Degradation of 2-Chloroethylvinylether by Ancylobacter aquaticus AD25 and AD27

Incubation of five different β-chloroethers with slurries prepared from brackish water sediment or activated sludge revealed that bis(2-chloroethyl)ether and 2-chloroethylvinylether (2-CVE) were biodegradable under aerobic conditions. After enrichment, two different cultures of Ancylobacter aquaticus that are capable of growth on 2-CVE were isolated. Both cultures were also able to grow on 1,2-dichloroethane. The cells contained a haloalkane dehalogenase that dehalogenated 2-CVE, 2-chloroethylmethylether, 2-bromoethylethylether, and epichlorohydrin. Experiments with cell extracts indicated that an alcohol dehydrogenase and an aldehyde dehydrogenase were also involved in the degradation of 2-CVE. This suggests that 2-CVE is metabolized via 2-hydroxyethylvinylether and vinyloxyacetaldehyde to vinyloxyacetic acid. Enzymatic ether cleavage was not detected. 2-CVE was also degraded by chemical ether cleavage, leading to the formation of 2-chloroethanol and acetaldehyde, both of which supported growth. We propose that A. aquaticus strains may be important for the detoxification and degradation of halogenated aliphatic compounds in the environment.     

Co-metabolism and microbial growth in the biodegradation of alkylbenzenesulphonates

Two organisms, CCMI507 and CCMI852, degrading undecylbenzenesulphonate (LAS) by the ortho- and meta- cleavage pathways were studied in cultures where glucose was used as carbon and energy source. CCMI507 ( ortho -pathway) started the degradation of LAS at the beginning of the culture development in parallel with glucose utilization. The degradation followed a steady profile of degradation until 77% of LAS was degraded in the culture containing initially 5 mg l⁻¹ of the compound and 81% in the cultures containing initially 10 and 20 mg l⁻¹ of LAS, after 72 h fermentation. The organism CCMI852 ( meta -pathway) started degrading the compound only after 20 h, when 75% of glucose was spent and well within the stationary phase. After 72 h fermentation the level of degradation by CCMI852 varied from 70% (5 mg l⁻¹ of LAS) to around 75% (10 and 20 mg l⁻¹ of LAS).     

Degradation of linear alkylbenzene sulfonate by a bacterial consortium isolated from the aquatic environment of Argentina

Aims:  To isolate and identify linear alkylbenzene sulfonate (LAS)-degrading bacteria from Río de la Plata and adjacent waters, and to assay their degradation capability as a consortium and as single organisms.
Methods and Results:  A consortium consisting of four bacterial strains: Aeromonas caviae (two strains), Pseudomonas alcaliphila and Vibrio sp. was identified by 16S rRNA analysis. Isolates grown as a consortium produced higher biomass from LAS and CO₂ release (mineralization) than individual cultures, and degraded 86% of LAS (20 mg l⁻¹), whereas pure strains degraded between 21% and 60%. Bacterial desulfonation from LAS was evidenced in the consortium and A. caviae strains. A complete disappearance of LAS (10 mg l⁻¹) was accomplished, and LAS levels of 50 and 100 mg l⁻¹ led to a pronounced decrease in the biodegradation extent and inhibition of culture growth.
Conclusions:  A bacterial consortium capable of complete LAS degradation was isolated from the Río de la Plata and adjacent waters. This consortium was more efficient for LAS degradation than individual cultures, and was sensitive to high LAS concentrations.
Significance and Impact of the Study:  The autochthonous consortium with high effectiveness on LAS biodegradation is a useful tool for LAS depletion from these polluted ecosystems.     

