The mineral carbon sequestration capacity of basic oxygen furnace (BOF) slag offers great potential to absorb carbon dioxide (CO2) from landfill emissions. The BOF slag is highly alkaline and rich in calcium (Ca) containing minerals that can react with the CO2to form stable carbonates. This property of BOF slag makes it appealing for use in CO2sequestration from landfill gas. In a previous study, CO2and CH4removal from the landfill gas was investigated by performing batch and column experiments with BOF slag under different moisture and synthetic landfill gas exposure conditions. The study showed two stage CO2removal mechanism: (1) initial rapid CO2removal, which was attributed to the carbonation of free lime (CaO) and portlandite [(Ca(OH)2)], and (2) long-term relatively slower CO2removal, which was attributed to be the gradual leaching of Ca2+from minerals (calcium-silicates) present in the BOF slag. Realising that the particle size could be an important factor affecting total CO2sequestration capacity, this study investigates the effect of gradation on the CO2sequestration capacity of the BOF slag under simulated landfill gas conditions. Batch and column experiments were performed with BOF slag using three gradations: (1) coarse (D50 = 3.05 mm), (2) original (D50 = 0.47 mm), and (3) fine (D50 = 0.094 mm). The respective CO2sequestration potentials attained were 255 mg g−1, 155 mg g−1, and 66 mg g−1. The highest CO2sequestration capacity of fine BOF slag was attributed to the availability of calcium containing minerals on the slag particle surface owing to the highest surface area and shortest leaching path for the Ca2+from the inner core of the slag particles.
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Remediation of Aqueous Phosphate Agricultural Runoff Using Slag and Al/Mg Modified Biochar
Slag and Al/Mg oxide modified Douglas fir biochar (AMOB) were compared for their phosphate adsorbing abilities for use individually or in combination for simulated agriculture run-off remediation in wetlands. Aqueous batch and column sorption experiments were performed for both low-cost materials. AMOB was prepared in bulk using a novel green method. Material analyses included XRD, elemental analysis, SEM, EDX, and BET. Biochar and slag have different phosphate removal mechanisms. In short residence times (≤2 h), adsorption phenomena dominate for both adsorbents. Surface area likely plays a role in adsorption performance; slag was measured to be 4.1 m2/g while biochar’s surface area was 364.1 m2/g. In longer residence times (>2 h), the slow leaching of metals (Ca, Al, and Mg) from slag continue to remove phosphate through the precipitation of metal phosphates. In 24 h, slag removed more free phosphate from the solution than AMOB. Preliminary fixed bed column adsorption of slag or AMOB alone and in tandem was performed adopting a scaled-up model that can be used to remediate agricultural runoff with high phosphate content. Additionally, a desorption study was performed to analyze the efficiency of material regeneration. While AMOB does not release any adsorbed phosphates, slag slowly releases 5.7% adsorbed phosphate over seven days.
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- Award ID(s):
- 1659830
- PAR ID:
- 10378427
- Date Published:
- Journal Name:
- Processes
- Volume:
- 10
- Issue:
- 8
- ISSN:
- 2227-9717
- Page Range / eLocation ID:
- 1561
- Format(s):
- Medium: X
- Sponsoring Org:
- National Science Foundation
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