In may 1991, the plant was commission, with member tanneries being gradually connected to the conveyance main of CETP system and has been in operation since such time. It was later, officially inaugurated by the then Chief Minister of Tamil Nadu, Dr. J.Jayalalitha on the 10th September 1994
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This CETP caters to the wastewater needs of a cluster of 110 tanneries. It is designed to accommodate 290 cubic meters of saline wastes and 2, 832 cubic meters of composite effluents.
The design of the CETP envisage the segregation of tannery wastewaters into two streams-saline wastewater that would be charged in impervious pans and solar evaporated and the composite effluent would undergo a physicals, chemical and biological treatment for the reduction of organic pollution loads in the waste stream.
The segregated wastewaters in the tanneries are carried, by gravity, through underground sever and flow into two pumping stations from whence it is pumped to the site of the Common Effluent Treatment Plant. Where the topography does not permit the flow of wastewater by gravity, tow lift stations are located at vantage points from where they are pumped through a pressure line to the main pumping stations.
In the site, the saline wastewaters are directly charged into impervious pans and allowed to solar evaporate. This CETP has a central solar evaporation facility and has the largest pan area available in the country pertaining to such an application in the leather industry. The total pan area measures about 65, 000 square meters eveuaivalent to nearly 7,00,000 square feet!
The composite effluents are collected in an equalization tank and as the name suggests, the wastewater are thoroughly-mixed and equalized. Equalization is essential as biological treatment systems cannot absorb the swinging chocks of alkalinity and acidity. The effluent is now pumped throu screen chambers that removes coarse particles like hair, fleshings, scraps of skin and other waste. Before the passage through the screens, the volume of waste waster is measured by means of an electromagnetic flow meter and logged onto the computer designed with a specific program to handle this data. The computer provides the operator instantaneous as well as cumulative readings for the day that has transpired.
The wastewater now moves on to the stage where chemical treatment is effected by adding such chemicals that promote the coagulation of suspended solids, thereby aggregating and settling to the bottom of the primary clarifier from where it is under-drawn as primary sludge. This primary sludge is pumped into sludge-drying beds and dried using freely available solar heat.
The supernatant from the primary clarifier flows to the anaerobic lagoon that is designed with a retention time of 10 days and a BOD-reduction efficiency of about 60-65%. The organic waste having been digested to the extent of efficiency of the anaerobic lagoon, now flows into an aerobic lagoon with designed retention time of 5 days equivalent to the total inflow into the CETP. Four fixed surface aerators with a power of 200 HP provide the aerobic bacteria its oxygen requirements. As this aerobic lagoon works in conjunction with the anaerobic lagoon, it is inevitable that sizeable levels of regenerated sulfides flow into the former. Hence, two floating aerators of 15 hp capacity each are placed in the aerobic lagoon and at points that would oxidizes the sulphides into sulphates. It should be noted that the major degradation of organic waste present in tannery wastewater have been cleaned-up at this stage. The aerobic bacteria present in the second aerobic lagoon safely and completely digest that quantum of organic load that has escaped these two lagoons. The chance of organic loads escaping further is very minimal unless there is a major operation and maintenance hitch or failure.
The nearly-clean water flows into the final clarifier where the mixed-liquor suspended solids settle at the bottom and are periodically drawn into the recirculation sump and recycled back into the aerobic lagoons. The treated water flows through an underground pipeline into the branch of the River Palar almost about 500 meters away from the CETP site.
The CETP has an analytical laboratory staffed by competent chemistry graduates and post-graduates. Samples are drawn, and composited, at key points down the treatment system and results are analyzed on daily basis. The results of these findings are graphically represented in a computer program and is available for display and scrutiny and is also used a diagnostic tool.
The treatment effected in this CETP has been meeting standards set by the Tamil Nadu Pollution Control Board, except the case of TDS, Chlorides and sulphates.