Degradation Of DDE Research Articles

The effect of farming techniques on degradation of DDT in historical cotton farms

DDT was used in the mid 20th century for crop and livestock production. After use, DDT and its degradates DDE and DDD (collectively DDX) remain in the environment for decades. A few studies have reported that the rate of degradation of DDT into its metabolites is affected by various farming techniques like tillage, irrigation, and use of fertilizers. However, most of these studies did not evaluate active farms, and none of them focused on the Southeast US or historical cotton farms. Therefore, in this study, we aimed to determine if different farming techniques affect the decomposition of DDT in Walton County, Georgia, where farms historically grew cotton. Five Walton County farms were sampled for soil, and churches were sampled as control sites. The extensive land history of the farms was recorded, and the soil levels of p,p’-DDT, p,p’-DDE, p,p’-DDD, o,p’-DDT, and o,p’-DDE were measured using gas chromatography-tandem mass spectrometry. All farm sites had detectable levels of p,p’-DDT, p,p’-DDE, and p,p’-DDD, while few sites had detectable levels of o,p’-DDT and o,p’-DDE. Tillage was found to speed up p,p’-DDE degradation, but there was no effect on p,p’-DDT degradation. Plowing was associated with an increase in decomposition of p,p’-DDT, but p,p’-DDE and p,p’-DDD were not significantly increased. The largest difference in the degradation of DDT was based on the fertilizer type. Natural fertilizer sped up degradation of p,p’-DDT and p,p’-DDE; synthetic fertilizer increased p,p’-DDE degradation, but not p,p’-DDT degradation.

Accelerated remediation of organochlorine pesticide-contaminated soils with phyto-Fenton approach: a field study.

Phytoremediation and advanced oxidationprocesses are among the most promising techniques for removing organic pollutants from soils. A field trial was performed for six months to evaluate the effect of nano-Fe3O4 on the degradation of organochlorine pesticide residues including Lindane, p,p'-dichlorodiphenyltrichloroethane (DDT), p,p'-dichlorodiphenyldichloroethylene (DDE), and p,p'-dichlorodiphenyldichloroethane (DDD) in pesticide-contaminated soils in the presence of vetiver in Bac Giang province, Vietnam. Vetiver was planted in three zones with different nano-Fe3O4 concentrations. Soil samples from each zone were periodically collected to determine the remaining concentrations of selected organochlorine pesticides via gas chromatography-electron capture detector. Results indicated that the total DDT concentrations in the examined soil were 1.9-13 times higher than the permissible threshold level (10µgg-1) established by the national technical regulation on pesticide residues in soil. The (p,p'-DDE + p,p'-DDD)/p,p'-DDT ratios ranged from 13.5 to 114, indicating the absence of recent inputs of technical DDTs at the study area. DDT dechlorination mainly occurred under aerobic pathways to form DDE. Furthermore, DDE degradation in soil was adequately described by the pseudo-first-order kinetics model (R2 > 0.892). In the presence of vetiver, the rate constants of DDE degradation were 0.264, 0.350, and 0.434month-1 with 0, 25, and 100mgkg-1 of added nano-Fe3O4, respectively, indicating that the degradation of DDE correlated positively with Fe3O4 concentration in the soil. Additionally, the presence of vetiver and nano-Fe3O4 in the soil increased DDT removal rates, which might be linked to the involvement of Fenton/Fenton-like reactions.

Black Carbon Facilitated Dechlorination of DDT and its Metabolites by Sulfide.

1,1-trichloro-2,2-di(4-chlorophenyl)ethane (DDT) and its metabolites 1,1-dichloro-2,2-bis(4-chlorophenyl)ethane (DDD) and 1,1-dichloro-2,2-bis(4-chlorophenyl)ethylene (DDE), are often detected in soils and sediments containing high concentrations of black carbon. Sulfide (∼5 mM) from biological sulfate reduction often coexists with black carbon and serves as both a strong reductant and a nucleophile for the abiotic transformation of contaminants. In this study, we found that the abiotic transformation of DDT, DDD, and DDE (collectively referred to as DDX) require both sulfide and black carbon. 89.3 ± 1.8% of DDT, 63.2 ± 1.9% of DDD, and 50.9 ± 1.6% of DDE were degraded by sulfide (5 mM) in the presence of graphite powder (21 g/L) after 28 days at pH 7. Chloride was a product of DDX degradation. To better understand the reaction pathways, electrochemical cells and batch reactor experiments with sulfide-pretreated graphite powder were used to differentiate the involvement of black carbon materials in DDX transformation by sulfide. Our results suggest that DDT and DDD are transformed by surface intermediates formed from the reaction between sulfide and black carbon, while DDE degradation involves reductive dechlorination. This research lays the groundwork for developing an alternative in situ remediation technique for rapidly decontaminating soils and sediments to lower toxic products under environmentally relevant conditions.

