levels of acceptor-acceptor pairs are significantly suppressed by the incorporation of N atoms, For [Cd] = [N] greater than or equal to 1 x 10(19) cm(-3), a moderately deep emission denoted by (Cd, N) is formed at around 1.45-1.41 eV. PL measurements using a Ge detector indicated that (Cd, N) is increasingly red-shifted in energy and its intensity is enhanced with increasing [Cd] = [N], (Cd, N) becomes a dominant emission for [Cd] = [N] = 1 x 10(20) cm(-3). The steep reduction of net hole carrier concentration observed for [Cd]/[N] less than or equal to 1 was ascribed to the formation of (Cd, N) which is presumed to be a novel radiative complex center between acceptor and isoelectronic atoms in GaAs.

Investigation on Fe, Mn, Zn, Cu, Pb and Cd fractions in the natural surface coatings sampled and surficial sediments collected in the Songhua River, China

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.

半磁半导体Cd（1-x）MnxTe压力光致发光研究

于2010-11-23批量导入