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Extended Abstract

Biopolymeric-Hydrothermal Carbon Beads for Decontamination of Polluted Waters †

by
Anca-Andreea Turcanu
1,
Stefan-Ovidiu Dima
2,*,
Maria Rapa
1,
Radu-Claudiu Fierascu
2,
Cristian-Andi Nicolae
2 and
Marius Ghiurea
2
1
Politehnica University of Bucharest, Centre for Research and Eco-Metallurgical Expertise UPB-ECOMET, 313 Splaiul Independentei, 060042 Bucharest, Romania
2
National Institute for Research & Development in Chemistry and Petrochemistry—ICECHIM Bucharest, 202 Spl. Independentei, 060021 Bucharest, Romania
*
Author to whom correspondence should be addressed.
Presented at the 15th International Symposium “Priorities of Chemistry for a Sustainable Development” PRIOCHEM, Bucharest, Romania, 30th October–1st November 2019.
Proceedings 2019, 29(1), 50; https://doi.org/10.3390/proceedings2019029050
Published: 14 October 2019
(This article belongs to the Proceedings of Priorities of Chemistry for a Sustainable Development-PRIOCHEM)
In the field of water depollution, considerable attention in past years was given to bio-based and biodegradable compounds from renewable resources, generically termed “biomass” [1]. Biomass represents the sum of raw materials from which one can produce bio-substances like alginate (from brown algae), chitosan (from shellfish), starch, cellulose, and also hydrothermal carbon (HTC). Sodium alginate is an extract from the walls of brown algae cells, used in the food industry and for body care products as an emulsifier, due to its viscosity [2]. HTC can be produced from lignocellulosic biomass by hydrothermal conversion in water, catalytic or non-catalytic, under thermally generated pressure in a hermetic reactor at temperatures ranging from 140 to 280 °C and different reaction times.
A 2% alginate solution was prepared by dissolving the alginate in water at 90 °C, under vigorous stirring. HTC was produced by hydrothermal treatment of lignocellulosic biomass from corn stalks at 200 °C, for 20 h. Then, 3% HTC (Figure 1b) was added to the alginate solution and homogenized for 1 h, and the obtained mixture was loaded in an automatic syringe and dripped with 180 mL/h flow in a CaCl2 bath for ionotropic reticulation. The beads of alginate (Figure 1a) and of alginate with HTC (Figure 1c) were washed to remove Cl ions and dried afterwards in an oven at 60 °C for 24 h. The beads were characterized by means of SEM-EDS, XRD, zeta potential, and batch adsorption experiments of Mn2+, evaluated with Atomic Adsorption Spectroscopy (AAS).
For comparison, simple alginate beads were also prepared and tested in the adsorption of metal ions from synthetic water solutions. A quantity of 0.5 g beads were added in batch adsorption experiments to 40 mL aqueous solution of 1 mg/L Mn(NO3)2. Alginate-only beads presented a maximum adsorption efficiency of approximately 76% after 60 min, while the alginate/HTC beads presented a maximum adsorption efficiency of approximately 83% after 45 min.
By adding hydrothermal carbon to the alginate beads, a more efficient adsorbent was obtained for the removal of metal ions from polluted waters, Mn2+ for this case, with an increased adsorption capacity, while maintaining the biodegradability, renewability, and low cost of bioadsorbents.

Acknowledgments

This work was supported by the Romanian Ministry for Research and Innovation through the National Authority for Scientific Research (ANCS) and Executive Unit for Financing Higher Education, Research, Development and Innovation (UEFISCDI) by the means of the project PN.19.23.03.01, contract No. 23N/2019.

References

  1. Rapa, M.; Matei, E.; Turcanu, A.; Predescu, A.M.; Pantilimon, M.C.; Predescu, C. Structural, morphological and thermal analysis of some alginate/starch/dellite HPS composites for aqueous Cu(ii) removal. Cellul. Chem Technol. 2019, 53, 561–571. [Google Scholar] [CrossRef]
  2. Han, Y.Y.; Yu, M.; Wang, L.J. Physical and antimicrobial properties of sodium alginate/carboxymethyl cellulose films incorporated with cinnamon essential oil. Food Packag. Shelf. 2018, 15, 35–42. [Google Scholar] [CrossRef]
Figure 1. (a) Alginate beads; (b) Hydrothermal carbon (HTC) from corn stalks; (c) Alginate/HTC beads.
Figure 1. (a) Alginate beads; (b) Hydrothermal carbon (HTC) from corn stalks; (c) Alginate/HTC beads.
Proceedings 29 00050 g001

Share and Cite

MDPI and ACS Style

Turcanu, A.-A.; Dima, S.-O.; Rapa, M.; Fierascu, R.-C.; Nicolae, C.-A.; Ghiurea, M. Biopolymeric-Hydrothermal Carbon Beads for Decontamination of Polluted Waters. Proceedings 2019, 29, 50. https://doi.org/10.3390/proceedings2019029050

AMA Style

Turcanu A-A, Dima S-O, Rapa M, Fierascu R-C, Nicolae C-A, Ghiurea M. Biopolymeric-Hydrothermal Carbon Beads for Decontamination of Polluted Waters. Proceedings. 2019; 29(1):50. https://doi.org/10.3390/proceedings2019029050

Chicago/Turabian Style

Turcanu, Anca-Andreea, Stefan-Ovidiu Dima, Maria Rapa, Radu-Claudiu Fierascu, Cristian-Andi Nicolae, and Marius Ghiurea. 2019. "Biopolymeric-Hydrothermal Carbon Beads for Decontamination of Polluted Waters" Proceedings 29, no. 1: 50. https://doi.org/10.3390/proceedings2019029050

APA Style

Turcanu, A. -A., Dima, S. -O., Rapa, M., Fierascu, R. -C., Nicolae, C. -A., & Ghiurea, M. (2019). Biopolymeric-Hydrothermal Carbon Beads for Decontamination of Polluted Waters. Proceedings, 29(1), 50. https://doi.org/10.3390/proceedings2019029050

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