Oxygenation of 4-Alkoxyl Groups in Alkoxybenzoic Acids by Polyporus dichrous

The degradation of several alkyl ethers of vanillic acid, of 3-ethoxy-4-hydroxybenzoic acid, and of syringic acid, by the lignin-decomposing fungus Polyporus dichrous included (i) 4-dealkylation (e.g., 3-ethoxy-4-isopropoxybenzoic acid was in part dealkylated to 3-ethoxy-4-hydroxybenzoic acid), (ii) hydroxylation of the 4-alkoxyl groups (e.g., 3-ethoxy-4-isopropoxybenzoic acid was oxidized in part to 2-[4-carboxy-2-ethoxyphenoxy]-propane-1-ol), and (iii) reduction of carboxyl groups (older cultures) (e.g., 3-ethoxy-4-isopropoxybenzoic acid was reduced to 3-ethoxy-4-isopropoxybenzaldehyde and 3-ethoxy-4-isopropoxybenzyl alcohol). Some ethers (e.g., tri-O-methyl gallic acid and glycerol-beta-[4-carboxy-2-ethoxyphenyl]-ether) were not affected. The dealkylations and hydroxylations indicate that the fungus has a relatively nonspecific mechanism for oxygenating various 4-alkoxyl groups of alkoxybenzoic acids; no evidence for oxygenation of 3-alkoxyl groups was obtained. Hydroxylation products were generally degraded further, probably via dealkylation. The vanillic acid and 3-ethoxy-4-hydroxybenzoic acid formed by dealkylations were readily metabolized. Although the isopropyl ether of syringic acid was hydroxylated to 2-(4-carboxy-2, 6-dimethoxyphenoxy)-propane-1-ol, neither this compound nor the parent isopropyl ether was dealkylated; syringic acid itself was only slowly and incompletely metabolized. The relationship of these results to lignin degradation is discussed.     

Metabolism of Radiolabeled beta-Guaiacyl Ether-Linked Lignin Dimeric Compounds by Phanerochaete chrysosporium

Phanerochaete chrysosporium metabolized the radiolabeled lignin model compounds [gamma-C]guaiacylglycerol-beta-guaiacyl ether and [4-methoxy-C]veratrylglycerol-beta-guaiacyl ether (VI) to CO(2) in stationary and in shaking cultures. CO(2) evolution was greater in stationary culture. CO(2) evolution from [gamma-C]guaiacyl-glycerol-beta-guaiacyl ether and [4-methoxy-C]veratrylglycerol-beta-guaiacyl ether in stationary cultures was two- to threefold greater when 100% O(2) rather than air (21% O(2)) was the gas phase above the cultures. CO(2) evolution from the metabolism of the substrates occurred only as the culture entered the stationary phase of growth. The presence of substrate levels of nitrogen in the medium suppressed CO(2) evolution from both substrates in stationary cultures. [C]veratryl alcohol and 4-ethoxy-3-methoxybenzyl alcohol were formed as products of the metabolism of VI and 4-ethoxy-3-methoxyphenylglycerol-beta-guaiacyl ether, respectively.     

Metabolism of 3,4-dimethoxycinnamyl alcohol and derivatives by Coriolus versicolor

Abstract 3,4-Dimethoxycinnamyl alcohol (I) was actively metabolized by a white-rot fungus Coriolus versicolor in low nitrogen and high oxygen stationary cultures favouring the ligninolytic activity in the fungus. Substrate I was mainly oxidized to veratrylglycerol (III) which was a mixture of erythro and threo forms. Both isomers were degraded by cleavage between Cα and Cβ of the side chain to give veratraldehyde (VI), and (VI) was then reduced to veratryl alcohol (VII). A part of I was also metabolized via 1-(3,4-dimethoxyphenyl)-propane-3-ol (IV) and 1-(3,4-dimethoxyphenyl) propane-1,3-diol (VIII) by the fungus.     

Biodegradation of tert-butyl alcohol and related xenobiotics by a methylotrophic bacterial isolate

A new aerobic bacterial strain, CIP 1-2052, isolated from an activated sludge sample, was able to use tert-butyl alcohol (TBA), a product of methyl tert-butyl ether (MTBE) and ethyl tert-butyl ether (ETBE) degradation, as its sole carbon and energy source. Cobalt ions stimulated TBA mineralization. The maximum growth and TBA degradation rates were 0.032 +/- 0.004 h(-1) and 35.8 +/- 8.5 mg TBA x g(-1) (cell dry mass) per h, respectively. The growth yield on TBA was 0.54 +/- 0.02 g x g(-1). Strain CIP 1-2052 exhibited a particular substrate specificity towards alcohols. It degraded tertiary alcohols, TBA and tert-amyl alcohol (TAA), but neither their primary and secondary alcohol homologues, nor ethanol. However, one-carbon compounds, namely methanol and formate, were degraded by strain CIP 1-2052, showing the methylotrophic nature of this isolate. The properties of this new strain suggest that it could be used for bioremediation of contaminated aquifers.     

