降解2,4-二氯酚微生物的分离及其2,4-二氯酚羟化酶基因的克隆和表达

从土壤中分离到一株降解2,4-二氯酚能力较强的细菌菌株GT241-1,经鉴定该菌株属于假单胞菌属。菌株GT241-1在最适条件下能在48h内将90mg/L的2,4-DCP降解91%,能利用2,4-二氯酚、2,4-二氯苯氧乙酸、苯甲酸和儿茶酚为唯一碳源生长。采用Southern杂交对2,4-二氯酚羟化酶基因（dcpA）定位后构建基因组文库,再用斑点杂交筛选目的转化子,克隆了该菌株的dcpA。序列测定得知含dcpA的亚克隆片段全长2389bp,其中dcpA基因编码区1797bp。核苷酸和氨基酸序列分析表明,dcpA与已在GenBank登记的相关基因有一定的差异。dcpA基因能够在大肠杆菌转化子中成功地表达有生物活性的酶。     

一种新的乙酰高丝氨酸内酯水解酶基因的克隆和表达

目的 获得新的降解革兰阴性细菌数量阈值感应信号分子乙酰高丝氨酸内酯类化合物(AHL)的水解酶基因。方法 选择性富集和培养土壤中耐热细菌,抽取细菌总DNA作为模板,特异性聚合酶链反应扩增乙酰高丝氨酸内酯水解酶基因,进行克隆和DNA序列分析及原核表达。结果 得到1个新的AHL水解酶基因,该基因与已知基因的核苷酸序列和对应的氨基酸序列同源性最高分别为87％和94％。该基因在原核表达系统中表达,得到了与预期相对分子质鲢(Mr)一致的蛋白质。结论 证实乙酰高丝氨酸内酯水解酶广泛存在于环境微生物中。为进一步研究提供条件。     

氯酚类化合物的微生物降解研究进展

综述了近年在具有降解氯酚类化合物能力的微生物的筛选、氯酚类化合物的好氧和厌氧降解机制以及现代生物技术的开发利用研究．阐述了氯酚类化合物在不同条件下的降解路径．在好氧条件下,单氯酚和二氯酚在氧化酶的攻击下形成氯代邻二酚,邻二酚开环生成相应的氯代粘康酸或半醛,粘康酸内酯化过程中释放氯离子;高度氯代的化合物则是在氢氧化酶作用下生成氯代醌,并逐步脱去所有的氯原子生成苯酚后才开环．在厌氧或缺氧条件下,氯酚进行还原脱氯,在得到电子的同时去掉一个氯取代基．     

厌氧微生物菌群XH-1对2,4,6-三氯苯酚的降解特性

有机污染物2,4,6-三氯苯酚(2,4,6-TCP)普遍存在于地下水和河流底泥等厌氧环境中。为了探究厌氧微生物菌群XH-1对2,4,6-TCP的降解能力,本研究以2,4,6-TCP为底物,接种XH-1建立微宇宙培养体系,并以中间产物4-氯苯酚(4-CP)和苯酚为底物分别进行分段富集培养,利用高效液相色谱分析底物的降解转化,同时基于16S rRNA基因高通量测序分析微生物群落结构变化。结果表明: 2,4,6-TCP(122 μmol·L^-1)以0.15 μmol·d^-1的速率在80 d内被完全降解转化,降解中间产物分别为2,4-二氯苯酚(2,4-DCP)、4-氯苯酚和苯酚,所有中间产物最终在325 d被完全降解。高通量测序结果表明,脱卤杆菌和脱卤球菌可能驱动2,4,6-TCP还原脱氯,其中,脱卤球菌可能在4-CP的脱氯转化中发挥重要作用,并与丁酸互营菌和产甲烷菌联合作用彻底降解2,4,6-TCP。     

哈茨木霉A25-2纤维二糖水解酶玉基因的克隆及其编码催化功能域的序列在绿色木酶HP35-3中的表达

本研究从哈茨木霉(Trichoderma harzianum) A25-2总RNA中利用RT-PCR的方法扩增到其纤维二糖水解酶I基因的cDNA序列,并对该基因编码的氨基酸序列进行分析,得到cbhI基因中编码催化功能域的序列。将催化功能域编码序列克隆到表达载体pCP-GH中,用PEG-CaCl2介导的原生质体转化方法将重组质粒转化到绿色木霉(Trichoderma viride) HP35-3中,筛选得到12个转化子。以p-NPC为底物,测定了该12个转化子的酶活力,获得比活力最高的转化子Tv/CDHl-CBM-5,其纤维二糖水解酶活力是HP35-3的3.8倍。SDS-PAGE分析表明,绿色木霉表达了导入的含A25-2纤维二糖水解酶I催化功能域的编码序列。     

