Related Experiment Video
Updated: Jun 6, 2026

06:27
Expression of Cementitious Pore Solution and the Analysis of Its Chemical Composition and Resistivity Using X-ray Fluorescence
Published on: September 23, 2018
Arsenic stability in arsenopyrite-rich cemented paste backfills: a leaching test-based assessment
Samuel Coussy1, Mostafa Benzaazoua, Denise Blanc
1Université du Québec en Abitibi-Témiscamingue, 445 Boul. de l'université, Rouyn-Noranda, QC, Canada. samuel.coussy@uqat.ca
Journal of Hazardous Materials
|November 16, 2010
Summary
Cemented paste backfill (CPB) can stabilize toxic arsenic (As) in mine tailings. Different binders affect As release, with fly ash showing better stabilization at lower pH.
Area of Science:
- Environmental Science
- Geochemistry
- Materials Science
Background:
- Arsenic (As) in mine tailings poses environmental risks due to its high solubility.
- Cemented Paste Backfill (CPB) is a tailings storage method that can immobilize pollutants like As.
- Casa Berardi mine tailings contain significant amounts of As, primarily in arsenopyrite form.
Purpose of the Study:
- To evaluate the effectiveness of different binders in stabilizing arsenic in cemented paste backfill.
- To investigate the mechanisms of arsenic release from CPB under various conditions.
- To compare the performance of fly ash, slag, and Portland cement-based CPB in immobilizing arsenic.
Main Methods:
- Synthesized three types of CPB using Casa Berardi tailings and different binders (fly ash, slag, Portland cement).
- Subjected the CPB samples to various leaching tests after 28 days of curing.
- Conducted accelerated weathering tests to assess sulphide reactivity and its influence on As release.
Main Results:
- Arsenic release was higher in fly ash-based CPB compared to slag- and Portland cement-based CPB under standard conditions.
- Fly ash-based CPB demonstrated superior arsenic stabilization at lower pH levels.
- CPB's neutralizing minerals buffered sulphide reactivity, reducing the oxidation of As-bearing sulphides and influencing As release.
Conclusions:
- The choice of binder significantly impacts arsenic stabilization in CPB.
- Fly ash-based CPB offers potential for arsenic immobilization, particularly in acidic mine environments.
- Understanding As-compound solubility and release mechanisms is crucial for effective tailings management.
More Related Videos
Related Concept Videos
Soundness of Cement
The soundness of cement refers to the ability of cement paste to retain its volume after setting. Unsound cement can lead to expansion and structural damage due to the presence of free lime, magnesia, and calcium sulfate. Free lime hydrates very slowly, expanding and causing unsoundness, which is difficult to detect because it intercrystallizes with other compounds. Magnesia also reacts with water, forming crystals that can disrupt the cement's structure. Calcium sulfate can create ettringite,...
Microbial Leaching
Microbial leaching, also known as bioleaching, is an environmentally favorable method for extracting metals from low-grade ores using specific microorganisms. This biotechnological approach is particularly valuable for mining operations targeting copper, gold, and uranium, where traditional extraction methods may be economically or environmentally impractical.Copper Leaching and Microbial CatalysisIn copper bioleaching, crushed ore is arranged into heaps and irrigated with a dilute sulfuric...
Porosity in Cement Paste
The porosity of concrete is a measure of the void spaces within its structure. These spaces impact its strength and durability significantly. When water and cement interact, a chemical reaction called hydration creates a semi-solid paste. This paste includes combined water, making up approximately 23% of the cement's dry mass, and gel water, which fills minuscule voids known as gel pores, accounting for about 28% of the cement gel volume.
The balance of water to cement in the mix is critical—it...
The balance of water to cement in the mix is critical—it...
Acid Mine Drainage
Mining activities that disturb sulfide-rich rocks, particularly those containing pyrite (FeS₂), initiate a cascade of geochemical and microbiological processes with serious environmental implications. When exposed to air and water, pyrite undergoes oxidation, releasing sulfate, ultimately forming sulfuric acid and mobilizing heavy metals into surrounding water systems. This phenomenon, known as acid mine drainage (AMD), results in low pH waters laden with toxic elements that threaten aquatic...
Strength of Cement
Strength tests for cement are not performed directly on neat cement paste due to difficulty in obtaining consistent, reliable specimens. Instead, cement is typically tested in the form of cement-sand mortar.
For compressive strength tests, ASTM C 109-05 standards prescribe a cement-sand mix ratio of 1:2.75 and a water/cement ratio of 0.485 for making 2-inch cubes. These cubes are mixed, cast, and cured in saturated lime water at 23°C until testing. Flexural strength testing, outlined in ASTM C...
For compressive strength tests, ASTM C 109-05 standards prescribe a cement-sand mix ratio of 1:2.75 and a water/cement ratio of 0.485 for making 2-inch cubes. These cubes are mixed, cast, and cured in saturated lime water at 23°C until testing. Flexural strength testing, outlined in ASTM C...
Testing Water Quality
When the quality of water for concrete preparation is uncertain, its impact on the setting time of cement and compressive strength of mortar is assessed by comparison with de-ionized or distilled water benchmarks. American Society for Testing and Materials (ASTM) C1602 requires the setting times to be within 90 minutes of the control, British Standard (BS) 3146:1980 allows a 30-minute variance in the initial setting, while British Standards European Norm (BS EN) 1008 specifies initial setting...

