目的通过验证稀有鮈鲫作是否适用于幼体生长试验,为相关化学品测试国家标准的制定提供依据。方法以重铬酸钾和3,4-二氯苯胺为参比物质,按照《OECD化学品测试准则No.215鱼类幼体生长试验》,分别开展三次实验室内稀有鮈鲫幼体生长试验以...目的通过验证稀有鮈鲫作是否适用于幼体生长试验,为相关化学品测试国家标准的制定提供依据。方法以重铬酸钾和3,4-二氯苯胺为参比物质,按照《OECD化学品测试准则No.215鱼类幼体生长试验》,分别开展三次实验室内稀有鮈鲫幼体生长试验以评价试验结果的重复性,进行实验室间比对试验以评价试验结果的再现性。结果实验室内重复试验中,重铬酸钾和3,4-二氯苯胺对稀有鮈鲫生长抑制效应(EC_(20))平均值分别为30.9 mg/L和163μg/L,变异系数均小于15%;实验室间比对试验中,虽然变异系数增大,但是各实验室的28 d EC_(20)均在【math14】±2s范围之内。结论稀有鮈鲫幼体生长试验结果具有良好的重复性和再现性,且稀有鮈鲫对3,4-二氯苯胺的敏感性与虹鳟(Oncorhynchus mykiss)相当,因此稀有鮈鲫可作为鱼类幼体生长试验的本土受试鱼种。展开更多
Twenty two fresh water fish samples namely Puntius sarana （Shawrputi）, Cyprinus carpio （Karp）, Oreochromis niloticos （Telapia）, Channa punctatus （Taki）, Wallogonia attu （Boal）, Eutropiichthys vacha （Bacha）...Twenty two fresh water fish samples namely Puntius sarana （Shawrputi）, Cyprinus carpio （Karp）, Oreochromis niloticos （Telapia）, Channa punctatus （Taki）, Wallogonia attu （Boal）, Eutropiichthys vacha （Bacha）, Macrognathus aculiatus （Baim）, Ailia coila （Kajoli）, Mystus cavasisus（Gulsa）, Ompok pabda （Pabdha）, Corica soborna （Kachki）, Mystus vittatus （Tengra）, Glossogobius giuris （Baila）, Macrobrachium malcolmsli （Chingri）, Amblypharyngodon microlepis （Mola）, Anabas testudineus （Koi）, Macrognathus aculiatus （Baim）, Channa striatus （Shole）, Heteropnueste fossilis （Shing）, Puntius sophore （Small Puti） and Pseudambassis ranga （Telapia） were collected from two rivers and one cultured fish pond. The samples were extracted by QuEChERS method, cleaned up with conc. H2SO4 treatment and cleaned extracts were analyzed by GC-ECD. Small size cultured rui fish sample which did show detectable amount of DDT and its metabohtes was used for the recovery experiments. Percent recovery was found to be in the range of 70%-113%. Amount of total DDTs were found to be 54.34, 48.81, 62.09, 54.72,78.81, 60.07, 47.0, 42.7, 26.31, 10.36, 25.32, 12.96, 20.10, 12.78, 17.65, and 4.71, 8.58, 11.3 and 19.01 ng/g in gulsa, pabhda, baila, bacha, baim, small purl, tengra, chanda, kachki, boal, taki, chingri, mola, shole, shing, koi, swarpurl, karp and telapia fish samples, respectively. However, the residual amounts of DDTs in all the fish samples were below maximum residue limit （MRL of DDTs in fish 5.0 mg/kg） according to Codex Alimentarius Commission. The ratios of 4,4＇-DDT/DDTs were in the range of 0.03-0.44 which indicated that exposure to DDT is not due to recent use.展开更多
文摘目的通过验证稀有鮈鲫作是否适用于幼体生长试验,为相关化学品测试国家标准的制定提供依据。方法以重铬酸钾和3,4-二氯苯胺为参比物质,按照《OECD化学品测试准则No.215鱼类幼体生长试验》,分别开展三次实验室内稀有鮈鲫幼体生长试验以评价试验结果的重复性,进行实验室间比对试验以评价试验结果的再现性。结果实验室内重复试验中,重铬酸钾和3,4-二氯苯胺对稀有鮈鲫生长抑制效应(EC_(20))平均值分别为30.9 mg/L和163μg/L,变异系数均小于15%;实验室间比对试验中,虽然变异系数增大,但是各实验室的28 d EC_(20)均在【math14】±2s范围之内。结论稀有鮈鲫幼体生长试验结果具有良好的重复性和再现性,且稀有鮈鲫对3,4-二氯苯胺的敏感性与虹鳟(Oncorhynchus mykiss)相当,因此稀有鮈鲫可作为鱼类幼体生长试验的本土受试鱼种。
文摘Twenty two fresh water fish samples namely Puntius sarana （Shawrputi）, Cyprinus carpio （Karp）, Oreochromis niloticos （Telapia）, Channa punctatus （Taki）, Wallogonia attu （Boal）, Eutropiichthys vacha （Bacha）, Macrognathus aculiatus （Baim）, Ailia coila （Kajoli）, Mystus cavasisus（Gulsa）, Ompok pabda （Pabdha）, Corica soborna （Kachki）, Mystus vittatus （Tengra）, Glossogobius giuris （Baila）, Macrobrachium malcolmsli （Chingri）, Amblypharyngodon microlepis （Mola）, Anabas testudineus （Koi）, Macrognathus aculiatus （Baim）, Channa striatus （Shole）, Heteropnueste fossilis （Shing）, Puntius sophore （Small Puti） and Pseudambassis ranga （Telapia） were collected from two rivers and one cultured fish pond. The samples were extracted by QuEChERS method, cleaned up with conc. H2SO4 treatment and cleaned extracts were analyzed by GC-ECD. Small size cultured rui fish sample which did show detectable amount of DDT and its metabohtes was used for the recovery experiments. Percent recovery was found to be in the range of 70%-113%. Amount of total DDTs were found to be 54.34, 48.81, 62.09, 54.72,78.81, 60.07, 47.0, 42.7, 26.31, 10.36, 25.32, 12.96, 20.10, 12.78, 17.65, and 4.71, 8.58, 11.3 and 19.01 ng/g in gulsa, pabhda, baila, bacha, baim, small purl, tengra, chanda, kachki, boal, taki, chingri, mola, shole, shing, koi, swarpurl, karp and telapia fish samples, respectively. However, the residual amounts of DDTs in all the fish samples were below maximum residue limit （MRL of DDTs in fish 5.0 mg/kg） according to Codex Alimentarius Commission. The ratios of 4,4＇-DDT/DDTs were in the range of 0.03-0.44 which indicated that exposure to DDT is not due to recent use.
