Patent ID: 12220680

DETAILED DESCRIPTION

It should be noted that the following detailed descriptions are all exemplary and are intended to provide a further understanding of this application. Unless otherwise specified, all technical and scientific terms used herein have the same meaning as commonly understood by a person of ordinary skill in the art to which this application belongs.

It should be noted that terms used herein are only for describing specific implementations and are not intended to limit exemplary implementations according to the present application. As used herein, the singular form is also intended to include the plural form unless the context clearly dictates otherwise. In addition, it should further be understood that, terms “include” and/or “comprise” used in this specification indicate that there are features, steps, operations, devices, components, and/or combinations thereof.

As introduced by the background technology, the inventor found that the current utilization of the red mud still has the defects including low utilization rate, high utilization cost and easiness to cause secondary pollution. Therefore, the present invention proposes a red mud-based sewage treatment agent and a preparation method thereof, and a red mud-based ceramsite concrete and a preparation method thereof. The present invention will be further described below in conjunction with specific embodiments.

Description of Involved Terms

The term “water-cement ratio” refers to a weight ratio of the amount of water to the amount of solid materials. It is well known that the water-cement ratio affects the rheological properties of the pulp, the cohesive structure and the compactness after hardening. Therefore, for a certain composition material, the water-cement ratio has an appropriate ratio range, and a too large or too small water-cement ratio will affect the properties such as strength.

The term “cementing material” refers to an inorganic cementing material of the red mud-based ceramsite concrete prepared in the present invention, which is mainly used as a construction material. In construction engineering, the cementing material can cement bulk materials (such as sand and stone) into a whole material, so as to form a composite solid with certain mechanical strength.

The term “water reducer” refers to a concrete admixture that can reduce the amount of water used for mixing while maintaining the slump of the concrete basically unchanged, such as a lignosulfonate water reducer and a polycarboxylic acid water reducer. The water reducer can reduce the amount of water and improve the porosity and mechanical strength of the sewage treatment agent.

The term “alkali activator” is mainly used in the cementing material, and the catalytic principle of the alkali activator can promote the hydration of the cementing material.

The term “red mud” refers to the polluting waste slag discharged from the aluminum industry during the extraction of alumina. The red mud contains components such as SiO2, Al2O3and CaO, the leaching liquid is alkaline, and the pH value is as high as 12 or more. By means of the acidification treatment, the present invention realizes the modification of the components of the red mud, and also avoids the negative impacts caused by strong alkalinity of the red mud.

The term “blast furnace slag” refers to a kind of waste slag discharged from a blast furnace when smelting pig iron. The main chemical components of the blast furnace slag include SiO2, Al2O3, CaO, MgO, MnO and FeO. By means of the acidification treatment, the present invention realizes the functional utilization of elements such as calcium and magnesium, which helps to improve the adsorption and solidification properties of the sewage treatment agent to pollutants.

The term “fly ash” refers to fine ash collected from the flue gas after coal combustion. The fly ash is the main solid waste discharged from coal-fired power plants. The fly ash mainly contains metal oxides such as SiO2, Al2O3, FeO, Fe2O3, CaO and TiO2. In the present invention, by means of the acidification treatment, metal elements such as calcium and iron are converted into nano carbonates, which helps to improve the adsorption and solidification properties of the sewage treatment agent for pollutants.

The term “coal gangue” refers to the solid waste discharged from a coal mining process and a coal washing process. The coal gangue has a low carbon content and a hard texture, so that the coal gangue is difficult to directly use as fuel like coal. The main components of the coal gangue are Fe2O3, CaO, MgO, Na2O, K2O, and the like. The coal gangue contains many alkali metal oxides. In the present invention, by means of carbonization treatment, nano carbides are formed and distributed in the treatment agent, which becomes a favorable factor for improving the adsorption property.

The term “iron tailings” refer to wastes after mineral separation. The main component of the iron tailings is SiO2, and the iron tailings also contain some Al2O3, Fe2O3, MgO, Na2O, K2O, and the like. In the present invention, the carbonization treatment on this solid waste helps to improve the adsorption property of the sewage treatment agent for pollutants. Furthermore, high-content silica can also be used as a framework material to ensure that the obtained treatment agent has certain hardness to prevent the treatment agent from being loosened after being soaked in sewage, which is not conducive to preparing the final product of the present invention after recovery.

The term “industrial tail gas” includes industrial waste gas containing acidic gases such as carbon dioxide and/or sulfur dioxide discharged from thermal power plants, steel plants, metal smelters, chemical plants, cement plants, and industrial or civil boilers.

