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GGE-degrading bacteria from a paper mill waste site were identified through a series of enrichments as described in Materials and Methods.
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SYK-6 and SG61-1L were both isolated from pulp and paper mill waste sites (50), but unlike SYK-6, SG61-1L waspecificallyly selected through rounds of enrichment culturing for the ability to utilize GGE as a sole carbon source.
Generally released from bacterial lysis, endotoxins are ubiquitous in the airborne environment, but high airborne-endotoxin levels are observed in industrial environments, such as cotton mills, waste collection sites, swine barns, and grain handling equipment, where organic dusts are present (Liebers et al. 2006).
Bacterial strains isolated from other industrial wastewaters or contaminated sites have been also applied for the detoxification of olive mill waste phenolic compounds.
RNA-Seq was performed from C. autoethanogenum growing in continuous culture in a 1.5-L continuous-stirred tank reactor (CSTR) with steel mill waste gas (composition: 42% CO, 36% N2, 20% CO2, and 2% H2; collected from a New Zealand Steel site in Glenbrook, New Zealand) as the sole energy and carbon source as described previously [ 52].
Briefly, RNA was isolated (RNeasy Mini Kit, Qiagen, Valencia, CA, USA) from 20 mL C. autoethanogenum culture growing in serum bottles at an optical density (OD)600 of 0.2 in PETC media and steel mill waste gas (composition: 42% CO, 36% N2, 20% CO2, and 2% H2; collected from a New Zealand Steel site in Glenbrook, New Zealand) as the sole energy and carbon source.
That plant will use paper mill waste.
Hazardous waste site remediation -- Economic aspects -- United States.
Solid material of olive mill waste.
liquid material of olive mill waste.
Dyeing with mill waste provides an economic option for an existing timber manufacturing byproduct.
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