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Improved Hypochlorination Techniques And Problems in Disinfection of Municipal Wastewaters Containing Refinery Thiosulfate WALTER E. GARRISON, Assistant Chief Engineer JAY G. KREMER, Head, Industrial Waste Section JOHN MURK, Operations Engineer Joint Water Pollution Control Plant The Sanitation Districts of Los Angeles County Los Angeles, California 90057 BACKGROUND The County Sanitation Districts of Los Angeles County, were formed under the authority of the California County Sanitation Districts Act of 1923. This act provided that a sanitation district was empowered to construct, operate and maintain facilities to treat and dispose of sewage and industrial wastes within boundaries determined by geographical and topographical rather than political subdivisions. The Sanitation Districts now consist of 27 individual districts which provide sewerage service to the major portion of Los Angeles County outside of the City of Los Angeles. Fifteen of these districts serve the more populous portion of the service area. These 15 districts are joined together into the joint outfall system which provides a common sewerage system for over 3,700,000 people, 750 square miles of area and approximately 25,000 industrial companies. The methods of wastewater treatment include primary, secondary and tertiary at various locations within the Districts. The largest treatment facility if the Joint Water Pollution Control Plant (J W PCP) located in the City of Carson at the south central portion of the service area, see Figure 1. The flow diagram of Figure 2 shows the processes of primary wastewater treatment and sludge digestion and disposal now used at JWPCP for about 370 MGD of wastewater. The treated wastewater is discharged into the ocean about 2 miles off the Southern California coast in about 200 feet of ocean water. During normal ocean conditions the design of the ocean diffuser system prevents any appearance of wastewater at the ocean surface. At present the Districts have five joint outfall activated sludge treatment plants totaling about 80 MGD of capacity. A committment has also been made to add secondary treatment to the JWPCP by July 1, 1977. The quality of wastewater discharged to the Pacific Ocean from the JWPCP is regulated by the State Regional Water Quality Control Board. Quality standards on treated wastewater have become more stringent in recent years. Prior to September 1970 the bacterial requirements for ocean coliform counts near the ocean outfalls were essentially those for swimming water quality, 1000 per 100 ml. In September 1970 these requirements were changed to essentially those for protection of shellfish. The coliform median most probable number (MPN) for any 6-month period at each ocean sampling station was required to not exceed 70 per 100 ml. Other statistical requirements were set for the single sample maximum coliform count and for the maximum levels in 10 and 20 percent of the samples collected. The practical significance of this requirement was to increase greatly the Districts requirement for disinfection of the JWPCP effluent. Under the swimming water standard of 1,000 coliforms per 100 ml only infrequent JWPCP effluent disinfection was required (by chlorination) when unsettled ocean conditions caused the diffused wastewater to rise to the ocean surface. During normal ocean conditions, occuring perhaps 50 weeks per year, the wastewater field remained submerged and was dispersed well below the ocean surface. Chlorination was thus required only 309
Object Description
Purdue Identification Number | ETRIWC197329 |
Title | Improved hypochlorination techniques and problems in disinfection of municipal wastewaters containing refinery thiosulfate |
Author |
Garrison, Walter E. Kremer, Jay G. Murk, John |
Date of Original | 1973 |
Conference Title | Proceedings of the 28th Industrial Waste Conference |
Conference Front Matter (copy and paste) | http://earchives.lib.purdue.edu/u?/engext,23197 |
Extent of Original | p. 309-322 |
Series | Engineering extension series no. 142 |
Collection Title | Engineering Technical Reports Collection, Purdue University |
Repository | Purdue University Libraries |
Rights Statement | Digital object copyright Purdue University. All rights reserved. |
Language | eng |
Type (DCMI) | text |
Format | JP2 |
Date Digitized | 2009-06-02 |
Capture Device | Fujitsu fi-5650C |
Capture Details | ScandAll 21 |
Resolution | 300 ppi |
Color Depth | 8 bit |
Description
Title | page 309 |
Collection Title | Engineering Technical Reports Collection, Purdue University |
Repository | Purdue University Libraries |
Rights Statement | Digital object copyright Purdue University. All rights reserved. |
Language | eng |
Type (DCMI) | text |
Format | JP2 |
Capture Device | Fujitsu fi-5650C |
Capture Details | ScandAll 21 |
Transcript | Improved Hypochlorination Techniques And Problems in Disinfection of Municipal Wastewaters Containing Refinery Thiosulfate WALTER E. GARRISON, Assistant Chief Engineer JAY G. KREMER, Head, Industrial Waste Section JOHN MURK, Operations Engineer Joint Water Pollution Control Plant The Sanitation Districts of Los Angeles County Los Angeles, California 90057 BACKGROUND The County Sanitation Districts of Los Angeles County, were formed under the authority of the California County Sanitation Districts Act of 1923. This act provided that a sanitation district was empowered to construct, operate and maintain facilities to treat and dispose of sewage and industrial wastes within boundaries determined by geographical and topographical rather than political subdivisions. The Sanitation Districts now consist of 27 individual districts which provide sewerage service to the major portion of Los Angeles County outside of the City of Los Angeles. Fifteen of these districts serve the more populous portion of the service area. These 15 districts are joined together into the joint outfall system which provides a common sewerage system for over 3,700,000 people, 750 square miles of area and approximately 25,000 industrial companies. The methods of wastewater treatment include primary, secondary and tertiary at various locations within the Districts. The largest treatment facility if the Joint Water Pollution Control Plant (J W PCP) located in the City of Carson at the south central portion of the service area, see Figure 1. The flow diagram of Figure 2 shows the processes of primary wastewater treatment and sludge digestion and disposal now used at JWPCP for about 370 MGD of wastewater. The treated wastewater is discharged into the ocean about 2 miles off the Southern California coast in about 200 feet of ocean water. During normal ocean conditions the design of the ocean diffuser system prevents any appearance of wastewater at the ocean surface. At present the Districts have five joint outfall activated sludge treatment plants totaling about 80 MGD of capacity. A committment has also been made to add secondary treatment to the JWPCP by July 1, 1977. The quality of wastewater discharged to the Pacific Ocean from the JWPCP is regulated by the State Regional Water Quality Control Board. Quality standards on treated wastewater have become more stringent in recent years. Prior to September 1970 the bacterial requirements for ocean coliform counts near the ocean outfalls were essentially those for swimming water quality, 1000 per 100 ml. In September 1970 these requirements were changed to essentially those for protection of shellfish. The coliform median most probable number (MPN) for any 6-month period at each ocean sampling station was required to not exceed 70 per 100 ml. Other statistical requirements were set for the single sample maximum coliform count and for the maximum levels in 10 and 20 percent of the samples collected. The practical significance of this requirement was to increase greatly the Districts requirement for disinfection of the JWPCP effluent. Under the swimming water standard of 1,000 coliforms per 100 ml only infrequent JWPCP effluent disinfection was required (by chlorination) when unsettled ocean conditions caused the diffused wastewater to rise to the ocean surface. During normal ocean conditions, occuring perhaps 50 weeks per year, the wastewater field remained submerged and was dispersed well below the ocean surface. Chlorination was thus required only 309 |
Resolution | 300 ppi |
Color Depth | 8 bit |
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