The term “acidification treatment” refers to the process of converting the existing form of certain metal elements in the solid waste through the carbon dioxide in the above-mentioned tail gas to obtain nano carbonates. Furthermore, the acidic property of the carbon dioxide can also be used to eliminate the problem of secondary pollution caused by certain alkaline solid wastes.

In the following embodiments, the red mud was purchased from Weiqiao Pioneering Co., Ltd and was ground, dried and sieved with a 400-mesh square hole sieve in the present invention to obtain slag powder used in the embodiments of the present invention.

In the following embodiments, the blast furnace slag was purchased from Lubi New Materials Co., Ltd., and was ground, dried and sieved with a 400-mesh square hole sieve in the present invention to obtain slag powder used in the embodiments of the present invention.

In the following embodiments, the coal gangue was purchased from Qiuji Coal Mine, and was ground, dried and sieved with a 400-mesh square hole sieve in the present invention to obtain coal gangue powder used in the embodiments of the present invention.

In the following embodiments, the fly ash was purchased from Weiqiao Pioneering Group Co., Ltd., and was ground, dried and sieved with a 400-mesh square hole sieve in the present invention to obtain smaller-scale target fly ash used in the embodiments of the present invention.

In the following embodiments, the iron tailings were purchased from Zhangmatun Iron Mine, and were ground, dried and sieved with a 400-mesh square hole sieve in the present invention to obtain iron tailings powder used in the embodiments of the present invention.

In the following embodiments, various solid wastes were obtained by grinding, drying and sieving with a 400-mesh square hole sieve.

In the following embodiments, the pollutant composition and pH value in sewage (simulation) were shown in Table 1.

TABLE 1Chemical composition of sewage (unit: mg/L)Ca2+Cu2+Cl−SO42−NO3−COD (%)pH34.441.61300.2812.7397.82

First Embodiment

1. A preparation method of a red mud-based sewage treatment agent includes the following steps:(1) in mass percent, red mud and blast furnace slag were respectively dried and ground and then sieved with a 400-mesh sieve to obtain red mud micro-powder and blast furnace slag micro-powder, and the red mud micro-powder and the blast furnace slag micro-powder were mixed in a mass ratio of 6:4 to obtain a solid waste complex;(2) simulated industrial tail gas (mass concentration of carbon dioxide was about 16%) was used to perform acidification treatment on the solid waste complex obtained in step (1) for 4.0 h under the conditions that the temperature was 100° C., the humidity was 80% and the pressure was 1.0 MPa, and after the acidification treatment was completed, the solid waste complex was dried and ground and then sieved with a 400-mesh sieve to obtain a modified solid waste complex; and(3) in mass percent, 90% of the modified solid waste complex obtained in step (2), 0.4% of a polycarboxylic acid water reducer, 4.0% of sodium silicate, 2.0% of ultrafine zeolite (900 meshes) and 3.6% of cetyl ammonium bromide were mixed uniformly for pulping according to a water-cement ratio of 0.35, then granulating was performed in a granulating machine, and after the granulating was completed, natural curing was performed for 24 h to prepare a spherical red mud-based sewage treatment agent with a diameter 5.0-8.0 mm.

2. A preparation method of a red mud-based ceramsite concrete includes the following steps:(I) the red mud-based sewage treatment agent prepared in step (3) of the present embodiment was placed in sewage (see Table 1 for components) to adsorb pollutants, after the concentration of the pollutants in the sewage remains unchanged, an adsorption saturation state was reached, and the red mud-based sewage treatment agent was dried for later use; and(II) preparation of the red mud-based ceramsite concrete: in mass percent, 30% of solid waste complex micro-powder after acidification treatment, 15% of water, 55% of the red mud-based sewage treatment agent obtained in step (I), sodium silicate accounting for 10% of the mass of the solid waste complex, ultrafine silica fume (900 meshes) accounting for 4.0% of the mass of the solid waste complex, and a polycarboxylic acid water reducer accounting for 1.0% of the mass of the solid waste complex were weighed, then the solid waste complex micro-powder, the red mud-based sewage treatment agent, the sodium silicate, the ultrafine silica fume and the polycarboxylic acid water reducer were put into a forced stirrer first so as to be stirred, then water was poured into the forced stirrer, the obtained mixture was stirred to form a pulp coating layer on the surface of the red mud-based sewage treatment agent, and natural curing was performed for 24 h to obtain the red mud-based ceramsite concrete.

