Degradation of Aroclor 1221 and survival of strains in soil microcosms

Three bacterial strains able to use different aromatic compounds as the sole carbon and energy source were tested for their potential to degrade Aroclor 1221 in soil microcosms when present in mixed culture. Disappearance of polychlorinated biphenyls (PCBs), occurrence of metabolites, release of chloride, and survival of the laboratory-selected strains were investigated under different conditions. In principle, complete mineralization of various congeners of Aroclor 1221, a technical mixture of PCBs, by the mixed culture was possible. The autochthonous microflora negatively affected the degradation due to formation of a toxic compound from 4-chlorobenzoate. 4-Chlorobenzoate was produced by one of the added strains, Pseudomonas sp. JHK, during degradation of 4-chlorobiphenyl. The unknown metabolite of 4-chlorobenzoate led to a rapid decrease in viable counts of the laboratory-selected strains in the soil microcosm.Correspondence to: J. Havel     

Degradation of 3-chlorobiphenyl by in vivo constructed hybrid pseudomonads

Abstract 3-Chlorobiphenyl-degrading bacteria were obtained from the mating between Pseudomonas putida strain BN10 and Pseudomonas sp. strain B13. Strains such as BN210 resulted from the transfer of the genes coding the enzyme sequence for the degradation of chlorocatechols from B13 into BN10, whereas B13 derivatives such as B131 have acquired the biphenyl degradation sequence from BN10. During growth of the hybrid strains on 3-chlorobiphenyl 90% chloride was released. Activities of phenylcatechol 2,3-dioxygenase, benzoate dioxygenase, catechol 1,2-dioxygenase, chloromuconate cyloisomerase and 4-carboxymethyl-enebut-2-en-4-olide hydrolase were found in 3-chlorobiphenyl-grown cells. The hybrid strains were found to convert some congeners of the Aroclor 1221 mixture such as mono- and dichloro-substituted biphenyls.     

Aerobic biodegradation of biphenyl and polychlorinated biphenyls by Arctic soil microorganisms.

We examined the degradation of biphenyl and the commercial polychlorinated biphenyl (PCB) mixture Aroclor 1221 by indigenous Arctic soil microorganisms to assess both the response of the soil microflora to PCB pollution and the potential of the microflora for bioremediation. In soil slurries, Arctic soil microflora and temperate-soil microflora had similar potentials to mineralize [14C]biphenyl. Mineralization began sooner and was more extensive in slurries of PCB-contaminated Arctic soils than in slurries of uncontaminated Arctic soils. The maximum mineralization rates at 30 and 7 degrees C were typically 1.2 to 1.4 and 0.52 to 1.0 mg of biphenyl g of dry soil-1 day-1, respectively. Slurries of PCB-contaminated Arctic soils degraded Aroclor 1221 more extensively at 30 degrees C (71 to 76% removal) than at 7 degrees C (14 to 40% removal). We isolated from Arctic soils organisms that were capable of psychrotolerant (growing at 7 to 30 degrees C) or psychrophilic (growing at 7 to 15 degrees C) growth on biphenyl. Two psychrotolerant isolates extensively degraded Aroclor 1221 at 7 degrees C (54 to 60% removal). The soil microflora and psychrotolerant isolates degraded all mono-, most di-, and some trichlorobiphenyl congeners. The results suggest that PCB pollution selected for biphenyl-mineralizing microorganisms in Arctic soils. While low temperatures severely limited Aroclor 1221 removal in slurries of Arctic soils, results with pure cultures suggest that more effective PCB biodegradation is possible under appropriate conditions.     

Cyclodextrins enhance the aerobic degradation and dechlorination of low-chlorinated biphenyls

Summary The aerobic dechlorination of 4-chlorobiphenyl and of Aroclor 1221 by Pseudomonas sp. CPE1 strain was enhanced by the presence of hydroxypropyl--cyclodextrin in the medium. The best dechlorination results were obtained when 4-chlorobiphenyl or Aroclor 1221 and the cyclodextrin were used at the molar ratios 1:1 and 1:1.5. This agent can be adopted to enhance the efficiency of PCB degradation tests.     