盐胁迫条件下古菌超氧化物歧化酶增强细菌降解硝基酚

【背景】Burkholderia sp. SJ98利用对硝基酚和2-氯-4-硝基酚为唯一碳源和能源进行生长,通过异源表达嗜盐古菌Haloferax sp. D1227中的超氧化物歧化酶SodA,使菌株SJ98在500 mmol/L NaCl条件下仍具有降解对硝基酚的能力。然而该重组细菌在普通和高盐条件下其降解基因的转录和降解酶比活力的高低,以及该菌在高盐条件下是否还能降解对硝基酚衍生物尚未知晓。【目的】研究Burkholderia sp. SJ98的耐盐上限,观察含有sodA的细菌SJ98在普通和高盐条件下降解对硝基酚和2-氯-4-硝基酚的能力,检测重组菌中pnpA基因的转录和硝基酚单加氧酶的活力。【方法】在添加葡萄糖、对硝基酚或2-氯-4-硝基酚的无机盐培养基(分别含400-800 mmol/L NaCl)或M9培养基(含0和500 mmol/L NaCl)中培养细菌SJ98及其重组菌。通过紫外分光光度计和高效液相色谱法检测菌株生长和底物降解。通过实时荧光定量PCR分别以两种硝基酚为诱导物,检测未添加和添加500 mmol/L NaCl时,硝基酚单加氧酶编码基因pnpA的转录量变化。利用紫外分光光度计分别以两种硝基酚为底物,检测在添加500 mmol/L NaCl时,重组菌和空载体菌的粗酶液中硝基酚单加氧酶对两种底物的活力变化。【结果】野生型菌株SJ98以葡萄糖为碳源生长的NaCl耐受浓度是600mmol/L。未添加NaCl时,重组菌SJ98[pCM-pnpR-PpnpA-sodA-rfp]生长和降解对硝基酚的能力远优于野生菌。添加500 mmol/L NaCl时,重组菌SJ98[pBBR-sodA]仍保持了利用2-氯-4-硝基苯酚底物生长和降解该底物的能力,而空载体菌SJ98[pBBR1MCS-2]的生长和降解能力完全丧失;重组菌SJ98[pBBR-sodA]粗酶液中单加氧酶对于对硝基酚和2-氯-4-硝基酚的活力均约为野生菌的1/3。分别以两种硝基酚为诱导物时,无论是否添加NaCl,重组菌SJ98[pBBR-sodA]中硝基酚单加氧酶编码基因pnpA的转录量比野生型中高出约17-25倍;但添加500 mmol/L NaCl时,pnpA的转录均受到部分抑制。【结论】本研究为利用古菌超氧化物歧化酶对细菌进行改造以提高普通环境和高盐环境中细菌降解硝基芳烃污染物能力的应用提供了潜在的可行性。     

固定化白腐真菌降解水溶液中2,4-二氯酚的研究

研究固定化黄孢原毛平革菌对水溶液中2,4-二氯酚（2,4-DCP）的降解效果,探讨固定化黄孢原毛平革菌处理水溶液中氯酚类污染物的可行性．结果表明,采用固定化方法处理的白腐真菌．其产酶稳定性及酶活均比游离态白腐真菌有显著提高．2,4-DCP降解效果受固定化孢子接种量、pH值、摇床转速、2,4-DCP的初始浓度和表面活性剂浓度的影响．当pH为4．5,摇床转速180r／min,培养基含有1％的Tween 80,2,4-DCP初始浓度为40mg／L时,加入10mL固定化白腐真菌孢子,2,4-DCP去除效果最好．     

