1. Results and Discussion
Title
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Introduction
Background
Part1
Part2
Part3
Aims of this study
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Example of the Figure
AMN with a purity of 95% was purchased from J&K Chemical Co., Ltd, China, Ltd. Three commercial available CNTs, including SWCNT, MWCNT, and SWCNT-COOH were purchased from Chengdu Organic Chemistry Co., Ltd., China, while activated carbon MSC25 and MSC30 were purchased from Kansai Coke and Chemicals Co., Ltd., Japan.
Materials and Methods
Figure 1 – Adsorption isotherms of AMN on ACs and CNTs: mass (a) and specific surface area (b) based.
Results and Discussion
Results 1
In mass based adsorption isotherms, MSC25 and MSC30 exhibited stronger adsorption affinity than SWCNT and MWCNT did at the same adsorbents dosage.
Results 2
In specific surface area based adsorption isotherms, the qe-A values of MSC25 and MSC30 were similar to those of SWCNT and MWCNT. The adsorption capacity on per unit specific surface area of CNTs were comparable to ACs.
Discussion
Figure 2 - Adsorption isotherm models simulation of AMN on active carbon and CNT
Activated carbon and CNTs were useful to remove AMN in solution.
The adsorption capacities of MSC25 and MSC30 were higher than those of SWCNT and MWCNT
Conclusions
References
[1] 胡洪营 等. (2015). 区域水资源介循环利用模式: 概念·结构·特征. 环境科学研究 28(6).
[2] Sun, Y., et al. (2016). Characteristics of water quality of municipal wastewater treatment plants in China: implications for resources utilization and management。 Journal of Cleaner Production 131.