Characterization of isofenphos hydrolases from Arthrobacter sp. strain B-5

Biodegradation of Atrazine by Mixed Bacteria of Klebsiella variicola Strain FH-1 and Arthrobacter sp. NJ-1

The purpose of this study is to enhance the biodegradability of atrazine with FH-1 and NJ-1 alone by selecting the mixing ratio, optimizing the culture medium and conditions. The results showed that FH-1 and NJ-1 have the best biodegradation effect on atrazine being mixed in a volume ratio of 3:2. In a single factor experiment, sucrose and NH₄Cl provided carbon and nitrogen sources for the mixed bacteria. Subsequently, composition of fermentation medium was further optimized using Box-Behnken design of response surface methodology. Based on the results, growth of mixed bacteria and biodegradation of atrazine performed best effects with a biodegradation rate of 85.6% when sucrose and NH₄Cl amounts were 35.30 g/L and 10.28 g/L. The optimal medium condition was 10% inoculum of mixed bacteria, with initial atrazine concentration of 50 mg/L, neutral or weakly alkaline pH value, 30°C. The biodegradation rate reached 97.4%, 11.8% higher than the unoptimized condition.

An isofenphos-methyl hydrolase (Imh) capable of hydrolyzing the P-O-Z moiety of organophosphorus pesticides containing an aryl or heterocyclic group

Organophosphorus pesticide (OP) hydrolases play key roles in the degradation and decontamination of agricultural and household OPs and in the detoxification of chemical warfare agents. In this study, an isofenphos-methyl hydrolase gene (imh) was cloned from the isocarbophos-degrading strain of Arthrobacter sp. scl-2 using the polymerase chain reaction method. Isofenphos-methyl hydrolase (Imh) showed 98% sequence identity with the isofenphos hydrolase from Arthrobacter sp. strain B-5. Imh was highly expressed in Escherichia coli BL21 (DE3), and the His(6)-tagged Imh was purified (1.7 mg/ml) with a specific activity of 14.35 U/mg for the substrate isofenphos-methyl. The molecular mass of the denatured Imh is about 44 kDa, and the isoelectric point (pI) value was estimated to be 3.4. The optimal pH and temperature for hydrolysis of isofenphos-methyl were pH 8.0 and 35 °C, respectively. The secondary structure of Imh shows that Imh is a metallo-dependent hydrolase, and it was found that Imh was completely inhibited by the metalloprotease inhibitor 1,10-phenanthroline (0.5 mM), and the catalytic activity was restored by the subsequent addition of Zn(2+). Interestingly, Imh had a relatively broader substrate specificity and was capable of hydrolyzing 12 of the tested oxon and thion OPs with the P-O-Z moiety instead of the P-S(C)-Z moiety. Furthermore, it was found that the existence of an aryl or heterocyclic group in the leaving group (Z) is also important in determining the substrate specificity. Among all the substrates hydrolyzed by Imh, it was assumed that Imh preferred P-O-Z substrates still with a phosphamide bond (P-N), such as isofenphos-methyl, isofenphos, isocarbophos, and butamifos. The newly characterized Imh has a great potential for use in the decontamination and detoxification of agricultural and household OPs and is a good candidate for the study of the catalytic mechanism and substrate specificity of OP hydrolases.

Fenamiphos and related organophosphorus pesticides: environmental fate and toxicology

In this review, we emphasize recent research on the fate, transport, and metabolism of tree selected organophosphorus pesticides (fenamiphos, isofenphos, and coumaphos) in soil an water environments. This review is also concerned with the side effects of these pesticides on nontarget organisms. Despite the fact that fenamiphos is not very mobile, its oxides have been detected in the groundwaters of Western Australia. Most organophosphorus pesticides generally are chemically unstable and underfo microbial degradation in soil and water environments. Enhanced biodegradation of many organophosphorus pesticides upon their repeted applications to soil and water is well established. Myriads of soil microorganisms, bacteria in particular, exhibit an exceptional capacity to transform many organophosphorus pesticides. Fenamiphos can undergo rapid microbially mediated degradation via oxidation to its oxides (sulfoxide and sulfone) and eventually to CO2 and water in soils, or via hydrolysis, in cultures of the soil bacterium, Brevinbacterium sp. There is evidence for enhanced biodegradation of (i) isofenphos in soils with a long history of use and (ii) coumaphos in cattle dip by bacterial cultures to chlorferon and diethylthiophosphoric acid.

Microbial degradation of organophosphorus xenobiotics: metabolic pathways and molecular basis