2,4-二氯苯酚在土壤与河流底泥中降解动力学

以南京化学工业园内四柳河沿岸土壤与河流底泥为研究对象,通过土壤灭菌、温度与污染物初始浓度调控,研究了2,4-二氯苯酚在土壤与河流底泥中降解动力学及其影响因子。结果表明:微生物对2,4-二氯苯酚降解起主导作用,在45d内,非灭菌土壤和河流底泥的降解率分别是灭菌条件下的1.5～3倍、1.4～2.8倍,土壤和河流底泥中的2,4-二氯苯酚微生物降解量分别为0.128～0.599和0.113～0.718mg·kg-1,非灭菌处理半衰期时间短于灭菌处理;(10±1)℃～(30±1)℃范围内,随着温度的增高,2,4-二氯苯酚降解加快,在(30±1)℃土壤与河流底泥中残留量最小,分别为0.305和0.203mg·kg-1,半衰期也最短;土壤与河流底泥中的2,4-二氯苯酚均在其浓度为0.5mg·kg-1时降解最快,随着初始浓度的增加,2,4-二氯苯酚降解速度呈现递减趋势,半衰期增长。     

零价铁对2,4-二氯酚生物还原脱氯的影响研究

采用间歇试验,接种驯化两月的厌氧混合微生物,考察厌氧体系中添加零价铁（Fe^0）对2,4-二氯酚（2,4-DCP）生物还原脱氯效果的影响,并对影响“Fe^O＋微生物”体系的一些因素进行了探索。结果显示：与零价铁或微生物的单独作用相比,“Fe^O＋微生物”体系能够有效促进2,4-DCP的脱氯反应,最佳Fe^O投加量和微生物接种量分别为0.5g／L和376.2mgVSS／L;初始pH=8.0对2,4-DCP的转化效果最好,偏酸性环境不利于污染物转化;微生物接种量与铁用量之间有一适宜比例,一定范围内增加微生物接种量可催生出更多可降解污染物的酶或酶系,提高2,4-DCP的降解效果。     

零价铁对2,4-二氯酚生物还原脱氯的影响研究

采用间歇试验, 接种驯化两月的厌氧混合微生物, 考察厌氧体系中添加零价铁(Fe0)对2,4-二氯酚(2,4-DCP)生物还原脱氯效果的影响, 并对影响“Fe0+微生物”体系的一些因素进行了探索。结果显示：与零价铁或微生物的单独作用相比, “Fe0+微生物”体系能够有效促进2,4-DCP的脱氯反应, 最佳Fe0投加量和微生物接种量分别为0.5 g/L和376.2 mgVSS/L; 初始pH = 8.0对2,4-DCP的转化效果最好, 偏酸性环境不利于污染物转化; 微生物接种量与铁用量之间有一适宜比例, 一定范围内增加微生物接种量可催生出更多可降解污染物的酶或酶系, 提高2,4-DCP的降解效果。     

Nucleotide sequence and expression of clcD, a plasmid-borne dienelactone hydrolase gene from Pseudomonas sp. strain B13.

The clcD structural gene encodes dienelactone hydrolase (EC 3.1.1.45), an enzyme that catalyzes the conversion of dienelactones to maleylacetate. The gene is part of the clc gene cluster involved in the utilization of chlorocatechol and is carried on a 4.3-kilobase-pair BglII fragment subcloned from the Pseudomonas degradative plasmid pAC27. A 1.9-kilobase-pair PstI-EcoRI segment subcloned from the BglII fragment was shown to carry the clcD gene, which was expressed inducibly under the tac promoter at levels similar to those found in 3-chlorobenzoate-grown Pseudomonas cells carrying the plasmid pAC27. In this study, we present the complete nucleotide sequence of the clcD gene and the amino acid sequence of dienelactone hydrolase deduced from the DNA sequence. The NH2-terminal amino acid sequence encoded by the clcD gene from plasmid pAC27 corresponds to a 33-residue sequence established for dienelactone hydrolase encoded by the Pseudomonas sp. strain B13 plasmid pWR1. A possible relationship between the clcD gene and pcaD, a Pseudomonas putida chromosomal gene encoding enol-lactone hydrolase (EC 3.1.1.24) is suggested by the fact that the gene products contain an apparently conserved pentapeptide neighboring a cysteinyl side chain that presumably lies at or near the active sites; the cysteinyl residue occupies position 60 in the predicted amino acid sequence of dienelactone hydrolase.     

Dienelactone hydrolase from Pseudomonas sp. strain B13.

