大麦TILLING群体的构建及EDR1基因突变的检测

该研究选用栽培大麦品种‘西引2号’,通过化学诱变剂甲基磺酸乙酯（ethyl methane sulfonate, EMS）处理,创建了3 750个 M₁及2 012个 M₂突变株系。结果表明：在M₂中,有115株表现黄化,98株表现矮化,101株表现极早或极晚抽穗,其他35株表现分蘖少、叶片小或者不育等性状,所有突变株系占M₂群体的17.35%;M₂的基因组DNA用于突变频率的研究,用优化的CELⅠ酶切体系对M₂株系进行了EDR1基因突变体筛选,获得了EDR1基因的3个突变体,其中一个发生在外显子区域,导致了氨基酸Pro到Ser的转换,突变频率平均为每661 kb一个点突变,这与前人研究的突变频率基本在一个范围内。该研究创建了大麦品种‘西引2号’的TILLING筛选群体,并用于EDR1突变体的筛选。为大麦性状研究提供了不同的思路,搭建了新的资源和技术平台。     

恶臭假单胞菌ND6菌株catA基因的克隆和表达及其儿茶酚裂解途径探讨

恶臭假单胞菌ND6菌株的萘降解质粒pND6-1中编码儿茶酚1,2-双加氧酶的catA基因在大肠杆菌中进行了克隆和表达,并研究表达产物的酶学性质。结果表明:酶的K_m为0.019μmol/L,V_max为1.434μmol/(min.mg);具有很好的耐热性,在50℃保温45min后仍能够保留酶活力的93.7%;Fe²⁺对酶活性有显著的促进作用,其比活力是对照反应的292%;酶对4-氯儿茶酚的催化活性非常低,属于Ⅰ型儿茶酚1,2-双加氧酶。以萘为底物生长时,ND6菌株的细胞提取液中既存在催化邻位裂解途径的儿茶酚1,2-双加氧酶活性,也存在催化间位裂解途径的儿茶酚2,3-双加氧酶活性。以苯甲酸、对羟基苯甲酸和苯乙酸为唯一碳源生长时,ND6菌株细胞提取液的儿茶酚1,2-双加氧酶活性远远大于儿茶酚2,3-双加氧酶活性。表明ND6菌株既能通过儿茶酚间位裂解途径降解萘,也能通过儿茶酚邻位裂解途径降解萘,而以苯甲酸、对羟基苯甲酸和苯乙酸为诱导物时只利用儿茶酚邻位裂解途径。     

温度与CO2浓度升高对集胞藻PCC 6803修复UV损伤的关键基因转录量的影响

通过Taqman探针绝对定量法研究了集胞藻PCC 6803在5种不同的环境条件下:(1)25℃+400μmol/mol CO₂,(2)29℃+400μmol/mol CO₂,(3)25℃+800μmol/mol CO₂,(4)29℃+800μmol/mol CO₂,(5)25℃+1200μmol/mol CO₂,其phrA/psbA1/psbA2/psbA3等UV修复基因和16S rRNA基因的转录本拷贝数的变化情况。结果表明:温度与CO₂浓度的升高可以导致集胞藻PCC 6803的psbA2/psbA3基因和16S rRNA转录本拷贝数的大幅减少,说明温室效应将有可能导致蓝藻的UV损伤修复能力与核糖体合成能力的下降;温度升高和CO₂浓度升高对psbA2/psbA3基因和16S rRNA转录本拷贝数的联合作用表现为互相抵消,说明温度升高与CO₂浓度升高的联合作用的机制较复杂,值得深入研究。     

p14ARF对人黑色素瘤细胞增殖的影响及其作用机理的初探

ARF(alternative reading frame)作为INK4a/ARF的β转录产物,能够稳定p53, 诱导细胞周期阻断或凋亡.利用高表达p14^ARF的人黑色素瘤细胞模型,探讨了ARF抑制细胞增殖的分子作用机理.研究发现p14^ARF高表达能将细胞周期阻断在G1和G2期, p53, p21^cip1和p27^kip1蛋白水平明显增强, 而p-ERK1/2,CyclinD1和CyclinE蛋白水平下降, 明显抑制细胞生长. 提示p14^ARF能通过ERK(extracellular signal-regulated kinase)信号通路相互协调作用抑制A375细胞增殖.     

