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Waste water installations

In waste water installations, the components are loaded by the waste water on the inside (e.g. pipes) as well as on the outside (e.g. air-inlet pipes, scrapers). The functioning of metallic pipes is influenced by local attack (shallow pit and pitting corrosion). Uniform surface corrosion generally plays a secondary role. A site particularly susceptible to local corrosion is the area close to an electrically conducting contact of different metals (contact corrosion). [Pg.291]

Within the class of stainless steels, ferritic chromium steels as well as austenitic chromium-nickel steels, with and without additional molybdenum, can be used as passivatible materials in waste water installations. Table 4 lists the most frequently used chromium-nickel steels, which are also listed in DIN EN 1124-1 [26]. [Pg.299]

Stress corrosion cracking and corrosion fatigue are only rarely observed in waste water installations [33]. These types of corrosion are only to be expected in materials listed in Table 4 only at temperatures above 323 K (50 °C). [Pg.303]

In waste water installations, the mixed construction i.e. the installation of components made of different materials, cannot be avoided. The risk of corrosion in mixed constructions is also discussed in [37]. [Pg.304]

According to [38], thick-walled CrNiMo rolled-steel pumps are to be favoured for use as components in waste water installations over those made of plastic or grey cast iron as they are resistant to corrosion and biocorrosion. [Pg.304]

When low boiling ingredients such as ethylene glycol are used, a special provision in the form of a partial condenser is needed to return them to the reactor. Otherwise, not only is the balance of the reactants upset and the raw material cost of the resin increased, but also they become part of the pollutant in the waste water and incur additional water treatment costs. Usually, a vertical reflux condenser or a packed column is used as the partial condenser, which is installed between the reactor and the overhead total condenser, as shown in Figure 3. The temperature in the partial condenser is monitored and maintained to effect a fractionation between water, which is to pass through, and the glycol or other materials, which are to be condensed and returned to the reactor. If the fractionation is poor, and water vapor is also condensed and returned, the reaction is retarded and there is a loss of productivity. As the reaction proceeds toward completion, water evolution slows down, and most of the glycol has combined into the resin stmcture. The temperature in the partial condenser may then be raised to faciUtate the removal of water vapor. [Pg.40]

Many cities of the world do not levy a separate fee on water distributed, and even in those places where water is in shortest supply, a minimal ration may be free to everyone. The problem of wasted water and unmetered water a dding to the overall water demand is not new. In ancient Rome, fountains were coimected to the pubHc water by privately installed and owned lead pipelines, many of which were unrecorded, illegal, and hence untaxed. Frontius, the water commissioner of Emperor Nerva of Rome in AD 96, developed cmde meters to increase revenue and cut demand. [Pg.236]

Except for the sewer, all utilities could be easily piped into the area. A water heater would have to be istalled, however, since the nearest one in the building was some distance away and already used to capacity. The concrete floor would have to be broken up to accommodate the sewer. A sewage mixing tank would be installed beneath the floor with access for sampling by a waste water inspector. [Pg.144]

Recoflo An ion-exchange process based on short beds and small beads. Developed by the University of Toronto in the 1960s and commercialized by Eco-Tec, Canada. Used for waste-water recovery and removal of metals from various metallurgical waste streams. In 1988,500 units had been installed in 27 countries. [Pg.224]

The Palo Verde nuclear power station near Phoenix, Arizona, was originally intended to have 10 nuclear reactors with a generating capacity of 1,243 megawatts each. As a result of public pressure, construction at Palo Verde was stopped after three operating reactors were completed. This installation is on 4,000 acres and is cooled by waste water from the city of Phoenix, which is nearby. An area of 4,000 acres is 6.25 square miles or 2.5 miles square. The power generating facilities occupy a small part of this area. [Pg.146]

The Bayer Pigment factory at Krefeld (FRG) installed a waste water treatment plant in the 1960s, well ahead of the environmental requirements of the day. [Pg.525]

Recent examples of co-generation are given by the installation of small binary plants at Altheim and Bad Blumenau in Austria, which use the waste water for district heating and thermal bathing, respectively. References can be found in Pemecker Uhlig (2002) for Altheim, and Legmann (2003) for Bad Blumenau. [Pg.373]

There are approximately 13,000 job and captive metal finishing shops and printed board shops in the USA. Almost all of these companies have installed waste water treatment systems to comply with the Clean Water Act (CWA). As a result, these companies generate toxic metal sludges which are regulated by the Resource Conservation and Recovery Act (RCRA). Compliance with these two Federal laws, in addition to laws passed by local, county and state regulatory agencies, can require industry to spend 10 to 15% of their sales dollar on compliance. [Pg.260]

