Research on co-disposal and utilization of ferrous packaging containers contaminated with hazardous wastes by steel converter
Sustainable Environment Research volume 32, Article number: 40 (2022)
The disposal of waste oil, paint and coating barrels (WOPCBs) after use is an ongoing social and environmental problem. In this paper, a novel technological scheme using steel converter co-processing is proposed for the safe disposal and resource utilization of WOPCBs. The scheme is mainly composed of WOPCBs pretreatment and converter disposal, focusing on the impact of converter co-processing WOPCBs on the environment and production process. Compared to the traditional technology, the scheme presented takes full advantages of the production process and environmental protection facilities of steel converter, and has many advantages, such as a large disposal capacity, low cost, highly efficient and environmentally friendly. The industrial trials results show that after adding 180–540 kg WOPCBs to each furnace load (nominal capacity 250 t), the converter operation is safe and controllable, and all the pollutant emission indicators generated in the process meet the Chinese national standards. In addition, WOPCBs are suitable to be used as a supplementary material for scrap steel. Therefore, this study provides important insights for sustainable resource utilization from WOPCBs.
Wuhan is the largest industrial city in central China, dominating in industries such as shipbuilding, automobile, petrochemical, and steel. In these industrial processes, a large number of waste iron packaging containers contaminated with waste oil, paint and coating barrels (WOPCBs) and other hazardous materials, are produced annually. According to the Chinese “National Hazardous Waste List”, WOPCBs are recognized as HW49 (900–041-49, National Hazardous Wastes Catalogue of China, 2016 version) hazardous waste and, therefore, improper disposal poses a great threat to environmental systems [1, 2]. For example, the disposal of the hazardous WOPCBs generates oil containing wastewater, which must be adequately treated prior to discharge into the receiving water body to avoid negative effects such as toxicity to aquatic organisms, reduced oxygen penetration and deterioration of natural photosynthetic activity.
Generally, the disposal of WOPCBs should conform to the principles of safety, resource utilization, and simplification. At present, there are two main methods for industrial disposal of WOPCBs, the first is chemical cleaning and reuse, the second is oxygen cutting, then followed by high-temperature alkali washing, or simple incineration . Both methods have their advantages, but they also have their fatal defects. The wet cleaning process can realize the recycling of resources. However, this method will discharge a large amount of cleaning waste liquid and strong alkali containing highly toxic organic substances. Existing incineration process is characterized by low incineration temperature (500–1000 °C), small disposal capacity (200–3000 t yr− 1), scattered distribution, and imperfect pollutant control measures, resulting in serious pollution to the surrounding atmospheric environment [4,5,6]. In contrast, pyrometallurgical processes have the potential to reduce environmental impact, are suitable for large scale applications, and have low capital cost . Chen  used a vertical melting pyrolysis furnace process to dispose of industrial slag steel and WOPCBs, using high-temperature melting treatment and slag iron separation. This method was shown to effectively recycle solid waste, generating good economic benefits.
Due to the comprehensive functions of steel plants (i.e., broaden-manufacturing function of steel product, function of energy conversion and function of waste recycling), much research has focused on exploring new ways to recycle metallurgic solid waste, based on the guidelines for energy conservation, emissions reduction, circular economy development and ecological protection [9,10,11,12].
Inspired by the application of co-processing scrap in converter steelmaking, this paper intends to use the converter in steelmaking plant to dispose WOPCBs. In this study, industrial trials for co-disposing WOPCBs through well-developed high-temperature process were first conducted using the converter in steelmaking plant. The large-scale converter had a large co-disposal capacity, which was operated at high temperature ranges from 1600 to 1700 °C during the smelting process. In this paper, we designed a novel process scheme for comprehensive utilization and safe disposal of WOPCBs. The scheme not only realized the comprehensive recovery of valuable iron resource from WOPCBs, but also avoided the production of secondary pollution such as strong alkali containing oily wastewater and toxic gas. Moreover, the treatment cost was greatly reduced due to the decomposition and exothermic reaction of organic compounds in WOPCBs, combination of this system with a highly effective flue gas treatment facility and utilization of iron resources. Therefore, a win-win goal of simultaneously obtaining valuable iron resources and minimizing their impact on the environment can be achieved, which also makes the steel plant a potentially important sustainable and low ecological impact industry.