Dienelactone hydrolase (EC 3.1.1.45) catalyzes the conversion of cis- or trans-4-carboxymethylenebut-2-en-4-olide (dienelactone) to maleylacetate. An approximately 24-fold purification from extracts of 3-chlorobenzoate-grown Pseudomonas sp. strain B13 yielded a homogeneous preparation of the enzyme. The purified enzyme crystallized readily and proved to be a monomer with a molecular weight of about 30,000. Each dienelactone hydrolase molecule contains two cysteinyl side chains. One of these was readily titrated by stoichiometric amounts of p-chloromercuribenzoate, resulting in inactivation of the enzyme; the inactivation could be reversed by the addition of dithiothreitol. The other cysteinyl side chain appeared to be protected in the native protein against chemical reaction with p-chloromercuribenzoate. The properties of sulfhydryl side chains in dienelactone hydrolase resembled those that have been characterized for bacterial 4-carboxymethylbut-3-en-4-olide (enol-lactone) hydrolases (EC 3.1.1.24), which also are monomers with molecular weights of about 30,000. The amino acid composition of the dienelactone hydrolase resembled the amino acid composition of enol-lactone hydrolase from Pseudomonas putida, and alignment of the NH2-terminal amino acid sequence of the dienelactone hydrolase with the corresponding sequence of an Acinetobacter calcoaceticus enol-lactone hydrolase revealed sequence identity at 8 of the 28 positions. These observations foster the hypothesis that the lactone hydrolases share a common ancestor. The lactone hydrolases differed in one significant property: the kcat of dienelactone hydrolase was 1,800 min-1, an order of magnitude below the kcat observed with enol-lactone hydrolases. The relatively low catalytic activity of dienelactone hydrolase may demand its production at the high levels observed for induced cultures of Pseudomonas sp. strain B13.     

Degradation of p-chlorotoluene by a mutant of Pseudomonas sp. strain JS6.

Pseudomonas sp. strain JS6 grows on chlorobenzene, p-dichlorobenzene, or toluene as a sole source of carbon and energy. It does not grow on p-chlorotoluene (p-CT). Growth on glucose in the presence of p-CT resulted in the accumulation of 4-chloro-2,3-dihydroxy-1-methylbenzene (3-chloro-6-methylcatechol), 4-chloro-2,3-dihydroxy-1-methylcyclohexa-4,6-diene (p-CT dihydrodiol), and 2-methyl-4-carboxymethylenebut-2-en-4-olide (2-methyl dienelactone). Strain JS21, a spontaneous mutant capable of growth on p-CT, was isolated from cultures of strain JS6 after extended exposure to p-CT. In addition to growing on p-CT, JS21 grew on all of the substrates that supported growth of the parent strain, including p-dichlorobenzene, chlorobenzene, benzene, toluene, benzoate, p-hydroxybenzoate, phenol, and ethylbenzene. The pathway for degradation of p-CT by JS21 was investigated by respirometry, isolation of intermediates, and assay of enzymes in cell extracts. p-CT was converted to 3-chloro-6-methylcatechol by dioxygenase and dihydrodiol dehydrogenase enzymes. 3-Chloro-6-methylcatechol underwent ortho ring cleavage catalyzed by a catechol 1,2-dioxygenase to form 2-chloro-5-methyl-cis,cis-muconate, which was converted to 2-methyl dienelactone. A dienelactone hydrolase converted 2-methyl dienelactone to 2-methylmaleylacetic acid. Preliminary results indicate that a change in wild-type induction patterns allows JS21 to grow on p-CT.     

Degradation of p-chlorotoluene by a mutant of Pseudomonas sp. strain JS6

Pseudomonas sp. strain JS6 grows on chlorobenzene, p-dichlorobenzene, or toluene as a sole source of carbon and energy. It does not grow on p-chlorotoluene (p-CT). Growth on glucose in the presence of p-CT resulted in the accumulation of 4-chloro-2,3-dihydroxy-1-methylbenzene (3-chloro-6-methylcatechol), 4-chloro-2,3-dihydroxy-1-methylcyclohexa-4,6-diene (p-CT dihydrodiol), and 2-methyl-4-carboxymethylenebut-2-en-4-olide (2-methyl dienelactone). Strain JS21, a spontaneous mutant capable of growth on p-CT, was isolated from cultures of strain JS6 after extended exposure to p-CT. In addition to growing on p-CT, JS21 grew on all of the substrates that supported growth of the parent strain, including p-dichlorobenzene, chlorobenzene, benzene, toluene, benzoate, p-hydroxybenzoate, phenol, and ethylbenzene. The pathway for degradation of p-CT by JS21 was investigated by respirometry, isolation of intermediates, and assay of enzymes in cell extracts. p-CT was converted to 3-chloro-6-methylcatechol by dioxygenase and dihydrodiol dehydrogenase enzymes. 3-Chloro-6-methylcatechol underwent ortho ring cleavage catalyzed by a catechol 1,2-dioxygenase to form 2-chloro-5-methyl-cis,cis-muconate, which was converted to 2-methyl dienelactone. A dienelactone hydrolase converted 2-methyl dienelactone to 2-methylmaleylacetic acid. Preliminary results indicate that a change in wild-type induction patterns allows JS21 to grow on p-CT.     

