Oryzias

Medaka Oryzias iatipes) MBTC 48-h LC50 38 38 Nagase et al. (1991)... 

Medaka (Oryzias latipes) DBTC 28-day NOEC (mortality, growth, and behaviour) 1.8 1.8 Wester Canton (1987)... 

Nagase H, Hamasaki T, Sato T, Kito H, Yoshioka Y, Ose Y (1991) Structure-activity relationships for organotin compounds on the red killifish Oryzias latipes. Applied Organometallic Chemistry, 5(2) 91-97. 

Metcalfe, T.L., Metcalfe, C.D., Kiparissis, Y. et al. (2000). Gonadal development and endocrine responses in Japanese medaka (Oryzias latipes) exposed to o,p -T)DT in water or through maternal transfer. Environmental Toxicology and Chemistry 19, 1893-1900. 

Yokota, H., Seki, M., and Maeda, M. et al. (2001). Life-cycle toxicity of 4-nonylphenol to medaka (Oryzias latipes). Environmental Toxicology and Chemistry 20, 2552-2560. 

Medaka, Oryzias latipes 949 vs. 455 White sucker, Catostomus commersoni ... 

Allinson, G., M. Ueoka, and M. Morita. 1994. Effect of dietary 1,3,6,8-tetrachlorodibenzo-p-dioxin on the Japanese freshwater fish Oryzias latipes (medaka) and aquatic snail Indoplanorbis exustus (indohira-makigai). Chemosphere 28 1369-1383. 

Schmeider, P., D. Lothenbach, J. Tietge, R. Erickson, and R. Johnson. 1995. [3H]-2,3,7,8-TCDD uptake and elimination kinetics of medaka (Oryzias latipes). Environ. Toxicol. Chem. 14 1735-1743. 

Shortfin molly, Poecilia mexicana Medaka, Oryzias latipes 12 LC50 (24 h) 5... 

Oryzias latipes 20-100 Freshwater-adapted fish had BCF of 1680 (vs. 370 for saltwater-adapted group) after 10 days 66... 

Tachikawa, M. and R. Sawamura. 1994. The effects of salinity on pentachlorophenol accumulation and elimination by killifish (Oryzias latipes). Arch. Environ. Contam. Toxicol. 26 304-308. 

MEDAKA, Oryzias latipes Exposed to approximately 5, 40, or 200 pg BaP/L for 6 h, once weekly, for up to 4 weeks 6-10-day-old fish Liver neoplasms at intermediate and high 26 concentration exposures... 

Radiation causes dominant lethal mutations in the medaka (Oryzias latipes) (Shima and Shimada 1991). Mosquitofish (Gambusia spp.) from radionuclide-contaminated ponds in South Carolina differed from conspecifics in reference ponds, as judged by the frequency of DNA markers, and this is consistent with the hypothesis that these DNA markers may originate from genetic elements that provide a selective advantage in contaminated habitats (Theodorakis et al. 1998). Ionizing radiation at low-level chronic exposure reportedly has no deleterious genetic effects on aquatic populations because exposure is compensated by density-dependent responses in fecundity (IAEA 1976). However, this needs verification. 

Medaka, Oryzias latipes adult males receiving single acute exposure of 0.64, 4.75, or 9.5 Gy Dose-dependent increase in total mutations in sperm, spermatids, and spermatogonia 16... 

Shima, A. and A. Shimada. 1991. Development of a possible nonmammalian test system for radiation-induced germ-cell mutagenesis using a fish, the Japanese medaka (Oryzias latipes). Proc. Natl. Acad. Sci. U.S.A. 88 2545-2549. 

Carlson, E.A., Li, Y., and Zelikoff, J.T., Exposure of Japanese medaka (Oryzias latipes) to benzo[a]pyrene suppresses immune function and host resistance against bacterial challenge, Aquat. Toxicol., 56, 289, 2002. 

Oncorhynchus mykiss [16,22—25,29], Lepomis macrochirus [28,31,66, 67], and Cyprinus carpio [19,30,34,60] being the species most frequently studied others include Salmo salar [26,41], Proterorhinus marmoratus [65], Carassius auratus [12] and Oryzias latipes [15]. 

In a series of studies on 2-amino-A-phenylthiazole (Piscaine), a fish anesthetic, Suzuki and co-workers (24) isolated and identified an N-glucuronide metabolite (2-amino-A-phenylthiazole-2-N-g-mono-D-glucopyranosiduronic acid) from medaka (Oryzias latipes), rainbow trout, and carp (Cyprinus oarpio) (Figure l). 

Rice PJ, Drewes CD, Klubertanz TM, et al. 1997. Acute toxicity and behavioral effects of chlorpyrifos, permethrin, phenol, strychnine, and 2,4-dinitrophenol to 30-day-old Japanese Medaka (Oryzias latipes). Environ Toxicol Chem 16 696-704. 

Phycotoxins accumulate in fish and shellfish because of the natural feeding habits of the respective organisms, rather than because of food handling or processing practices. The toxins causing the diseases discussed in this chapter are heat stable (Australia New Zealand Food Authority, 2001 Committee on Evaluation of the Safety of Fishery Products, 1991). Complete inactivation of saxitoxin (associated with PSP) requires at least ten minutes of exposure to 260°C dry heat. Brevetoxins (associated with NSP) were inactivated (i.e., to levels below the limit of assay detection using Japanese medaka [Oryzias latipes]) by exposure to 500°C heat for 10 to 15 minutes (Poli, 1988). Complete inactivation required 10 minutes exposure to 2760°C dry heat (Wannamacher, 2000). 

LC50 (48-h static or semi-static conditions) for Hyale plumulosa 310 mg/L in seawater, red killifish Oryzias latipes) 350 and 94 mg/L in seawater and freshwater, respectively (Onitsuka et al, 1989). 

LC50 (96-h static bioassay) for rainbow trout 14 mg/L, fathead minnows 12 mg/L, channel catfish 23 mg/L, bluegill sunfish 2 mg/L (quoted, Verschueren, 1983), Japanese medaka Oryzias latipes) 37.7 mg/L (Holcombe et al, 1995). 

LC50 (3-d post hatch) for Japanese medaka Oryzias latipes) ranged from 9 to 13 ng/L (Wisk and Cooper, 1990,1990a). 

Allyl isothiocyanate [57-06-7] Aluminum chloride Oryzias latlpes LC50 (96-h) -1.11 Holcombe et ak, 1995... 

Salvelinus fontinalis Daphnia pulex Oryzias latipes... 

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