Draft Genome Sequence of Enterobacter aerogenes, a DDE-Degrading and Plant Growth-Promoting Strain Isolated from Cucurbita pepo.

We report here the draft genome of Enterobacter aerogenes, a Gram-negative bacterium of the Enterobacteriaceae isolated from Cucurbita pepo root tissue. This bacterium shows 2,2-bis(p-chlorophenyl)-1,1-dichloroethylene (DDE)-degrading potential and plant growth-promoting capacity. An analysis of its 4.5-Mb draft genome will enhance the understanding of DDE degradation pathways and phytoremediation applications for DDE-contaminated soils.

Gene cluster and regulation system for 1,1-dichloro-2,2-bis(4-chlorophenyl)ethylene (DDE) degradation in Janibacter sp. TYM3221

A DDE-degrading bacterium, Janibacter sp. TYM3221, is able to grow on biphenyl and degrades 1,1-dichloro-2,2-bis(4-chlorophenyl)ethylene (DDE) via a meta-ring cleavage pathway. The bphAa gene, encoding a biphenyl dioxygenase large subunit, was previously demonstrated to be involved in the degradation of DDE in TYM3221. The bph gene cluster, containing orf2 and bphDAaAbAcAdBCST was cloned and characterized. Reverse transcription-PCR (RT-PCR) analysis indicated that these genes were transcribed as an operon. The real-time RT-PCR on orf2, bphAa, bphC, and bphS suggest the presence of the inducible orf2 promoter (orf2p) and constitutive bphAa promoter (bphAap). The TYM3221 bphST conducted biphenyl-dependent inducible activation plus constitutive basal activation of orf2p and constitutive activation of bphAap in a rhodococcal host strain, Rhodococcus erythropolis IAM1399, suggesting that expression of the TYM3221 bph operon depends on the bphST-coded two-component regulatory system. Both of these promoters were also induced by the bphS1T1 of a biphenyl degrader, Rhodococcus jostii RHA1, and contained the 24-bp consensus sequences of RHA1 bphS1T1-dependent promoters. The replacement of RHA1 bphS1 with TYM3221 bphS in combination with RHA1 bphT1 suggests that TYM3221 bphS is responsible for low inducible and high constitutive activation of orf2p in IAM1399 by the TYM3221 bphST-system. Expression of bphAaAbAcAdBC in IAM1399 resulted in the transformation of DDE to the meta-ring cleavage product via 2,3-hydroxylation, suggesting that these genes are involved in DDE degradation.

Characterization of the 1,1-dichloro-2,2-bis(4-chlorophenyl)ethylene (DDE) degradation system in Janibacter sp. TYM3221

Bacterial degradation of 1,1-dichloro-2,2-bis(4-chlorophenyl)ethylene (DDE) has been previously reported, however, its degradation enzyme system has not been characterized. In this study, a DDE-degrading bacterium, Janibacter sp. TYM3221, was isolated and characterized. Transformation of DDE was demonstrated by TYM3211 resting cells grown in LB in the presence and absence of biphenyl. Gas chromatography–mass spectrometry analysis revealed five metabolites of DDE containing a meta-ring cleavage product and 4-chlorobenzoic acid, suggesting that TYM3221 degrades DDE to 4-chlorobenzoic acid via a meta-ring cleavage product. A gene cluster, bphAaAbAcAd, which codes for biphenyl dioxygenase subunits, was cloned from TYM3221. A mutant strain with a bphAa-gene inactivation did not grow on biphenyl, and showed no DDE degradation activity. These results indicate that in strain TYM3221, the bphAa-coded biphenyl dioxygenase is involved not only in the metabolism of biphenyl but also in the degradation of DDE.

Bioremediation of DDT in soil by genetically improved strains of soil fungus Fusarium solani.

