Department of Chemical Engineering, National Taiwan University, Taipei, 10617, Taiwan.
Department of Chemical Engineering, College of Engineering, Tunghai University, Taichung, 40704, Taiwan.
Chemosphere. 2020 Aug;253:126736. doi: 10.1016/j.chemosphere.2020.126736. Epub 2020 Apr 10.
The covalent organic framework (COF) is made light elements linked by covalent networks. This study synthesize and characterized, and for the first time applied the produced EB-COF:Br as adsorbent for phosphate and arsenate removal from nearly neutral waters. The synthesized COF was first proven structurally stable in solutions of 75% HPO, 6 M HCl, or 6 M NaOH. Then the phosphate adsorption onto the EB-COF:Br was shown to be an endothermic process with maximum adsorption capacity at 25, 35 and 45 °C as 25.3, 34.7 and 35.3 mg/g COF, respectively; and the corresponding arsenate adsorption process being an exothermic process with maximnum adsorption capacity as 53.1, 27.5 and 5.1 mg/g, respectively. The synthesized COF could also effectively adsorb phosphate and arsenate ions from river water (pH 7.45) but at reduced adsorption capacities. The electrostatic interactions between the negative charge on phosphate or arsenate ions and the positively charged (N-) of COF, and the hydrogen bondings between H atom on phosphate or arsenate ions and the (-CO) group of COF were the dominating mechanisms for the present adsorption process. The strong electrostatic interactions for arsenate contributed to its higer adsorption capacity than noted for phosphate at 25 °C. However, the disturbed hydrogen bonding induced by mismatched sizes of arsenate ion and the adsorption sites surrounded by the (N-) and the (-CO) groups reduced the stability of arsenate to against temperature and external anion challenges. The use of the EB-COF; Br as industrial adsorbent was also discussed.
共价有机骨架(COF)是由共价网络连接的轻元素制成的。本研究合成并对其进行了表征,并首次将所制备的 EB-COF:Br 用作吸附剂,用于从近中性水中去除磷酸盐和砷酸盐。合成的 COF 首先被证明在 75% HPO、6 M HCl 或 6 M NaOH 的溶液中结构稳定。然后,证明了 EB-COF:Br 对磷酸盐的吸附是一个吸热过程,在 25、35 和 45°C 下的最大吸附容量分别为 25.3、34.7 和 35.3mg/g COF,而相应的砷酸盐吸附过程是一个放热过程,最大吸附容量分别为 53.1、27.5 和 5.1mg/g。所合成的 COF 还可以从河水(pH 7.45)中有效地吸附磷酸盐和砷酸盐离子,但吸附容量降低。磷酸盐或砷酸盐离子上的负电荷与 COF 上的正电荷(N-)之间的静电相互作用,以及磷酸盐或砷酸盐离子上的 H 原子与 COF 上的(-CO)基团之间的氢键是本吸附过程的主要机制。静电相互作用对于砷酸盐的吸附能力更强,这是因为在 25°C 下,砷酸盐的吸附容量高于磷酸盐。然而,砷酸盐离子的大小不匹配和吸附位点周围的(N-)和(-CO)基团引起的氢键的干扰降低了砷酸盐的稳定性,使其难以抵抗温度和外部阴离子的挑战。还讨论了将 EB-COF;Br 用作工业吸附剂的用途。