
Turning Industrial Residues into Resources: An Environmental Impact Assessment of Goethite Valorization
Andrea Di Maria, Karel Van Acker
Engineering ›› 2018, Vol. 4 ›› Issue (3) : 421-429.
Turning Industrial Residues into Resources: An Environmental Impact Assessment of Goethite Valorization
Goethite is a metals-rich residue that occurs during zinc production. The feasibility of metal recovery from goethite has been demonstrated, but is not economically viable on an industrial scale. Therefore, goethite is landfilled with considerable economic costs and environmental risks. The goal of this study is to evaluate the environmental performance of a new valorization strategy for goethite residues from zinc production, with the aims of: ① recovering the valuable zinc contained in the goethite and ② avoiding the landfilling of goethite by producing a clean byproduct. The presented goethite valorization strategy consists of a sequence of two processes: ① plasma fuming and ② inorganic polymerization of the fumed slag. Plasma fuming recovers the valuable metals by fuming the goethite. The metals-free fumed slag undergoes a process of inorganic polymerization to form inorganic polymers, that can be used as a novel building material, as an alternative to ordinary Portland cement (OPC)-based concrete. Life-cycle assessment (LCA) is used to compare the environmental performance of the inorganic polymer with the environmental performances of equivalent OPC-based concrete. The LCA results show the tradeoff between the environmental burdens of the fuming process and inorganic polymerization versus the environmental benefits of metal recovery, OPC concrete substitution, and the avoidance of goethite landfilling. The goethite-based inorganic polymers production shows better performances in several environmental impact categories, thanks to the avoided landfilling of goethite. However, in other environmental impact categories, such as global warming, the goethite valorization is strongly affected by the high-energy requirements of the plasma-fuming process, which represent the environmental hotspots of the proposed goethite recycling scheme. The key elements toward the sustainability of goethite valorization have been identified, and include the use of a clean electric mix, more effective control of the fumed gas emissions, and a reduced use of fumed slag through increased efficiency of the inorganic polymerization process.
Goethite recycling / Slag plasma fuming / Inorganic polymerization / Life cycle assessment
[1] |
Van Genderen E., Wildnauer M., Santero N., Sidi N.. A global life cycle assessment for primary zinc production. Int J Life Cycle Assess. 2016; 21(11): 1580-1593.
|
[2] |
Ismael M.R.C., Carvalho J.M.R.. Iron recovery from sulphate leach liquors in zinc hydrometallurgy. Miner Eng. 2003; 16(1): 31-39.
|
[3] |
Welham N., Malatt K., Vukcevic S.. The stability of iron phases presently used for disposal from metallurgical systems—a review. Miner Eng. 2000; 13(8): 911-931.
|
[4] |
Piga L., Stoppa L., Massidda R.. Recycling of industrial goethite wastes by thermal treatment. Resour Conserv Recycling. 1995; 14(1): 11-20.
|
[5] |
Pelino M., Cantalini C., Abbruzzese C., Plescia P.. Treatment and recycling of goethite waste arising from the hydrometallurgy of zinc. Hydrometallurgy. 1996; 40(1–2): 25-35.
|
[6] |
Hoang J., Reuter M.A., Matusewicz R., Hughes S., Piret N.. Top submerged lance direct zinc smelting. Hydrometallurgy. 2009; 22(9–10): 742-751.
|
[7] |
Verscheure K., Van Camp M., Blanpain B., Wollants P., Hayes P., Jak E.. Continuous fuming of zinc-bearing residues: part II. The submerged-plasma zinc-fuming process. Metall Mater Trans B. 2007; 38(1): 21-33.
|
[8] |
Verscheure K., Van Camp M., Blanpain B., Wollants P., Hayes P., Jak E.. Continuous fuming of zinc-bearing residues: part I. Model development. Metall Mater Trans B. 2007; 38(1): 13-20.
|
[9] |
Alemán J.V., Chadwick A.V., He J., Hess M., Horie K., Jones R.G.,
|
[10] |
Van Deventer J.S.J., Provis J.L., Duxson P., Brice D.G.. Chemical research and climate change as drivers in the commercial adoption of alkali activated materials. Waste Biomass Valoriz. 2010; 1(1): 145-155.
