Literature DB >> 28879215

Synthesis of adsorbent from Tamarix hispida and modified by lanthanum metal for fluoride ions removal from wastewater: Adsorbent characteristics and real wastewater treatment data.

Nasim Habibi1, Parham Rouhi1, Bahman Ramavandi2.   

Abstract

This data article describes a facile method for production of an adsorbent from Tamarix hispida wasted wood and modified by lanthanum metal for fluoride ions removal from wastewater. The main characteristics of the adsorbent consist of BET surface area, functional groups, and elemental analysis is presented. The data for attenuating the pollutants from a real wastewater treatment which was provided from a glass factory is also represented. More than 90% of fluoride content of the real wastewater was treated by the adsorbent. Generally, these data would be informative for extend research aim to industrial wastewater treatment and those who work in the wastewater treatment plants.

Entities:  

Keywords:  Adsorbent; Fluoride ions; Glass factory; Tamarix hispida; lanthanum metal

Year:  2017        PMID: 28879215      PMCID: PMC5575414          DOI: 10.1016/j.dib.2017.07.010

Source DB:  PubMed          Journal:  Data Brief        ISSN: 2352-3409


Specifications Table Tamirex hispida biochar was prepared from T. hispida wood at 105 °C during 24 h. The dried wood chips were amended by lanthanum metal by pyrolyzed method at 350 °C for 3.5 h. The final product was used for fluoride removal from a glass factory wastewater. Value of the data A facile method for modification of the biochar Tamarix hispida by lanthanum chloride is provided in this dataset compare to other biomass/adsorbents reported in the literature [1], [2], [3]. The data may be useful for future researches that aim to glass factory wastewater treatment. This data allows wastewater treatment plants managers and engineers to extend the practical usage of the adsorbent.

Data

The data regarding to potential of the adsorbent prepared from T. hispida and modified by lanthanum chloride for treating of the glass factory wastewater are presented in Table 1. The information about main characteristics of the adsorbent including FTIR spectrum, SEM image, N2 adsorption–desorption isotherm, and EDS spectrum are also shown in Fig. 1, Fig. 2, Fig. 3, Fig. 4.
Table 1

The quality of glass factory wastewater before and after treatment by the prepared adsorbent.

Wastewater qualityConcentration before treatment (mg/l)Concentration after treatment (mg/l)
F232
NO36944
Cl212.554
SO4124120
Total hardness458438
TDS1060905
BOD5285273.4
COD564555
pH7.98.1
Fig. 1

FTIR spectrum of the adsorbent from Tamarix hispida and modified by lanthanum chloride.

Fig. 2

SEM image of the adsorbent from Tamarix hispida and modified by lanthanum metal.

Fig. 3

N2 adsorption–desorption isotherm of adsorbent prepared from Tamarix hispida and modified by lanthanum metal.

Fig. 4

The EDS spectrum of the adsorbent from Tamarix hispida and modified by lanthanum metal.

FTIR spectrum of the adsorbent from Tamarix hispida and modified by lanthanum chloride. SEM image of the adsorbent from Tamarix hispida and modified by lanthanum metal. N2 adsorption–desorption isotherm of adsorbent prepared from Tamarix hispida and modified by lanthanum metal. The EDS spectrum of the adsorbent from Tamarix hispida and modified by lanthanum metal. The quality of glass factory wastewater before and after treatment by the prepared adsorbent.

Experimental design, materials and methods

Adsorbent preparation

Dried T. hispida wood which was collected from surrounding area of Bushehr city was applied the initial material for the adsorbent providing. The method for production of the adsorbent from T. hispida was similar to methods provided in our previous studies [4], [5], [6]. The T. hispida wood was initially debarked and then chopped up into small pieces (1–3 cm). The wood chips were put in an oven (Shimaz Co., Iran) with 105 °C during 24 h. The dried chips were then milled and the achieved particles were amended by lanthanum chloride according to methods in the literature [7], [8], [9]. Briefly, 10 g of the particles produced in the previous stage and 0.27 g of lanthanum was poured in a 250 ml flasks and the amount of 150 ml double distilled water with pH of 12 was added to the flasks. The mixture was then agitated by a shaker incubator (Parsazma Co., Iran) at 150 rpm for 24 h. After this time, the solution was filtered by 0.42µ-Whatman filters. The particles trapped on the filter surface was dried at 105 °C during 24 h and then pyrolyzed at 350 °C for 3.5 h in the absence of oxygen. After that, the pyrolyzed pieces were milled and finally passed through 40 and 120 mesh ASTM sieves to obtain powder with diameters of 0.125–0.4 mm and used as adsorbent in the experiments.

Real wastewater sampling

A bulk of glass factory wastewater was provided from a factory around Shiraz city, Iran. This wastewater was treated by the prepared adsorbent. For this purpose, 150 ml wastewater and 10 g/l adsorbent was poured in 250 ml flasks and after a 60 min contact time the solutions were filtered. The original pH of the wastewater was changed during the experiment. The physic-chemical properties of the filtrate were analyzed (see Table 1). This test was repeated three times and average values were stated.

Analysis

The BET specific surface area the adsorbent was carried out by the N2 adsorption/desorption method at −196 °C using a Micromeritics model TriStar II-3020 instrument. For this purpose, the adsorbent samples were degassed for around 24 h at environment with temperature of 250 °C to remove any adsorbed contaminants or water content that might have been exist on the surface. Micrograph of pristine adsorbent was obtained by scanning electron microscopy (SEM, Sirion from FEI). For determination the functional groups on the adsorbent surface a Fourier transform infrared (FTIR) spectrometer (NICOLET 5700-FTIR) was applied. The elemental composition of the adsorbent provided from T. hispida and modified by lanthanum chloride was achieved by energy dispersive spectroscopy (EDS, Horiba EX-250, Japan). The fluoride concentration of the real wastewater sample was analyzed by an expandable ion analysis (Orion EA 940 ion meter) according to the method presented in the Standard Methods for the Examination of Water and Wastewater [10].
Subject areaChemical engineering
More specific subject areaEnvironmental technology
Type of dataTable and image
How data was acquiredThe BET surface area (Micromeritics model TriStar II-3020), scanning electron microscopy (SEM, Sirion from FEI), Fourier transform infrared (FTIR, NICOLET 5700-FTIR), and energy dispersive spectroscopy (EDS, Horiba EX-250, Japan) was applied to analyze the characteristics of the adsorbent. The fluoride ion concentration was measured by an expandable ion analysis (Orion EA 940 ion meter).
Data formatAnalyzed
Experimental factors

Tamirex hispida biochar was prepared from T. hispida wood at 105 °C during 24 h.

The dried wood chips were amended by lanthanum metal by pyrolyzed method at 350 °C for 3.5 h.

The final product was used for fluoride removal from a glass factory wastewater.

Experimental featuresSynthesis Tamarix hispida biochar and modified by lanthanum metal for fluoride removal
Data source locationBushehr, Iran
Data accessibilityData provided with the article
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