WOPCBs were collected from WISCO Metal Resources Co., China. After manual oil cleaning and liquid leaching, these WOPCBs and packaging materials were sent to the packing machine for flattening and compression into blocks. Steel slag, dust, mud cake and washing water of converter gas used in this work were collected from Wuhan Iron and Steel Co. (WISCO, China). All the solvents were of analytical grade, unless otherwise stated. The solvent such as H2SO4 (~ 98%), HNO3 (~ 68%) were purchased from Shanghai Aladdin Biochemical Technology Co., China. Deionized water was obtained by a water purification system (Milli-Q Academic, Merck Millipore, Darmstadt, Germany), with the electrical conductivity less than 0.055 μS cm− 1. Other chemical reagents (Sinopharm Chemical Reagent, China) were of analytical reagent grade.
2.2 Analytical methods
The heavy metals were leached from steel slag, dust and mud cake following the Chinese standard procedure HJ/T299–2007. The leachates were filtered with a 0.6–0.8 μm micropore membrane. The leachates were digested in a mixture of H2SO4 and HNO3. The concentrations of heavy metals and element analysis of P, Si and Mn in samples were analyzed by Inductively Coupled Plasma Optical Emission Spectroscopy (ICP-OES; Thermo Fisher Scientific, ICAP 6500, USA). Moreover, the chromium (VI) concentrations in these leachates were measured by using the standard “Water Quality - Determination of Chromium (VI) – 1,5-Diphenylcarbohydrazide Spectrophotometric Method” (GB7467–87, China). Elemental analyzer (Elementar/UNICUBE, Germany) was used for quantitative analysis and determination of C, H, N, S, O elements in organic solids, highly volatile and sensitive substances. Volatile organic compounds (VOCs) and dioxins in flue gas were analyzed by HP 6890 Gas Chromatography (GC) equipped with HP5975B Mass Spectroscopy (MS) Detector (Agilent, USA). All the analyses were performed in duplicate.
2.3 Disposal process
The procedures of co-disposal of WOPCBs by converter steelmaking had been tested in a commercial (nominal capacity 250 t) basic oxygen furnace, No. 3 steelmaking plant at WISCO, Wuhan, China. According to the steelmaking production plan, after cleaning, extrusion and packing the WOPCBs were transported and used as a raw material in the scrap steel room in No. 3 steelmaking plant of WISCO. It was preliminarily determined that the load of WOPCBs added was 180 kg per furnace, accounting for 0.072% of the total capacity. If the addition of 180 kg per furnace load was confirmed to present no safety problems, the adding amount could be adjusted to 180–540 kg per furnace load. During the test period, the concentrations of nonmethane hydrocarbons (NMHC), VOCs and dioxins in the converter flue gas and the content of heavy metals in the scrap steel, gas washing water and mud cake, were monitored. The experimental process was carried out continuously for 90 d.
2.4 Disposal method
The collected and stacked WOPCBs in the factory were weighed and transported by truck to the WOPCBs packaging operation area of WISCO plant. It should be noted that the residue in WOPCBs must be less than 5 wt% of the total mass. After degreasing and cleaning, these WOPCBs and packaging materials were sent to the packing machine for flattening and compression into blocks. The final products were transported to the product stacking area via a conveyor belt and fork-lift truck. The liquid generated during the compression process was collected and transported to the leachate storage area.
A piece of pressed block of WOPCBs was about 180 kg and the total amount of pressed block of WOPCBs was approximately 3.24 t. Generally, 1–3 WOPCBs pressed blocks were first moved into the converter hopper by the magnetic crane, and then poured into the converter ladle together with the scrap in the hopper for smelting. Calculation of the variation in the main raw material content and flux in the test furnace efficiency were performed. In order to prevent excessive dust when pouring melted iron, the test furnace was shaken 4 times at a ± 50 degree angle after the addition of WOPCBs pressed blocks and scrap steel. The disposal process should be immediately stopped if any spray explosion occurred. Under the high temperature and strong oxidation conditions of the converter system, the inorganic components in the WOPCBs are melted into molten iron or steel slag, and the organic components in the WOPCBs are decomposed into flue gas, which is sent to the converter exhaust gas purification and recovery system. The technical process of comprehensive utilization and disposal of WOPCBs is shown in Fig. 1 with the practical disposal process shown in Fig. 2.
