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Waste systems

Based on the evidence that acceptable recycled petroleum products can be produced, there is a considerable legislative record encouraging the recycling of used oil. Starting with the Resource Conservation and Recovery Act in 1976 (20), used oil was held apart from the normal hazardous waste system because the oil was viewed as a valuable commodity. This was followed by the Used Oil Recycling Act in 1980 (33), which removed any federal requirement that lubricants containing re-refined base oil carry special labeling. [Pg.4]

Drain and waste systems AICliE, AWWA, CMA, USCG... [Pg.489]

The initiation of corrosion due to bacteria is well recognised in a number of areas, in particular in oil production, the pulp and paper industry and municipal waste systems . ... [Pg.1142]

Fowler EB, Essington EH, Polzer WL. 1981. The interactions of low-level, liquid wastes with soils 1. Behavior of radionuclides in soil-waste systems. Soil Sci 132(1) 2-12. [Pg.237]

A British Standard has been published to assist with the management of waste systems, BS EN ISO 14401 (1996). [Pg.903]

There are four types of regulated participants in the universal waste system ... [Pg.445]

The third part, called the surface water collection and removal (SWCR) system, lies above the waste system in a cap or closure above the closed facility. Its purpose is to redirect surface water coming through the cover soil from the flexible membrane in the cap to the outside perimeter of the system. The location of all three parts of the liquid management system is illustrated in Figure 26.21. [Pg.1127]

The induction periods for the reaction of sodium nitrate-bitumen mixtures (43 57 wt) heated at 195, 234 or 260°C are 44, 2 and 0.5 h, respectively. Further study of sodium nitrate/bitumenised waste systems held at these temperatures showed an initial weak exotherm around 260°C and a larger exotherm (0.96-1.21 kJ/g) accompanied by 50% wt loss around 430°C. [Pg.1778]

Radioactive substances (radionuclides) are known health hazards that emit energetic waves and/or particles that can cause both carcinogenic and noncarcinogenic health effects. Radionuclides pose unique threats to source water supplies and chemical processing, storage, or distribution systems because radiation emitted from radionuclides in chemical or industrial waste systems can affect individuals through several pathways by direct contact with, ingestion or inhalation of, or external exposure to, the contaminated waste stream. While radiation can occur naturally in some cases due to the decay of some minerals, intentional and nonintentional releases of... [Pg.202]

Pave runoff areas to rednce transfer of solids to waste systems. Use water softeners in cooling-water systems to extend the nsefnl cycling time of the water. [Pg.319]

American Waste Systems Waste oil, PCBs" 2,300 FFTNH 115,000 Total project costs... [Pg.570]

Based on information from the Eco Waste commercial pilot facility in 1995, costs for a full-scale SCWO unit were estimated to be 10 to 20 cents per gallon of waste treated (D11868N, p. 3). Detailed cost estimates are provided for the Eco Waste system (T0877), the Foster Wheeler system (T0314), and the General Atomics system (T0329). [Pg.1013]

Chemical Flash Point, °F voc Hazardous Waste Systemic Skin Irritant Toxicity Reproductive Effects... [Pg.190]

The present study was initiated in order to obtain quantitative data on the relative adsorption potentials of metal ions in the region of the z.p.c. of hydrous manganese oxide. This information is of considerable importance in a variety of practical phenomena ranging from the mechanism of trace metal inclusion in ocean-floor manganese nodules and pisolitic manganese ores to the sorption behavior of manganese precipitates in natural water and waste systems. [Pg.83]

Figure 10. Animal recycle feedlot wastes system... Figure 10. Animal recycle feedlot wastes system...
Fly ash increases the density, decreases the permeability, and increases the leaching resistance of Ordinary Portland Cement (OPC). It is a truism that The leach resistance of solidified cement-waste systems can be improved by any process which accelerates curing, limits porosity, or chemically bonds fission product or actinide elements. (Jantzen et al., 1984). Supercritical C02 treatment of a modified Portland cement is expected to further increase the density over the untreated material, so that a reduced porosity and improved leachability should result. In addition, the high silica content of fly ash, with its well-known sorbent properties toward actinides and certain other radionuclides, enhances the immobilization characteristics. [Pg.252]

The first two of these parameters require a survey of the entire laboratory by the waste system manager. For small laboratories, a brief survey, which includes discussion with the individual(s) responsible for each segment of the operation, may suffice. For large, diverse departments it may be desirable to precede the survey with a simple questionnaire. It is almost inevitable that such a survey will uncover waste problems that must be solved at the outset, (e.g., caches of... [Pg.414]

