Stuart E. Strand

Anaerobic Naphthalene Degradation by Microbial Pure Cultures under Nitrate-Reducing Conditions

ABSTRACT Pure bacterial cultures were isolated from a highly enriched denitrifying consortium previously shown to anaerobically biodegrade naphthalene. The isolates were screened for the ability to grow anaerobically in liquid culture with naphthalene as the sole source of carbon and energy in the presence of nitrate. Three naphthalene-degrading pure cultures were obtained, designated NAP-3-1, NAP-3-2, and NAP-4. Isolate NAP-3-1 tested positive for denitrification using a standard denitrification assay. Neither isolate NAP-3-2 nor isolate NAP-4 produced gas in the assay, but both consumed nitrate and NAP-4 produced significant amounts of nitrite. Isolates NAP-4 and NAP-3-1 transformed 70 to 90% of added naphthalene, and the transformation was nitrate dependent. No significant removal of naphthalene occurred under nitrate-limited conditions or in cell-free controls. Both cultures exhibited partial mineralization of naphthalene, representing 7 to 20% of the initial added14C-labeled naphthalene. After 57 days of incubation, the largest fraction of the radiolabel in both cultures was recovered in the cell mass (30 to 50%), with minor amounts recovered as unknown soluble metabolites. Nitrate consumption, along with the results from the 14C radiolabel study, are consistent with the oxidation of naphthalene coupled to denitrification for NAP-3-1 and nitrate reduction to nitrite for NAP-4. Phylogenetic analyses based on 16S ribosomal DNA sequences of NAP-3-1 showed that it was closely related to Pseudomonas stutzeri and that NAP-4 was closely related to Vibrio pelagius. This is the first report we know of that demonstrates nitrate-dependent anaerobic degradation and mineralization of naphthalene by pure cultures.

Enhanced phytoremediation of volatile environmental pollutants with transgenic trees.

Small, volatile hydrocarbons, including trichloroethylene, vinyl chloride, carbon tetrachloride, benzene, and chloroform, are common environmental pollutants that pose serious health effects. We have developed transgenic poplar (Populus tremula × Populus alba) plants with greatly increased rates of metabolism and removal of these pollutants through the overexpression of cytochrome P450 2E1, a key enzyme in the metabolism of a variety of halogenated compounds. The transgenic poplar plants exhibited increased removal rates of these pollutants from hydroponic solution. When the plants were exposed to gaseous trichloroethylene, chloroform, and benzene, they also demonstrated superior removal of the pollutants from the air. In view of their large size and extensive root systems, these transgenic poplars may provide the means to effectively remediate sites contaminated with a variety of pollutants at much faster rates and at lower costs than can be achieved with current conventional techniques.

An explosive-degrading cytochrome P450 activity and its targeted application for the phytoremediation of RDX

The widespread presence in the environment of hexahydro-1,3,5-trinitro-1,3,5-triazine (RDX), one of the most widely used military explosives, has raised concern owing to its toxicity and recalcitrance to degradation. To investigate the potential of plants to remove RDX from contaminated soil and water, we engineered Arabidopsis thaliana to express a bacterial gene xplA encoding an RDX-degrading cytochrome P450 (ref. 1). We demonstrate that the P450 domain of XplA is fused to a flavodoxin redox partner and catalyzes the degradation of RDX in the absence of oxygen. Transgenic A. thaliana expressing xplA removed and detoxified RDX from liquid media. As a model system for RDX phytoremediation, A. thaliana expressing xplA was grown in RDX-contaminated soil and found to be resistant to RDX phytotoxicity, producing shoot and root biomasses greater than those of wild-type plants. Our work suggests that expression of xplA in landscape plants may provide a suitable remediation strategy for sites contaminated by this class of explosives.

Combined aerobic heterotrophic oxidation, nitrification and denitrification in a permeable-support biofilm

Abstract A biofilm reactor, termed the permeable-support biofilm (PSB), was developed in which oxygen was supplied to the interior of the biofilm through a permeable membrane. The reactor was tested on filtered sewage supplemented with nutrient broth; the bulk solution was anoxic and the interior of the biofilm was supplied with pure oxygen. All tests were performed on a non-steady state biofilm with a depth of 1 mm. Mass balances on total organic carbon, ammonia, organic nitrogen and nitrate showed that combined heterotrophic oxidation of organics, denitrification and nitrification occurred simultaneously within the biofilm. The advantages of such a reactor are discussed.

ANAEROBIC BIODEGRADATION OF NAPHTHALENE, PHENANTHRENE, AND BIPHENYL BY A DENITRIFYING ENRICHMENT CULTURE

In previous results [Rockne and Strand (1998) Environ. Sci. Technol. 32, 2962-3967], anaerobic biodegradation of the polycyclic aromatic hydrocarbons, naphthalene, phenanthrene, and biphenyl in a fluidized bed reactor (FBR) enrichment was demonstrated. In this paper, re-feeding and mineralization experiments with sub-cultures of the nitrate-reducing enrichment are described. The subcultures continued to remove the PAHs after three feedings. PAH biodegradation ceased when nitrate was depleted and resumed when the enrichment was fed nitrate, demonstrating that PAH biodegradation was dependent upon nitrate reduction. Tests with radiolabeled PAH confirmed that PAH was mineralized, although the extent of mineralization differed greatly with different PAHs. Only partial mineralization (17% of initial carbon) was observed when the culture was fed naphthalene, whereas nearly complete mineralization (96%) was observed with phenanthrene. PAH carbon was incorporated into cell mass and mineralized after complete biodegradation of the PAHs, with 78-102% recoveries of radiolabel for naphthalene and phenanthrene, respectively. PAH carbon incorporation into biomass also varied considerably. Minor assimilation of biphenyl or phenanthrene was observed in the culture, whereas extensive assimilation of naphthalene carbon (57%) was observed when the culture was challenged with naphthalene. PAH degradation was approximately stoichiometric with the amount of nitrate consumed. Headspace analysis showed production of N2O, suggesting the enrichment coupled the biodegradation of PAH to denitrification.

