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Biocides toxicity

Slimicide and biocide toxic pollutants containing pentachlorophenol are used at mills in the pulp, paper, and paperboard industry. Initially, pentachlorophenol was used as a replacement for heavy metal salts, particularly mercuric types. Trichlorophenols are also used because of their availability as a byproduct from the manufacture of certain herbicides. Formulations containing organo-bromides and organo-sulfur compounds are also being used. Substitution of alternative slimicide and biocide formulations can lead to the virtual elimination of pentachlorophenol and trichlorophenol from these sources. [Pg.892]

Selective toxicity. If toxic compounds are to be used for controlling diseases, pests, and parasites, it is important to develop selective biocides, toxic to the target organism but less toxic to other organisms, particularly humans. [Pg.172]

Tra-Cide [Nalco], TM for testing service. Use To determine biocide toxicity and microbiological activity in industrial process waters. [Pg.1256]

Jensen J (1999) Terrestrial Hazard Classification of Toxic Substances A Study to Evaluate Specific Terrestrial Hazard Criteria Using Pesticide and Biocide Toxicity Data, ECBI/19/99 Add. 7. National Environment Research Institute, Silkeborg, Denmark EOOTPRINT (2008) The FOOTPRINT PESTICIDE PROPERTIES DATABASE, http //www.eu-footprint.org/ppdb.html. Accessed 17 Jan 2008 Belfroid AC, Van Drunen M, Beek MA, Schrap SM, Van Gestel CAM, Van Hattum B (1998) Sci Total Environ 222 167... [Pg.204]

Stewart, M.E., W.J. Blogoslawski, R.Y. Hsu, and G.R. Helz. 1979. By-products of oxidative biocides toxicity to oyster larvae. Marine Pollution Bulletin 10 166-169. [Pg.41]

Prior to the 1990s phenyhnercuric acetate was the primary bactericide and fungicide in latex and waterborne paints. Because of the increasing concerns of mercury toxicity and the potential for high consumer and occupational exposures to mercury when present in paints, the U.S. Environmental Protection Agency (EPA) induced U.S. manufacturers of PMA and other mercury compounds to withdraw their registrations for use of these substances as biocides in paints (see AIercury). Mercury compounds are used only for very limited, specific purposes, such as the use of phenyhnercuric mXx.2LX.e[55-68-5] as a bactericide in cosmetic eye preparations (see Cosmetics). [Pg.114]

Table 3. Coastal Water Quality Criteria for Toxic Substances Other Than Biocides ... Table 3. Coastal Water Quality Criteria for Toxic Substances Other Than Biocides ...
Although phosphine [7803-51-2] was discovered over 200 years ago ia 1783 by the French chemist Gingembre, derivatives of this toxic and pyrophoric gas were not manufactured on an industrial scale until the mid- to late 1970s. Commercial production was only possible after the development of practical, economic processes for phosphine manufacture which were patented in 1961 (1) and 1962 (2). This article describes both of these processes briefly but more focus is given to the preparation of a number of novel phosphine derivatives used in a wide variety of important commercial appHcations, for example, as flame retardants (qv), flotation collectors, biocides, solvent extraction reagents, phase-transfer catalysts, and uv photoinitiators. [Pg.317]

Quaternary ammonium compounds biocidal activity mechanism, 1, 401 toxicity, 1, 124 Quaternization heterocyclic compounds reviews, 1, 73 ( )-Quebrach amine synthesis, 1, 490 Queen substance synthesis, 1, 439 4, 777 Quercetin occurrence, 3, 878 pentamethyl ether photolysis, 3, 696 photooxidation, 3, 695 Quercetrin hydrolysis, 3, 878 Quinacetol sulfate as fungicide, 2, 514 Quinacridone, 2,9-dimethyl-, 1, 336 Quinacridone pigments, 1, 335-336 Quinacrine... [Pg.826]

TL50). The concentration of a toxicant, such as a biocide, in which 50% of test animals (typically fish species) survive for 96 hours under prescribed conditions. [Pg.760]

