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Toxicity evaluations

chronic and other toxicity tests for clacyfos were carried out according to the standard operational procedures of pesticidal registration. The toxicity evaluation was performed by National Pesticide Engineering Research Center (Shenyang) in Chain. Test results suggested that clacyfos has low acute toxicity against rats and non-harmfiil to other tested animals. [Pg.377]

This procedure includes oral toxicity, dermal toxicity, inhalation toxicity, eye irritation, and dermal sensitization. The acute oral and acute dermal toxicity tests were performed in rates to determine the LD50. The evaluation showed that both technical grade of clacyfos and 30 % clacyfos EC had low acute toxicity against rats. Neither significant eye irritation nor negative dermal sensitization of rabbit was observed. [Pg.377]

Detailed information of the acute toxicity is listed in Tables 8.18 and 8.19. [Pg.377]

Two-generation-reproduction (rat) No effect on development or reproduction observed [Pg.378]

Chronic Ames, chromosome aberration of spermatocytes, and micronucleus tests were performed in rat. All tests results were negative. [Pg.378]


Kannan, K., Tanabe, S., and Borrell, A. et al. (1993). Isomer specific analysis and toxic evaluation of PCBs in striped dolphins affected by an epizootic in the western Mediterranean sea. Archives Environmental Contamination and Toxicology 25, 227-233. [Pg.355]

Kinkead ER, Wolfe RE, Bunger SK, et al. 1992b. The acute toxicity evaluation of a low-temperature hydraulic fluid. J Am Ind Hyg Assoc 53 163-168. [Pg.343]

Current guidelines for toxicity evaluation of ophthalmic formulations involve both single and multiple applications, dependent on the proposed clinical use [39]. The multiple applications may extend over a 9-month period and incorporate evaluations of ocular irritation and toxicity, systemic toxicity, and determinations of systemic exposure (toxicokinetics). In many cases the systemic exposure from an ocular route is less than by parenteral administration, information that will assist in determining whether additional studies may be needed to establish systemic safety of the ophthalmic preparation. U.S. and international guidance documents are available [71,72], and regulations and tests have been summarized for ophthalmic preparations [39,73,74],... [Pg.427]

Davoren, M. et al. (2007) In vitro toxicity evaluation of single walled carbon nanotubes on human A549 lung cells. Toxicology in Vitro, 21 (3), 438-448. [Pg.211]

Todd MD et al. Emerging technologies for accelerated toxicity evaluation of potential dmg candidates. Curr Opin Dmg Discovery Dev 1999 2 58-68. [Pg.125]

Chronic toxicity evaluation of wastewater and treatment-plant effluents a 170 comparison between BL bacterial, invertebrate, and fish assays General or basic studies... [Pg.264]

IRDC (International Research and Development Corporation). 1985. LC50 Acute Inhalation Toxicity Evaluation in Rats [with cover letter to the Office of Pollution Prevention and Toxics, dated Feb. 21, 1992], Report Nos. 533-001, 533-002, 533- 003. Basking Ridge, NJ. AT T Bell Laboratories. [Pg.116]

Eisler, R. 1977. Toxicity evaluation of a complex metal mixture to the softshell clam Mya arenaria. Mar. Biol. 43 265-276. [Pg.329]

Schreiner, C., et al., Toxicity evaluation of petroleum blending streams Reproductive and developmental effects of hydmdesulfuri/.cd kerosene,./. Toxicol. Environ. Health, 52,211, 1997. [Pg.237]

Most commonly, bioassays for the evaluation of the acute toxic effects of pesticides are based on single aquatic species selected to be representative of a range of taxonomic and functional groups, i.e., bacteria, algae, invertebrates or fish [ 53,54]. Generally, toxicity evaluation using a single species is the alternative of choice rather than the use of multiple species, because extrapolation of effects to an ecosystem is more difficult and can often lead to incorrect conclusions. [Pg.66]

On-line or on-site toxicity evaluation is a great challenge due to the complexity of measuring the different impacts (from trouble from to death of organisms) of several substances, the effect of which is often increased by synergy. Furthermore for wastewater, toxicity monitoring must be implemented in several locations raw sewer, treatment plant or discharge point. Toxicity can be eval-... [Pg.262]

Tanimura, T. (1990). The Japanese perspectives on the reproductive and developmental toxicity evaluation of pharmaceuticals. J. Am. Coll. Toxicol. 9 27-38. [Pg.295]

Farland, W.H., Tyson, C.A. and Sawhney, D.S. (1985). Rationale and use of functions tests in toxicity testing a review. In Organ Function Tests in Toxicity Evaluation (Tyson, C.A. and Sawhney, D.S., Eds.). Noyes Publications, Park Ridge, NJ, pp. 1-22. [Pg.679]

Lewis TR, Anger WK, Te Vault RK. 1984. Toxicity evaluation of sub-chronic exposures to cyanogen in monkeys and rats. J Environ Pathol Toxicol Oncol 5 151-163. [Pg.258]

Nematollahi J, Guess WL, Autian J. 1967. Plasticizers in medical application I. Analysis and toxicity evaluation of dialkyl benzenedicarboxylates. J Pharmacol Sci 56 1446-1453. [Pg.123]

HTS facilitates early elimination of unsuitable compounds [35] and became indispensable in all stages of drug discovery, from target identification to toxicity evaluation. [Pg.60]

Sabaliunas, D. Ellington, J. Sabaliuniene, I. 1999, Screening bioavailable hydrophobic toxicants in surface waters with semipermeable membrane devices Role of inherent oleic acid in toxicity evaluations. Ecotox. Environ. Safe. 44 160-167. [Pg.138]


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Bioavailable toxicity identification evaluation

Evaluation of Toxicity

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Toxicity Identification Evaluation (TIE) Methods

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