首页> 外文会议>European corrosion congress;EUROCORR 2010 >CORROSION-ACTIVE MICROFLORA OF WATER TECHNOLOGICAL ENVIRONMENTS OF THE ATOMIC POWER STATION
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CORROSION-ACTIVE MICROFLORA OF WATER TECHNOLOGICAL ENVIRONMENTS OF THE ATOMIC POWER STATION

机译:原子能发电站水技术环境的抗腐蚀微丝

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In the course of nuclear power plants (NPP) work in the process equipment with natural water there is a continuous receipt of impurity, in particular the microbiological origin, constructional materials causing biological corrosion (Fig. 2,3). Application of chemical methods for an estimation of quality of technological water not always yields effective result owing to a lack of the information on a biological component of analyzed environments and consequences of its influence on reliability of the systems executed from various materials. Bacteria of corrosion group get to pipelines of power installations through systems chemical-water-treatment (CWT) (Fig.l), ionic materials which do not possess bactericidal properties, and on the contrary, are a necessary substratum for microflora ability to live. In large quantities breeding on ionic-resin (IR), especially at lay modes or in reserve branches of water purification, the microflora blocks IR groups. Without preliminary antimicrobic processing, there can be a fast bacterial poisoning of resins, frequently the irreversible. Investigated presence of some corrosion-active groups of microorganisms in natural water and systems CWT on the NPP. Number sulfate-reducing bacterium (SRB) in ground deposits of the river more than on depth 1,5 m (accordingly, 150 and 50 cl./ml). Amount in water CWT SRB are not revealed. It is connected with adverse conditions for their development (increase pH environments after clarifying agent). The maximum number denitrifying bacteria (DNB) and thiobacterium (TB) is revealed in the end of chain CWT (accordingly, 2,0·10~6 and 9,5·10~6 cl/ml), minimum - after clarifying agent (3,0·10~3 and 9,5·10~3 cl/ml) and in tank of a dirty condensate (3,0·10~3 and 3,0·10~4 cl/ml) (tabl.).
机译:在使用天然水的过程设备中,核电厂(NPP)运行过程中,会不断接收杂质,特别是微生物来源的杂质,这些成分会引起生物腐蚀(图2,3)。由于缺乏有关所分析环境的生物成分的信息及其对由各种材料执行的系统的可靠性的影响所致的结果,应用化学方法估算工业用水的质量并不总能产生有效的结果。腐蚀基团的细菌通过化学水处理系统(CWT)进入电力设备的管道(图1),离子材料不具有杀菌特性,相反,它们是微生物群落生存的必要基础。在离子树脂(IR)上进行大量繁殖时,尤其是在非繁殖模式或净水储备分支中,微生物区系会阻止IR基团。如果不进行初步的抗微生物处理,树脂就会迅速发生细菌中毒,这通常是不可逆的。研究了天然水和NPP上CWT系统中某些微生物的腐蚀活性基团的存在。河流地面沉积物中的硫酸盐还原细菌(SRB)数量超过深度1.5 m(分别为150和50 cl./ml)。未披露水中CWT SRB的量。它与不利的条件发展有关(澄清剂后增加pH值环境)。反硝化细菌(DNB)和硫细菌(TB)的最大数量在CWT链末端显示(分别为2,0·10〜6和9,5·10〜6 cl / ml)-最少-在澄清剂之后( 3,0·10〜3和9,5·10〜3 cl / ml)以及在脏冷凝水箱中(3,0·10〜3和3,0·10〜4 cl / ml)(表) 。

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