The potential cost savings to HP from installation of filtration equipment to remove GaAs solids prior to the waste water entering the HF treatment system are ... [Pg.358]

Trie previous installment in this senes, wtuch appeared In World Oil last March, inventoried waste water treating equipment installed downstream of the free water knockout. This installment adds another piece of equipment to the list—SP packs that can substitute for plate coalescers in some applications—and details how equipment is selected and sized to meet project requirements. Authors divide the design process into simple, easy-to-folow steps and demonstrate the procedure with an example problem. [Pg.176]

Figure 24. Scheme of multilamp immersion-type photochemical installation for the photocatalyzed oxidative degradation of industrial waste water [12]. A Bypass circuit. B Reactor circuit. 1 Gas-liquid mixture and injection. 2 Reservoir. 3 Pump (ceramics). 4 Water pump. 5 Heating circuit. 6 Cooling circuit, hv Medium pressure mercury lamps (Pyrex). T Thermometers. [Pg.281]

In recent years, environmental concerns over water quality have led to installation of waste water treatment plants at pulp and paper mills. The underflow from the primary clarifier has generated another solid waste disposal problem. To solve this problem, some mills are feeding clarifier sludge to hog fuel boilers. The high moisture content of the sludge in conjunction with its low Btu content creates more difficult operating conditions for the furnace. Comparative composition of TDF, coal, wood waste,... [Pg.228]

Membrane technology has been applied to various types of wastewater. The largest number of installations is probably for industrial wastewater applications, however, municipal wastewater is largest in volume treated. The emphasis of wastewater treatment by membranes in this chapter will be for municipal waste-water treatment. [Pg.365]

An aromatic compound from industrial waste water from a reactor is removed by MBSE in a HFcrossflow contactor. This installation, with a capacity of 15 m3h 1 of water, went into operation in 1998 [37, 100]. As a solvent is used the feed into the reactor, and in this way pollutant, is recycled into the process. [Pg.521]

The sediment from the conical bottoms of the settling boxes is continuously withdrawn into reservoir 17. It is partially removed as dirt and partially sent with pumps 18 and 26 to installation 27 to dehydrate. At the stage of biochemical purification the clarified waste waters from settling boxes 16 self-flow into the top channel of the clarified water of aerotank 10. The aerotank is a six-section open concrete precast reservoir with bubble and aeration systems. All sections of the aerotank function parallel to each other. Each consists of two corridors the oxidation corridor, where the process of biochemical purification takes place, and the regeneration corridor, which serves to prepare silt for purification in the oxidation corridor. [Pg.363]

Since the extreme oxidizing power of the oxyl spin centers is successfully employed in waste water treatment, an application of these intermediates seems to be self-contradictory in terms of synthetic use. However, alkoxylation of hydrocarbons is a very important technical field since it allows the installation of functionalities without using the detour via halogenations. The selective introduction of functional groups on a completely nonactivated hydrocarbon has not yet been realized by BDD technology. In contrast, the direct anodic methoxylations of activated carbons exhibiting benzylic or allylic moieties can be performed at BDD anodes. The results obtained with BDD electrodes are quite similar to those when graphite serves as anode [57]. The anodic synthesis of benzaldehyde dimethyl ketals is industrially relevant and performed on the scale of several thousand tons. A detailed study of the anodic methoxylation of 4-tert-butyltoluene (10) at BDD was performed [58]. Usually, the first methoxylation product 11 and the twofold functionalized derivative 12 are found upon electrochemical treatment (Scheme 5). [Pg.11]


See other pages where Waste water installations is mentioned: [Pg.305]    [Pg.305]    [Pg.336]    [Pg.1808]    [Pg.405]    [Pg.309]    [Pg.638]    [Pg.800]    [Pg.91]    [Pg.34]    [Pg.566]    [Pg.1156]    [Pg.1235]    [Pg.126]    [Pg.102]    [Pg.222]    [Pg.202]    [Pg.32]    [Pg.79]    [Pg.23]    [Pg.336]    [Pg.404]    [Pg.409]    [Pg.70]    [Pg.140]    [Pg.285]    [Pg.37]    [Pg.516]    [Pg.55]   
See also in sourсe #XX -- [ Pg.299 , Pg.303 , Pg.304 ]




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