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Copper toxic pollutants

Refining operations have two principal wastestreams, waste electrolyte and cathode and anode washwater. Spent electrolyte is normally recycled. A bleed stream is treated to reduce copper and impurity concentration. Varying degrees of treatment are necessary because of the differences in the anode copper. Anode impurities, including nickel, arsenic, and traces of antimony and bismuth, may be present in the effluent if the spent electrolyte bleed stream is discharged. Tables 3.14 and 3.15 present classical and toxic pollutant data for raw wastewater in this subcategory. [Pg.104]

Concentrations of Toxic Pollutants Found in Primary Copper Wastewater... [Pg.105]

Concentrations of Toxic Pollutants in the Raw Wastewater of the Secondary Copper Subcategory... [Pg.107]

Many toxic pollutants were detected in the process wastewaters from metal molding and casting processes. The toxic pollutants detected most frequently in concentrations at or above 0.1 mg/L were phenolic compounds and heavy metals. The pollutants include 2,4,6-trichlorophenol, 2,4-dimethyl-phenol, phenol, 2-ethylhexyl, cadmium, chromium, copper, lead, nickel, and zinc. Each type of operation in the foundry industry can produce different types of pollutants in the wastewater stream. Also, because each subcategory operation often involves different processes, pollutant concentrations per casting metals may vary. [Pg.163]

Erickson, S.J., N. Lackie, and T.E. Maloney. 1970. A screening technique for estimating copper toxicity to estuarine phytoplankton. Jour. Water Pollut. Control Feder. 42(8), Part 2 R270-R278. [Pg.220]

Gummow, B., C.J. Botha, A.T. Basson, and S.A. Bastianello. 1991. Copper toxicity in ruminants air pollution as a possible cause. Onderstepoort Jour. Veterin. Res. 58 33-40. [Pg.221]

In addition to the conventional pollutant constituents, USEPA made a survey of the presence of the 126 toxic pollutants listed as priority pollutants in refinery operations in 1977 [5]. The survey responses indicated that 71 toxic pollutants were purchased as raw or intermediate materials 19 of these were purchased by single refineries. At least 10% of aU refineries purchase the following toxic pollutants benzene, carbon tetrachloride, 1,1,1-trichloroethane, phenol, toluene, zinc and its compounds, chromium and its compounds, copper and its compounds, and lead and its compounds. Zinc and chromium are purchased by 28% of all refineries, and lead is purchased by nearly 48% of all plants. [Pg.256]

At emulsion crumb rubber facilities, a well-operated biological treatment facility permits compliance with BPT limitations and reduces organic toxic pollutant levels. Toxic metals that may not be reduced include chromium, cadmium, copper, selenium, and mercury. Tables 16 and 17 show pollutant removal efficiencies at two emulsion cmmb plants. [Pg.569]

Harrison, W.G., Eppley, R.W. and Renger, E.H., 1977. Phytoplankton nitrogen metabolism, nitrogen budgets, and observations on copper toxicity controlled ecosystem pollution experiment. Bull. Mar. Sci., 27 44-57. [Pg.94]

Bossuyt BTA, Janssen CR. 2004. Copper toxicity to different field-collected cladoceran species intra- and inter-species sensitivity. Environ Pollut 136 145-154. [Pg.327]

Mercury and arsenic are extremely toxic heavy metal and metalloid pollutants that adversely affect file health of millions of people worldwide (/). These toxic pollutants have reached unacceptably high levels in file environment due to industrial, def e, agricultural, and municipal properties. The U.S. Department of Energy (DOE) and other government and industrial sites in the United States are heavily contaminated with mercury, arsenic, and other toxic metals such as cadmium, copper, lead, and zinc. Each of these elemental pollutants has common environmentally relevant electrochemical species that are thiol-reactive and thus relevant to the phytoremediation strategies oufiined in Figure 1. Hundreds of Superfimd sites in the United States are listed on file... [Pg.97]

Arnold, W.R., R.C. Santore, and J.S. Cotsifas. 2005. Predicting copper toxicity in estuarine and marine waters nsing the Biotic Ligand Model. Mar. Pollut. Bull. 50 1634-1640. [Pg.233]

Copper and copper compounds are regulated under Superfund, SARA 313, Clean Water Act Toxic Pollutant, California State Superfund Hazardous Substances, CAL-OSHA Director s List of Hazardous Substances, and California HWCL Hazardous Wastes. [Pg.70]

Table 13.8 identifies common pollutants in aqueous effluents. Of the metals, the most toxic are salts of the heavy metals beryllium, cadmium, chromium, copper, lead, mercury, nickel and zinc. [Pg.344]

Removability of Toxic Organic Pollutants from Wastewater in the Primary Copper Subcategory... [Pg.125]

Trace amounts of copper are essential for life. However, as with iron, excess copper is also toxic, on account of its capacity to catalyse the Fenton reaction. There are analogies and differences between these two elements successively selected by Nature as it was obliged to adapt life to the first general irreversible pollution of the earth, namely the advent of dioxygen. [Pg.322]

The sol-gel-entrapped microbial cells have shown excellent tolerance to different alcohols [99], The immobilized E. coli cells followed the Michaelis-Menten equation when quantified with the (3-glucosidase activity via the hydrolysis of 4-nitrophenyl-(3-D-galactopyranosdie [142], The sol-gel matrices doped with gelatin prevented the cell lysis, which usually occurs during the initial gelation process [143], Microorganisms are now widely used in the biosorption of different pollutants and toxicants. Bacillus sphaericus JG-A12 isolated from uranium mining water has been entrapped in aqueous silica nanosol for the accumulation of copper and uranium [144], Premkumar et al. [145] immobilized recombinant luminous bacteria into TEOS sol-gel to study the effect of sol-gel conditions on the cell response (luminescence). The entrapped and free cells showed almost the same intensity of luminescence (little lower), but the entrapped cells were more stable than the free cells (4 weeks at 4°C). This kind of stable cell could be employed in biosensors in the near future. [Pg.545]

Aziz, J.B., N.M. Akrawi, and G.A. Nassori. 1991. The effect of chronic toxicity of copper on the activity of Balbiani rings and nucleolar organizing region in the salivary gland chromosomes of Chironomus ninevah larvae. Environ. Pollut. 69 125-130. [Pg.216]

Ma, W.C. 1984. Sublethal toxic effects of copper on growth, reproduction and litter breakdown activity in the earthworm Lumbricus rubellus, with observations on the influence of temperature, and soil pH. Environ. Pollut. 33A 207-219. [Pg.225]

Table 6 presents a summary of toxic and classical pollutants detected in three common cleansing solutions ammoniacal sodium bromate, hydrochloric acid without copper complexer, and hydrochloric acid with copper complexer. [Pg.608]


See other pages where Copper toxic pollutants is mentioned: [Pg.104]    [Pg.921]    [Pg.926]    [Pg.945]    [Pg.133]    [Pg.287]    [Pg.133]    [Pg.28]    [Pg.243]    [Pg.202]    [Pg.166]    [Pg.376]    [Pg.49]    [Pg.422]    [Pg.1322]    [Pg.284]    [Pg.285]    [Pg.324]    [Pg.272]    [Pg.582]    [Pg.200]    [Pg.227]    [Pg.8]    [Pg.605]    [Pg.29]   
See also in sourсe #XX -- [ Pg.105 ]




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