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A secondary stage sewerage treatment plant treats all waste water from the station.
However, in the nutrient-rich waste water, biofilms form rapidly on the heat exchanger and significantly reduce its efficiency.
There was no detailed information about how long the subjects had been exposed to waste water.
If the sulfide production exceeds its potential sinks, sulfide will enter the flowing waste water.
Similarly, the consumption of washing powder leads to waste water.
In addition, hydrogen sulfide can be released from the waste water, potentially resulting in a hydrogen sulfide build-up in the sewer atmosphere.
The risk is potentially higher for workers who use untreated waste water and their family members than for those who only eat uncooked crops.
The treatment plant serves approximately 22 000 person-equivalents and the waste water is without industrial inputs.
Iron-supplemented waste water was fed throughout the experiment and sulfate addition started after 5 days, as indicated by the vertical dashed line.
Apart from this effect, no other significant effects attributable to the addition of sulfate to the waste water were observed in the sequential extractions.
The speciation and subtyping of campylobacter isolates from sewage plants and waste water from a connected poultry abattoir using molecular techniques.
The potable and waste water systems of the hotel were reviewed to identify opportunities for contamination of the potable water system and deficiencies in the management of these systems.
Households therefore did not use the quantities of water that they were to do later, and human waste was mainly disposed of separately from waste water.
The reduced precipitation of zinc and copper relative to sulfur when iron was added to the waste water indicated that metal sulfides accumulated only partly as zinc and copper sulfides.
Large areas were flooded with over 5 million cubic metres of contaminated hazardous waste water from mining operations when a retaining dam burst.