Synthetic organophosphorus compounds are used as pesticides, plasticizers, air fuel ingredients and chemical warfare agents. Organophosphorus compounds are the most widely used insecticides, accounting for an estimated 34% of world-wide insecticide sales. Contamination of soil from pesticides as a result of their bulk handling at the farmyard or following application in the field or accidental release may lead occasionally to contamination of surface and ground water. Several reports suggest that a wide range of water and terrestrial ecosystems may be contaminated with organophosphorus compounds. These compounds possess high mammalian toxicity and it is therefore essential to remove them from the environments. In addition, about 200 000 metric tons of nerve (chemical warfare) agents have to be destroyed world-wide under Chemical Weapons Convention (1993). Bioremediation can offer an efficient and cheap option for decontamination of polluted ecosystems and destruction of nerve agents. The first micro-organism that could degrade organophosphorus compounds was isolated in 1973 and identified as Flavobacterium sp. Since then several bacterial and a few fungal species have been isolated which can degrade a wide range of organophosphorus compounds in liquid cultures and soil systems. The biochemistry of organophosphorus compound degradation by most of the bacteria seems to be identical, in which a structurally similar enzyme called organophosphate hydrolase or phosphotriesterase catalyzes the first step of the degradation. organophosphate hydrolase encoding gene opd (organophosphate degrading) gene has been isolated from geographically different regions and taxonomically different species. This gene has been sequenced, cloned in different organisms, and altered for better activity and stability. Recently, genes with similar function but different sequences have also been isolated and characterized. Engineered microorganisms have been tested for their ability to degrade different organophosphorus pollutants, including nerve agents. In this article, we review and propose pathways for degradation of some organophosphorus compounds by microorganisms. Isolation, characterization, utilization and manipulation of the major detoxifying enzymes and the molecular basis of degradation are discussed. The major achievements and technological advancements towards bioremediation of organophosphorus compounds, limitations of available technologies and future challenge are also discussed.

Microbial degradation of organophosphorus compounds

1. Scope of Article and Previous Related Reviews 5346 2. Introduction 5346 2.1. Destruction 5347 2.2. Sensing 5347 2.3. Historical Context 5348 2.3.1. Brief History and Molecular Structure 5348 2.4. Related Compounds and Nomenclature 5348 2.4.1. Phosphorus(V) Parent Compounds and Fundamental Chemistry 5348 2.4.2. Pesticides 5349 2.4.3. Simulants 5349 2.4.4. Decomposition Products 5350 2.5. Toxicology 5351 2.5.1. Acetylcholine Esterase (AChE) Inhibition 5351 2.5.2. Endocannabinoid System Activation 5352 2.6. Critical Needs To Decontaminate and Detect 5353 2.7. Treaties and Conventions 5354 3. Stockpile Destruction 5355 3.1. Agent Storage 5355 3.2. Protection Protocols and Logistics 5355 3.3. Background 5355 3.4. Methods Currently Employed 5355 3.4.1. Incineration 5355 3.4.2. Neutralization by Base Hydrolysis 5356 4. Decomposition Reactions 5357 4.1. Hydrolysis 5357 4.2. Autocatalytic Hydrolysis or Hydrolysis Byproducts 5358 4.3. Use of Peroxide 5359 4.4. Oxidation with Bleach and Related Reagents 5360 4.5. Alkoxide as Nucleophile 5360 4.5.1. Basic Media 5360 4.5.2. Metal-Catalyzed Reactions 5361 4.5.3. Metal-Assisted Reactions 5363 4.5.4. Biotechnological Degradation 5363 4.5.5. Cyclodextrin-Assisted Reactions 5370 4.6. Halogen as the Nucleophile 5370 4.6.1. Use of BrOx 5370 4.6.2. Use of Other Halogens 5371 4.6.3. Use of Group 13 Chelates 5371 4.7. Surface Chemistry 5371 4.7.1. Bare Metals and Solid Nanoparticles 5371 4.7.2. Metal Oxides 5371 4.7.3. Representative Elements 5372 4.7.4. d-Block (Groups 4 10) 5373 4.7.5. Solid Metal Oxides of Group 3 and the Lanthanides 5375 4.7.6. Porous Silicon and Related Systems 5375 4.7.7. Zeolites 5375 4.7.8. Comparative IR Data 5375 4.8. Other Types of Systems 5375 5. Decontamination 5376 5.1. Overview: Ability to React with All Types of Agents, Ease of Application, and Compatibility with Treated Objects 5376 6. Agent Fate and Disposal 5378 6.1. Indoor 5378 6.2. Concrete and Construction Surfaces 5378 6.3. Landfills 5379 7. Sensing and Detection 5379 7.1. Possible Metal Ion Binding Modes in Solution 5379 7.1.1. Early Reports of Phosph(on)ate [R3PdO 3 3 3M nþ] Interactions (R= Alkyl, Alkoxyl) 5380 7.1.2. Coordination Chemistry of Downstream Non-P-Containing Products of Decomposition 5380 7.2. Colorimetric Detection 5381 7.3. Chemiluminescence: Fluorescence and Phosphorescence 5382 7.3.1. Lanthanide-Based Catalysts 5382 7.3.2. Organometallic-Based Sensors 5382 7.3.3. Organic Design 5382 7.3.4. Biologically-Based Luminescence Detection 5382 7.3.5. Polymer and Bead Supports 5382 7.4. Porous Silicon 5383 7.5. Carbon Nanotubes 5383

