RETRACTED ARTICLE: Role of UV photolysis in accelerating the biodegradation of 2,4,6-TCP.

Abstract

2,4,6-TCP, a kind of chlorinated aromatic and aliphatic compound, is difficult to be biodegraded by ordinary microorganisms. UV photolysis and biodegradation of 2,4,6-TCP by Bacillus amyloliquefaciens intimate coupling is a potential means to accelerate its biotransformation. The initial steps of 2,4,6-TCP biodegradation involve mono-oxygenation reactions that have molecular oxygen and an intracellular electron carrier as cosubstrates. It was demonstrated that B. amyloliquefaciens has the 2,4,6-TCP monooxygenase gene tcpA which could encode 2,4,6-TCP monooxygenase (TCP-MO). TCP-MO would catalytically decompose 2,4,6-TCP into 2,6-DCHQ. We employed an internal loop photolytic biofilm reactor for 2,4,6-TCP degradation. Sequentially coupled photolysis and biodegradation experimental results suggested that 2,4,6-TCP removal rate in P+B (TCP(UV)+phenol) protocol was higher by 77 and 103% when compared to B (TCP+phenol) and B (TCP-only) protocols respectively. The corresponding loss rate coefficient (k) values were 0.069, 0.039, 0.034mg/L·min-1 respectively. This is because UV photolysis converted 2,4,6-TCP into its intermediates: 2,4-dichlorophenol (2,4-DCP), 4-monochlorophenol (4-MCP), phenol, 2,6-dichloro-p-hydroquinone (2,6-DCHQ), with all displaying less inhibition to bacterial action. In addition, phenol was the crucial UV-photolysis product from 2,4,6-TCP, its catabolic oxidation generating internal electron carriers that may accelerate the initial steps of 2,4,6-TCP biodegradation. Intimately coupled photolysis and biodegradation experimental results suggested that 2,4,6-TCP removal rate in P&B (TCP+phenol) protocol was higher by 166 and 681% when compared to P&B (TCP-only) and P+B protocols respectively. The corresponding loss rate coefficient (k) values were 0.539, 0.203, 0.069mg/L·min-1 respectively. It provided sufficient evidence to demonstrate that intimately coupled photolysis and biodegradation accelerated 2,4,6-TCP removal much faster than sequentially coupled photolysis and biodegradation. In addition, oxidation of phenol was the mechanism by which intimately coupled photolysis and biodegradation accelerated rapid 2,4,6-TCP removal producing electron equivalents that stimulated the initial mono-oxygenation reactions for 2,4,6-TCP biodegradation. It is important to note that 2,6-DCHQ (produced from UV-photolysis products or initial mono-oxygenation reactions) would be catalytically decomposed into 6-chlorohydroxyquinol (6-CHQ). Based on this, a tentative reaction mechanism for the photo-biodegradation 2,4,6-TCP was proposed.