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Sewage treatment

Many treatments consist broadly of three steps The first step involves the ranoval of large solid particles by settling or filtration. The ranaining effluent usually contains fine solids, organic waste and dissolved mineral salts. In settling ponds natural bioprocesses may result in limited removal [Pg.39]

In the second step, the organic waste is decomposed by air and/or bacterial action to produce a sludge. This sewage sludge may contain up to about one-third of the original P in the form of [Pg.39]

In the third step, the rest of the phosphate is removed from the ranaining liquor by treatment with lime to precipitate hydroxyapatite. Further filtration through carbon beds can succeed in ronoving up to 98% of the phosphate originally present. [Pg.39]

Effluents from sewage plants in Sweden and Switzerland are treated with soluble aluminium or iron salts to precipitate insoluble aluminium or iron phosphates. Alum, Al2(S04)3 I4H2O is much favoured as an additive to precipitate AIPO4. Over 90% of the phosphate can be removed by treatment with FeClj, but this may lead to sludge problems. Up to 99.9% of phosphate can be removed from sewage sludge by absorption on to activated alumina. [Pg.39]

The comparatively high nitrogen and phosphorus contents of some sewage sludges render them suitable for fertilisers (Chapter 12.2). Fly-ash from municipal incinerators can have a P content of 0.5-1.0 wt% [61,73] (Table 2.14). [Pg.39]

Sewage treatment plants are very efficient at removing lead and other heavy metals from raw sewage. They thus act as effective controls on lead discharges not only within domestic sewage but also from industrial sources and urban stormwater runoff, both of which are frequently directed to sewage treatment plants. [Pg.125]

Sewage treatment plants thus prove an effective means of reducing lead discharges to surface waters. Care must be taken, however, to avoid poisoning of the biological treatment by limiting the heavy metal input to the plant (Section 6.2.4). [Pg.125]

Commercial quick- and hydrated limes are suitable for the treatment of waste water. In some situations, due consideration will need to be given to the permissible levels of trace elements in the lime, in the context of consent levels for discharges to water courses. [Pg.329]

Sewage consists of domestic and trade effluent. It contains suspended solids, dissolved colloidal organic matter and nutrients (phosphate and ammonia). It may also contain heavy metals, particularly from trade effluents. [Pg.329]

Lime products have been used extensively in the treatment of sewage for over one hundred years. Its roles have included  [Pg.329]

Although sewage treatment processes vary widely in terms of the equipment, treatments and sequence of unit operations, most fit into one of six categories [28.2]. Only one of these uses substantial quantities of lime [28.11]. [Pg.329]

In this process (Fig. 28.3), milk of lime is used in conjunction with a coagulating agent (e.g. ferric chloride) to coagulate and flocculate the suspended and colloidal solids. The suspension is then fed to a clarifier. [Pg.330]

Methanol is used in the point souree tertiary sewage treatment facility as an oxidizable or nic substrate to provide energy to the bacteria used in the biologieal nitrification-denitrifieation process. This process is often the best process available for the removal of nitrogen for the following reasons (1) hi potential removal effieiency, (2) hi process stability and reliability, (3) relatively [Pg.266]

Component Methanol SCP Fishmeal Soybean meal NFDM [Pg.267]

The reaction of nitrogen compounds in the denitrification process proceeds as follows [29, 33] [Pg.268]

Convert nitrite ion to nitrogen gas and remove it from the effluent  [Pg.268]

Methanol is also used as an energy source for bacterial growth, which requires about 30% of the stoichiometric amount en in these equations. Adding this consideration, the total amount of methanol required can be estimated from the equation [29, 32, 34] [Pg.268]

Hoffmann developed an ingenious fiber optic device that can bring light into otherwise inaccessible (e.g., underground) bodies of polluted water and photolyze organic contaminants on a Ti02 coating on the surface of the quartz optical fibers. [Pg.277]

The processing of sewage is mainly microbiological, and the details lie outside the scope of this book. In outline, there are three levels to which sewage may be treated. [Pg.277]

In principle, the dewatered sludge is a valuable fertilizer, but it usually contains too many heavy metal ions to be safe for use in growing foodstuffs (it is often used to fertilize golf courses and the like). Methane is a by-product of sewage treatment that can be used [Pg.277]