Influence of chlorobenzoates on the utilisation of chlorobiphenyls and chlorobenzoate mixtures by chlorobiphenyl/chlorobenzoate-mineralising hybrid bacterial strains

Chlorobenzoates (CBA) arise as intermediates during the degradation of polychlorinated biphenyls (PCBs) and some chlorinated herbicides. Since PCBs were produced as complex mixtures, a range of mono-, di-, and possibly trichloro-substituted benzoates would be formed. Chlorobenzoate degradation has been proposed to be one of the rate-limiting steps in the overall PCB-degradation process. Three hybrid bacteria constructed to have the ability to completely mineralise 2-, 3-, or 4-monochlorobiphenyl respectively, have been studied to establish the range of mono- and diCBAs that can be utilised. The three strains were able to mineralise one or more of the following CBAs: 2-, 3-, and 4-monochlorobenzoate and 3,5-dichlorobenzoate. No utilisation of 2,3-, 2,5-, 2,6-, or 3,4-diCBA was observed, and only a low concentration (0.11 mM) of 2,4-diCBA was mineralised. When the strain with the widest substrate range (Burkholderia cepacia JHR22) was simultaneously supplied with two CBAs, one that it could utilise plus one that it was unable to utilise, inhibitory effects were observed. The utilisation of 2-CBA (2.5 mM) by this strain was inhibited by 2,3-CBA (200 M) and 3,4-CBA (50 M). Although 2,5-CBA and 2,6-CBA were not utilised as carbon sources by strain JHR22, they did not inhibit 2-CBA utilisation at the concentrations studied, whereas 2,4-CBA was co-metabolised with 2-CBA. The utilisation of 2-, 3-, and 4-chlorobiphenyl by strain JHR22 was also inhibited by the presence of 2,3- or 3,4-diCBA. We conclude that the effect of the formation of toxic intermediates is an important consideration when designing remediation strategies.Abbreviations PCB Polychlorinated biphenyl - CBA Chlorobenzoate     

The degradation of biphenyl and chlorobiphenyls by mixed bacterial cultures

Abstract Pseudomonas sp. HV3 grows on naphthalene but not on biphenyl, as the sole source of carbon. When the cells of Pseudomonas sp. HV3 grown on naphthalene were shaken with biphenyl as the carbon source in a mineral salt solution, a yellow metabolite identified as the meta -cleavage product of biphenyl was excreted. The degradation of biphenyl stopped here, but was completed if either 2-methyl-4-chlorophenoxy acetic acid (MCPA)-degrading mixed culture or a Nocardia strain was added to the growth solution. Neither of these uses naphthalene or biphenyl as growth substrate. The mixed culture of Pseudomonas sp. HV3 and Nocardia sp. also degrades the commercial polychlorinated biphenyl (PCB) mixture Aroclor 1221. A yellow metabolite was likewise produced in the degradation, and sometimes two different peaks of the yellow metabolite were observed. The gas chromatography-mass spectrometry (GC-MS) analyses showed that 40–87% of Aroclor 1221 was degraded during an incubation time of 6–21 days. Chlorobenzoic acids were found as metabolites.     

Aerobic mineralization of 4,4′-dichlorobiphenyl and 4-chlorobenzoic acid by a novel natural bacterial strain that grows poorly on benzoate and biphenyl

Achromobacter xylosoxidans strain IR08 was isolated from soil contaminated with electrical transformer fluid by enrichment culture containing Aroclor 1221 as the sole carbon source. This strain was found to grow on all monochlorobiphenyls, 4,4′-dichlorobiphenyl (4,4′-diCB) and a wide range of other xenobiotic compounds. During growth on 4,4′-diCB, a near-stoichiometric amount of chloride was excreted into the culture fluid in less than 5 days and growth yield was more than twice that achieved on biphenyl. The production of 4-CBA or chlorocatechol as a metabolite was not observed. Quite unusually, coincubation of strain IR08 with 4,4′-diCB and biphenyl at relatively equal concentrations showed preferential utilization of the chlorobiphenyl: 4,4′-diCB was mineralized in less than 5 days concomitant with stoichiometric release of chloride, while biphenyl was poorly degraded. Growth on 2.5 mM CBA also resulted in complete disappearance of the substrate, however, inorganic chloride recovered from the culture broth was less than 65%. The isolation of a dichlorobiphenyl-mineralizing rather than transformation strain such as IR08 is an important advance in an effort to develop effective bioremediation strategy for polychlorinated biphenyl-contaminated soil.     