Second Embodiment

1. A preparation method of a red mud-based sewage treatment agent includes the following steps:(1) in mass percent, red mud, coal gangue and iron tailings were respectively dried and ground and then sieved with a 400-mesh sieve to obtain red mud micro-powder, coal gangue micro-powder and iron tailings micro-powder, and the red mud micro-powder, the coal gangue micro-powder and the iron tailings micro-powder were mixed in a mass ratio of 6:3:1 to obtain a solid waste complex;(2) simulated industrial tail gas (mass concentration of carbon dioxide was about 16%) was used to perform acidification treatment on the solid waste complex obtained in step (1) for 4 h under the conditions that the temperature was 200° C., the humidity was 100% and the pressure was 2.0 MPa, and after the acidification treatment was completed, the solid waste complex was dried and ground and then sieved with a 400-mesh sieve to obtain a modified solid waste complex; and(3) in mass percent, 90% of the modified solid waste complex obtained in step (2), 0.4% of a naphthalene water reducer, 4.0% of sodium hydroxide, 2.0% of ultrafine zeolite (900 meshes) and 3.6% of sodium dodecylsulfonate were mixed uniformly for pulping according to a water-cement ratio of 0.3, then granulating was performed in a granulating machine, and after the granulating was completed, natural curing was performed for 24 h to prepare a spherical red mud-based sewage treatment agent with a diameter 9.0-13.0 mm.

2. A preparation method of a red mud-based ceramsite concrete includes the following steps:(I) the red mud-based sewage treatment agent prepared in step (3) of the present embodiment was placed in sewage (see Table 1) to adsorb pollutants, after the concentration of the pollutants in the sewage remains unchanged, an adsorption saturation state was reached, and the red mud-based sewage treatment agent was dried for later use; and(II) preparation of the red mud-based ceramsite concrete: in mass percent, 30% of solid waste complex micro-powder after acidification treatment, 15% of water, 55% of the red mud-based sewage treatment agent obtained in step (I), sodium silicate accounting for 10% of the mass of the solid waste complex, nano calcium carbonate accounting for 4.0% of the mass of the solid waste complex, and a naphthalene water reducer accounting for 1.0% of the mass of the solid waste complex were weighed, then the solid waste complex micro-powder, the red mud-based sewage treatment agent, the sodium silicate, the nano calcium carbonate and the naphthalene water reducer were put into a forced stirrer first so as to be stirred, then water was poured into the forced stirrer, the obtained mixture was stirred to form a pulp coating layer on the surface of the red mud-based sewage treatment agent, and natural curing was performed for 24 h to obtain the red mud-based ceramsite concrete.

Third Embodiment

1. A preparation method of a red mud-based sewage treatment agent includes the following steps:(1) in mass percent, red mud and fly ash were respectively dried and ground and then sieved with a 400-mesh sieve to obtain red mud micro-powder and fly ash micro-powder, and the red mud micro-powder and the fly ash micro-powder were mixed in a mass ratio of 6:4 to obtain a solid waste complex;(2) simulated industrial tail gas (mass concentration of carbon dioxide was about 16%) was used to perform acidification treatment on the solid waste complex obtained in step (1) for 4 h under the conditions that the temperature was 150° C., the humidity was 80% and the pressure was 1.5 MPa, and after the acidification treatment was completed, the solid waste complex was dried and ground and then sieved with a 400-mesh sieve to obtain a modified solid waste complex; and(3) in mass percent, 90% of the modified solid waste complex obtained in step (2), 0.5% of an aliphatic water reducer, 3.0% of potassium silicate, 1.0% of ultrafine metal organic framework materials (ZIFs, 800 meshes), and 5.0% of cetyl ammonium bromide were mixed uniformly for pulping according to a water-cement ratio of 0.5, then granulating was performed in a granulating machine, and after the granulating was completed, natural curing was performed for 24 h to prepare a spherical red mud-based sewage treatment agent with a diameter 15-21 mm.

2. A preparation method of a red mud-based ceramsite concrete includes the following steps:(I) the red mud-based sewage treatment agent prepared in step (3) of the present embodiment was placed in sewage to adsorb pollutants, after the concentration of the pollutants in the sewage remains unchanged, an adsorption saturation state was reached, and the red mud-based sewage treatment agent was dried; and(II) preparation of the red mud-based ceramsite concrete: in mass percent, 20% of solid waste complex micro-powder after acidification treatment, 20% of water, 60% of the red mud-based sewage treatment agent obtained in step (I), sodium hydroxide accounting for 6.0% of the mass of the solid waste complex, nano alumina accounting for 0.5% of the mass of the solid waste complex, and an aliphatic water reducer accounting for 0.5% of the mass of the solid waste complex were weighed, then the solid waste complex micro-powder, the red mud-based sewage treatment agent, the sodium hydroxide, the nano alumina and the aliphatic water reducer were put into a forced stirrer first so as to be stirred, then water was poured into the forced stirrer, the obtained mixture was stirred to form a pulp coating layer on the surface of the red mud-based sewage treatment agent, and natural curing was performed for 24 h to obtain the red mud-based ceramsite concrete.