Somatic embryogenic tissue establishment from mature Pinus nigra Arn. ssp. salzmannii embryos

Summary Somatic embryogenesis from mature zygotic embryos of salgare?o pine (Pinus nigra Arn. ssp. salzmannii) was induced after 2 wk of culture in L₁ medium [Murashige and Skoog mineral solution with 10.7 μM naphthaleneacetic acid (NAA) and 8.8 μM 6-benzyladenine (BA)] or L₂ medium [Gupta and Durzan mineral solution (DCR)] supplemented with the phytohormone combination as above. Four different combinations of growth regulators, NAA (2.6–10.7 μM) and BA (6.6–8.8 μM), were tried for subsequent passage. The best percentage of embryo induction and manifestation was obtained on DCR medium with 2.6 μM NAA and 6.6–8.8 μM BA. Transfer of isolated somatic embryos from the basal media to L₃ medium (Quoirin and Le Poivre modified mineral solution without hormones and supplemented with 0.3% activated charcoal), facilitated random embryo maturation and some development into plantlets.     

Effects of micromolar concentrations of manganese, copper, and zinc on α1-adrenoceptor-mediating contraction in rat aorta

To determine the influences of the Mn, Cu, and Zn on α₁-adrenoceptor (AR)-mediated vasoconstriction, we investigated their effects on vasoconstriction produced by the α₁-AR agonist phenylephrine in isolated rings of rat thoracic aorta. The cumulative concentration-contraction curves for phenylephrine were obtained in the absence and presence of Mn (0.3, 1, 3 μM), Cu (1, 10, 16 μM), and Zn (0.3, 1, 10 μM). Mn, Cu, and Zn each inhibited phenylephrine-mediated contraction in a dose-dependent manner. The maximal phenylephrine-induced contraction was significantly reduced by the pretreatment of the arterial rings with 10 and 16 μM Cu (p<0.05). The results suggest that variations in the plasma concentrations of metal might lead to changes in α₁-AR-mediated constrictive response.     

茄科作物青枯菌NADH脱氢酶F亚基在细胞运动和致病性中的功能研究

[目的]劳尔氏菌（Ralstonia solanacearum）在茄科作物上引起严重的细菌性青枯病,本研究旨在发掘青枯劳尔氏菌与致病相关的基因。[方法]利用Tn5转座子构建随机插入突变体,分析生物膜形成、细胞运动和致病性;对有表型变化的突变体,运用TAIL-PCR方法鉴定Tn5插入位点,确定所突变的基因。[结果]以模式菌株GMI000为出发菌,总共获得了400个突变体,其中2个突变体不能形成生物膜,在软琼脂平板上的运动能力下降;接种感病番茄植物,这2个突变体都不能引起萎焉症状。TAIL-PCR结果显示,2个突变体的Tn5插入位点都在NADH脱氢酶F亚基（nuoF）中,距离翻译起始位点分别为103-bp和225-bp。ripAY基因启动子推动的nuoF基因互补载体,完全恢复了2个突变体的表型。[结论]NADH脱氢酶复合物是微生物呼吸电子传递链中的第一步催化酶。我们的结果表明,NADH脱氢酶复合物对R.solanacearum生物膜形成、细胞运动和致病性也有重要作用。     

细菌视紫红质光循环中间体M412的动力学初探

采用紫外可见吸收光谱技术和闪光光解技术,初步观察了细菌视紫红质(BR)分子在宽pH范围（2.1～12.3）内的特征吸收峰以及M₄₁₂的相对浓度和M₄₁₂的慢成分半衰期的变化,并对其结构和光循环功能进行了讨论.紫外可见吸收光谱实验结果显示：pH=5.0～10.0时,BR最大特征吸收峰值约为568 nm;pH＜5.0时,BR最大特征吸收峰发生红移;pH＞10.0时,BR最大特征吸收峰发生蓝移.闪光动力学光谱结果显示：pH为7.3～9.5时,M₄₁₂的相对浓度(M₀)基本稳定在0.038左右;pH＜7.3时,M₀逐渐减小;pH＞9.5时,M₀明显上升,在pH=11.8时达到最大值0.1355,随后又快速下降.pH为2.1～7.3时,M₄₁₂的慢成分半衰期(t^s_1/2)值在(4.1±1.1)ms左右;pH＞7.3时,t^s_1/2值急剧延长到40 677.4 ms.推测在高pH条件下,BR分子的光循环有新的路径和机理.     