Initial reactions in the fungal degradation of guaiacylglycerol-β-coniferyl ether,a lignin substructure model

Fusarium solani M-13-1 was shake-cultured in a medium containing guaiacylglycerol-β-coniferyl ether (I), a model compound representing the arylglycerol-β-aryl ether linkage in lignin, as sole carbon source. From the culture filtrate guaiacylglycerol-β-coniferyl aldehyde ether (II) and guaiacylglycerol-β-ferulic acid ether (III) were isolated as metabolic products. Incubation with (III) resulted in formation of guaiacylglycerol-β-vanillin ether (IV), which was further metabolized to guaiacyglycerol-β-vanillic acid ether (V). The results indicate that the cinnamyl alcohol group of (I) is initially oxidized to an aldehyde group, which is further oxidized to a carboxyl group, yielding (II) and (III). Compound (III) is converted to (IV) by the release of a C₂ fragment, and the aldehyde group of (IV) is further oxidized to a carboxyl group, giving (V). In the pathway from (I) to (V), neither oxidation of the benzylic secondary alcohol to ketone nor cleavage of the arylglycerol-β-aryl ether linkage was observed. The fungus was found to attack both erythro and threo form without distinction.     

Parvibaculum lavamentivorans converts linear alkylbenzenesulphonate surfactant to sulphophenylcarboxylates, alpha,beta-unsaturated sulphophenylcarboxylates and sulphophenyldicarboxylates, which are degraded in communities

AIMS: The aims were to test whether Parvibaculum lavamentivoransT degraded commercial linear alkylbenzenesulphonate (LAS) surfactant via omega-oxygenation and beta-oxidation to sulphophenylcarboxylates (SPCs), whether the organism was widespread and reisolable, and whether the degradative community used the 4-sulphocatechol 1,2-dioxygenase to cleave the aromatic ring from LAS. METHODS AND RESULTS: Heterotrophic P. lavamentivoransT converted LAS (side chain length C10-C13) to SPCs (C4-C13), alpha,beta-unsaturated SPCs (C4-C13) and sulphophenyldicarboxylates (SPdCs) (at least C8-C12). Identifications came from high performance liquid chromatography (HPLC) separation, an electrospray interface and mass spectrometry. No evidence for other paths was found. The degradation of LAS in trickling filters inoculated with environmental samples always showed transient SPC intermediates (HPLC) and the presence of the P. lavamentivorans morphotype in the community. One new isolate was obtained. A community able to mineralize LAS contained 4-sulphocatechol-1,2-dioxygenase at high specific activity. CONCLUSIONS: Parvibaculum lavamentivoransT degrades commercial LAS via omega-oxygenation, oxidation and chain shortening through beta-oxidation to yield a wide range of SPCs. The latter are degraded in bacterial communities which contain organisms like P. lavamentivorans, and which utilize sulphocatechol dioxygenase for ring cleavage. SIGNIFICANCE AND IMPACT OF THE STUDY: There is one widespread pathway to degrade LAS. Any traces of LAS and larger amounts of SPCs in the effluent from sewage works are exposed to degradative organisms in acclimated and pristine environments. These degradative reactions can now be studied in pure cultures.     

A real-time qPCR assay for the detection of the nifH gene of Methanobrevibacter smithii, a potential indicator of sewage pollution

Aims: To degrade ether‐type polyurethane (ether‐PUR), ether‐PUR–degrading micro‐organism was isolated. Moreover, ether‐PUR–degrading mechanisms were analysed using model compounds of ether‐PUR. Methods and Results: A fungus designated as strain PURDK2, capable of changing the configuration of ether‐PUR, has been isolated. This isolated fungus was identified as Alternaria sp. Using a scanning electron microscope, the grid structure of ether‐PUR was shown to be melted and disrupted by the fungus. The degradation of ether‐PUR by the fungus was analysed, and the ether‐PUR was degraded by the fungus by about 27·5%. To analyse the urethane‐bond degradation by the fungus, a degraded product of ethylphenylcarbamate was analysed using GC/MS. Aniline and ethanol were detected by degradation with the supernatant, indicating that the fungus secreted urethane‐bond–degrading enzyme(s). PURDK2 also degraded urea bonds when diphenylmethane‐4,4′‐dibutylurea was used as a substrate. Conclusions: The enzyme(s) from PURDK2 degraded urethane and urea bonds to convert the high molecular weight structure of ether‐PUR to small molecules; and then the fungus seems to use the small molecules as an energy source. Significance and Impact of the Study: Ether‐PUR–degrading fungus, strain PURDK2, was isolated, and the urethane‐ and urea‐bonds–degrading enzymes from strain PURDK2 could contribute to the material recycling of ether‐PUR.     

