首页> 外文会议>Conference on site remediation technologies environmental management practices in the utility industry >OXIDATIVE DESTRUCTION OF IRON-COMPLEXED CYANIDE AT ATMOSPHERIC PRESSURE AND TEMPERATURES BELOW 100°C
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OXIDATIVE DESTRUCTION OF IRON-COMPLEXED CYANIDE AT ATMOSPHERIC PRESSURE AND TEMPERATURES BELOW 100°C

机译:在大气压下在大气压和低于100°C的温度下氧化破坏铁络氰化物

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Due to leaching from purifier bed wastes, iron-cyanide complexes are routinely found in the groundwater of manufactured gas plant sites. Iron-cyanide complexes will persist in groundwater sources, and are difficult to destroy. As with other strong acid dissociable (SAD) cyanide complexes, iron-complexed cyanides tend to be chemically inert unless exposed to ultraviolet (UV) radiation. When exposed to sunlight, iron-cyanide complexes in surface waters may release the toxic free cyanide ion, which is potentially toxic to aquatic life. Although free cyanide and weak acid dissociable (WAD) cyanide complexes may be easily destroyed through oxidation at room temperature, SAD cyanide complexes are resistant to such measures. The research presented in this paper has been undertaken to adapt traditional oxidative techniques to iron-cyanide complexes in a cost effective manner Potassium ferricyanide and potassium ferrocyanide have been successfully destroyed (oxidized) at atmospheric pressure and temperatures below 100°C within a reasonable time frame (hours). Successful oxidizers include sodium hypochlorite (chlorine bleach), ozone, and potassium permanganate. Successful destruction was not achieved through the use of hydrogen peroxide. Based on a literature search into the chemistry of iron-cyanide complexes, it appears that the hexacyano-complex decays into the pentacyano-complex, that subsequently breaks down into free cyanide and the ferric or ferrous ion. When the oxidizer concentration is sufficiently high, these two dissociations become the rate limiting steps. The activation energies for the hexacyano- and pentacyano-complex dissociations were found to be 1.562 x 10~3 J/mol and 918.9 J/mol, respectively. The first and second frequency factors equal 3.245 x 10~(14) min~(-1) and 7.856 x 10~7 min~(-1), respectively.
机译:由于从净化床废物浸出,铁氰化物复合物制气厂区的地下水常规发现。铁氰化物复合物将在地下水源依然存在,并且是难以摧毁。作为与其它强酸解离(SAD)氰化物络合物,铁络合氰化物往往是化学惰性的,除非暴露于紫外(UV)辐射。当暴露在阳光下,在地表水中的铁氰化物配合可释放有毒的游离氰化物离子,其是对水生生物具有潜在毒性。虽然无氰化物和弱酸解离(WAD)氰化物配合物可以通过在室温下的氧化容易被破坏,SAD氰化物络合物是这些措施有抗性。在本文提出的研究已经进行以成本有效的方式铁氰化钾和亚铁氰化钾,以适应传统的氧化技术,以铁氰化物配合物已经成功地销毁(氧化)在低于100℃的大气压力和温度下在合理的时间框架内(小时)。成功的氧化剂包括次氯酸钠(氯漂白剂),臭氧,和高锰酸钾。成功的破坏不是通过使用过氧化氢来实现。基于文献检索到铁氰化物络合物的化学性质,看来该六氰基复合物衰变到五氰基配合物,其随后分解成游离氰化物和铁或亚铁离子。当氧化剂浓度足够高时,这两个解离成为限制步骤的速率。被发现为hexacyano-和五氰基复合物解离活化能为1.562×10 -3焦耳/摩尔分别和918.9焦耳/摩尔。在第一和第二频率的因素等于3.245×10(14)分钟〜(-1)和7.856×10 -7分钟〜(-1),分别。

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