Nasir Noreen, Raza Junaid, Hamid Abdul, Khan Naseem Ahmad, Majeed Mubushar, Aslam Muhammad Sohail, Shah Anis Ali, Iftikhar Muhammad, Arshad Bilal, Sohail Muhammad, Saeed Muhammad, Shaffique Shifa, Gatasheh Mansour K
Department of Chemistry, University of Okara, 2-KM, Renala Khurd, Okara, 56300, Punjab, Pakistan.
Department of Chemistry, Pakistan Institute of Engineering and Applied Sciences, Islamabad, PIEAS-45650, Pakistan.
Environ Monit Assess. 2025 Jul 30;197(8):969. doi: 10.1007/s10661-025-14359-x.
Heavy metals cause significant harm to both flora and fauna. Hence, it is mandatory to efficaciously eliminate them from drinking water preceding their release into the ecosystem. Herein, we first prepared Na-polyacrylate (PA) powder from sim-sim balls and graphene oxide (GO) using sugar cane bagasse as an adsorptive material. The prepared adsorbents were mixed with poly(vinyl chloride) (PVC) to fabricate novel adsorptive composite polymer membranes, pure PVC, PVC/GO, and PVC/PA-GO shortly named as PPGO-CPMs using the solution casting method. The as-synthesized membranes were used for the removal of Hg (II) and Pb (II) from contaminated water through the adsorption technique. Among the prepared PPGO membranes, PVC/PA-GO showed a maximum adsorption capacity of 18.04 ± 0.3 mg/g and 17.73 ± 0.4 mg/g for Pb (II) and Hg (II) respectively. PVC/PA-GO also showed greater removal efficiency for Pb (72.87 ± 0.4%) and Hg (71.62 ± 0.5%) among the other CPMs. Additionally, the effects of changes in initial metal concentration, interaction time, solution pH, and temperature on the removal performance were investigated. Maximum removal efficiencies for all the membranes were observed at 40 ppm initial metal concentration, a reaction time of 300 min, a pH value of 6, and 338 K temperature. The adsorption mechanism was studied through the linear form of Langmuir and Freundlich adsorption models. By comparing R, it was found that the Freundlich model best explained the adsorption process. For understanding reaction kinetics, pseudo-first-order and second-order kinetics were studied. The adsorption data was best aligned with pseudo-first-order kinetics. Adsorption on the surface of PVC was exothermic while it was endothermic on the surface of PVC/GO and PVC/PA-GO membranes. Functional groups present in PPGO-CPMs were confirmed by Fourier transform infrared spectroscopy (FTIR). Thermo gravimetric analysis/differential scanning calorimeter (TGA/DSC) tool reported high thermal stability, and the X-ray diffraction technique described the amorphous nature of the prepared composites. Porosity, water uptake, and ion adsorption capacity of the composite membranes were also studied to understand the hydrophilic nature of the CPMs. These resulting composites can help to treat water as a pH-stable composite membrane at pH 6.
重金属对动植物都会造成严重危害。因此,在将其排放到生态系统之前,必须有效地从饮用水中去除它们。在此,我们首先以甘蔗渣为吸附材料,从蓖麻籽和氧化石墨烯(GO)制备了聚丙烯酸钠(PA)粉末。将制备的吸附剂与聚氯乙烯(PVC)混合,采用溶液浇铸法制备了新型吸附复合聚合物膜,即纯PVC、PVC/GO和PVC/PA-GO,简称为PPGO-CPMs。合成的膜通过吸附技术用于去除污染水中的汞(II)和铅(II)。在制备的PPGO膜中,PVC/PA-GO对铅(II)和汞(II)的最大吸附容量分别为18.04±0.3mg/g和17.73±0.4mg/g。在其他CPMs中,PVC/PA-GO对铅(72.87±0.4%)和汞(71.62±0.5%)也表现出更高的去除效率。此外,还研究了初始金属浓度、相互作用时间、溶液pH值和温度变化对去除性能的影响。在初始金属浓度为40ppm、反应时间为300分钟、pH值为6和温度为338K时,观察到所有膜的最大去除效率。通过Langmuir和Freundlich吸附模型的线性形式研究了吸附机理。通过比较R,发现Freundlich模型最能解释吸附过程。为了理解反应动力学,研究了准一级和二级动力学模型;吸附数据与准一级动力学模型最吻合。PVC表面的吸附是放热的,而PVC/GO和PVC/PA-GO膜表面的吸附是吸热的。通过傅里叶变换红外光谱(FTIR)证实了PPGO-CPMs中存在的官能团。热重分析/差示扫描量热仪(TGA/DSC)工具显示出高的热稳定性,X射线衍射技术描述了制备的复合材料的无定形性质。还研究了复合膜的孔隙率、吸水率和离子吸附容量,以了解CPMs的亲水性。这些所得复合材料有助于在pH值为6时作为pH稳定的复合膜处理水。