943 resultados para Antigens, CD


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Seasonal sampling from 40 immature Caspian salmon were performed in summer, autumn, winter and spring. The maximum ranges of RBC counts, Hct, Hb, WBC count and clotting times were observed in spring, summer, spring, spring and winter, respectively. The minimum amounts of these factors were counted in summer, winter, winter, winter and winter, respectively. Blood Samples were taken from healthy smolt, immature and adult Caspian salmon in spawning time. Hematological determinations and biochemical serum analysis were performed in 101 fish in the three samples. The ranges of hematological values for sample mean were counted. Red blood cell counts were 866600 mm3 and 1259400 mm3 in smolt and adult respectively. Hematocrit was 48.39% in smolt and 44.29% in adult. Hemoglobin was 8.85 gr/dl in smolt and 10.91 gr/dl in adult. White blood cell count was 8781.58 mm3 in smolt and 5217.55 mm3 in adult and mean were differential of WBC, Lymphocyte 90.57%in smolt and73.22% in adult. Neutrophil was 5.12% in smolt and 16.92% in adult, Monocyte were 1.27% in smolt and 4.24% in adult, Clotting time was 282.34 Seconds in smolt and 291.47 seconds in adult MCV, MCH and MCHC also meagered in smolt and adult. Biochemical parameter in immature and mature Caspian salmon meagered .Glucose concentration was 2.97 mmol.l- in immature and 1.99 mmol.l- in mature .Cholesterol concentration was 4.26 mmol.l- in immature and 7.06 mmol.l- in mature. Triglyceride amount was 2.35 mmol.l- in immature and 2.47 mmol.l- in mature and Calcium was 2.47 in immature and 2.61 mmol.l- in mature. An in situ study was made on erythrocytic isoantigens and hetero-antigen and their corresponding iso-and hetero-antibodies of sera by means of hemoagglutination tests on the blood sample, of 450 immature and 50 mature Caspian salmon. The absence of erythrocyte iso-antigens and hetero-antigen and their corresponding iso-and hetero-antibodies were shown by the experimental. It could be indicated an intra-specific variation and differences in species for kelardasht hatchery.

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Surface- and bottom-water samples were collected from October 1996 to August 1997 to study levels of iron, copper, and cadmium species in their dissolved labile as well as non-labile and particulate forms in the waters of El-Mex Bay. The results showed that the non-labile concentration of the metals was generally more abundant than that of the labile form: its content reached more than 90% of the total dissolved metal for Cu and more than 80% for Fe. The particulate form was almost at the level of the labile form. The annual concentration of the trace metals of the labile form was 13 µglˉ¹ for Fe; 3µglˉ¹ for Cu, and 1.2 µglˉ¹ for Cd in the surface- and bottom-waters.

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AIM: To investigate the interaction between human CCR5 receptors (CCR5) and HIV-1 envelope glycoprotein gp120 (HIV-1 gp120) and HIV-1 receptor CD4 antigens (CD4). METHODS: The structurally con served regions (SCR) of human CCR5 was built by the SYBYL/Biopolymer module using the corresponding transmembrane (TM) domain of bacteriorhodopsin (bR) as the template. The coordinates for amino-ter minal residue sequence, and carboxyl-terminal residue sequence, extracellular and cytoplasmic loops were generated using LOOP SEARCH algorithm. Subsequently the structural model was merged into the complex with HIV-1 gp120 and CD4. RESULTS: Human CCR5 interacted with both an HIV-1 gp120 and CD4. The N-terminal residues (especially Met1 and Gln4) of human CCR5, contacted with CD4 residues, mainly 7Nith one span (56 - 59) of CD4 in electrostatic interaction and hydrogen-bonds. The binding sites of human CCR5 were buried in a hydrophobic center surrounded by a highly basic periphery. On the other hand, direct interatomic contacts were made between ? CCR5 residues and 6 gp120 amino-acid residues, which included van der Waals contacts, hydrophobic interaction, and hydrogen bonds. CONCLUSION: The interaction model should be helpful for rational design of novel anti-HIV drugs.

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在自然条件下,采用人工模拟水缸培养方法,研究了湖泊底泥不同Cu、Cd处理对沉水植物伊乐藻生长、叶绿素含量以及Cu、Cd吸收和积累的影响。结果表明,较低浓度Cu刺激伊乐藻的生长(生物量、叶绿素),高浓度抑制伊乐藻的生长;随着Cd处理浓度的增加,伊乐藻的生物量、叶绿素含量均一直降低,在底泥Cd含量为168.69mg·kg-1DW(含背景值)时,植株出现死亡。随着Cu处理浓度的增加,伊乐藻体内的Cu含量一直增加,在底泥Cu含量为414mg·kg-1DW(含背景值)时,根部、叶部的富集系数均达到最大(0.21和0

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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

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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

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

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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

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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

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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

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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

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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。

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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。