Spent resin is transferred from the column through a 10-mm-diam tube to a resin storage tank. The flush water continuously overflows the storage tank through a screen to the ORNL Intermediate Level Liquid Waste System. [Pg.156]

The sequence of process steps shown in Fig. 4 produces three batches of spent resin (a total of about 4 L) and introduces about 50 kg of LiCl into the liquid waste system. The initial product recovery steps require about two weeks of operating time, and the clean rework recovery requires another 2 weeks. [Pg.156]

The cell voltage changed between 2.7 and 2.9 V. After an operation, the same reactor treated other waste systems successfully, also on a long-term basis. The data demonstrated that the Pd cathodes can be subjected for a relatively long HDH operation. [Pg.320]

Short-circuiting is one of the major problems associated with mechanical aeration equipment. Combined mechanical- and diffused-aeration systems have enjoyed some popularity for industrial-waste systems that treat variable organic loads. The mechanical mixers provide the fluid mixing with the diffused aeration varied for different oxygen-transfer rates. [Pg.71]

Each CMP waste system will have two primary components ... [Pg.628]


See other pages where Waste systems is mentioned: [Pg.134]    [Pg.136]    [Pg.873]    [Pg.2221]    [Pg.62]    [Pg.412]    [Pg.164]    [Pg.160]    [Pg.192]    [Pg.373]    [Pg.72]    [Pg.312]    [Pg.32]    [Pg.451]    [Pg.467]    [Pg.134]    [Pg.136]    [Pg.350]    [Pg.140]    [Pg.141]    [Pg.331]    [Pg.337]    [Pg.697]    [Pg.1977]   
See also in sourсe #XX -- [ Pg.383 , Pg.384 , Pg.385 , Pg.386 , Pg.387 , Pg.388 , Pg.389 , Pg.390 ]

See also in sourсe #XX -- [ Pg.878 ]




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Acid waste systems

Aerobic waste treatment system

Agricultural systems waste management

Anaerobic-aerobic waste treatment system

Attributes of a Waste Classification System

Chemical engineering waste management systems

Classification System for Hazardous Chemical Waste Under the Resource Conservation and Recovery Act

Combustion systems waste

Combustion systems waste from

Comparison of Classification Systems for Radioactive and Hazardous Chemical Wastes

Comparison of the United States and IAEA Radioactive Waste Classification Systems

Cradle-to-grave hazardous waste management system

Establishing a Waste Classification System Based on the Framework and Risk Index

Farming system, hazardous waste

Feedstock recycling waste collection systems

GASEOUS RADIOACTIVE WASTE SYSTEM

Gasification waste heat recovery system

Hazardous waste system, existing chemical

Integrated waste management system

LIQUID RADIOACTIVE WASTE SYSTEM

Liquid waste processing system

Management systems, waste

Minimization of Waste from the Separation and Recycle System

Municipal solid waste system design

Nickel-chromium plating wastes treatment systems

Other Radioactive Waste Classification Systems

Public waste water system

Radioactive Waste Drain System

Radioactive waste treatment system

Risk, general considerations Waste classification system

SOLID RADIOACTIVE WASTE SYSTEM

Shortcomings of Current Waste Classification Systems

Solid waste management systems

Steam generating systems waste heat boilers

Summary of Existing Waste Classification Systems

The Waste Management System

The systems approach to waste management

Urban Waste and Municipal Systems

Utility systems waste heat boiler

Utility systems, waste minimization

WASTE STREAMS FROM TRANSPORTABLE TREATMENT SYSTEMS

Waste Classification System Proposed by LeMone and Jacobi

Waste classification system

Waste classification system INDEX

Waste classification system allowable dose or risk

Waste classification system applicability

Waste classification system association with disposal

Waste classification system assumptions

Waste classification system bases

Waste classification system characteristically hazardous

Waste classification system characteristics

Waste classification system deficiencies

Waste classification system description

Waste classification system disposal requirements

Waste classification system exemption

Waste classification system existing chemical

Waste classification system existing radioactive

Waste classification system general

Waste classification system implications

Waste classification system recommendations

Waste classification system subclassification

Waste classification system subclassifications

Waste classification system technologies

Waste containment systems

Waste containment systems final cover system

Waste digestion system, advanced

Waste feed systems

Waste heat system

Waste management collection systems

Waste management systems approach

Waste processing systems

Waste steam system

Waste system around

Waste treatment and control systems

Waste treatment systems

Waste water recycling system analysis

Waste water systems

Wastes system, animal recycle

Water-soil systems, hazardous waste

Zero waste system

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