Different types of dienelactone hydrolase in 4-fluorobenzoate-utilizing bacteria

Of various benzoate-utilizing bacteria tested, Alcaligenes eutrophus 335, A. eutrophus H16, A. eutrophus JMP222, A. eutrophus JMP134, Alcaligenes strain A7, and Pseudomonas cepacia were able to grow with 4-fluorobenzoate as the sole source of carbon and energy. P. cepacia also utilizes 3-fluorobenzoate. Except for A. eutrophus JMP134, which is known to grow with 2,4-dichlorophenoxyacetate and 3-chlorobenzoate (R. H. Don and J. M. Pemberton, J. Bacteriol. 145:681-686, 1981), the strains were unable to grow at the expense of these compounds or 4-chlorobenzoate. Assays of cell extracts revealed that all strains express dienelactone hydrolase and maleylacetate reductase activities in addition to enzymes of the catechol branch of the 3-oxoadipate pathway when growing with 4-fluorobenzoate. Induction of dienelactone hydrolase and maleylacetate reductase apparently is not necessarily connected to synthesis of catechol 1,2-dioxygenase type II and chloromuconate cycloisomerase activities, which are indispensable for the degradation of chlorocatechols. Substrate specificities of the dienelactone hydrolases provisionally differentiate among three types of this activity. (i) Extracts of A. eutrophus 335, A. eutrophus H16, A. eutrophus JMP222, and Alcaligenes strain A7 convert trans-4-carboxymethylenebut-2-en-4-olide (trans-dienelactone) much faster than the cis-isomer (type I). (ii) The enzyme present in P. cepacia shows the opposite preference for the isomeric substrates (type II). (iii) Cell extracts of A. eutrophus JMP134, as well as purified dienelactone hydrolase from Pseudomonas strain B13 (E. Schmidt and H.-J. Knackmuss, Biochem. J. 192:339-347, 1980), hydrolyze both dienelactones at rates that are of the same order of magnitude (type III). This classification implies that A. eutrophus JMP134 possesses at least two different dienelactone hydrolases, one of type III encoded by the plasmid pJP4 and one of type I, which is also present in the cured strain JMP222.     

Dienelactone hydrolase from Rhodococcus erythropolis 1 CP: purification and properties

Dienelactone hydrolases (EC 3.1.1.45) have been shown to play an indispensable role in the degradation of chloroaromatic compounds via ortho-cleavage of chlorocatechols. We report on the purification of dienelactone hydrolase of the chlorophenol-utilizing strain Rhodococcus erythropolis 1CP to apparent homogeneity. Dienelactone hydrolase differed fron the corresponding enzymes of other chloroaromatic compound-catabolizing strains in being restricted to substrates with a cis-dienelactone structure. From the cis-dienelactone-hydrolyzing enzyme of a 4-fluorobenzoate-utilizing Burkholderia (Pseudomonas) cepacia strain, it differed considerably in properties such as pH optimum of activity, inhibition by p-chloromercuribenzoate, and amino acid composition. Thus, there is not necessarily a close relationship between substrate specificity and other properties of dienelactone hydrolases.     

Bioconversion of 3-chlorobenzoate to 2-chloromuconate controlled by on line HPLC

Summary Strain RD330 a transposon mutant of Alcaligenes eutrophus JMP134 was considered to be dienelactone hydrolase defective (Don et al. 1985). During a bioconversion experiment with 3CB (3-chlorobenzoate) 2CMA (2-chloro-cis,cis-muconate) was accumulated by RD330 with an overall amount of 31%, but no dienelactone could be detected. Enzyme tests revealed that both enzymes 2CMA-cycloisomerase and dienelactone-hydrolase were induced at low levels in RD330 by 3CB and its metabolites.The control of 3CB addition during the bioconversion experiment was performed by on line HPLC (high pressure liquid chromatography).     