Alternatively, addition of alum precipitates AIPO4, while FeCls brings down FeP04. Another possibility is to rely on bacteria to consume the excess phosphate and any ammonia in the treated sewage. [Pg.278]


Sewage gases Sewage methane Sewage treatment... [Pg.881]

Most aquaculture faciUties release water constandy or periodically into the environment without passing it through a municipal sewage treatment plant. The effects of those efduents on natural systems have become a subject of intense scmtiny in recent years and have, in some instances, resulted in opposition to further development of aquaculture faciUties in some locales. There have even been demands that some existing operations should be shut down. [Pg.20]

Flotation or froth flotation is a physicochemical property-based separation process. It is widely utilised in the area of mineral processing also known as ore dressing and mineral beneftciation for mineral concentration. In addition to the mining and metallurgical industries, flotation also finds appHcations in sewage treatment, water purification, bitumen recovery from tar sands, and coal desulfurization. Nearly one biUion tons of ore are treated by this process aimuaHy in the world. Phosphate rock, precious metals, lead, zinc, copper, molybdenum, and tin-containing ores as well as coal are treated routinely by this process some flotation plants treat 200,000 tons of ore per day (see Mineral recovery and processing). Various aspects of flotation theory and practice have been treated in books and reviews (1 9). [Pg.40]

Substances other than enzymes can be immobilized. Examples include the fixing of heparin on polytetrafluoroethylene with the aid of PEI (424), the controUed release of pesticides which are bound to PEI (425), and the inhibition of herbicide suspensions by addition of PEI (426). The uptake of anionic dyes by fabric or paper is improved if the paper is first catonized with PEI (427). In addition, PEI is able to absorb odorizing substances such as fatty acids and aldehydes. Because of its high molecular weight, PEI can be used in cosmetics and body care products, as weU as in industrial elimination of odors, such as the improvement of ambient air quaHty in sewage treatment plants (428). [Pg.13]

Other appHcations of firefly hioluminescence include measurement of the activity of bacteria in secondary sewage treatment activated sludge (296,297), detection of bacteria in clean rooms and operating rooms, measurement of bacteria in bottled foods, beverages (298), and pharmaceuticals (299), determination of the antimicrobial activity of potential dmgs (300), determination of the viabiHty of seeds (301), and measuring marine biomass concentrations as a function of ocean depth or geographical location (302). [Pg.275]

There are two reasons why the concentration of quaternaries is beheved to remain at a low level in sewage treatment systems. First, quaternaries appear to bind anionic compounds and thus are effectively removed from wastewater by producing stable, lower toxicity compounds (205). Anionic compounds are present in sewer systems at significantly higher concentrations than are cations (202). Second, the nature of how most quaternaries are used ensures that their concentrations in wastewater treatment systems are always relatively low but steady. Consumer products such as fabric softeners, hair conditioners, and disinfectants contain only a small amount of quaternary compounds. This material is then diluted with large volumes of water during use. [Pg.379]

Membrane-retained components are collectively called concentrate or retentate. Materials permeating the membrane are called filtrate, ultrafiltrate, or permeate. It is the objective of ultrafiltration to recover or concentrate particular species in the retentate (eg, latex concentration, pigment recovery, protein recovery from cheese and casein wheys, and concentration of proteins for biopharmaceuticals) or to produce a purified permeate (eg, sewage treatment, production of sterile water or antibiotics, etc). Diafiltration is a specific ultrafiltration process in which the retentate is further purified or the permeable sohds are extracted further by the addition of water or, in the case of proteins, buffer to the retentate. [Pg.293]

Saline Water for Municipal Distribution. Only a very small amount of potable water is actually taken by people or animals internally, and it is quite uneconomical to desalinate all municipally piped water, although all distributed water must be clear and free of harmful bacteria. Most of the water piped to cities and industry is used for Htfle more than to carry off small amounts of waste materials or waste heat. In many locations, seawater can be used for most of this service. If chlorination is requited, it can be accompHshed by direct electrolysis of the dissolved salt (21). Arrayed against the obvious advantage of economy, there are several disadvantages use of seawater requites different detergents sewage treatment plants must be modified the usual metal pipes, pumps, condensers, coolers, meters, and other equipment corrode more readily chlorination could cause environmental poUution and dual water systems must be built and maintained. [Pg.237]