3 Results and discussion
3.1 Principle of utilization and disposal of WOPCBs
The purpose of converter systems in steelmaking is to produce steel with optimal physical, chemical and mechanical properties, by oxidizing carbon, silicon, manganese, and other impurities in pig iron under pure oxygen conditions. Converter systems complete the process using the physical heat generated from molten iron and the chemical heat formed from the reaction of inner components. Hot metal, scrap steel and ferroalloys are the main raw materials in this process. The melting point temperature of pig iron ranges from 1100 to 1250 °C, while the temperature of molten steel ranges from 1450 to 1700 °C . Oxygen is lanced to the furnace to oxidize the impurities in the hot metal. After the blowing, smelting temperatures can reach levels of up to 1700 °C, the impurities (C, Si, S, etc.) present in steel is utilized in reducing the iron oxide contained in the WOPCBs and melting as Fe or slag; thereafter, metal and slag are collected separately and the iron of WOPCBs provides an effective supplement to scrap steel. The remaining oil in WOPCBs is fully decomposed, the emissions from this process entering the converter off gas purification system through the dust removal system and finally being recovered by gas holder or discharged via a chimney. The possible chemical reactions during disposal process are shown in Fig. 3.
3.2 Analysis of influence on steelmaking production
Three pieces of WOPCBs (~ 540 kg per batch) pressed block scrap steel were added, the converter was shaken 4 times at ±50 degree angle. The flame and dust concentration at the furnace mouth were observed to be normal. Two minutes later, iron mixing was initiated for a duration of 4 min. The smoke and flame levels at the furnace mouth were increased slightly, although no splashing or shooting was observed during the process. Blowing was performed from the 7 to 16 min, with no splashing or abnormal noises observed in the furnace. At the 31 min, the process was returned to normal functioning and steel was discharged. The chemical components of hot metal are presented in the Table 1.
These results illustrate that it is feasible to use scrap steel from WOPCBs pressed blocks as the test raw material. Compared with the disposal process for ordinary scrap steel, the modified scrap steel disposal process required 4-cycles of shaking and prolonging the production cycle time. According to the presented data, the WOPCBs pressing block scrap steel could be used in ladle furnace desulfurization steel. There were no obvious differences observed in the converter blowing process and both production and safety conditions could be controlled, which did not affect the quality of steel products and allowed control of the sulfur content of molten steel.
3.3 Impact on the environment
3.3.1 Flue gas purification, recovery and treatment
For the converter off-gas generated in the converter refining process, the dedusting technique of oxygen converter gas recovery is used. Dust is then scrubbed out of the off-gas from the process through wet venturi scrubber systems before the off-gas is suitable to either collect for gas recovery or to flare to the atmosphere. The flue gas escaping from the converter smelting process, as well as the flue gas produced by slag stripping and desulfurization in ladle argon blowing station, adopts the type of smoke hood in front of the furnace to collect, and then sends it to the bag filter for purification, and then discharges it to the atmosphere through the exhaust pipe. There is a general concern about problems related to the odor, toxic gases and particles during the WOPCBs disposal. The rigorous tests of off-gas generated in the process have been detected by a third party, and VOCs, dioxins, benzene, toluene, xylene, NMHC and other organic pollutants were analyzed by HP 6890 GC equipped with HP5975B MS detector.
Monitoring results showed that the concentrations of benzene, toluene, xylene, NMHC, VOCs and dioxins in emissions were slightly increased from 0.024, 0.21, 0.024, 0.44, 0.84 mg m− 3 and 0.032 (ng-TEQ m− 3) prior to testing, to 0.33, 0.38, 0.046, 2.22, 2.97 mg m− 3 and 0.039 ng-TEQ m− 3 during testing, as indicated in Table 2. However, the concentrations of all pollutants met the limits of Chinese Standards “Integrated Emission Standard of Air Pollutants” in China (GB16297–1996)  and the “Emission Standard of Air Pollutants for Steel Smelt Industry” in China (GB28664–2012) . It should be pointed out that it is unnecessary for much concern about the increase of dioxin concentration when the WOPCBs disposal process. The boiling points of the dioxins ranged between 421 and 447 °C and the decomposition temperature was above 800 °C . A key characteristic of steelmaking converter systems was that the instantaneous temperature of added WOPCBs was over 1300 °C, while the smelting temperature can reach above 1600 °C. Therefore, the temperature conditions required for the formation of dioxins are not formed during the smelting process. Subsequently, the converter off-gas was cooled and atomized efficiently to make the flue gas rapidly cool from above 1000 to 170–200 °C. This ensured that dioxins can be completely decomposed and would not be generated again during cooling [17, 18].