一株联苯降解菌的特性及鉴定*

从华北油田污染土壤中筛选出一株能够以联苯为唯一碳源和能源生长的菌株。该菌生长的最适联苯浓度为0．2％～0．4％,在联苯浓度为0．1％的培养基中培养36h后降解率达99．8%。该菌还可以降解苯甲酸钠、邻苯二酚、间苯二酚、对苯二酚和多氯联苯Aroclorl221、Aroclorl242等芳香族化合物。通过16S rDNA基因序列分析鉴定该菌为嗜吡啶红球菌(Rhodococcus pyridinovorans)。     

Fungal degradation of chlorpyrifos by Verticillium sp. DSP in pure cultures and its use in bioremediation of contaminated soil and pakchoi

Pesticides residues in soils and on vegetables are a public safety concern. Pretreatment with microorganisms degrading pesticides has the potential to alleviate the conditions. For this purpose, the degradation characteristics of chlorpyrifos by an isolated fungal strain Verticillium sp. DSP in pure cultures, soil, and on pakchoi (Brassica chinensis L.) were investigated. Degradation rate of chlorpyrifos in the mineral salts medium was proportional to the concentrations of chlorpyrifos ranging from 1 to 100 mg l⁻¹. The rate of degradation for chlorpyrifos (1 mg l⁻¹) in the mineral salts medium was 1.12 and 1.04 times faster at pH 7.0 than those at pHs 5.0 and 9.0, and the degradation at 35 °C was 1.15 and 1.12 times faster, respectively, than those at 15 and 20 °C. The addition of the fungal strain DSP into the contaminated soils was found to significantly increase the degradation of chlorpyrifos. Degradation rates of chlorpyrifos in inoculated soils were 3.61, 1.50 and 1.10 times faster in comparison with the sterilized soil, previously chlorpyrifos-untreated soil, and previously chlorpyrifos-treated soil under laboratory conditions. In contrast to the controls, the half-lives of chlorpyrifos were significantly shortened by 10.9% and 17.6% on treated pakchoi, 12.0% and 37.1% in inoculated soils, respectively, in the greenhouse and open field. The results indicate that the fungal strain DSP can be used successfully for the removal or detoxification of chlorpyrifos residues in/on contaminated soil and vegetable.     

Co-metabolic degradation of tribenuron methyl,a sulfonylurea herbicide,by Pseudomonas sp. strain NyZ42

A co-metabolic degradation of tribenuron methyl bacterial strain NyZ42 was isolated from polluted agricultural soil and classified as genus Pseudomonas by its 16S rRNA gene sequencing. The degradation efficiency of tribenuron methyl was about 80% of the originally supplemented 200 mg l⁻¹ tribenuron methyl in liquid minimal medium within four days, when either glucose or succinate was used as a supplemental carbon source. Three intermediates formed during the degradation of tribenuron methyl mediated by strain NyZ42 were captured by LC-MS, and two alternative pathways were proposed for the microbial mediated tribenuron methyl degradation, via either cleavage of the sulfonylurea bridge or saponification of alkyl-group. Furthermore, inoculation of strain NyZ42 enhanced the degradation of tribenuron methyl in the sterilized soil samples, although the biodegradation/co-metabolism ability of NyZ42 was not obvious in the nonsterilized soil samples when compared with the indigenous microbial consortium under current laboratory conditions.     

