Iron carbon material and preparation method and application thereof
A technology of iron carbon and activated carbon, which is applied in the field of water treatment, can solve the problems of short half-life, easy failure, loss of water purification function, etc., and achieve the effect of accelerating the reduction and degradation speed, increasing the removal capacity, and avoiding secondary pollution
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[0052]
[0053] A preparation method of iron-carbon material, comprising:
[0054] (1), an activation process for activating granular activated carbon;
[0055] (2), the preparation process of preparing iron carbon material by adopting inorganic iron salt and activated granular activated carbon.
[0056] Wherein, the activation procedure of step (1) can adopt any one of boiling water activation method, ultrasonic activation method and nitric acid activation method.
[0057] The boiling water activation method comprises the following steps:
[0058] a1. Mix granular activated carbon with deionized water, heat to boiling state and keep it for 20-30 minutes;
[0059] a2. Naturally cool to room temperature and place for 5-8 hours;
[0060] a3. Take the precipitate and wash it with deionized water for 2 to 4 times;
[0061] a4. Dry to constant weight at 110-130°C to obtain activated granular activated carbon, and put it into a ground-mouth bottle for later use.
[0062] The ...
Embodiment 1
[0076] This embodiment provides an iron-carbon material for reducing and degrading bromate contained in water. The iron-carbon material contains activated carbon and nano-hydroxy iron loaded on the activated carbon, and the nano-hydroxy iron is FeOOH. The mass ratio of activated carbon to nano-hydroxy iron is 1:2.5.
[0077] Among them, this embodiment uses FeSO 4 ·7H 2 O impregnated granular activated carbon prepared as an example to illustrate the nano-hydroxy iron. The bromate removal capacity of nano-hydroxy iron with different iron content is as follows: Figure 7 shown. Figure 7 Denotes the adsorption isotherms of GAC and Fe‐GAC with different iron contents for the removal of bromate after 72 h. Figure 7 The abscissa of represents the initial bromate concentration (Initial bromate concentration), the unit is mmol / L. Figure 7 The vertical axis of represents bromate removal capacity (Bromate removal). From Figure 7 It can be seen that when the iron content is 1...
Embodiment 2
[0079] This embodiment provides a method for preparing an iron-carbon material, which is used to prepare the iron-carbon material in Example 1. This preparation method comprises the steps:
[0080] (1) Mix granular activated carbon with deionized water, heat to boiling state and keep for 35 minutes, cool to room temperature naturally and leave for 6 hours, take the precipitate and wash it with deionized water for 3 times, dry at 120°C to constant weight, The activated granular activated carbon is obtained.
[0081] (2) Mix the inorganic iron salt and the activated granular activated carbon at a mass ratio of 1:2.5, heat at 120°C for 24 hours under the infiltration of deionized water, and wash with deionized water until the cleaned liquid becomes clear , to obtain iron-carbon material after drying.
[0082] Wherein, in the heating process of step (2), it should be ensured that the deionized water does not completely evaporate to dryness, that is, it should be ensured that a w...
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