|
[11] |
Iacobescu R.I., Angelopoulos G.N., Jones P.T., Blanpain B., Pontikes Y.. Ladle metallurgy stainless steel slag as a raw material in ordinary portland cement production: a possibility for industrial symbiosis. J Clean Prod. 2016; 112(Pt 1): 872-881.
|
[12] |
Oh J.E., Monteiro P.J.M., Jun S.S., Choi S., Clark S.M.. The evolution of strength and crystalline phases for alkali-activated ground blast furnace slag and fly ash-based geopolymers. Cement Concr Res. 2010; 40(2): 189-196.
|
[13] |
Setién J., Hernández D., González J.J.. Characterization of ladle furnace basic slag for use as a construction material. Constr Build Mater. 2009; 23(5): 1788-1794.
|
[14] |
Shi C., Qian J.. High performance cementing materials from industrial slags—a review. Resour Conserv Recycling. 2000; 29(3): 195-207.
|
[15] |
Heijungs R., Guinée J.B.. Allocation and “what-if” scenarios in life cycle assessment of waste management systems. Waste Manage. 2007; 27(8): 997-1005.
|
[16] |
Rebitzer G., Ekvall T., Frischknecht R., Hunkeler D., Norris G., Rydberg T.,
|
[17] |
ISO 14040:2006. Environmental management—life cycle assessment—principles and frameworks. ISO standard.
|
[18] |
Doka G.. Life cycle inventories of waste treatment services.
|
[19] |
Richards G.G., Brimacombe J.K., Toop G.W.. Kinetics of the zinc slag-fuming process: part I. Industrial measurements. Metall Trans B. 1985; 16(3): 513-527.
|
[20] |
Abdel-latif M.A.. Fundamentals of zinc recovery from metallurgical wastes in the Enviroplas process. Miner Eng. 2002; 15(11 Suppl 1): 945-952.
|
[21] |
Electricity [Internet]. Oslo: Statistics Norway; c2018 [cited 2017 Jul 17]. Available from: https://www.ssb.no/en/energi-og-industri/statistikker/elektrisitet.
|
[22] |
Classen M., Althaus H.J., Blaser S., Doka G., Jungbluth N., Tuchschmid M.. Life cycle inventories of metals.
|
[23] |
Generating facilities [Internet]. New York: Elia; c2018 [cited 2017 Jul 17]. Available from: http://www.elia.be/en/grid-data/power-generation/generating-facilities.
|
[24] |
Machiels L., Arnout L., Jones P.T., Blanpain B., Pontikes Y.. Inorganic polymer cement from Fe-silicate glasses: varying the activating solution to glass ratio. Waste Biomass Valoriz. 2014; 5(3): 411-428.
|
[25] |
Peys A., Peeters M., Katsiki A., Pontikes Y.. Performance and durability of Fe-rich inorganic polymer composites with basalt fibers. In: Proceedings of the 41st International Conference and Expo on Advanced Ceramics and Composites; 2017 Jan 22–27; Daytona Beach, FL, USA. 2017.
|
[26] |
Fédération belge Béton Cellulaire. Le Béton Cellulaire: Materiau d’Avenir. Bruxelles: Fédération belge Béton Cellulaire; 2009. French.
|
[27] |
Kellenberger D., Althaus H.J., Jungbluth N., Künniger T.. Life cycle inventories of building products.
|
[28] |
Benetto E., Rousseaux P., Blondin J.. Life cycle assessment of coal by-products based electric power production scenarios. Fuel. 2004; 83(7–8): 957-970.
|
[29] |
Belboom S., Digneffe J.M., Renzoni R., Germain A., Léonard A.. Comparing technologies for municipal solid waste management using life cycle assessment methodology: a Belgian case study. Int J Life Cycle Assess. 2013; 18(8): 1513-1523.
|
[30] |
Goedkoop M., Heijungs R., Huijbregts M., De Schryver A., Struijs J., Van Zelm R.. A life cycle impact assessment method which comprises harmonised category indicators at the midpoint and the endpoint level.
|
/
〈 |
|
〉 |