Destruction and Detection of Chemical Warfare Agents

The implementation of increasingly stringent standards for the dis- charge of wastes into the environment has necessitated the need for the develop- ment of alternative waste treatment processes. A review of research directed toward developing enzymatic treatment systems for solid, liquid and hazardous wastes is presented. A large number of enzymes from a variety of di†erent plants and microorganisms have been reported to play an important role in an array of waste treatment applications. Enzymes can act on speci-c recalcitrant pollutants to remove them by precipitation or transformation to other products. They also can change the characteristics of a given waste to render it more amenable to treatment or aid in converting waste material to value-added products. Before the full potential of enzymes may be realized, it is recommended that a number of issues be addressed in future research endeavors including the identi-cation and characterization of reaction by-products, the disposal of reaction products and reduction of the cost of enzymatic treatment.

Potential Applications of Enzymes in Waste Treatment

A Moraxella strain grew on p-nitrophenol with stoichiometric release of nitrite. During induction of the enzymes for growth on p-nitrophenol, traces of hydroquinone accumulated in the medium. In the presence of 2,2′-dipyridyl, p-nitrophenol was converted stoichiometrically to hydroquinone. Particulate enzymes catalyzed the conversion of p-nitrophenol to hydroquinone in the presence of NADPH and oxygen. Soluble enzymes catalyzed the conversion of hydroquinone to γ-hydroxymuconic semialdehyde, which was identified by high-performance liquid chromatography (HPLC)-mass spectroscopy. Upon addition of catalytic amounts of NAD+, γ-hydroxymuconic semialdehyde was converted to β-ketoadipic acid. In the presence of pyruvate and lactic dehydrogenase, substrate amounts of NAD were required and γ-hydroxymuconic semialdehyde was converted to maleylacetic acid, which was identified by HPLC-mass spectroscopy. Similar results were obtained when the reaction was carried out in the presence of potassium ferricyanide. Extracts prepared from p-nitrophenol-growth cells also contained an enzyme that catalyzed the oxidation of 1,2,4-benzenetriol to maleylacetic acid. The enzyme responsible for the oxidation of 1,2,4-benzenetriol was separated from the enzyme responsible for hydroquinone oxidation by DEAE-cellulose chromatography. The results indicate that the pathway for biodegradation of p-nitrophenol involves the initial removal of the nitro group as nitrite and formation of hydroquinone. 1,4-Benzoquinone, a likely intermediate in the initial reaction, was not detected. Hydroquinone is converted to β-ketoadipic acid via γ-hydroxymuconic semialdehyde and maleylacetic acid.

Pathway for Biodegradation of p-Nitrophenol in a Moraxella sp

Understanding pesticide metabolism in plants and microorganisms is necessary for pesticide development, for safe and efficient use, as well as for developing pesticide bioremediation strategies for contaminated soil and water. Pesticide biotransformation may occur via multistep processes known as metabolism or cometabolism. Cometabolism is the biotransformation of an organic compound that is not used as an energy source or as a constitutive element of the organism. Individual reactions of degradation–detoxification pathways include oxidation, reduction, hydrolysis, and conjugation. Metabolic pathway diversity depends on the chemical structure of the xenobiotic compound, the organism, environmental conditions, metabolic factors, and the regulating expression of these biochemical pathways. Knowledge of these enzymatic processes, especially concepts related to pesticide mechanism of action, resistance, selectivity, tolerance, and environmental fate, has advanced our understanding of pesticide scienc...