Bioremediation of DDT in soil by genetically improved recombinants of the soil fungus Fusarium solani was studied. The parent strains were isolated from soil enriched with DDD or DDE (immediate anaerobic and aerobic degradation products of DDT), as further degradation of these products are slow processes compared to the parent compound. These naturally occurring strains isolated from soil, however, are poor degraders of DDT and differed in their capability to degrade its metabolites such as DDD, DDE, DDOH and DBP and other organochlorine pesticides viz. kelthane and lindane. Synergistic effect was shown by some of these strains, when grown together in the medium containing DDD and kelthane under mixed culture condition. No synergism in DDE degradation was observed with the strains isolated from enriched soil. DDD-induced proteins extracted from individual culture filtrate (exo-enzyme) when subjected to SDS-Polyacrylamide Gel Electrophoresis (SDS-PAGE) showed complementary polypeptide bands in these strains i.e., each strain produced distinct DDD degrading polypeptide bands and the recombinant or hybrid strains produced all of the bands of the two parents and degraded DDD better than the parental strains. Recombinant hybrid strains with improved dehalogenase activity were raised by parasexual hybridisation of two such complementary isolates viz. isolate 1(P-1) and 4(P-2) showing highest complementation and are compatible for hyphal fusion inducing heterokaryosis. These strains are genetically characterised as Kel+Ben(R)DBP-Lin- and Kel-Ben(r)DBP+Lin+ respectively. Recombinants with mixed genotype, i.e., Kel+Ben(R)DBP+Lin+ showing superior degradation quality for DDT were selected for bioremediation study. Recombination was confirmed by polypeptide band analysis of DDD induced exo-proteins from culture filtrate using SDS-Polyacrylamide Gel Electrophoresis (PAGE) and RAPD (Random Amplified Polymorphic DNA) of genomic DNA using PCR (Polymerase Chain Reaction) technique. SDS-PAGE showed combination of DDD induced polypeptide bands characteristic of both the parents in the recombinants or the hybrids. PCR study showed the parent specific bands in the recombinant strains confirming gene transformation.

Recalcitrance of DDE (2,2‐BIS‐(4‐chlorophenyl)‐1,1 dichloroethylene) and DPE (1,1‐diphenylethylene) to cometabolic aerobic biodegradation

Bacterial degradation of the persistent DDT [1,1,1‐trichloro‐2,2‐bis(4‐chloro‐pheny‐l)ethane] metabolite DDE has not previously been reported. Bacteria from DDT, PCP and PAH contaminated soils and sediments were extracted and evaluated for their ability to degrade DDE and its dehalogenated derivative DPE. Aerobic aromatic hydrocarbon degrading bacteria were enriched using chemostat techniques under both carbon limited and nitrogen limited selection conditions. DDE, ethylbenzene (EB), DPE and dipyridyl ketone oxime (DPKO) were added as structurally related potentially biodegradable carbon and nitrogen sources. No significant degradation of DDE and DPE was observed under these conditions. Pure cultures isolated from the enrichments on nonselective growth media were able to utilise EB and DPKO as carbon and nitrogen sources, respectively but were unable to degrade DDE or DPE alone or in the presence of EB and DPKO. The absence of DDE degradation capacity in the microbial community was confirmed by adding 14C‐DDE to operating chemostats. Labelled volatile degradation products and 14CO2 were not detected. In addition, no products of 14C‐DDE degradation were detected in aqueous or solvent extracts of the reactor contents. The inability to enrich DDE and DPE degrading bacteria may explain DDE persistence in DDT contaminated soils.

The effect of commercial processing on incurred residues of DDE in meat products.

The influence of processing on the degradation of DDE in meat products was investigated. First, the current level of contamination in six different types of Spanish meat products was determined. Analysis were carried out by capillary gas chromatography with electron capture detector. Of the three residues analysed (both o,p' and p,p' isomers of DDT, DDD, and DDE), only p,p'-DDE was found above the detection limit of 4 micrograms/kg fat. The frequency of p,p'-DDE detection for the various products investigated varied between 78 and 100% of the 129 samples analysed, although mean levels were very low, in the range within 6-16 micrograms/kg. No sample contained DDE residues above the EC maximum residue limit of 1 mg/kg for DDT and metabolites on meat products. Mean concentrations of DDE in Spanish meat products have declined since 1980 by more than 10-fold as compared with previously reported data. Meat products following three commercial processes were analysed to compare the levels of DDE in the finished products with those obtained in the starting material. The average levels of DDE remained unchanged after 30 days of curing in 26 samples of pork sausage. Similarly, mean DDE concentrations were essentially constant throughout the ripening process to which 30 hams were subjected. Finally, cooking in an oven (80-82 degrees C for 100 min) of 20 pork bologna samples produced an apparent increase of 12.5% in mean p,p'-DDE levels that was not statistically significant (p > 0.05).(ABSTRACT TRUNCATED AT 250 WORDS)