首页> 外文期刊>Environmental toxicology and chemistry >Influence of salinity and organic carbon on the chronic toxicity of silver to mysids (Americamysis bahia) and silversides (Menidia beryllina).
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Influence of salinity and organic carbon on the chronic toxicity of silver to mysids (Americamysis bahia) and silversides (Menidia beryllina).

机译:盐度和有机碳对银对类蝇((Americamysis bahia)和银苷(Menidia beryllina)的慢性毒性的影响。

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Tests were conducted with mysids (Americamysis bahia) and silversides (Menidia beryllina) to evaluate the influence of salinity and organic carbon on the chronic toxicity of silver. During 7- and 28-d tests conducted at 10, 20, and 30% per hundred salinity, higher concentrations of dissolved silver generally were required to cause a chronic effect as the salinity of the seawater was increased. The 28-d mysid and silverside 20%-effective concentration values (expressed as dissolved silver) ranged from 3.9 to 60 and from 38 to 170 microg/L, respectively, over the salinity range. This pattern was not observed when the same test results were evaluated against the concentrations of free ionic silver (measured directly during toxicity tests), as predicted by the free-ion activity model. Increasing the concentration of dissolved organic carbon from 1 mg/L to the apparent maximum achievable concentration of 6 mg/L in seawater caused a slight decrease in chronic toxicity to silversides but had no effect on the chronic toxicity to mysids. The possible additive toxicity of silver in both food and water also was investigated. Even at the maximum achievable foodborne concentration, the chronic toxicity of silver added to the water was not affected when silver was also added to the food, based on the most sensitive endpoint (growth). However, although fecundity was unaffected at all five tested concentrations during the test with silver in water only, it was significantly reduced at the two highest waterborne silver concentrations (12 and 24 microg/L) during the test with silver dosed into food and water.
机译:用mysids(Americamysis bahia)和silversides(Menidia beryllina)进行了测试,以评估盐度和有机碳对银的慢性毒性的影响。在以每百盐度10%,20%和30%进行的7天和28天试验中,随着海水盐度的增加,通常需要更高浓度的溶解银才能引起慢性影响。在盐度范围内,28 d mysid和银苷20%有效浓度值(表示为溶解的银)分别为3.9至60 microg / L和38至170 microg / L。如自由离子活性模型所预测,当针对游离离子银的浓度(直接在毒性测试中测量)评估相同的测试结果时,未观察到这种模式。将海水中的溶解有机碳浓度从1 mg / L增加到表观最大可达到的6 mg / L浓度,对银苷的慢性毒性略有降低,但对对类腮腺炎的慢性毒性没有影响。还研究了银在食物和水中的可能的附加毒性。根据最敏感的终点(增长),即使在最大可食进食浓度下,当向食物中添加银时,向水中添加银的慢性毒性也不会受到影响。但是,尽管仅在水中使用银时,在所有五个测试浓度下生育力都没有受到影响,但在食物和水中加入银的情况下,在两个最高的水性银浓度(12和24 microg / L)下,生育力都显着降低。

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