Organophosphorus (OP) xenobiotics are used worldwide as pesticides and petroleum additives. OP compounds share the major portion of the pesticide market globally. Owing to large-scale use of OP compounds, contaminations of soil and water systems have been reported from all parts of the world. OP compounds possess very high mammalian toxicity and therefore early detection and subsequent decontamination and detoxification of the polluted environment is essential. Additionally, about 200,000 tons of extremely toxic OP chemical warfare agents are required to be destroyed by 2007 under Chemical Warfare Convention (1993). Chemical and physical methods of decontamination are not only expensive and time-consuming, but also in most cases they do not provide a complete solution. These approaches convert compounds from toxic into less toxic states, which in some cases can accumulate in the environment and still be toxic to a range of organisms. Bioremediation provides a suitable way to remove contaminants from the environment as, in most of the cases, OP compounds are totally mineralized by the microorganisms. Most OP compounds are degraded by microorganisms in the environment as a source of phosphorus or carbon or both. Several soil bacteria have been isolated and characterized, which can degrade OP compounds in laboratory cultures and in the field. The biochemical and genetic basis of microbial degradation has received considerable attention. Several genes/enzymes, which provide microorganisms with the ability to degrade OP compounds, have been identified and characterized. Some of these genes and enzymes have been engineered for better efficacy. Bacteria capable of complete mineralization are constructed by transferring the complete degradation pathway for specific compounds to one bacterium. In the present article, we review microbial degradation and metabolic pathways for some OP compounds. The biochemical and molecular basis of OP degradation by microbes and the evolution and distribution of genes/enzymes are also reviewed. This article also examines applications and future use of OP-degrading microbes and enzymes for bioremediation, treatment of OP poisoning, and as biosensors.

Purification and characterization of fenitrothion hydrolase from Burkholderia sp. NF100

The organophosphorus pesticide hydrolase was purified to homogeneity from Burkholderia sp. NF100 by detergent extraction of the cell membrane fraction, anion-exchange, chromatofocusing, and gel filtration chromatographies. The purified enzyme had a molecular mass of 55 kDa and a pI 5.8, and the hydrolase activity was strongly inhibited by EDTA, dithiothreitol (DTT), Hg2+ and 1,10-phenanthroline. The optimum pH and temperature for the enzyme activity were 8.0 and 40 degrees C, respectively. The enzyme hydrolyzed five organophosphorus pesticides.

Molecular cloning and nucleotide sequencing of organophosphorus insecticide hydrolase gene from Arthrobacter sp. strain B-5

The organophosphorus insecticide hydrolase (OPH) gene of Arthrobacter sp. strain B-5, isolated from turf green soil was cloned into Escherichia coli JM109. Three clones, termed EpB511, EpB521 and EpB531, exhibiting OPH activity were obtained. However, these three clones showed lower OP-degrading ability than strain B-5. A 7.7-kb inserted fragment of the plasmid pB521 harbored by EpB521 was subcloned, resulting in construction of a plasmid, pB526, carrying the 2.6-kb inserted fragment with OP-degrading ability. In this sequence, an open reading frame (ORF) that encodes a 43,607 Da polypeptide composed of 415 amino acids was identified. The N-terminal amino acid sequence deduced from the nucleotide sequence was identical to that of purified OPHs. The deduced amino acid sequence was compared with the sequences in the data bank and a 58.1% amino acid identity was found with the aryldialkylphosphatase from Nocardia sp. strain B-1, an enzyme that possesses catalytic functions similar to OPH.

Reductive cleavage of demeton-S-methyl by Corynebacterium glutamicum in cometabolism on more readily metabolizable substrates

Corynebacterium glutamicum is able to biotransform demeton-S-methyl, an organophosphorus compound, during cometabolism with more readily metabolizable substrates. Among the cosubstrates used, fructose is the growth substrate that is most favorable for demeton-S-methyl biotransformation. The reaction mechanism of demeton-S-methyl biotransformation involves reductive cleavage of an S-C bond, which leads to accumulation of dimethyl thiophosphate in the culture medium.

Characterization of a novel organophosphorus hydrolase from Nocardiodes simplex NRRL B-24074

We characterized a novel organophosphorus hydrolase (OPH) activity expressed by Nocardiodes simplex NRRL B-24074, a member of a coumaphos-degrading microbial consortium from cattle dip waste. Like the previously characterized OPH from Nocardia sp. strain B- (NRRL B- 16944), OPH activity in N. simplex is located in the cytoplasm and is expressed constitutively. The purified enzyme is monomeric, has a native molecular size of 45,000 Da and has a specific activity toward ethyl parathion of 33 micromole/min x mg protein. Km constants for the enzyme with the structurally related organophosphate pesticides ethyl parathion and EPN were 100 microM and 345 microM, respectively. Although OPH activity in extracts did not require the addition of divalent cations, the purified enzyme lost activity during dialysis against phosphate buffer and this activity could be restored after incubation in buffer containing either CoSO4 or CuSO4. Our results suggest that OPH activity in N. simplex is distinct from other known OPHs and that the responsible gene is unrelated to known genes.

Selective deletions involving the organophosphorus hydrolase gene adpB from Nocardia strain B-1

The organophosphorus hydrolase (OPH) of Nocardia sp. strain B-1 is capable of hydrolyzing organophosphate insecticides such as coumaphos and parathion. The 40,000 dalton OPH and the responsible gene (termed adpB) have been previously isolated and described. OPH activity in Nocardia strain B-1 is spontaneously lost at high frequency during the growth of laboratory cultures. In order to understand the genetic basis of this phenomenon, hybridization experiments were performed in which digested genomic DNAs from OPH negative derivatives were probed with BstE1 and BamH1 restriction fragments containing adpB and regions flanking this gene. These experiments revealed that a region containing adpB was missing in all OPH negative derivatives. However, these OPH negative derivatives were shown to contain sequences that hybridized to probes for DNA regions flanking adpB. On the basis of the hybridization patterns from thirteen OPH negative derivatives, there are two primary types of deletions with their sizes ranging from 33 kb to greater than 35.5 kb.