Microbial degradation of secondaryn-alkyl sulfates and secondary alkanols

Secondaryn-alkyl sulfates (and secondary alkanols) prove to be degraded aerobically by aPseudomonas species (Ps. B-2) to carbon dioxide, water and sulfate. The proposed mechanism for the biodegradation proceeds via the alcohol → ketone → hydroxyketone → dione → aldehyde + acid. Consequently, two fatty acids are formed which are subsequently degraded by β-oxidation. This pathway requires the presence of molecular oxygen for the hydroxylation of the ketone. Attempts to isolate bacteria growing on secondary alcohols anaerobically were unsuccessful.     

Biosynthesis of the secondary metabolite veratryl alcohol in relation to lignin degradation in Phanerochaete chrysosporium

The lignin-degrading basidiomycete Phanerochaete chrysosporium synthesizes veratryl alcohol (3,4-dimethoxybenzyl alcohol) via phenylalanine, 3,4-dimethoxycinnamyl alcohol and veratrylglycerol. Study of the conversion of 3,4-dimethoxycinnamyl alcohol to veratrylglycerol and veratryl alcohol showed is to be (a) catalyzed by a secondary metabolic system, (b) markedly suppressed by culture agitation, and (c) strongly inhibited by l-glutamate. The amount of veratryl alcohol synthesized de novo was positively correlated with the O₂ concentration after primary growth. Other work has shown that the cinnamyl alcohol terminal residue in a lignin substructure model compound is degraded via arylglycerol and benzyl alcohol structures in ligninolytic cultures of P. chrysosporium, and that the ligninolytic system exhibits traits (a)-(c) above. Ligninolytic activity is also strongly and positively correlated with O₂ concentration. The results here suggest, therefore, that the actual biosynthetic secondary metabolic product is 3,4-dimethoxycinnamyl alcohol, but that this is degraded by the ligninolytic system to veratryl alcohol via veratrylglycerol. Veratryl alcohol is only slowly metabolized by the fungus, and accumulates.Non-standard abbreviation tlc thin layer chromatography     

Two squid skin proteoglycans each containing chondroitin sulfates with different sulfation patterns.

Two chondroitin sulfate containing proteoglycans, amounting to approximately 6% of the tissue proteoglycans, were isolated from the skin of the squid. They were almost completely extracted by 4 M guanidine hydrochloride in the presence of proteinase inhibitors, and then they were separated by DEAE-Sephacel chromatography and isolated by further chromatography on Sepharose CL-4B. Each proteoglycan contained two types of chondroitin sulfates that differed in their sulfation patterns. One proteoglycan (molecular mass (M(r)) 5.6 x 10(5)) contained, on the average, four chondroitins (M(r) 8.4 x 10(4)) and five chondroitin sulfates (M(r) 3.4 x 10(4)), whereas the other proteoglycan (M(r) 5.2 x 10(5)) contained three chondroitin sulfates (M(r) 1.1 x 10(5)) and five oversulfated chondroitin sulfates (M(r) 4.3 x 10(4)). The glycosaminoglycans were released from the proteoglycans by treatment with alkaline borohydride, separated from the oligosaccharides by chromatography on Bio-Gel P-30, and isolated by chromatography on DEAE-Sephacel and Sepharose CL-6B. Chondroitin sulfates were degraded by chondroitinase AC to an extent of 70% and consisted of significant amounts of disaccharides sulfated at C-4 of the galactosamine, disulfated disaccharides, and small amounts of nonsulfated disaccharides, as well as disaccharides that bore sulfates at C-6. Oversulfated chondroitin sulfate was degraded by chondroitinase AC to only 40% and contained appreciable amounts of disulfated and trisulfated disaccharides. The glycosaminoglycans also contained neutral monosaccharides; glucose was the predominant neutral sugar. A part of the oligosaccharides of both proteoglycans was of identical structure to that of chondroitin sulfate.     

