Relationship between pore structure and application of activated carbon

Activated carbon is often used to adsorb molecules, and adsorption determines the applicability, while adsorption is related to the pore size distribution of various carbon types. Take the steam-activated peat-based, lignite-based and coconut-shell-based powdered activated carbon as examples:

Peat-based activated carbon has micropores and mesopores for a variety of applications;

The lignite-based carbon material has more mesopores and a larger mesopores, providing excellent accessibility;

The coconut shell-based carbon is mainly microporous and is only suitable for low molecular removal.

Chemically activated activated carbon is very porous, mostly in the microporous and mesoporous range, however, compared to water vapor activated activated carbon, chemically activated activated carbon has a less hydrophobic surface and more negative charge.

Take extruded and broken granular activated carbon as an example:

Peat-based extruded activated carbon can be made into a variety of different pore size distribution varieties. Microporous-based varieties are mainly used for gold recovery in gas phase applications. Most of the microporous and mesoporous varieties are used in liquid phase applications, such as adsorption of small molecules and macromolecular impurities in water purification.

Broken coal-based carbon combines micropores and mesopores for a variety of applications.

The lignite-based or coconut-shell-based granular activated carbon has the same microporous and mesoporous structure as the powdered charcoal.

What are the performance indicators of activated carbon?

The performance indicators of activated carbon products can be divided into physical performance indicators, chemical performance indicators, and adsorption performance indicators. Three performance indicators play a very important role in the selection and application of activated carbon.

The main physical performance indicators are: shape, appearance, specific surface area, pore volume, specific gravity, mesh number, particle size, wear resistance, and floating rate.

The main chemical performance indicators are: PH value, ash, moisture, ignition point, uncarbide, sulfide, chloride, cyanide, sulfate, acid soluble, alcohol soluble, iron content, zinc content, lead content, arsenic content, Calcium and magnesium content, heavy metal content, phosphate, etc.

The main adsorption performance indicators are: methylene blue adsorption value, iodine adsorption value, phenol adsorption value, carbon tetrachloride adsorption value, caramel adsorption value, quinine sulfate adsorption value, saturated sulfur capacity, sulfur penetration capacity, water capacity, Ethyl chloride vapor protection time, ABS value, etc.

The main influencing factors of activated carbon water treatment:

Since the adsorption process and the principle of action involved in the treatment of activated carbon water are complicated, there are many influencing factors. It is mainly related to the nature of activated carbon, the nature of pollutants in water, the process principle of activated carbon treatment, and the selected operating parameters and operating conditions.

First, the nature of activated carbon

Since the adsorption phenomenon occurs on the surface of the adsorbent, the specific surface area of ​​the adsorbent is one of the important factors affecting the adsorption. The larger the specific surface area, the better the adsorption performance.

Because the adsorption process can be regarded as three stages, the internal diffusion has a great influence on the adsorption speed, so the micropore distribution of activated carbon is another important factor affecting the adsorption.

In addition, the surface chemistry, polarity and charge of the activated carbon also affect the adsorption effect.

Activated carbon for water treatment should have three requirements: large adsorption capacity, fast adsorption speed, and good mechanical strength. The adsorption capacity of activated carbon is related to the specific surface area of ​​activated carbon, and the specific surface area is large, the number of micropores is large, and the adsorbate adsorbed on the pore wall is more. The adsorption rate is mainly related to the particle size and pore distribution. The activated carbon for water treatment requires a transition hole (radius 20~1000A) to be developed, which is beneficial to the diffusion of the adsorption mass into the micropores. The smaller the particle size of activated carbon, the faster the adsorption speed, but the head loss should be increased, generally in the range of 8~30 mesh. The mechanical wear resistance of activated carbon directly affects the service life of activated carbon.

Second, the nature of the adsorbate (solute or pollutant)

The same activated carbon has great differences in the adsorption capacity of different pollutants.

(1) Solubility

The solubility of a substance of the same group decreases as the chain lengthens, and the adsorption capacity increases as the series of homologues rises or the molecular weight increases. The smaller the solubility, the easier it is to adsorb.

For example, the order in which activated carbon adsorbs organic acids from water is increased by formic acid-acetic acid-propionic acid-butyric acid.

(2) Molecular structure

The size and chemical structure of the adsorbate molecules also have a large effect on adsorption. Because the adsorption rate is affected by the internal diffusion rate, the size of the adsorbate (solute) molecule is proportional to the pore size of the activated carbon, which is most favorable for adsorption. In homologues, molecules larger than molecules are easily adsorbed. The organic matter of the unsaturated bond is more soluble than the saturated one. Aromatic organics are easier to adsorb than aliphatic organics.

(three) polarity

Activated carbon can be regarded as a non-polar adsorbent, and its adsorption capacity for non-polar substances in water is greater than that of polar substances.

(4) Adsorption sanctions (solute)

When the concentration of the adsorbate is within a certain range, the adsorption capacity increases as the concentration increases. Therefore, the concentration of the adsorbate (solute) changes, and the adsorption capacity of the activated carbon for the adsorbate (solute) also changes.

Third, the effect of solution pH

The effect of pH on the adsorption should be considered in combination with the effects of activated carbon and adsorbate (solute).

The pH of the solution controls the degree of dissociation of acidic or basic compounds. When the pH reaches a certain range, these compounds dissociate and affect the adsorption of these compounds.

The pH of the solution also affects the solubility of the adsorbate (solute) and the charge of the adsorbate (solute) of the colloid.

Since activated carbon can adsorb hydrogen and oxygen ions in water, it affects the adsorption of other ions.

The effect of activated carbon adsorbing organic pollutants from water generally decreases with the increase of pH value of the solution. When the pH value is higher than 9.0, it is not easy to adsorb, and the lower the pH value, the better the effect. In practical applications, the optimum pH range is determined experimentally.

Fourth, the effect of solution temperature

Since the adsorption heat is small when the liquid phase is adsorbed, the influence of the solution temperature is small.

Adsorption is an exothermic reaction. The heat of adsorption, that is, the total heat released by the activated carbon adsorption unit weight of the adsorbate (solute), in KJ/mol. The greater the heat of adsorption, the greater the effect of temperature on adsorption.

On the other hand, temperature has an effect on the solubility of the substance and therefore also on the adsorption.

When water is treated with activated carbon, the effect of temperature on adsorption is not significant.

5. The influence of coexistence of multi-component adsorbate

When water is applied by adsorption, usually water is not a single pollutant, but a mixture of multi-component pollutants. When adsorbed, they can co-adsorb, promote each other or interfere with each other. In general, the adsorption capacity of the multi-component adsorption is lower than that of the single-component adsorption.

Sixth, adsorption operating conditions

Since the diffusion rate of the external diffusion (liquid film diffusion) affects the adsorption during the liquid phase adsorption of the activated carbon, the type of the adsorption device and the contact time (water passing rate) have an effect on the adsorption effect.

In summary, there are many factors affecting adsorption. Comprehensive analysis should be carried out. According to the specific conditions, the best adsorption conditions should be selected to achieve the best adsorption effect.

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