特异腐质霉角质酶-OMP25融合蛋白在大肠杆菌中的高效表达

【目的】通过探究特异腐质霉角质酶-OMP25融合蛋白(HiC-OMP25)在不同大肠杆菌(Escherichia coli)菌株中的表达情况、底物降解情况、热稳定性及宿主菌细胞膜通透性与细胞表面疏水性,揭示表达HiC-OMP25时不同宿主菌的差异性,并进一步提高HiC-OMP25在大肠杆菌中的表达量。【方法】分别在E.coli BL21(DE3)及E.coli C43(DE3)中表达HiC-OMP25,并测定其对对硝基苯丁酸酯(4-nitrophenol butyrate,pNPB)、聚丙烯酸乙酯(polyethyl acrylate,PEA)的降解效果、50℃稳定性;测定表达HiC-OMP25时宿主菌的细胞膜通透性及细胞表面疏水性变化;共表达伴侣蛋白提高HiC-OMP25在E.coli C43(DE3)中的表达量。【结果】HiC-OMP25在E.coli BL21(DE3)与E.coli C43(DE3)中均成功表达并降解pNPB,但前者对PEA的降解效果及50 ℃稳定性均低于后者。同时,表达HiC-OMP25显著增强了E.coli BL21(DE3)的细胞膜通透性及细胞表面疏水性。HiC-OMP25与巯基氧化酶(Erv1p)、二硫键异构酶(DsbC)在E.coli C43(DE3)中共表达时,其表达量为原始菌株的2.14倍,且对pNPB及PEA均有良好的降解效果。【结论】异源表达时,HiC-OMP25在E.coli C43(DE3)中正确折叠,而在E.coli BL21(DE3)中未完全正确折叠;通过共表达伴侣蛋白提高了HiC-OMP25在E.coli C43(DE3)中的表达量,为以后HiC-OMP25的工业化生产及应用奠定了基础。     

Arsenic suppresses necrosis induced by selenite in human leukemia HL-60 cells

Selenium, an essential trace element for humans, has been shown to have anticancer effects. Arsenic, a possibly essential ultratrace element for humans, has been used in the treatment of leukemia. Anticancer effects of selenium and arsenic have been related to their ability to induce apoptosis. Because humans are exposed to diverse trace elements simultaneously, it is important to learn their interrelationship. In this study, we demonstrate that sodium selenite (Na₂SeO₃) causes apoptosis at 3 μM and necrosis at high concentrations (>3 μM) in HL-60 cells. Similarly, both sodium arsenite (NaAsO₂) at 50 μM and sodium arsenate (Na₂HAsO₄) induce apoptosis at 500 μM and necrosis at higher concentrations (>50 μM and >500 μM, respectively) in HL-60 cells. Arsenite/arsenate, but not selenite, enhances AP-1 DNA-binding activity. This finding indicates different mechanisms through which apoptosis is induced by these two elements. Interestingly, we observed that HL-60 cell necrosis induced by a high concentration (>3 μM) of selenite was essentially inhibited by arsenic (50 μM of NaAsO₂ or 500 μM of Na₂HAsO₄), which resulted in a net effect of apoptosis. Because AP-1 DNA-binding activity was not induced in the presence of a combination of necrotic amount of selenite and apoptotic amount of arsenite/arsenate, the observed apoptosis apparently was through the mechanism used by selenite. Our results suggest, for the first time, that the toxic necrotic effect of selenite can be neutralized by arsenite/arsenate at the cellular level. The U.S. Department of Agriculture, Agricultural Research Service, Northern Plains Area, is an equal opportunity/affirmative action employer and all agency services are available without discrimination. Mention of a trademark or proprietary product does not constitute a guarantee or warranty of the product by the U.S. Department of Agriculture and does not imply its approval to the exclusion of other products that may also be suitable.     

