首页> 外国专利> Sequential treatment of organics and heavy metal ions wastewater, comprises initializing fenton process by adding ferrous salt and hydrogen peroxide into continuously mixing wastewater, and adding iron salt to re-adjust molar ratio

Sequential treatment of organics and heavy metal ions wastewater, comprises initializing fenton process by adding ferrous salt and hydrogen peroxide into continuously mixing wastewater, and adding iron salt to re-adjust molar ratio

机译:依次处理有机物和重金属离子废水,包括通过在连续混合的废水中添加亚铁盐和过氧化氢来初始化芬顿过程,并添加铁盐以重新调节摩尔比

摘要

Sequential treatment of organics and heavy metal ions wastewater, comprises initializing fenton process by adding ferrous salt and hydrogen peroxide into continuously mixing wastewater to adjust molar ratio of organics:hydrogen peroxide:ferrous ions in proper molar ratio; and adding iron salt to re-adjust the molar ratio of organics:hydrogen peroxide:ferrous ions to control a molar ratio of ferrous ions:heavy metal ions greater than 4. Sequential treatment of organics and heavy metal ions wastewater, comprises: (1) initializing a fenton process by adding proper amount of ferrous (Fe) salt and hydrogen peroxide (H 2O2) into continuously mixing wastewater to adjust a molar ratio of organics:H 2O 2:ferrous ions (Fe 2 +)) in proper molar ratio, where reactive environment is controlled under 20-100[deg]C and pH of 2-5, and where a mixing rate is adjusted properly, and then monitoring variance of pH and oxidation-reduction potential (ORP) during the fenton process in determining the terminal time of the fenton process as pH and ORP both reach a steady state; (2) adding proper amount of Fe salt to re-adjust the molar ratio of organics:H 2O 2:Fe 2 + to control a molar ratio of Fe 2 +:heavy metal ions greater than 4; (3) heating to 20-100[deg]C, and adding proper amount of Fe salt and alkali to adjust pH ranging from 8 to 12 for conducting a concentration for heavy metal ions; (4) sequentially aerating air with a proper aerating rate to initialize a ferrite process, and then monitoring variance of pH and ORP during the ferrite process in determining the terminal time of the ferrite process as pH and ORP both reach a steady state, by which ferrite products are capable of being formed; (5) delivering slurry out of an outlet of a reactor tank and into a sedimentation tank for solid/liquid separation and filtration, by which solid sediment of the ferrite products may be further examined with a toxicity characteristic leaching procedure (TCLP), and filtrate that is filtered and separated from the slurry may be recirculated to the step (3) for reuse or directly drained away after an aqueous analysis and a pH adjustment. The above steps may sequentially treat the organics and the heavy metal ions contained the mixed wastewater by using the fenton process to reduce the effect of the organics on the magnetism of the ferrite products so as to enhance the quality of the ferrite products. Fe ions taken as catalysts in the fenton process may be turned into a reactant in the recyclable ferrite process to solve a color problem of the wastewater caused by ferric ion (Fe 3 +) and reduce iron sludge caused by coagulation after the fenton process.
机译:依次处理有机物和重金属离子废水,包括通过在连续混合的废水中加入亚铁盐和过氧化氢来初始化芬顿过程,以适当的摩尔比调节有机物:过氧化氢:亚铁离子的摩尔比;加入铁盐,重新调节有机物:过氧化氢:亚铁离子的摩尔比,以控制亚铁离子:重金属离子的摩尔比大于4。依次处理有机物和重金属离子废水,包括:(1)通过向连续混合的废水中添加适量的亚铁(Fe)盐和过氧化氢(H 2O2)来初始化芬顿过程,以调整适当摩尔数的有机物:H 2O 2:亚铁离子(Fe 2> +>)的摩尔比比率,其中反应环境控制在20-100℃,pH值控制在2-5,适当调整混合速率,然后监测芬顿过程中pH和氧化还原电位(ORP)的变化确定pH和ORP均达到稳态时芬顿过程的终止时间; (2)加入适量的铁盐,重新调节有机物∶H 2 O 2 ∶Fe 2 >>>的摩尔比,以控制Fe 2 >>>:重金属离子的摩尔比大于4。 (3)加热至20-100℃,并加入适量的铁盐和碱以调节pH值在8-12之间,以进行重金属离子的浓缩。 (4)以适当的充气速率顺序充气,以初始化铁氧体过程,然后在铁氧体过程中监视pH和ORP的变化,以确定铁氧体过程的终止时间,因为pH和ORP均达到稳态。可以形成铁素体产品; (5)将浆液从反应罐的出口送出到沉淀罐中进行固/液分离和过滤,通过该沉淀物可以进一步通过毒性特征浸出程序(TCLP)检查铁素体产品的固体沉淀物和滤液从浆液中过滤并分离出的水可以再循环至步骤(3)以重复使用,或在进行水分析和调节pH后直接排掉。上述步骤可以通过使用芬顿法依次处理混合废水中的有机物和重金属离子,以减少有机物对铁氧体产品磁性的影响,从而提高铁氧体产品的质量。在fenton工艺中作为催化剂的Fe离子在可循环铁氧体工艺中可以转变为反应物,以解决由三价铁离子(Fe 3> +>)引起的废水的变色问题,并减少fenton工艺后由于混凝而导致的铁渣。

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