Degradation of chlorobenzenes in soil slurry by a specialized organism

The microbial degradation of monochloro-, 1,2-dichloro-, 1,4-dichloro-, and 1,2,4-trichlorobenzene in soil slurries was examined with single compounds as well as in mixtures. The indigenous soil populations brought about the degradation of monochlorobenzene when incubated at 27°C in slurries with 29% (w/w) suspended solids. In contrast, the other chlorobenzenes persisted during an incubation period of 1 month. Supplementation with buffer, mineral salts and acetate did not significantly influence the degradation. However, inoculation withPseudomonas aeruginosa strain RHO1, a monochloro- and 1,4-dichlorobenzene-degrading organism, to a titre of 1 × 10⁵ cells/g soil, led to rapid and complete degradation of 0.8 mm growth substrate within 30 h. In addition, the strain was able to degrade 1,2-dichloro- and 1,2,4-trichlorobenzene with stoichiometric release of chloride in the presence of acetate, ethanol, monochloro- or 1,4-dichlorobenzene as growth substrates. In mixtures of chlorobenzenes the co-metabolism of 1,2-dichloro- and 1,2,4-trichlorobenzene occurred until the growth substrates monochloroand 1,4-dichlorobenzene were degraded. The degradation was faster in the slurries of garden soil containing 8% organic carbon than in soil with the lower content of 2.6%.     

Characterization of multiple novel aerobic polychlorinated biphenyl (PCB)-utilizing bacterial strains indigenous to contaminated tropical African soils

Contaminated sites in Lagos, Nigeria were screened for the presence of chlorobiphenyl-degrading bacteria. The technique of continual enrichment on Askarel fluid yielded bacterial isolates able to utilize dichlorobiphenyls (diCBs) as growth substrates and six were selected for further studies. Phenotypic typing and 16S rDNA analysis classified these organisms as species of Enterobacter, Ralstonia and Pseudomonas. All the strains readily utilized a broad spectrum of xenobiotics as sole sources of carbon and energy. Growth was observed on all monochlorobiphenyls (CBs), 2,2′-, 2,3-, 2,4′-, 3,3′- and 3,5-diCB as well as di- and trichlorobenzenes Growth was also sustainable on Askarel electrical transformer fluid and Aroclor 1221. Time-course studies using 100 ppm of 2-, 3- or 4-CB resulted in rapid exponential increases in cell numbers and CB transformation to respective chlorobenzoates (CBAs) within 70 h. Significant amounts of chloride were recovered in culture media of cells incubated with 2-CB and 3-CB, suggesting susceptibilities of both 2- and 3-chlorophenyl rings to attack, while the 4-CB was stoichiometrically transformed to 4-CBA. Extensive degradation of most of the congeners in Aroclor 1221 was observed when isolates were cultivated with the mixture as a sole carbon source. Aroclor 1221 was depleted by a minimum of 51% and maximum of 71%. Substantial amounts of chloride eliminated from the mixture ranged between 15 and 43%. These results suggest that some contaminated soils in the tropics may contain exotic micro-organisms whose abilities and potentials are previously unknown. An understanding of these novel strains therefore, may help answer questions about the microbial degradation of polychlorinated biphenyls (PCBs) in natural systems and enhance the potential use of bioremediation as an effective tool for cleanup of PCB-contaminated soils.     

Biodegradation of diazinon by Serratia marcescens DI101 and its use in bioremediation of contaminated environment

Four diazinon-degrading bacteria were isolated from agricultural soil by using an enrichment technique. The biochemical analysis and molecular method including RFLP indicated that these isolates were identical, and one strain designated DI101 was selected for further study. Phylogenetic analysis based on 16S rDNA sequencing indicated that the strain DI101 clearly belongs to the Serratia marcescens group. The ability of the strain to utilize diazinon as a source of carbon and phosphorus was investigated under different culture conditions. The DI101 strain was able to completely degrade 50 mg/l diazinon in MSM within 11 days with a degradation rate of 0.226 day-1. The inoculation of sterilized soil treated with 100 mg/kg of diazinon with 10(6) CFU/g DI101 resulted in a faster degradation rate than was recorded in non-sterilized soil. The diazinon degradation rate by DI101 was efficient at temperatures from 25 to 30degrees C and at pHs from 7.0 to 8.0. The degradation rate of diazinon was not affected by the absence of a phosphorus supplement, and addition of other carbon sources (glucose or succinate) resulted in the slowing down of the degradation rate. The maximum degradation rate (Vmax) of diazinon was 0.292 day-1 and its saturation constant (Ks) was 11 mg/l, as determined by a Michaelis-Menten curve. The strain was able to degrade diethylthiophosphate-containing organophosphates such as chlorpyrifos, coumaphos, parathion, and isazofos when provided as a source of carbon and phosphorus, but not ethoprophos, cadusafos, and fenamiphos. These results propose useful information for the potential application of the DI101 strain in bioremediation of pesticide-contaminated environments.     