Insight into the metabolism of 1,1,1-trichloro-2,2-bis(4-chlorophenyl)ethane (DDT) by biphenyl dioxygenases

In this work we have investigated the ability of the biphenyl dioxygenase of Burkholderia xenovorans LB400 (BphAE_LB400) and of Pandoraea pnomenusa B356 (BphAE_B356) to metabolize DDT. Data show BphAE_LB400 is unable to metabolize this substrate but BphAE_B356 metabolizes DDT to produce two stereoisomers. Structural analysis of DDT-docked BphAE_LB400 and BphAE_B356 identified residue Phe336 of BphAE_LB400 as critical to prevent productive binding of DDT to BphAE_LB400. Furthermore, the fact that residue Gly319 of BphAE_B356 is less constrained than Gly321 of BphAE_LB400 most likely contributes to the ability of BphAE_B356 to bind DDT productively. This was confirmed by examining the ability of BphAE chimeras obtained by shuffling bphA genes from strain B356 and LB400. Chimeras where residues Thr335 (which modulates the constraints on Gly321) and Phe336 (which contacts the substrate) of BphAE_LB400 were replaced by Gly and Ile respectively were able to metabolize DDT. However their stereospecificities varied depending on the presence of other segments or residues from BphAE_B356. Structural analysis suggests that either one or both of residue 267 and a segments comprised of residue 247–260 are likely involved in stereospecificity.     

Structural insight into the expanded PCB-degrading abilities of a biphenyl dioxygenase obtained by directed evolution

The biphenyl dioxygenase of Burkholderia xenovorans LB400 is a multicomponent Rieske-type oxygenase that catalyzes the dihydroxylation of biphenyl and many polychlorinated biphenyls (PCBs). The structural bases for the substrate specificity of the enzyme's oxygenase component (BphAE_LB400) are largely unknown. BphAE_p4, a variant previously obtained through directed evolution, transforms several chlorobiphenyls, including 2,6-dichlorobiphenyl, more efficiently than BphAE_LB400, yet differs from the parent oxygenase at only two positions: T335A/F336M. Here, we compare the structures of BphAE_LB400 and BphAE_p4 and examine the biochemical properties of two BphAE_LB400 variants with single substitutions, T335A or F336M. Our data show that residue 336 contacts the biphenyl and influences the regiospecificity of the reaction, but does not enhance the enzyme's reactivity toward 2,6-dichlorobiphenyl. By contrast, residue 335 does not contact biphenyl but contributes significantly to expansion of the enzyme's substrate range. Crystal structures indicate that Thr335 imposes constraints through hydrogen bonds and nonbonded contacts to the segment from Val320 to Gln322. These contacts are lost when Thr is replaced by Ala, relieving intramolecular constraints and allowing for significant movement of this segment during binding of 2,6-dichlorobiphenyl, which increases the space available to accommodate the doubly ortho-chlorinated congener 2,6-dichlorobiphenyl. This study provides important insight about how Rieske-type oxygenases can expand substrate range through mutations that increase the plasticity and/or mobility of protein segments lining the catalytic cavity.     

Metabolism of dibenzofuran and dibenzo-p-dioxin by the biphenyl dioxygenase of Burkholderia xenovorans LB400 and Comamonas testosteroni B-356

We examined the metabolism of dibenzofuran (DF) and dibenzo-p-dioxin (DD) by the biphenyl dioxygenase (BPDO) of Comamonas testosteroni B-356 and compared it with that of Burkholderia xenovorans LB400. Data showed that both enzymes oxygenated DF at a low rate, but Escherichia coli cells expressing LB400 BPDO degraded DF at higher rate (30 nmol in 18 h) compared with cells expressing B-356 BPDO (2 nmol in 18 h). Furthermore, both BPDOs produced dihydro-dihydroxy-dibenzofuran as a major metabolite, which resulted from the lateral oxygenation of DF. 2,2,3-Trihydroxybiphenyl (resulting from angular oxygenation of DF) was a minor metabolite produced by both enzymes. Deuterated DF was used to demonstrate the production of 2,2,3-dihydroxybiphenyl through angular oxygenation of DF. When tested for their ability to oxygenate DD, both enzymes produced as sole metabolite, 2,2,3-trihydroxybiphenyl ether at about the same rate, indicating similar catalytic properties toward this substrate. Altogether, although LB400 and B-356 BPDOs oxygenate a different range of chlorobiphenyls, their metabolite profiles toward DF and DD are similar. This suggests that co-planarity influences the regiospecificity of BPDO toward DF and DD to a higher extent than the presence of an ortho substituent on the molecule.     