Modifications have been developed in response to specific operating needs. The basis of biological treatment is the formation of an environment in which the microorganisms can thrive under controlled conditions (14). The microorganisms originate in the sewage. A suitable environment is rich in food and maintained in an aerobic state. It has been said that a sewage-treatment plant is a river in miniature (14). [Pg.283]

K. Imhoff and G. Fair, Sewage Treatments 2nd ed., John Wiley Sons, Inc., New York, 1956. [Pg.289]

Other Uses. The quantity of coal used for purposes other than combustion or processing is quite small (2,6). Coal, especially anthracite, has estabHshed markets for use as purifying and filtering agents in either the natural form or converted to activated carbon (see Carbon). The latter can be prepared from bituminous coal or coke, and is used in sewage treatment, water purification, respirator absorbers, solvent recovery, and in the food industry. Some of these markets are quite profitable and new uses are continually being sought for this material. [Pg.237]

The effluent from the isolation wash belt is the principal wastewater stream from the polymerization process. It contains highly diluted acetic acid and a surfactant that is not biodegradable. The wastewater streams are sent to sewage treatment plants where BOD is reduced to acceptable levels. Alternative biodegradable surfactants have been reported in the Hterature (173). [Pg.549]

Secondary Emissions from Basic Oxygen Process Steelmaking Facilities for Which Construction Commenced after January 20, 1983 Sewage Treatment Plants Primary Copper Smelters Primary Zinc Smelters... [Pg.2156]

Effluents of oil refineries, textile mills, power stations, pulp mills, sewage treatment works, vegetable oil factories... [Pg.45]


See other pages where Sewage treatment is mentioned: [Pg.356]    [Pg.425]    [Pg.233]    [Pg.312]    [Pg.136]    [Pg.508]    [Pg.397]    [Pg.54]    [Pg.5]    [Pg.438]    [Pg.175]    [Pg.178]    [Pg.117]    [Pg.119]    [Pg.391]    [Pg.345]    [Pg.459]    [Pg.474]    [Pg.475]    [Pg.99]    [Pg.99]    [Pg.148]    [Pg.172]    [Pg.316]    [Pg.303]    [Pg.203]    [Pg.237]    [Pg.237]    [Pg.282]    [Pg.283]    [Pg.535]    [Pg.450]    [Pg.237]    [Pg.540]    [Pg.122]    [Pg.2046]    [Pg.2047]   
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Aerobic sewage treatment

Bacteria sewage treatment

Biodegradability Sewage treatment plants

Biological sewage treatment plant

Biological treatment, sewage

Carbon dioxide sewage treatment

Control sewage treatment

MBR sewage and wastewater treatment

Membrane sewage treatment

Microorganisms and sewage treatment

Municipal sewage treatment

Municipal sewage treatment, schematic

Municipal sewage-treatment/effluent disposal

Oxygen sewage treatment

Polycylic aromatic musk compounds in sewage treatment plant effluents of Canada and Sweden

Primary sewage treatment

Residence Times and Sewage Treatment

Screens, sewage treatment

Secondary sewage treatment

Sedimentation sewage treatment

Sewage

Sewage discharges wastewater treatment

Sewage effluents treatment

Sewage sludge advanced treatment

Sewage sludge digestion treatment

Sewage sludge, treatment

Sewage treatment plant models

Sewage treatment plant water

Sewage treatment plants

Sewage treatment plants pollution control

Sewage treatment plants pollution source

Sewage treatment works

Sewage wastewater treatment

Sewage, Liquid Effluent and Water Treatment

Sludges from sewage treatment

Standard sewage treatment

Tertiary sewage treatment

Treatment of Sewage Sludge

Treatment, drinking water sewage effluent

Ultrafiltration sewage treatment

Waste water/sewage treatment

Waste water/sewage treatment products

Wastewater municipal sewage treatment

Water and Sewage Treatment

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