Biodegradation of ethyl t-butyl ether (ETBE), methyl t-butyl ether (MTBE) and t-amyl methyl ether (TAME) by Gordonia terrae

Gordonia terrae strain IFP 2001 was selected from activated sludge for its capacity to grow on ethyl t-butyl ether (ETBE) as sole carbon and energy source. ETBE was stoichiometrically degraded to t-butyl alcohol (TBA) and the activity was inducible. A constitutive strain, G. terrae IFP 2007, derived from strain IFP 2001, was also selected. Methyl t-butyl ether (MTBE) and t-amyl methyl ether (TAME) were not used as carbon and energy sources by the two strains, but cometabolic degradation of MTBE and TAME was demonstrated, to TBA and t-amyl alcohol (TAA) respectively, in the presence of a carbon source such as ethanol. No two-carbon compound was detected during growth on ETBE, but formate was produced during cometabolic degradation of MTBE or TAME. A monooxygenase was involved in the degradation of ethers, because no degradation of ETBE was observed under anaerobic conditions and the presence of a cytochrome P-450 was demonstrated in G. terrae IFP 2001 after induction by cultivation on ETBE.     

Sequential enzyme-catalyzed metabolism of 4-nitrotoluene to S-(4-nitrobenzyl)glutathione

[14C]-4-Nitrotoluene was metabolized by rat liver postmitochondrial supernatant containing NADPH, reduced glutathione and a sulfate activating system to 4-nitrobenzyl alcohol, 4-nitrobenzyl sulfate, and S-(4-nitrobenzyl) glutathione. Formation of both sulfur-containing metabolites was dependent on the presence of a sulfate activating system. These results suggest that the glutathione conjugate was derived from 4-nitrobenzyl sulfate. Reaction of 4-nitrobenzyl sulfate with glutathione was not detected in pH 7.4 buffer, but rat liver cytosol catalyzed the formation of the glutathione conjugate from 4-nitrobenzyl sulfate. These results show that 4-nitrotoluene is metabolized in rat liver by sequential side chain oxidation, sulfation, and glutathione conjugation. Furthermore, they indicate that, unlike certain other arylmethyl sulfates, 4-nitrobenzyl sulfate is not highly reactive.     

An alpha-proteobacterium converts linear alkylbenzenesulfonate surfactants into sulfophenylcarboxylates and linear alkyldiphenyletherdisulfonate surfactants into sulfodiphenylethercarboxylates

The surfactant linear alkylbenzenesulfonate (LAS; 0.5 mM) or linear monoalkyldiphenyletherdisulfonate (LADPEDS; 0.5 mM) in salts medium was easily degraded in laboratory trickling filters, whereas carbon-limited, aerobic enrichment cultures in suspended culture with the same inocula did not grow. We took portions of the trickling filters which degraded LADPEDS, shook the organisms from the solid support (polyester), and found that growth in suspended culture in LADPEDS-salts medium occurred only in the presence of some solid support (polyester fleece or glass wool), though little biomass was immobilized on the support. The end products in suspended culture were identical with those from the trickling filters. There was low plating efficiency of LADPEDS-grown cultures on complex medium, and no picked colony or mixture of colonies grew in LADPEDS-salts-glass wool medium. However, selective plates containing LADPEDS-salts medium solidified with agarose yielded LADPEDS-dependent, pinpoint colonies which could be picked singly and subcultured in selective liquid medium. Isolate DS-1 was a bacterium which showed 93% sequence homology (16S ribosomal DNA) to its nearest phylogenetic neighbor, an alpha-proteobacterium. Strain DS-1 grew heterotrophically in LADPEDS-salts-glass wool medium and converted the set of aryl-substituted alkanes to the corresponding aryl-substituted carboxylic acids of shorter chain length. Similarly, strain DS-1 grew heterotrophically with commercial LAS, converting it to a set of sulfophenylcarboxylates. Growth with a single isomer of LAS [3-(4-sulfophenyl)dodecane] was concomitant with excretion of 4-(4-sulfophenyl)hexanoate, which was identified by matrix-assisted laser desorption ionization mass spectrometry. The growth yield (6.4 g of protein/mol of C) indicated mass balance, which, with the specific growth rate (0.05 h(-1)), indicated a specific utilization rate of LAS of 2.2 mkat/kg of protein.     