3.3.2 Circulating cooling water treatment and reuse
The wastewater mainly comes from the water for primary converter off-gas cooling and dust removal, which is recycled and not discharged. The process flow of circulating wastewater treatment system can be described as: firstly, the backwater of circulating water entered the coarse particle separator through the elevated flow tank, then after separating the coarse particles, the supernatant was pumped into the distribution tank, and then coagulated sedimentation in radial-flow sedimentation tank. At last, the clear water was cooled to room temperature and sent back to the circulating water system for reuse. ICP-MS analysis in circulating water showed that the concentrations of seven heavy metals such as Hg, Cd, Ni, Pb, Cr, As and Cu in circulating water were found to be close to the limit of detection, and all the concentrations of heavy metals from washing water could meet the corresponding standard requirements of the “Discharge Standard of Water Pollutants for Iron and Steel industry of China (GB13456-2012)”. The results are shown in Table 3.
3.3.3 Solid waste treatment and utilization
The main solid waste produced in the disposal process of WOPCBs was steel slag, mud cake produced by circulating water treatment system and dust collected by converter off-gas treatment. Ministry of Ecology and Environment of China has developed a regulatory definition and process that identifies specific substances known to be hazardous and provides objective criteria for “Identification Standard for Hazardous Wastes-Identification for Extraction Procedure Toxicity” (GB 5085.3–2007). The sequential leaching test were performed to investigate the leachability of heavy metals from the original steel slag, mud cake and dust in aqueous solution according to the Chinese Standard Procedure HJ/T299–2007. The leaching results for these heavy metals are shown in Table 4.
The results in Table 4 indicate that the concentrations of heavy metal leaching solution of all metallurgical solid wastes were far lower than the standard limits of Chinese Standards (GB5085.3–2007). This means that all metallurgical solid wastes can generally be categorized as a non-hazardous by-product from the steel industry and could potentially be used directly in environmental applications. Currently, mud cake and dust were used as raw materials of sintering, and steel slag was used as cement aggregate [11, 19]. WOPCBs contained a small quantity of inorganic substances, mainly Ca and Si compounds and trace amounts of heavy metals, such as Hg, Cd, Ni, Pb, Cr, As, Zn, and other heavy metals or other harmful metal elements, which can be eventually reacted under high temperatures with strong liming effects to form a very stable silicate which eventually combined with the steel slag [20, 21]. Steel slag is a residual product from the steel smelting process, consisting of oxides such as calcium oxide, silicon oxide, and iron oxide. It should be noted that the precipitation of calcium carbonate on the surface of the steel slag particles blocked the liquid phase from reaching the surface of the soluble mineral phase, and this action caused a decrease in the dissolution rate of the mineral phases, affecting the leachability of heavy metal ions in the encapsulated crystal phase. Because of the stable properties of silicates, their use did not lead to environmental concern . Meanwhile, Silicates and steel slag can be comprehensively reused as a building material such as cement.
3.4 Material balance
Materials balance principle is the balance of the materials between inputs, desirable outputs and undesirable outputs in the production progress . The process diagram (see Fig. 1) shows the inputs and outputs of steel converter. The mass balance of the process is presented in the Table 5. It is worth noting that this calculation does not take into account the withdrawal of molten steel samples, losses of hot metal splash and flue gas leakages.
Table 5 shows that the molten steel would have increase 8.5%, this is attributed to the addition of scrap steel, ferroalloys and WOPCBs in the steelmaking process. As usual, the proportion of scrap steel added is 16.5–18.8%, and the increase proportion of molten steel is within the normal range (i.e., WOPCBs as scrap steel substitutes). This can be explained in two ways: firstly, most of the coating residue of WOPCBs is formed of organic substances (below 10 wt%), which was reduced in the smelting process to a coating residue proportion of less than 0.004% . In the steelmaking converter, all organic substances are completely decomposed as volatile gases, such as carbon monoxide, carbon dioxide, sulfur dioxide, vapour, and various other gases under the high temperature (above 1500 °C) and oxidation atmosphere, which does not affect the safety and quality of the products smelted by the converter . Secondly, the inorganic substances components in the WOPCBs, such as silicon, manganese, phosphorus, and sulfur, etc., react with lime at high temperatures to form very stable silicate materials, which becomes part of the steel slag. Ferrite in the WOPCBs also enters the molten iron in the converter and becomes a partial substitute of scrap steel .