Verification of Degradation of <Emphasis Type="Italic">n</Emphasis>-Alkanes in Diesel Oil by <Emphasis Type="Italic">Pseudomonas aeruginosa</Emphasis> Strain WatG in Soil Microcosms

Degradation of n-alkanes in diesel oil by Pseudomonas aeruginosa strain WatG (WatG) was verified in soil microcosms. The total petroleum hydrocarbon (TPH) degradation level in two bioaugmentation samples was 51% and 46% for 1 week in unsterilized and sterilized soil microcosms, respectively. The TPH degradation in the biostimulation was of control level (15%). The TPH degradation in aeration-limited samples was clearly reduced when compared with that in aeration-unlimited ones under both sterilized and unsterilized conditions. Addition of WatG into soil microcosms was accompanied by dirhamnolipid production only in the presence of diesel oil. These findings suggest that degradation of n-alkanes in diesel oil in soil microcosms would be facilitated by bioaugmentation of WatG, with production of dirhamnolipid, and also by participation of biostimulated indigenous soil bacteria.     

Impact of Inoculation Protocols, Salinity, and pH on the Degradation of Polycyclic Aromatic Hydrocarbons (PAHs) and Survival of PAH-Degrading Bacteria Introduced into Soil

Degradation of polycyclic aromatic hydrocarbons (PAHs) and survival of bacteria in soil was investigated by applying different inoculation protocols. The soil was inoculated with Sphingomonas paucimobilis BA 2 and strain BP 9, which are able to degrade anthracene and pyrene, respectively. CFU of soil bacteria and of the introduced bacteria were monitored in native and sterilized soil at different pHs. Introduction with mineral medium inhibited PAH degradation by the autochthonous microflora and by the strains tested. After introduction with water (without increase of the pore water salinity), no inhibition of the autochthonous microflora was observed and both strains exhibited PAH degradation.     

一株敌草胺降解菌的分离鉴定及降解性能

为探讨酰胺类除草剂敌草胺的微生物降解机理和土壤中敌草胺降解的生物强化性能,从长期使用敌草胺的烟田土壤中分离到一株敌草胺降解细菌菌株,命名为LGY06.经形态特征、生理生化特性及16S rDNA序列分析将其鉴定为蜡状芽孢杆菌.在纯培养条件下,菌株LGY06对敌草胺的降解符合一级动力学特征,7 d内对50 mg·L^-1敌草胺降解率达到75.7%;LGY06降解敌草胺的最适温度和最适pH值分别为35 ℃和8.0.通过气相色谱-质谱鉴定了菌株LGY06降解敌草胺的降解产物并分析了其降解途径,α-萘酚和丙酰胺是主要的降解产物,LGY06对敌草胺的作用方式主要有脱烷基、氧化(或水解),为矿化过程.室内模拟条件下,LGY06能有效促进土壤中敌草胺残留的降解,与未接种灭菌土、非根际土和根际土相比,敌草胺在接种LGY06土壤中的降解半衰期分别缩短了79.5%、36.6%和41.1%.     

Fate of aluminium and nickel in soil. Evaluation through lysimeters under laboratory conditions

