2019
DOI: 10.1016/j.watres.2018.10.070
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Response and recovery of microbial communities subjected to oxidative and biological treatments of 1,4-dioxane and co-contaminants

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Cited by 46 publications
(17 citation statements)
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“…Apart from the uncultured and unknown bacteria, Pseudolabrys, Rhizomicrobium, Candidatus_Solibacter, Opitutus and Bryobacter were the dominant genera across all samples. Pseudolabrys are ubiquitous in hydrocarbon-rich soil, and had been identified as hydrocarbon degraders (Miao et al 2019). In this study, Pseudolabrys was the most abundant genus; Fig.…”
Section: Discussionmentioning
confidence: 61%
“…Apart from the uncultured and unknown bacteria, Pseudolabrys, Rhizomicrobium, Candidatus_Solibacter, Opitutus and Bryobacter were the dominant genera across all samples. Pseudolabrys are ubiquitous in hydrocarbon-rich soil, and had been identified as hydrocarbon degraders (Miao et al 2019). In this study, Pseudolabrys was the most abundant genus; Fig.…”
Section: Discussionmentioning
confidence: 61%
“…Fenton-HPCD surfactant 16 PAH listed by USEPA 1090 mg/kg 99 [109] Fenton-bioremediation 16 PAHs 263.6 ± 73.3 and 385.2 ± 39.6 mg/kg 5-6 rings 78-90; 2-4 rings 52-85 [28] Fenton-bioremediation 1,4-dioxane 100 [110] Fenton-bioremediation Lubricants 10,000 mg/kg 99.2 [70] Fenton-bioaugmentation serial foam PEH 7470 mg/kg 92 [111] Fenton-anoxicbiodegradation 16 PAHs 350.07 mg/kg 33.2-95.9 [112] Fenton-pre-oxidationbioremediation PEH 12,178 ± 390 mg/kg 42 ± 1.43 [113] Fenton Fenton-pre-oxidationbioremediation Crude oil 23,440 ± 390 mg/kg 53 [115] Fenton-like treatment-bioremediation Diesel 700-2600 mg/kg 75 [116] Fenton-like reaction combined with Phanerochaete chrysosporium Polybrominated diphenyl ethers 18.70 ± 0.08 ng/g 55.5 ± 6.0-72.6 ± 3.6 [117] Tween 80 surfactant-electro-Fenton Diesel 50 g/kg 87.2 [118] Sono-photo-Fenton TPH 15 g/kg 99 [119] PMS in presence of Fe (V) PCB > 1000 mg/kg 40 [120] PS…”
Section: Process Description Contaminant and Concentration Removal Ef...mentioning
confidence: 99%
“…In the environment, 1,4-dioxane has shown remarkable recalcitrance to natural biological and chemical attenuation processes, and its removal by traditional water treatment approaches has proven to be a challenge. Generally, strong oxidants are needed to activate the diether ring. Several studies have demonstrated that advanced oxidation processes (AOPs) such as H 2 O 2 , plasma, UV, peroxymonosulfate, and ozone treatment are effective in generating reactive oxygen species (ROS) to degrade 1,4-dioxane. Electrochemical oxidation has emerged as a promising technology to remove persistent organic pollutants because it is cost-competitive with other AOPs and can be implemented for in situ groundwater treatment by using mesh electrodes. , Indirect oxidation through generated ROS such as ·OH and direct electron transfer were shown as the main degradation mechanism of this technology . However, in spite of the effectiveness of the electrochemical oxidation processes, high capital costs and considerable energy consumption have thus far deferred field-scale applications.…”
Section: Introductionmentioning
confidence: 99%