Detoxification of Protoanemonin by Dienelactone Hydrolase

Protoanemonin is a toxic metabolite which may be formed during the degradation of some chloroaromatic compounds, such as polychlorinated biphenyls, by natural microbial consortia. We show here that protoanemonin can be transformed by dienelactone hydrolase of Pseudomonas sp. strain B13 to cis-acetylacrylate. Although similar K_m values were observed for cis-dienelactone and protoanemonin, the turnover rate of protoanemonin was only 1% that of cis-dienelactone. This indicates that at least this percentage of the enzyme is in the active state, even in the absence of activation. The trans-dienelactone hydrolase of Pseudomonas sp. strain RW10 did not detectably transform protoanemonin. Obviously, Pseudomonas sp. strain B13 possesses at least two mechanisms to avoid protoanemonin toxicity, namely a highly active chloromuconate cycloisomerase, which routes most of the 3-chloro-cis,cis-muconate to the cis-dienelactone, thereby largely preventing protoanemonin formation, and dienelactone hydrolase, which detoxifies any small amount of protoanemonin that might nevertheless be formed.     

Identification and expression of the cym, cmt, and tod catabolic genes from Pseudomonas putida KL47: expression of the regulatory todST genes as a factor for catabolic adaptation

Pseudomonas putida KL47 is a natural isolate that assimilates benzene, 1-alkylbenzene (C(1)-C(4)), biphenyl, p-cumate, and p-cymene. The genetic background of strain KL47 underlying the broad range of growth substrates was examined. It was found that the cym and cmt operons are constitutively expressed due to a lack of the cymR gene, and the tod operon is still inducible by toluene and biphenyl. The entire array of gene clusters responsible for the catabolism of toluene and p-cymene/p-cumate has been cloned in a cosmid vector, pLAFR3, and were named pEK6 and pEK27, respectively. The two inserts overlap one another and the nucleotide sequence (42,505 bp) comprising the cym, cmt, and tod operons and its flanking genes in KL47 are almost identical (>99%) to those of P. putida F1. In the cloned DNA fragment, two genes with unknown functions, labeled cymZ and cmtR, were newly identified and show high sequence homology to dienelactone hydrolase and CymR proteins, respectively. The cmtR gene was identified in the place of the cmtI gene of previous annotation. Western blot analysis showed that, in strains F1 and KL47, the todT gene is not expressed during growth on Luria Bertani medium. In minimal basal salt medium, expression of the todT gene is inducible by toluene, but not by biphenyl in strain F1; however, it is constantly expressed in strain KL47, indicating that high levels of expression of the todST genes with one amino acid substitution in TodS might provide strain KL47 with a means of adaptation of the tod catabolic operon to various aromatic hydrocarbons.     

A novel dienelactone hydrolase from the thermoacidophilic archaeon Sulfolobus solfataricus P1: Purification,characterization, and expression

Background

Dienelactone hydrolases catalyze the hydrolysis of dienelactone to maleylacetate, which play a key role for the microbial degradation of chloroaromatics via chlorocatechols. Here, a thermostable dienelactone hydrolase from thermoacidophilic archaeon Sulfolobus solfataricus P1 was the first purified and characterized and then expressed in Escherichia coli.

Methods

The enzyme was purified by using several column chromatographys and characterized by determining the enzyme activity using p-nitrophenyl caprylate and dienelactones. In addition, the amino acids related to the catalytic mechanism were examined by site-directed mutagenesis using the identified gene.

Results

The enzyme, approximately 29 kDa monomeric, showed the maximal activity at 74 °C and pH 5.0, respectively. The enzyme displayed remarkable thermostability: it retained approximately 50% of its activity after 50 h of incubation at 90 °C, and showed high stability against denaturing agents, including various detergents, urea, and organic solvents. The enzyme displayed substrate specificities toward trans-dienelactone, not cis-isomer, and also carboxylesterase activity toward p-nitrophenyl esters ranging from butyrate (C₄) to laurate (C₁₂). The k_cat/K_m ratios for trans-dienelactone and p-nitrophenyl caprylate (C₈), the best substrate, were 92.5 and 54.7 s⁻¹ μM⁻¹, respectively.

Conclusions

The enzyme is a typical dienelactone hydrolase belonging to α/β hydrolase family and containing a catalytic triad composed of Cys151, Asp198, and His229 in the active site.

General significance

The enzyme is the first characterized archaeal dienelactone hydrolase.