ABSTRACT

Nanomaterials (Nms) applications and environmental deposition are continuously increasing. Aluminum (Al) and nickel (Ni) fate in soil, both from gamma alumina-based Nms and as chloride salts were evaluted through lysimeters. After 85 days of treatment, which included irrigation and collection of eluates, the soil of each lysimeter was divided into four sections. The metal concentration was analyzed in eluates, soil samples, and extracts. Al and iron (Fe) present in soil eluted from Control lysimeter. Al from Nms suspension treatment was quantified in the eluates since 30 days on. Ni eluted upon solid salt deposition on top of one device. These results indicate that Al and Ni applied under certain conditions on soil, could leach and reach groundwater. The total concentration and bioavailability (extractable metals) of Al and Fe in soils showed similar patterns. Ni was retained only in the soil of devices treated with chloride salts. Bioavailability % results were of concern for Ni under certain conditions of treatment: 15.57% and 11.08% in two chloride salt-treated lysimeters versus 0.55% and 0.47% of those in control and treated with Nms lysimeters. Conducting studies with different kinds of soil and longer treatment periods should be useful to understand Nms-metals fate in the environment. The results presented here constitute important evidences both for significant metal release from Nms and elution and for considerable Ni bioavailability, after deposition on soil in the form of Nms or as a chloride salt, respectively. Then, possible toxic effects could occur through exposure of aquatic and terrestrial organisms.     

Biodegradation of Ethametsulfuron-Methyl by <Emphasis Type="Italic">Pseudomonas</Emphasis> sp. SW4 Isolated from Contaminated Soil

A soil bacterium SW4, capable of degrading the sulfonylurea herbicide ethametsulfuron-methyl (ESM), was isolated from the bottom soil of a herbicide factory. Based on physiological characteristics, biochemical tests and phylogenetic analysis of the 16S rRNA gene sequence, the strain was identified as a Pseudomonas sp. The total degradation of ESM in the medium containing glucose was up to 84.6% after 6 days of inoculation with SW4 strain. The inoculation of strain SW4 to soil treated with ESM resulted in a higher degradation rate than in noninoculated soil regardless of the soil sterilized or nonsterilized. Five metabolites of ESM degradation were analyzed by liquid chromatography/mass spectrometry. Based on the identified products, strain SW4 seemed to degrade ESM after two separate and different pathways: one leads to the cleavage of the sulfonylurea bridge, whereas the other to the dealkylation and opening of the triazine ring of ESM.     

Survival of Cowpea Rhizobia in Soil as Affected by Soil Temperature and Moisture

Successful inoculation of peanuts and cowpeas depends on the survival of rhizobia in soils which fluctuate between wide temperature and moisture extremes. Survival of two cowpea rhizobial strains (TAL309 and 3281) and two peanut rhizobial strains (T-1 and 201) was measured in two soils under three moisture conditions (air-dry, moist (−0.33 bar), and saturated soil) and at two temperatures (25 and 35°C) when soil was not sterilized and at 40°C when soil was sterilized. Populations of rhizobia were measured periodically for 45 days. The results in nonsterilized soil indicated that strain 201 survived relatively well under all environmental conditions. The 35°C temperature in conjunction with the air-dry or saturated soil was the most detrimental to survival. At this temperature, the numbers of strains T-1, TAL309, and 3281 decreased about 2 logs in dry soil and 2.5 logs in saturated soil during 45 days of incubation. In sterilized soil, the populations of all strains in moist soil increased during the first 2 weeks, but decreased rapidly when incubated under dry conditions. The populations did not decline under saturated soil conditions. From these results it appears that rhizobial strains to be used for inoculant production should be screened under simulated field conditions for enhanced survival before their selection for commercial inoculant production.     

Genetic activity in Saccharomyces cerevisiae and thin-layer chromatographic comparisons of medical grades of pyrvinium pamoate and monopyrvinium salts

The pamoate, chloride, and iodide salts of pyrvinium, a cyanine dye with anthelmintic properties, were studied in a diploid mitotic recombination and gene conversion assay system (strain D5 of Saccharomyces cerevisiae) and a haploid yeast reversion assay (strain XV185-14C). With the use of a thin-layer chromatographic (TLC) detection technique, samples of pyrvinium pamoate from several sources were found to contain different numbers and quantities of impurities. All samples of pyrvinium pamoate and the monopyrvinium salts were recombinogenic in strain D5 and mutagenic in strain XV185-14C; the degree of genetic activity varied among the tested medical grades of pyrvinium pamoate. Monopotassium pamoate was found to be genetically inactive in both strains. Light-catalyzed degradation did not enhance the genetic activity of pyrvinium in either of the yeast strains; the degraded samples were not mutagenic.