Characterization of hybrid biphenyl dioxygenases obtained by recombining Burkholderia sp. strain LB400 bphA with the homologous gene of Comamonas testosteroni B-356.

The bacterial degradation of polychlorinated biphenyls depends on the ability of the enzyme biphenyl 2,3-dioxygenase (BPDO) to catalyze their oxygenation. Analysis of hybrid BPDOs obtained using common restriction sites to exchange large DNA fragments between LB400 bphA and B-356 bphA showed that the C-terminal portion of LB400 alpha subunit can withstand extensive structural modifications, and that these modifications can change the catalytic properties of the enzyme. On the other hand, exchanging the C-terminal portion of B-356 BPDO alpha subunit with that of LB400 alpha subunit generated inactive chimeras. Data encourage an enzyme engineering approach, consisting of introducing extensive modifications of the C-terminal portion of LB400 bphA to extend BPDO catalytic properties toward polychlorinated biphenyls.     

Family shuffling of soil DNA to change the regiospecificity of Burkholderia xenovorans LB400 biphenyl dioxygenase

Previous work has shown that the C-terminal portion of BphA, especially two amino acid segments designated region III and region IV, influence the regiospecificity of the biphenyl dioxygenase (BPDO) toward 2,2'-dichlorobiphenyl (2,2'-CB). In this work, we evolved BPDO by shuffling bphA genes amplified from polychlorinated biphenyl-contaminated soil DNA. Sets of approximately 1-kb DNA fragments were amplified with degenerate primers designed to amplify the C-terminal portion of bphA. These fragments were shuffled, and the resulting library was used to replace the corresponding fragment of Burkholderia xenovorans LB400 bphA. Variants were screened for their ability to oxygenate 2,2'-CB onto carbons 5 and 6, which are positions that LB400 BPDO is unable to attack. Variants S100, S149, and S151 were obtained and exhibited this feature. Variant S100 BPDO produced exclusively cis-5,6-dihydro-5,6-dihydroxy-2,2'-dichlorobiphenyl from 2,2'-CB. Moreover, unlike LB400 BPDO, S100 BphA catalyzed the oxygenation of 2,2',3,3'-tetrachlorobiphenyl onto carbons 5 and 6 exclusively and it was unable to oxygenate 2,2',5,5'-tetrachlorobiphenyl. Based on oxygen consumption measurements, variant S100 oxygenated 2,2'-CB at a rate of 16 +/- 1 nmol min(-1) per nmol enzyme, which was similar to the value observed for LB400 BPDO. cis-5,6-Dihydro-5,6-dihydroxy-2,2'-dichlorobiphenyl was further oxidized by 2,3-dihydro-2,3-dihydroxybiphenyl dehydrogenase (BphB) and 2,3-dihydroxybiphenyl dioxygenase (BphC). Variant S100 was, in addition, able to oxygenate benzene, toluene, and ethyl benzene. Sequence analysis identified amino acid residues M237 S238 and S283 outside regions III and IV that influence the activity toward doubly ortho-substituted chlorobiphenyls.     

Revisiting the regiospecificity of Burkholderia xenovorans LB400 biphenyl dioxygenase toward 2,2'-dichlorobiphenyl and 2,3,2',3'-tetrachlorobiphenyl

