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101.
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103.
综述了铬在渔业中应用的研究进展,包括铬作为水产养殖饲料添加剂,对水生生物生长、毒性和生理活性的影响,及铬对养殖水体的污染、对渔业生物的危害以及检测方法等等,并提出了今后的研究展望。 相似文献
104.
在室内培养条件下,采用菌丝生长速率法测定了6种杀菌剂对桑膝节霉的抑制效果。结果显示,6种杀菌剂对桑树轮纹病病原菌桑膝节霉的菌丝生长均有不同程度的抑制作用,其中50%多菌灵、75%百菌清、10%苯醚甲环唑、250 g/L丙环唑、450 g/L咪酰胺和70%甲基硫菌灵的EC50分别为2.45 mg/L、2.51 mg/L、1.68 mg/L、1.31 mg/L、0.46 mg/L和7.99 mg/L。测试药剂中,供试桑树轮纹病菌对450 g/L咪酰胺最为敏感,250 g/L丙环唑次之。450 g/L咪酰胺和250 g/L丙环唑皆可作为防治桑树轮纹病的最佳药剂,用于田间试验。 相似文献
105.
池塘中亚硝酸盐对草鱼种的毒害及防治 总被引:45,自引:2,他引:45
亚硝酸盐对草鱼种有很高的毒性,特别是水温超过30℃以上时。它主要是诱导草鱼血液中的血红蛋白转变为高铁血红蛋白,高铁血红蛋白超过血红蛋白总量的23.0%时,容易诱发草鱼出血病。随着草鱼血液中高铁血红蛋白的增高,红细胞数量和血红蛋白含量逐渐减少。池中亚硝酸盐氮含量到0.099±0.03毫克/升时,草鱼会出现出血病。清除水中亚硝酸盐氮的方法是在池塘中施加次氯酸钠,亚硝酸盐氮超过0.15毫克/升时,最好在池塘中先施加熟石灰,然后施加次氯酸钠,且以分次施用,效果较好。 相似文献
106.
Ca^2+、Mg^2+对凡纳滨对虾存活及生长的影响 总被引:18,自引:1,他引:18
通过单因子静态急性毒性试验和正交设计法,研究水环境中Ca~(2 )、Mg~(2 )、Ca~(2 ) Mg~(2 )总量及Ca~(2 )/Mg~(2 )比值对凡纳滨对虾存活及生长的影响。结果表明:(1)凡纳滨对虾48h的Ca~(2 )的LC_50为407.38mg·L~(-1)、Mg~(2 )的LC_(50)为741.31mg·L~(-1)。(2)在Ca~(2 )/Mg~(2 )比值为1:10时,对凡纳滨对虾生存没有影响;(3)凡纳滨对虾的生长与Ca~(2 )浓度有密切关系,其值过高或过低均会影响凡纳滨对虾的生长;在Ca~(2 )/Mg~(2 )比值为1:3时,凡纳滨对虾生长和存活率随着Ca~(2 ) Mg~(2 )质量浓度的增加而上升,但达到一定质量浓度后,又随着Ca~(2 ) Mg~(2 )质量浓度的继续增加而下降。 相似文献
107.
Atlantic salmon ( Salmo salar L.) fry were reared on a fishmeal-based diet with three different levels of vitamin D3 (0.2, 5 and 57 mg vitamin D3 kg–1 feed, ww) from first-feeding for 14 weeks. No significant differences were recorded in weight, length, specific growth rate, mortality, or kidney calcium concentration between the different dietary groups. No skeletal malformations or histopathological changes were recorded in any of the dietary groups. These results suggest Atlantic salmon fry to be highly tolerant of megadoses of vitamin D3 over a limited period of time. 相似文献
108.
通过对含有元素磷的水体中鱼类的血清胆碱酯酶和三磷酸腺苷(ATP)酶活性的测定,发现元素磷对上述两类酶的活性有一定的抑制作用。当抑制率为40%~70%时,即可导致鱼类亚急性中毒死亡。结果表明:元素磷不但是一种剧毒物质,能引起鱼类的急性中毒,而且是一种稳定的可积累的毒物,它能破坏鱼类的肝细胞,抑制正常代谢,造成神经毒性,以致引起鱼类的亚急性和慢性中毒死亡。 相似文献
109.
- 1. The purpose of this report is to determine the concentrations of tributyltin in sediments that would be protective against adverse effects on prey species of salmonids listed under the US Endangered Species Act.
- 2. Two approaches for determining adverse sediment concentrations due to tributyltin (TBT) contamination are presented here. The first is the equilibrium partitioning (EqP) approach, which relies on a sediment‐water partition coefficient and toxicological data for water exposures. The EqP approach utilizes the large water quality database that has been generated over the last two decades for TBT and provides strong evidence for adverse effects at low exposure concentrations.
- 3. The second approach involves determination of a TBT tissue residue that is considered harmful for most species, which is then used to predict the sediment concentration that would likely produce this adverse tissue concentration.
- 4. Both approaches are presented here because they generally support each other but based on the information presented below, and the inherent difficulty in measuring porewater concentrations, the tissue residue approach is the recommended method for determining adverse sediment concentrations.
- 5. Using this analysis, the protective sediment concentration for TBT proposed here is 6000 ng g?1organic carbon. Direct effects are not expected on salmonids at this sediment concentration because of their relatively short residence time in the estuary, general lack of interaction with sediment, and relatively high metabolic capacity. This concentration may ensure adequate abundance of salmonid prey species; however, it may not be low enough for the protection of sensitive benthic species.
110.
Rahmi?Ayd?nEmail author Kenan?K?prücü Mustafa?D?rücü Sibel??im?ek?K?prücü Murat?Pala 《Aquaculture International》2005,13(5):451-458
In this study, the toxic effects on the embryos and larvae of the common carp were used as a model to investigate the synthetic pyrethroid pesticide, cypermethrin, which contaminates aquatic ecosystems. Data obtained from the cypermethrin acute toxicity tests were evaluated using the Probit Analysis Statistical Method. The control and eight test experiments were repeated five times. The number of dead embryos significantly increased in response to cypermethrin concentrations 0.0001, 0.001, 0.01, 0.1, 1, 2, 4 and 8 μg l−1 (p<0.05 for each case). The 48 h LC50 value (with 95% confidence limits) of cypermethrin for common carp embryos was estimated at 0.909 (0.256–5.074) μg l−1. Dose–response decreases in hatching success were recorded as 87.4, 85.0, 80.2, 71.4, 56.3, 48.6, 38.8 and 23.5%, respectively. The lowest concentration of cypermethrin (0.0001 μg l−1) produced a significant increase in the number of dead larvae compared to the control group (p<0.05). The number of dead larvae significantly increased with increasing cypermethrin concentrations exposed for 1–96 h (p<0.05). The highest concentration (8 μg l−1) showed the highest larvae mortality. The 96 h LC50 value (with 95% confidence limits) of cypermethrin for common carp larvae was estimated at 0.809 (0.530–1.308) μg l−1. The results of the study suggest that low levels of cypermethrin in the aquatic environment may have a significant effect on the reproduction and development of carp. 相似文献