School of Mechanical Engineering, Beijing Institute of Petrochemical Technology, Beijing 102617, PR China; Beijing Key Laboratory of Pipeline Critical Technology and Equipment for Deepwater Oil & Gas Development, Beijing 102617, PR China.
Beijing BHT Environment Technology Co., Ltd, Beijing 100102, PR China.
Chemosphere. 2018 Nov;210:624-632. doi: 10.1016/j.chemosphere.2018.07.073. Epub 2018 Jul 17.
Raw coal fly ash (RCFA) was used directly as adsorbent to treat coking wastewater. The results show that the RCFA can introduce COD (14, 4, and 11 mg L at pH = 1.0, 7.0, and 14.0, respectively) into water due to the dissolution of reductive components from RCFA, this can be avoided by washing (6 times) using distilled water. The concentration of leached metal elements in wastewater is lower than the standard in GB18918-2002, China. The adsorption process accords with the pseudo-second order adsorption kinetic model and Langmuir thermodynamics model better than other ones, and it belongs to a physical and exothermic process. More loading of RCFA (10-60 mg L) means less adsorption capacity, and 40 g L is the optimal value. The variation of regeneration rate of SRCFA for the first time (RR) with regeneration time accords with the behavior of hyperbolic function (1RR=0.986+53.913t), and the [HO], [Fe] and regeneration temperature can affect the RR at the manner of exponential function ( [Formula: see text] , [Formula: see text] , and RR=2.064·e). At the optimal regeneration condition of SRCFA ([HO] = 5 mM, [Fe] = 8 mM and temperature = 293 K), the RR can reach 87.1% after 270 min. The stability of RCFA shows two different stages, i.e., within the first 4 regenerations the RR increases from 87.1% to 89.7% and then decreases gradually and always. This variation trend can be confirmed by the results of SEM and BET tests.
原状粉煤灰(RCFA)直接用作吸附剂处理焦化废水。结果表明,RCFA 中的还原性成分溶解会导致水中 COD(pH 值分别为 1.0、7.0 和 14.0 时,COD 为 14、4 和 11mg/L),可以通过用蒸馏水(6 次)冲洗来避免。废水中浸出金属元素的浓度低于中国 GB18918-2002 标准。吸附过程更符合准二级吸附动力学模型和 Langmuir 热力学模型,而不是其他模型,属于物理和放热过程。RCFA 的负载量(10-60mg/L)越高,吸附能力越低,40g/L 是最佳值。SRCFA 的首次再生率(RR)随再生时间的变化符合双曲线函数的行为(1RR=0.986+53.913t),[HO]、[Fe]和再生温度以指数函数的方式影响 RR([Formula: see text]、[Formula: see text]和 RR=2.064·e)。在 SRCFA 的最佳再生条件下([HO]=5mM、[Fe]=8mM 和温度=293K),经过 270min,RR 可达到 87.1%。RCFA 的稳定性表现出两个不同的阶段,即在最初的 4 次再生中,RR 从 87.1%增加到 89.7%,然后逐渐下降并一直保持。这种变化趋势可以通过 SEM 和 BET 测试的结果得到证实。