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氨对污水氧化塘中藻类的毒性

Toxicity of ammonia to algae in sewage oxidation ponds.

作者信息

Abeliovich A, Azov Y

出版信息

Appl Environ Microbiol. 1976 Jun;31(6):801-6. doi: 10.1128/aem.31.6.801-806.1976.

Abstract

Ammonia, at concentrations over 2.0 mM and at pH values over 8.0, inhibits photosynthesis and growth of Scenedesmus obliquus, a dominant species in high-rate sewage oxidation ponds. Photosynthesis of Chlorella pyrenoidosa, Anacystis nidulans, and Plectonema boryanum is also susceptible to ammonia inhibition. Dark respiration and cell morphology were unaffected by any combination of pH and ammonia concentrations tested, thus limiting the apparent effect to inhibition of the normal function of the chloroplasts. Methylamine had the same effect as ammonia, and its penetration into the cells was found to be pH dependent. Therefore, the dependence of toxicity of amines to algae on pH apparently results from the inability to penetrate the cell membrane in the ionized form. When operated at 120-h detention time of raw wastewater, the high-rate oxidation pond maintained a steady state with respect to algal growth and oxygen concentration, and the concentration of ammonia did not exceed 1.0 mM. Shifting the pond to 48-h detention time caused an increase in ammonia concentration in the pond water to 2.5 mM, and the pond gradually turned anaerobic. Photosynthesis, which usually elevates the pH of the pond water to 9.0 to 10.0, could not proceed beyond pH 7.9 because of the high concentration of ammonia, and the algal population was washed out and reduced to a concentration that could maintain a doubling time of 48 h without photosynthesis bringing the pH to inhibitory levels. Under these conditions, the pH of the bond becomes a factor that limits the operational efficiency of the oxidation pond.

摘要

氨浓度超过2.0 mM且pH值超过8.0时,会抑制斜生栅藻(高速污水氧化塘中的优势物种)的光合作用和生长。蛋白核小球藻、集胞藻和鞘丝藻的光合作用也易受氨抑制影响。黑暗呼吸和细胞形态不受所测试的任何pH值与氨浓度组合的影响,因此,明显的影响仅限于抑制叶绿体的正常功能。甲胺与氨具有相同作用,且发现其进入细胞的过程取决于pH值。因此,胺类对藻类的毒性对pH值的依赖性显然源于其无法以离子形式穿透细胞膜。当原废水的停留时间为120小时时,高速氧化塘在藻类生长和氧气浓度方面保持稳定状态,氨浓度不超过1.0 mM。将氧化塘的停留时间缩短至48小时,导致塘水中氨浓度升至2.5 mM,氧化塘逐渐转为厌氧状态。通常会将塘水pH值提升至9.0至10.0的光合作用,由于氨浓度过高,无法在pH值超过7.9时继续进行,藻类种群被冲走,数量减少至在无光合作用将pH值提升至抑制水平的情况下能保持48小时倍增时间的浓度。在这些条件下,氧化塘的pH值成为限制其运行效率的一个因素。

相似文献

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Toxicity of ammonia to algae in sewage oxidation ponds.氨对污水氧化塘中藻类的毒性
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