3.5 Economic benefits of the treatment of WOPCBs in converter steelmaking
The operational costs for the process tested at industrial trials were estimated and results summarized in Table 6. Based on the results of the industrial trials and the design of the integrated treatment flow sheet, the key operation factors for the developed process were estimated and an economic feasibility study was carried out. The operating cost is mainly composed of four parts: materials, fuel and power, labor service and depreciation and maintenance. Calculation of the co-processing cost is based on a WOPCBs capacity of 5 kt yr− 1. As shown in Table 6, the total cost per ton for this novel technology is 48% lower than that of the traditional WOPCBs treatment and disposal methods ($126.31 vs. $242.85 USD) . Furthermore, the WOPCBs can be sold as steel products for steel scrap substitutes and earn an extra profit (about $230 USD t− 1 WOPCBs obtained as end product). Therefore, we can conclude that this proposed novel technology is promising from an economic perspective.
The novel technology of co-disposal of WOPCBs by converter steelmaking carried out for this study is proven to be successful and feasible. The industrial trial results indicate that co-disposal of WOPCBs by converter steelmaking is more efficient than the traditional chemical clean process, and reduce treatment costs per ton by about 48%. With the addition of 180–540 kg of WOPCB per furnace load, both the steel product quality and the production process are proven to be safe and controllable. This technology is economical and environmental friendly and can solve WOPCBs disposal problems, and recover WOPCBs as steel scrap substitutes. Flue gas, wastewater generated in this process after treatment can meet related standards of China, and the leachability of heavy metals in metallurgical solid wastes is far lower than the standard threshold. Therefore, this novel technology can be a total solution for the emerging WOPCBs disposal problem with resource utilization, environmental protection and security concern. Meanwhile, due to the lack of information on WOPCBs disposal in the literatures, this study can be used as a reference for future research work on this topic. Further work is necessary to address more detailed study for the dioxin distribution characteristics in flue gas along the purification system and the migration and diffusion mechanism of heavy metals in this process.
Availability of data and materials
All data generated or analyzed during this study are presented within the submitted manuscript.
Guo JL, Bao YP, Wang M. Steel slag in China: treatment, recycling, and management. Waste Manage. 2018;78:318–30.
Sadeghi N, Alamdari EK. An innovative method for recycling vanadium and valuable materials from high-lime steel making slag disposal. Int J Environ Sci Te. 2021;18:2597–606.
Zou EP, Yong Y, Wu Y, Fu Q, Ma FJ, Huang X. Study of recycling disposal process and disposal costs of the paint barrel. Sichuan Environ. 2017;36:13–6. https://doi.org/10.14034/j.cnki.schj.2017.s1.003. [in Chinese].
Kruskopf A, Holappa L. Scrap melting model for steel converter founded on interfacial solid/liquid phenomena. Metall Res Technol. 2018;115:201.
Kruskopf A. A model for scrap melting in steel converter. Metall Mater Trans B. 2015;46:1195–206.
De Gisi S, Romaniello L, Dalessandro M, Todaro F, Notarnicola M. Recovery of iron rich residues from integrated steel making process by hydrated lime/molasses pressurised cold agglomeration. J Clean Prod. 2019;233:830–40.
Khanna R, Konyukhov YV, Ikram-ul-haq M, Burmistrov I, Cayumil R, Belov VA, et al. An innovative route for valorising iron and aluminium oxide rich industrial wastes: recovery of multiple metals. J Environ Manage. 2021;295:113035.
Chen M. Application of melting pyrolysis technology in solid waste treatment of iron and steel industry. China Metall. 2019;29:66–9. https://doi.org/10.13228/j.boyuan.issn1006-9356.20180410. [in Chinese].
Maruoka N, Mizuochi T, Purwanto H, Akiyama T. Feasibility study for recovering waste heat in the steelmaking industry using a chemical recuperator. ISIJ Int. 2004;44:257–62.
