Preparation method and application of a vulcanized modified zero-valent iron composite material
A composite material, zero-valent iron technology, applied in chemical instruments and methods, oxidized water/sewage treatment, water/sludge/sewage treatment, etc. problem, to achieve the effect of good universality, wide pH working band, and short time consumption
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preparation example 1
[0037] This embodiment provides a method for preparing a sulfide-modified zero-valent iron composite material.
[0038] The room temperature is 20±2°C. According to the mass ratio (in this example, pyrite: iron powder = 1:9), weigh an appropriate amount of pyrite (10 mesh) and zero-valent iron powder (200 mesh) and mix them, add 9mm oxide Zirconium ball milling beads are placed in a 100mL lined zirconia ball milling tank, set the ball milling speed to 600rpm, pause for 10 minutes after ball milling for 10 minutes, change the direction and ball mill again, and cycle three times, take out after a total of 30 minutes of ball milling, pass through a 100-mesh screen and collect in a centrifuge tube Store in a desiccator. The nitrogen content in the desiccator is 85%, and the humidity is 10%.
Embodiment 2
[0040] This example uses the composite material prepared in Preparation Example 1 to provide a water treatment method for degrading heavy metal Cr(VI) under anaerobic conditions.
[0041] The room temperature is 18°C, add 250ml of acetic acid-sodium acetate buffer solution to the 250ml reaction bottle, control its pH between 5.5-6.5, add 1mL of 5mg / ml Cr(VI) stock solution, and prepare the artificial Synthesize Cr(VI) wastewater, sample 1.5mL, add 0.3g iron powder (Fe 0bm ), pyrite (FeS 2 bm ), iron powder mixed with pyrite ((Fe 0 +FeS 2 ) bm ), after ultrasonic reaction for 10 minutes, the reaction bottle was then placed in an overturning oscillator at 120 rpm and 25°C for anoxic reaction for 1 hour, and the oxygen content in the wastewater was 2 mg / L.
[0042] The result is as figure 1 As shown, the reaction effect in 60min is (Fe 0 +FeS 2 ) bm >FeS 2 bm >Fe 0bm , conforms to pseudo-first-order kinetics before the end of the reaction, that is, (Fe0 +FeS 2 ) bm ...
Embodiment 3
[0044] This implementation uses the composite material prepared in Preparation Example 1 to provide a water treatment method for degrading high-concentration organic chloride CAP under anaerobic conditions.
[0045] The room temperature is 18°C, add 250ml deionized water, 8mM Na 2 SO 4 Electrolyte, dilute sulfuric acid to adjust the pH to 3±0.2, add 0.5mL 50mg / ml CAP stock solution to prepare synthetic CAP organic wastewater with a concentration of 100mg / L, sample 1.5mL, and then add 0.1g ball-milled iron Powder (Fe 0bm ), pyrite (FeS 2 bm ), iron powder mixed with pyrite ((Fe 0 +FeS 2 ) bm ), the reaction bottle was placed in an overturning shaker at 120 rpm and 25° C. for 1.5 hours of anoxic reaction, and the oxygen content in the waste water was 8 mg / L.
[0046] The result is as figure 2 As shown, within 90min there is (Fe 0 +FeS 2 ) bm , Fe 0bm , FeS 2 bm The removal rate is 60%, 28%, 0% respectively, and the reaction effect is (Fe 0 +FeS 2 ) bm >Fe 0bm ...
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