2,2'-Dichlorobiphenyl (CB) is transformed by the biphenyl dioxygenase of Burkholderia xenovorans LB400 (LB400 BPDO) into two metabolites (1 and 2). The most abundant metabolite, 1, was previously identified as 2,3-dihydroxy-2'-chlorobiphenyl and was presumed to originate from the initial attack by the oxygenase on the chlorine-bearing ortho carbon and on its adjacent meta carbon of one phenyl ring. 2,3,2',3'-Tetrachlorobiphenyl is transformed by LB400 BPDO into two metabolites that had never been fully characterized structurally. We determined the precise identity of the metabolites produced by LB400 BPDO from 2,2'-CB and 2,3,2',3'-CB, thus providing new insights on the mechanism by which 2,2'-CB is dehalogenated to generate 2,3-dihydroxy-2'-chlorobiphenyl. We reacted 2,2'-CB with the BPDO variant p4, which produces a larger proportion of metabolite 2. The structure of this compound was determined as cis-3,4-dihydro-3,4-dihydroxy-2,2'-dichlorobiphenyl by NMR. Metabolite 1 obtained from 2,2'-CB-d(8) was determined to be a dihydroxychlorobiphenyl-d(7) by gas chromatographic-mass spectrometric analysis, and the observed loss of only one deuterium clearly shows that the oxygenase attack occurs on carbons 2 and 3. An alternative attack at the 5 and 6 carbons followed by a rearrangement leading to the loss of the ortho chlorine would have caused the loss of more than one deuterium. The major metabolite produced from catalytic oxygenation of 2,3,2',3'-CB by LB400 BPDO was identified by NMR as cis-4,5-dihydro-4,5-dihydroxy-2,3,2',3'-tetrachlorobiphenyl. These findings show that LB400 BPDO oxygenates 2,2'-CB principally on carbons 2 and 3 and that BPDO regiospecificity toward 2,2'-CB and 2,3,2,',3'-CB disfavors the dioxygenation of the chlorine-free ortho-meta carbons 5 and 6 for both congeners.     

Characterization of biphenyl dioxygenase of Pandoraea pnomenusa B-356 as a potent polychlorinated biphenyl-degrading enzyme

Biphenyl dioxygenase (BPDO) catalyzes the aerobic transformation of biphenyl and various polychlorinated biphenyls (PCBs). In three different assays, BPDO(B356) from Pandoraea pnomenusa B-356 was a more potent PCB-degrading enzyme than BPDO(LB400) from Burkholderia xenovorans LB400 (75% amino acid sequence identity), transforming nine congeners in the following order of preference: 2,3',4-trichloro approximately 2,3,4'-trichloro > 3,3'-dichloro > 2,4,4'-trichloro > 4,4'-dichloro approximately 2,2'-dichloro > 2,6-dichloro > 2,2',3,3'-tetrachloro approximately 2,2',5,5'-tetrachloro. Except for 2,2',5,5'-tetrachlorobiphenyl, BPDO(B356) transformed each congener at a higher rate than BPDO(LB400). The assays used either whole cells or purified enzymes and either individual congeners or mixtures of congeners. Product analyses established previously unrecognized BPDO(B356) activities, including the 3,4-dihydroxylation of 2,6-dichlorobiphenyl. BPDO(LB400) had a greater apparent specificity for biphenyl than BPDO(B356) (k(cat)/K(m) = 2.4 x 10(6) +/- 0.7 x 10(6) M(-1) s(-1) versus k(cat)/K(m) = 0.21 x 10(6) +/- 0.04 x 10(6) M(-1) s(-1)). However, the latter transformed biphenyl at a higher maximal rate (k(cat) = 4.1 +/- 0.2 s(-1) versus k(cat) = 0.4 +/- 0.1 s(-1)). A variant of BPDO(LB400) containing four active site residues of BPDO(B356) transformed para-substituted congeners better than BPDO(LB400). Interestingly, a substitution remote from the active site, A267S, increased the enzyme's preference for meta-substituted congeners. Moreover, this substitution had a greater effect on the kinetics of biphenyl utilization than substitutions in the substrate-binding pocket. In all variants, the degree of coupling between congener depletion and O(2) consumption was approximately proportional to congener depletion. At 2.4-A resolution, the crystal structure of the BPDO(B356)-2,6-dichlorobiphenyl complex, the first crystal structure of a BPDO-PCB complex, provided additional insight into the reactivity of this isozyme with this congener, as well as into the differences in congener preferences of the BPDOs.     

