当前位置: X-MOL 学术Langmuir › 论文详情
Our official English website, www.x-mol.net, welcomes your feedback! (Note: you will need to create a separate account there.)
Synthesis of Aminomethylpyridine-Decorated Polyamidoamine Dendrimer/Apple Residue for the Efficient Capture of Cd(II)
Langmuir ( IF 3.7 ) Pub Date : 2024-01-18 , DOI: 10.1021/acs.langmuir.3c03447
Mengchen Cong 1 , Kaiyan Wu 1, 2 , Jiaxuan Wang 1 , Ziwei Li 1 , Ruiyu Mao 1 , Yuzhong Niu 1 , Hou Chen 1
Affiliation  

Water contamination irritated by Cd(II) brings about severe damage to the ecosystem and to human health. The decontamination of Cd(II) by the adsorption method is a promising technology. Here, we construct aminomethylpyridine-functionalized polyamidoamine (PAMAM) dendrimer/apple residue biosorbents (AP-G1.0-AMP and AP-G2.0-AMP) for adsorbing Cd(II) from aqueous solution. The adsorption behaviors of the biosorbents for Cd(II) were comprehensively evaluated. The maximum adsorption capacities of AP-G1.0-AMP and AP-G2.0-AMP for Cd(II) are 1.40 and 1.44 mmol·g–1 at pH 6. The adsorption process for Cd(II) is swift and can reach equilibrium after 120 min. The film diffusion process dominates the adsorption kinetics, and a pseudo-second-order model is appropriate to depict this process. The uptake of Cd(II) can be promoted by increasing concentration and temperature. The adsorption isotherm follows the Langmuir model with a chemisorption mechanism. The biosorbents also display satisfied adsorption for Cd(II) in real aqueous media. The adsorption mechanism indicates that C–N, N═C, C–O, CONH, N–H, and O–H groups participate in the adsorption for Cd(II). The biosorbents display a good regeneration property and can be reused with practical value. The as-prepared biosorbents show great potential for removing Cd(II) from water solutions with remarkable significance.

中文翻译:


氨甲基吡啶修饰的聚酰胺胺树枝状聚合物/苹果渣的合成用于有效捕获 Cd(II)



Cd(II)刺激的水污染给生态系统和人类健康带来严重损害。吸附法净化Cd(II)污染是一项很有前景的技术。在这里,我们构建了氨甲基吡啶官能化聚酰胺胺(PAMAM)树枝状聚合物/苹果渣生物吸附剂(AP-G1.0-AMP和AP-G2.0-AMP)用于从水溶液中吸附Cd(II)。综合评价了生物吸附剂对Cd(II)的吸附行为。 AP-G1.0-AMP 和 AP-G2.0-AMP 在 pH 6 时对 Cd(II) 的最大吸附容量分别为 1.40 和 1.44 mmol·g –1 。对 Cd(II) 的吸附过程迅速且可以120分钟后达到平衡。薄膜扩散过程在吸附动力学中占主导地位,伪二阶模型适合描述该过程。提高浓度和温度可以促进 Cd(II) 的吸收。吸附等温线遵循具有化学吸附机制的朗缪尔模型。该生物吸附剂在实际水介质中对 Cd(II) 也表现出令人满意的吸附作用。吸附机理表明C-N、N=C、C-O、CONH、N-H和O-H基团参与了Cd(II)的吸附。该生物吸附剂具有良好的再生性能,可重复使用,具有实用价值。所制备的生物吸附剂在去除水溶液中的 Cd(II) 方面表现出巨大的潜力,具有显着的意义。
更新日期:2024-01-18
down
wechat
bug