Effect of alcohol sulfate, linear alkylbenzene sulfonate and natural soap on the development of fertilized eggs of the mouse in vitro

Eggs from B6 x C3F1 female mice, which were fertilized in vitro with sperm from C3 x 101F1 male mice, were treated with synthetic surfactants, alcohol sulfate (AS) and linear alkylbenzene sulfonate (LAS), and natural soap for 1 h at the pronucleus stage, and then cultivated for 5 days. Eggs treated with AS or LAS at concentrations of less than 0.025% developed to the blastocyst stage as well as the untreated ones. At concentrations of AS or LAS higher than 0.03% no egg developed beyond the 1-cell stage. There appeared to be a threshold concentration between 0.025% and 0.03% of AS or LAS on the development of the mouse egg. However, natural soap had no effect on the development of the mouse egg up to 0.05%. When AS or LAS was applied to the culture medium throughout the cultivation of fertilized eggs for 5 days, there also appeared to be a threshold concentration between 0.01% and 0.025%, but not in the case of natural soap. The results provide additional support to our previous observations that AS and LAS can interrupt mouse pregnancy by killing fertilized eggs.     

Biotransformation of alkyl and aryl carbonates. Microbial degradation

Summary An enriched mixed culture was successfully grown on model alkyl and aryl carbonates. These compounds were degraded by microorganisms at different rates.P-Chlorophenyl-2-octyl carbonate andp-nitrobenzyl-2-octyl carbonate were metabolized through the formation ofp-chlorophenol andp-nitrobenzyl alcohol respectively. A strain ofAcinetobacter calcoacefcus isolated from the mixed culture utilized phenyl-2-octyl carbonate by an intracellular hydrolase to phenol and 2-octanol which were further metabolized.     

Mineralization of methyl tert-butyl ether and other gasoline oxygenates by Pseudomonads using short n-alkanes as growth source

Biodegradation of methyl tert-butyl ether (MTBE) by cometabolism has shown to produce recalcitrant metabolic intermediates that often accumulate. In this work, a consortium containing Pseudomonads was studied for its ability to fully degrade oxygenates by cometabolism. This consortium mineralized MTBE and TBA with C3-C7 n-alkanes. The highest degradation rates for MTBE (75 +/- 5 mg g(protein) (-1) h(-1)) and TBA (86.9 +/- 7.3 mg g(protein) (-1) h(-1)) were obtained with n-pentane and n-propane, respectively. When incubated with radiolabeled MTBE and n-pentane, it converted more than 96% of the added MTBE to (14)C-CO(2). Furthermore, the consortium degraded tert-amyl methyl ether, tert-butyl alcohol (TBA), tert-amyl alcohol, ethyl tert-butyl ether (ETBE) when n-pentane was used as growth source. Three Pseudomonads were isolated but only two showed independent MTBE degradation activity. The maximum degradation rates were 101 and 182 mg g(protein) (-1) h(-1) for Pseudomonas aeruginosa and Pseudomonas citronellolis, respectively. The highest specific affinity (a degrees (MTBE)) value of 4.39 l g(protein) (-1) h(-1) was obtained for Pseudomonas aeruginosa and complete mineralization was attained with a MTBE: n-pentane ratio (w/w) of 0.7. This is the first time that Pseudomonads have been reported to fully mineralize MTBE by cometabolic degradation.     

Long term performance of a constructed wetland for landfill leachate treatment

The constructed wetland (CW) was developed as a pilot integrated system for the capital city's old sanitary landfill site. It consisted of three interconnected beds, two of vertical flow and one of horizontal flow stage. The CW covered 311 m² with an intermittent hydraulic load of 0.5 cm d⁻¹, filled with sand media and planted with reeds and cattails. The performance efficiency of the CW systems was evaluated for 7 years through physical and chemical parameters. Some monitored parameters varied noticeable. The efficiency for COD was 50%, BOD₅ (59%), ammonia nitrogen (51%), nitrate (negative), total phosphorus (P) (53%), sulfates (negative), sulfides (49%), chlorides (35%), and Fe (84%). The average concentrations of suspended solids, COD, BOD₅, nitrate, total P, sulfates, sulfides, and Fe were below limits after treatment. The ratio between N and P showed a limited level of P for biological processes. The performance of the system did not vary significantly with regard to temperature, however, it varied with precipitation. The results showed that the CW system, as a tertiary system or as an independent system, could be a low-cost alternative for the treatment of leachate from old landfill sites.