Phytoremediation of Organic Contaminants: A Review of Phytoremediation Research at the University of Washington

As overwhelmingly positive results have become available regarding the ability of plants to degrade compounds such as trichloroethylene, phytoremediation studies are expanding. Studies to determine the potential for phytoremediation of fully chlorinated compounds, such as carbon tetrachloride and tetrachloroethylene, brominated compounds, such as ethylene dibromide and dibromochloropropane, and nonhalogenated compounds, such as methyl-t-butyl ether (MTBE), are underway. When using phytoremediation, it is important to select not only a plant that is capable of degrading the pollutant in question, but also one that will grow well in that specific environment. In ecologically sensitive areas, such as the Hawaiian Islands, only plants native to the area can be used. One way to supplement the arsenal of plants available for remedial actions is to utilize genetic engineering tools to insert into plants those genes that will enable the plant to metabolize a particular pollutant. Hybrid technologies, such as usin...

Phytoremediation of small organic contaminants using transgenic plants.

The efficacy of transgenic plants in the phytoremediation of small organic contaminants has been investigated. Two principal strategies have been pursued (1) the manipulation of phase I metabolic activity to enhance in planta degradation rates, or to impart novel metabolic activity, and (2) the enhanced secretion of reactive enzymes from roots leading to accelerated ex planta degradation of organic contaminants. A pair of dehalogenase genes from Xanthobacter autotrophicus was expressed in tobacco resulting in the dehalogenation of 1,2-dichloroethane, which was otherwise recalcitrant. A laccase gene from cotton was overexpressed in Arabidopsis thaliana resulting in increased secretory laccase activity and the enhanced resistance to trichlorophenol in soils. Although the results to date are promising, much of the work has been limited to laboratory settings; field demonstrations are needed.

Engineering plants for the phytoremediation of RDX in the presence of the co‐contaminating explosive TNT

The explosive compounds hexahydro-1,3,5-trinitro-1,3,5-triazine (RDX) and 2,4,6-trinitrotoluene (TNT) are widespread environmental contaminants commonly found as co-pollutants on military training ranges. TNT is a toxic carcinogen which remains tightly bound to the soil, whereas RDX is highly mobile leaching into groundwater and threatening drinking water supplies. We have engineered Arabidopsis plants that are able to degrade RDX, whilst withstanding the phytotoxicity of TNT. Arabidopsis thaliana (Arabidopsis) was transformed with the bacterial RDX-degrading xplA, and associated reductase xplB, from Rhodococcus rhodochrous strain 11Y, in combination with the TNT-detoxifying nitroreductase (NR), nfsI, from Enterobacter cloacae. Plants expressing XplA, XplB and NR remove RDX from soil leachate and grow on soil contaminated with RDX and TNT at concentrations inhibitory to XplA-only expressing plants. This is the first study to demonstrate the use of transgenic plants to tackle two chemically diverse organic compounds at levels comparable with those found on contaminated training ranges, indicating that this technology is capable of remediating concentrations of RDX found in situ. In addition, plants expressing XplA and XplB have substantially less RDX available in aerial tissues for herbivory and potential bioaccumulation.

Metabolism of the soil and groundwater contaminants, ethylene dibromide and trichloroethylene, by the tropical leguminous tree, Leuceana leucocephala

Ethylene dibromide (EDB; dibromoethane) and trichloroethylene (TCE) are hazardous environmental pollutants. The use of plants to treat polluted sites and groundwater, termed phytoremediation, requires plants that can both effectively remove the pollutant as well as grow in the climatic region of the site. In this paper, we report that the tropical leguminous tree, Leuceana leucocephala var. K636, is able to take up and metabolize EDB and TCE. The plants were grown in sterile hydroponic solution without its symbiont, Rhizobium. EDB and TCE were both metabolized by the plant, as indicated by the formation of bromide ion from EDB and trichloroethanol from TCE. Each plant organ was independently capable of debromination of EDB. L. leucocephala is being used to treat perched groundwater as part of a remedial alternative to address an accidental EDB spill in Hawaii. Bromide levels of plant tissues from the trees grown in the phytoremediation treatment cells at the Hawaii Site were elevated, indicating uptake and degradation of brominated compounds in the trees. This report is the first evidence of a tropical tree effectively metabolizing these common organic pollutants.

The explosive-degrading cytochrome P450 XplA: biochemistry, structural features and prospects for bioremediation.

XplA is a cytochrome P450 that mediates the microbial metabolism of the military explosive hexahydro-1,3,5-trinitro-1,3,5-triazine (RDX). It has an unusual structural organisation comprising a heme domain that is fused to its flavodoxin redox partner. XplA along with its partnering reductase XplB are plasmid encoded and the gene xplA has now been found in divergent genera across the globe with near sequence identity. Importantly, it has only been detected at explosives contaminated sites suggesting rapid dissemination of this novel catabolic activity, possibly within the 50-year period since the introduction of RDX into the environment. The X-ray structure of XplA-heme has been solved, providing fundamental information on the heme binding site. Interestingly, oxygen is not required for the degradation of RDX, but its presence determines the final degradation products, demonstrating that the degradation chemistry is flexible with both anaerobic and aerobic pathways resulting in the release of nitrite from the substrate. Transgenic plants expressing xplA are able to remove saturating levels of RDX from soil leachate and may provide a low cost sustainable remediation strategy for contaminated military sites.