Dippenaar R. Industrial uses of slag (the use and re-use of iron and steelmaking slags). Ironmak Steelmak. 2005;32:35–46.
Jiang Y, Ling TC, Shi CJ, Pan SY. Characteristics of steel slags and their use in cement and concrete – a review. Resour Conserv Recy. 2018;136:187–97.
Mohamed A, Jacek G, Marian N, Jan P, Malgorzata G. Recycle option for metallurgical sludge waste as a partial replacement for natural sand in mortars containing CSA cement to save the environment and natural resources. J Hazard Mater. 2020;398:123101.
Han BC, Wei GS, Zhu R, Wu WH, Jiang JJ, Feng C, et al. Utilization of carbon dioxide injection in BOF-RH steelmaking process. J Co2 Util. 2019;34:53–62.
MEE. Standard for Pollution Control on the Municipal Solid Waste Incineration (GB 18485-2014). Beijing: Ministry of Ecology and Environment; 2014. [in Chinese]. https://www.mee.gov.cn/ywgz/fgbz/bz/bzwb/gthw/gtfwwrkzbz/201405/t20140530_276307.shtml.
MEE. Emission Standard of Air Pollutants for Steel Smelt Industry (GB 28664-2012). Beijing: Ministry of Ecology and Environment; 2014 [in Chinese]. https://www.mee.gov.cn/ywgz/fgbz/bz/bzwb/dqhjbh/dqgdwrywrwpfbz/201207/t20120731_234142.htm.
Xiao HP, Cheng QY, Liu MJ, Li L, Ru Y, Yan DH. Industrial disposal processes for treatment of polychlorinated dibenzo-p-dioxins and dibenzofurans in municipal solid waste incineration fly ash. Chemosphere. 2020;243:125351.
Anderson DR, Fisher R. Sources of dioxins in the United Kingdom: the steel industry and other sources. Chemosphere. 2002;46:371–81.
Liu JP, Tang LP. Research of converter burning waste paint bucket. Baosteel Technol. 2017;1:39–42. doi:https://doi.org/10.3969/j.issn.1008-0716.2017.01.008. [in Chinese].
Stewart DJC, Barron AR. Pyrometallurgical removal of zinc from basic oxygen steelmaking dust – a review of best available technology. Resour Conserv Recy. 2020;157:104746.
Wang F, Yu JX, Xiong WL, Xu YL, Chi RA. A two-step leaching method designed based on chemical fraction distribution of the heavy metals for selective leaching of Cd, Zn, Cu, and Pb from metallurgical sludge. Environ Sci Pollut R. 2018;25:1752–65.
Fisher LV, Barron AR. The recycling and reuse of steelmaking slags - a review. Resour Conserv Recy. 2019;146:244–55.
Wang YJ, Zeng YN, Li JG, Zhang YZ, Zhang YJ, Zhao QZ. Carbonation of argon oxygen decarburization stainless steel slag and its effect on chromium leachability. J Clean Prod. 2020;256:120377.
Xian YJ, Yang KX, Wang K, Wei YM, Huang ZM. Cost-environment efficiency analysis of construction industry in China: a materials balance approach. J Clean Prod. 2019;221:457–68.
Varvara DAI, Tintelecan M, Aciu C, Boca IMS, Hadarean A, Rus T, et al. An assessment of the substance losses from charge composition used to the steelmaking – key factor for sustainable steel manufacturing. Procedia Manufacturing. 2019;32:15–21.
Rajshekar Y, Alex TC, Sahoo DP, Babu GA, Balakrishnan V, Venugopalan T, et al. Iron ore slime as an alternate coolant in steelmaking: performance evaluation at commercial scale. J Clean Prod. 2016;139:886–93.
The authors wish to thank the specialists at Wuhan Huace Testing Technology Co., WISCO Metal Resources Co., Ltd. and Wuhan Iron & Steel Co., Ltd. for their help with the analyses.
This work was supported by the Scientific Research Foundation of Wuhan Polytechnic University (Grant No. 118–53210052171, 118–53210052144 and 118–53210052136).
The authors declare they have no competing interests.
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Wang, Y., Chen, J., Fu, B. et al. Research on co-disposal and utilization of ferrous packaging containers contaminated with hazardous wastes by steel converter. Sustain Environ Res 32, 40 (2022). https://doi.org/10.1186/s42834-022-00148-5