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利用污水处理厂的电凝污泥作为吸附剂去除直接红28染料。

Utilizations of electro-coagulated sludge from wastewater treatment plant as an adsorbent for direct red 28 dye removal.

作者信息

Aragaw Tadele Assefa

机构信息

Faculty of Chemical and Food Engineering, Bahir Dar Institute of Technology, Bahir Dar University, Ethiopia.

出版信息

Data Brief. 2019 Nov 22;28:104848. doi: 10.1016/j.dib.2019.104848. eCollection 2020 Feb.

DOI:10.1016/j.dib.2019.104848
PMID:31871990
原文链接:https://pmc.ncbi.nlm.nih.gov/articles/PMC6909148/
Abstract

This work reported on the adsorptions of direct red 28 dye on to the raw and calcined electro-coagulated, EC, sludge adsorbents collected from the textile wastewater treatment plant. EC sludge adsorbent was prepared with wet treatment by deionized water and calcination at 500 °C. Raw and processed data on main adsorption operation parameters and adsorbent characterization were reported. Also, adsorption isotherm, adsorption kinetics; and thermodynamic models for direct red 28 dye (DR28) removal mechanism on to the raw and calcined EC sludge adsorbents were reported. Instrumental analysis, such as Fourier Transformation infrared spectrometer (FTIR) and Ultraviolet/Visible (UV/Vis) spectroscopy were used for adsorbent characterization and dye absorbance measurement before and after adsorption respectively. UV-Visible spectrometer was used throughout the batch experiment. The effect of adsorption temperature (25 ± 2 °C (ambient), 40 °C, 60 °C and 80 °C), pH (2, 4, 6, 8 and 10), initial dye concentration (20, 40, 60 and 80 mg/L), contact time (10, 20, 40, 60, 80 and 100 min) and adsorbent dosage (0.1, 0.5, 1, 1.5, 2 g/100ml) were examined. For EC sludge adsorbent characteristics, FTIR analysis data is provided as raw and processed data before and after dye adsorption for both raw and calcined EC adsorbent. UV-Vis spectral analysis before and after dye removal with a pH range of 2-10 and batch adsorption experimental data records such as initial dye concentration, solution pH, temperature, adsorbent dosage and mixing time are reported.

摘要

这项工作报道了直接红28染料在从纺织废水处理厂收集的未经煅烧和煅烧后的电凝聚(EC)污泥吸附剂上的吸附情况。EC污泥吸附剂通过用去离子水进行湿法处理并在500℃下煅烧来制备。报告了主要吸附操作参数和吸附剂表征的原始数据及处理后的数据。此外,还报道了直接红28染料(DR28)在未经煅烧和煅烧后的EC污泥吸附剂上的吸附等温线、吸附动力学以及去除机理的热力学模型。分别使用傅里叶变换红外光谱仪(FTIR)和紫外/可见(UV/Vis)光谱仪等仪器分析对吸附剂进行表征以及在吸附前后测量染料吸光度。在整个间歇实验中使用紫外可见光谱仪。考察了吸附温度(25±2℃(环境温度)、40℃、60℃和80℃)、pH值(2、4、6、8和10)、初始染料浓度(20、40、60和80mg/L)、接触时间(10、20、40、60、80和100分钟)以及吸附剂用量(0.1、0.5、1、1.5、2g/100ml)的影响。对于EC污泥吸附剂的特性,提供了未经煅烧和煅烧后的EC吸附剂在染料吸附前后的FTIR分析原始数据及处理后的数据。报道了在pH值范围为2 - 10时染料去除前后的紫外可见光谱分析以及间歇吸附实验数据记录,如初始染料浓度、溶液pH值、温度、吸附剂用量和混合时间。

https://cdn.ncbi.nlm.nih.gov/pmc/blobs/80c4/6909148/8aa45cdd3016/gr5.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/80c4/6909148/9bff6c7364b1/gr1.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/80c4/6909148/b40155a9882c/gr2.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/80c4/6909148/8e2a20b309a1/gr3.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/80c4/6909148/739c5de4fbe9/gr4.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/80c4/6909148/8aa45cdd3016/gr5.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/80c4/6909148/9bff6c7364b1/gr1.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/80c4/6909148/b40155a9882c/gr2.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/80c4/6909148/8e2a20b309a1/gr3.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/80c4/6909148/739c5de4fbe9/gr4.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/80c4/6909148/8aa45cdd3016/gr5.jpg

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