Mechanistic studies have shown that TBT and certain other forms of trialkyltin have two distinct modes of toxic action in vertebrates. On the one hand they act as inhibitors of oxidative phosphorylation in mitochondria (Aldridge and Street 1964). Inhibition is associated with repression of ATP synthesis, disturbance of ion transport across the mitochondrial membrane, and swelling of the membrane. Oxidative phosphorylation is a vital process in animals and plants, and so trialkyltin compounds act as wide-ranging biocides. Another mode of action involves the inhibition of forms of cytochrome P450, which was referred to earlier in connection with metabolism. This has been demonstrated in mammals, aquatic invertebrates and fish (Morcillo et al. 2004, Oberdorster 2002). TBTO has been shown to inhibit P450 activity in cells from various tissues of mammals, including liver, kidney, and small intestine mucosa, both in vivo and in vitro (Rosenberg and Drummond 1983, Environmental Health Criteria 116). [Pg.174]

Chemical treatments for bacteria control represent significant cost and environmental liability. Because the regulatory pressure on the use of toxic biocides is increasing, more environmentally acceptable control measures are being developed. [Pg.70]

Physical methods for the control of microbial biofilms, although often effective, are in many situations impractical. In this context it is notable that an almost universal feature of the biofilm mode of growth is their profound resistance to antibacterial compounds. Conventional chemical control methods, developed for use against fastgrowing planktonic cultures are only poorly effective against biofilm bacteria. Large doses of biocide or antibiotics, which are either environmentally undesirable or above toxic thresholds respectively, are required to eradicate biofilms in industry and medicine. [Pg.42]

Biocides are by their nature intrinsically toxic, in this respect any adventitious release to the environment requires an assessment of the relative risk posed. The 5th Environmental Action Plan of the EU is committed to a substantial reduction in the use of biocides. In particular, the Biocidal Products Directive (98/08/EC) is concerned with controlling biocidal products in the market place. Compliance with this directive is required from all member states by 14th May 2000. In this context, a strategy to control the release of biocides is timely, if continued protection is to be afforded to industry and consumer alike. One approach to controlling the release of biocide is to encapsulate in an inert inorganic framework, prior to incorporation in the coating.1... [Pg.84]

Secondly, customers are applying ever greater pressures on formulators to make less use of some chemistries, for example formaldehyde release biocides. Customers would prefer preservatives that are good for die environment and possess no adverse mammalian toxicity characteristics. This would require that new actives are developed. This is unlikely considering the new regulatory frameworks. [Pg.118]

PHMB is very toxic to fish and aquatic life. It is moreover irritating to skin and may cause sensitization by skin contact. It can cause irritation to the eyes, nose and respiratory tract. The PHMB is not compatible with most common swimming pool chemicals. Not compatible with chlorine and chlorinated chemicals and bromine donors. Not compatible with ionic sterilizers, copper based QAC-algicides, anionic detergents, water softening chemicals, persulfate oxidants etc. The defence of the inventors of PHMB is that one should not combine it with other biocides because it should be a bactericide/algicide. But the algicidal properties of PHMB are very weak in brochures and manuals the dose is 200 ppm. [Pg.135]

Best available technology economically achievable (BAT) guidelines for the control of nonconventional and toxic pollutants (trichlorophenol and pentachlorophenol, which are chemicals used as biocides)... [Pg.884]

In general, plant-protection products are biocidal active substances and are therefore by nature toxic to target organisms. At least some of them are also toxic to humans therefore, the safe use of plant-protection products presupposes, among other things, an evaluation of worker exposure during re-entry, an adequate risk assessment on the basis of the various practical scenarios in agriculture and horticulture, and, if necessary, specific instructions for worker protection on the product label. [Pg.108]


See other pages where Biocides toxicity is mentioned: [Pg.173]    [Pg.564]    [Pg.296]    [Pg.173]    [Pg.564]    [Pg.296]    [Pg.290]    [Pg.540]    [Pg.228]    [Pg.245]    [Pg.473]    [Pg.473]    [Pg.71]    [Pg.531]    [Pg.135]    [Pg.2421]    [Pg.89]    [Pg.480]    [Pg.400]    [Pg.357]    [Pg.4]    [Pg.60]    [Pg.173]    [Pg.247]    [Pg.257]    [Pg.593]    [Pg.49]    [Pg.776]    [Pg.96]    [Pg.13]    [Pg.209]    [Pg.214]    [Pg.278]   
See also in sourсe #XX -- [ Pg.119 ]




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