Pesticide metabolism in plants and microorganisms

A crude cell extract from a mixed bacterial culture growing on parathion, an organophosphate insecticide, hydrolyzed parathion (21 C) at a rate of 416 nmol/min per mg of protein. This rate of enzymatic hydrolysis, when compared with chemical hydrolysis by 0.1 N sodium hydroxide at 40 C, was 2, 450 times faster. Eight of 12 commonly used organophosphate insecticides were enzymatically hydrolyzed with this enzyme preparation at rates ranging from 12 to 1,360 nmol/min per mg of protein. Seven pesticides were hydrolyzed at rates significantly higher (40 to 1,005 times faster) than chemical hydrolysis. The pH optimum for enzymatic hydrolysis of the eight pesticides ranged from 8.5 to 9.5, with less than 50% of maximal activity expressed at pH 7.0. Maximal enzyme activity occurred at 35 C. The crude extract lost its activity at the rate of only 0.75%/day when stored at 6 C. Eight organic solvents, ranging from methanol to hexane, at low concentrations stimulated enzymatic hydrolysis by 3 to 20%, whereas at higher concentrations (1,000 mg/liter) they inhibited the reaction (9 to 50%). Parathion metabolites p-nitrophenol, hydroquinone, and diethylthiophosphoric acid, at up to 100-mg/liter concentrations, did not significantly influence enzyme activity.

Enzymatic hydrolysis of organophosphate insecticides, a possible pesticide disposal method.

A mixed microbial culture was adapted to growth on parathion to determine the feasibility of using microorganisms to detoxify concentrated parathion in agricultural wastes. In a 600-ml chemostat, the culture was able to degrade 50 mg of parathion per liter per h. Para-nitrophenol, produced by enzymatic hydrolysis of parathion, caused delays in exponential growth which were directly proportional to its concentration. A pseudomonad, isolated from the mixed culture, exhibited optimal growth at 0.21 mM p-nitrophenol and grew in concentrations up to 3.5 mM. In metabolic studies using [14C]p-nitrophenol, the nitro group was removed in stoichiometric quantities as nitrite and hydroquinone was tentatively identified as a metabolite.

Microbial decontamination of parathion and p-nitrophenol in aqueous media

A bacterial enzyme(s) capable of hydrolyzing nine organophosphate insecticides was covalently bound to glass. The efficiency of this binding reaction ranged from 4 to 17%. Under continuous column operation, the immobilized enzyme(s) had an extrapolated half-life of 280 days. The specific activity of this glass-covalently bound hydrolase activity for parathion varied from 0.035 to 0.15 μmol/min per g of glass. The bound activity increased with decreasing glass particle size; however, the flow resistance also increased. Immobilized enzyme(s) kinetics were approximately 50% slower than those of the free enzyme(s), but there was no significant difference in the effect pH and temperature had on the activity of immobilized and free enzyme(s).

Properties of an Immobilized Pesticide-Hydrolyzing Enzyme

A mixed bacterial culture was adapted to growth on a mixed carbon substrate consisting of the pesticide parathion and its xylene-based formulation. The environmental growth parameters of temperature, pH, and dissolved oxygen concentration were optimized to obtain complete metabolism of parathion from this mixed carbon substrate. This adapted culture grew rapidly (μ = 0.7 per h) on the pesticide formulation at high parathion suspensions (3,000 mg/liter). Carbon utilization from this mixed substrate was strongly dependent on pH. At slightly acidic pH, xylene was preferentially metabolized, whereas at slightly alkaline pH, parathion was preferentially metabolized. Diethylthiophosphoric acid, a metabolite from parathion, and toluic acid, a metabolite from xylene, also influenced the selection of the primary carbon source.

Douglas M. Munnecke

Papers

Enzymatic hydrolysis of organophosphate insecticides, a possible pesticide disposal method.

Microbial decontamination of parathion and p-nitrophenol in aqueous media

Properties of an Immobilized Pesticide-Hydrolyzing Enzyme

Microbial metabolism of a parathion-xylene pesticide formulation.

Decontamination of noncombustible agricultural pesticide containers by removal of emulsifiable parathion