Biphenyl dioxygenase from an arctic isolate is not cold adapted

Biphenyl dioxygenase from the psychrotolerant bacterium Pseudomonas sp. strain Cam-1 (BPDO(Cam-1)) was purified and found to have an apparent k(cat) for biphenyl of 1.1 +/- 0.1 s(-1) (mean +/- standard deviation) at 4 degrees C. In contrast, BPDO(LB400) from the mesophile Burkholderia xenovorans LB400 had no detectable activity at this temperature. At 57 degrees C, the half-life of the BPDO(Cam-1) oxygenase was less than half that of the BPDO(LB400) oxygenase. Nevertheless, BPDO(Cam-1) appears to be a typical Pseudomonas pseudoalcaligenes KF707-type dioxygenase.     

Metabolism of Doubly para-Substituted Hydroxychlorobiphenyls by Bacterial Biphenyl Dioxygenases

In this work, we examined the profile of metabolites produced from the doubly para-substituted biphenyl analogs 4,4′-dihydroxybiphenyl, 4-hydroxy-4′-chlorobiphenyl, 3-hydroxy-4,4′-dichlorobiphenyl, and 3,3′-dihydroxy-4,4′-chlorobiphenyl by biphenyl-induced Pandoraea pnomenusa B356 and by its biphenyl dioxygenase (BPDO). 4-Hydroxy-4′-chlorobiphenyl was hydroxylated principally through a 2,3-dioxygenation of the hydroxylated ring to generate 2,3-dihydro-2,3,4-trihydroxy-4′-chlorobiphenyl and 3,4-dihydroxy-4′-chlorobiphenyl after the removal of water. The former was further oxidized by the biphenyl dioxygenase to produce ultimately 3,4,5-trihydroxy-4′-chlorobiphenyl, a dead-end metabolite. 3-Hydroxy-4,4′-dichlorobiphenyl was oxygenated on both rings. Hydroxylation of the nonhydroxylated ring generated 2,3,3′-trihydroxy-4′-chlorobiphenyl with concomitant dechlorination, and 2,3,3′-trihydroxy-4′-chlorobiphenyl was ultimately metabolized to 2-hydroxy-4-chlorobenzoate, but hydroxylation of the hydroxylated ring generated dead-end metabolites. 3,3′-Dihydroxy-4,4′-dichlorobiphenyl was principally metabolized through a 2,3-dioxygenation to generate 2,3-dihydro-2,3,3′-trihydroxy-4,4′-dichlorobiphenyl, which was ultimately converted to 3-hydroxy-4-chlorobenzoate. Similar metabolites were produced when the biphenyl dioxygenase of Burkholderia xenovorans LB400 was used to catalyze the reactions, except that for the three substrates used, the BPDO of LB400 was less efficient than that of B356, and unlike that of B356, it was unable to further oxidize the initial reaction products. Together the data show that BPDO oxidation of doubly para-substituted hydroxychlorobiphenyls may generate nonnegligible amounts of dead-end metabolites. Therefore, biphenyl dioxygenase could produce metabolites other than those expected, corresponding to dihydrodihydroxy metabolites from initial doubly para-substituted substrates. This finding shows that a clear picture of the fate of polychlorinated biphenyls in contaminated sites will require more insights into the bacterial metabolism of hydroxychlorobiphenyls and the chemistry of the dihydrodihydroxylated metabolites derived from them.     

The phytoremediation potential of bioenergy crop Ricinus communis for DDTs and cadmium co-contaminated soil

Cadmium (Cd) and dichlorodiphenyltrichloroethane (DDT) or its metabolite residues are frequently detected in agricultural soils and food, posing a threat to human health. The objective of this study was to compare the ability of 23 genotypes of Ricinus communis in mobilizing and uptake of Cd and DDTs (p,p′-DDT, o,p′-DDT, p,p′-DDD and p,p′-DDE) in the co-contaminated soil. The plant genotypes varied largely in the uptake and accumulation of DDTs and Cd, with mean concentrations of 0.37, 0.43 and 70.51 for DDTs, and 1.22, 2.27 and 37.63 mg kg⁻¹ dw for Cd in leaf, stem and root, respectively. The total uptake of DDTs and Cd varied from 83.1 to 267.8 and 66.0 to 155.1 μg per pot, respectively. These results indicate that R. communis has great potential for removing DDTs and Cd from contaminated soils attributed to its fast growth, high biomass, strong absorption and accumulation for both DDTs and Cd.