Fourth Embodiment

1. A preparation method of a red mud-based sewage treatment agent includes the following steps:(1) in mass percent, red mud, fly ash and iron tailings were respectively dried and ground and then sieved with a 400-mesh sieve to obtain red mud micro-powder, fly ash micro-powder and iron tailings micro-powder, and the red mud micro-powder, the fly ash micro-powder and the iron tailings micro-powder were mixed in a mass ratio of 4:5:1 to obtain a solid waste complex;(2) simulated industrial tail gas (mass concentration of carbon dioxide was about 16%) was used to perform acidification treatment on the solid waste complex obtained in step (1) for 36 h under the conditions that the temperature was 60° C., the humidity was 40% and the pressure was 2.0 MPa, and after the acidification treatment was completed, the solid waste complex was dried and ground and then sieved with a 400-mesh sieve to obtain a modified solid waste complex; and(3) in mass percent, 80% of the modified solid waste complex obtained in step (2), 1% of a polycarboxylic acid water reducer, 15% of sodium silicate, 1.0% of ultrafine zeolite (900 meshes) and 3.0% of cetyl ammonium bromide were mixed uniformly for pulping according to a water-cement ratio of 0.35, then granulating was performed in a granulating machine, and after the granulating was completed, natural curing was performed for 20 h to prepare a spherical red mud-based sewage treatment agent with a diameter 33-37 mm.

2. A preparation method of a red mud-based ceramsite concrete includes the following steps:(I) the red mud-based sewage treatment agent prepared in step (3) of the present embodiment was placed in sewage to adsorb pollutants, after the concentration of the pollutants in the sewage remains unchanged, an adsorption saturation state was reached, and the red mud-based sewage treatment agent was dried for later use; and(II) preparation of the red mud-based ceramsite concrete: in mass percent, 15% of solid waste complex micro-powder after acidification treatment, 10% of water, 75% of the red mud-based sewage treatment agent obtained in step (I), sodium carbonate accounting for 20% of the mass of the solid waste complex, nano alumina accounting for 2.5% of the mass of the solid waste complex, and a polycarboxylic acid water reducer accounting for 0.2% of the mass of the solid waste complex were weighed, then the solid waste complex micro-powder, the red mud-based sewage treatment agent, the sodium carbonate, the nano alumina and the polycarboxylic acid water reducer were put into a forced stirrer first so as to be stirred, then water was poured into the forced stirrer, the obtained mixture was stirred to form a pulp coating layer on the surface of the red mud-based sewage treatment agent, and natural curing was performed for 24 h to obtain the red mud-based ceramsite concrete.

Fifth Embodiment

1. A preparation method of a red mud-based sewage treatment agent includes the following steps:(1) in mass percent, red mud, coal gangue and iron tailings were respectively dried and ground and then sieved with a 400-mesh sieve to obtain red mud micro-powder, coal gangue micro-powder and iron tailings micro-powder, and the red mud micro-powder, the coal gangue micro-powder and the iron tailings micro-powder were mixed in a mass ratio of 4:2.5:3.5 to obtain a solid waste complex;(2) simulated industrial tail gas (mass concentration of carbon dioxide was about 16%) was used to perform acidification treatment on the solid waste complex obtained in step (1) for 2 h under the conditions that the temperature was 400° C., the humidity was 90% and the pressure was 0.2 MPa, and after the acidification treatment was completed, the solid waste complex was dried and ground and then sieved with a 400-mesh sieve to obtain a modified solid waste complex; and(3) in mass percent, 90% of the modified solid waste complex obtained in step (2), 4.5% of Portland cement, 0.5% of ultrafine silica fume (800 meshes), and 5.0% of cetyl ammonium bromide were mixed uniformly for pulping according to a water-cement ratio of 0.4, then granulating was performed in a granulating machine, and after the granulating was completed, natural curing was performed for 22 h to prepare a spherical red mud-based sewage treatment agent with a diameter 36-38 mm.

2. A preparation method of a red mud-based ceramsite concrete includes the following steps:(I) the red mud-based sewage treatment agent prepared in step (3) of the present embodiment was placed in sewage to adsorb pollutants, after the concentration of the pollutants in the sewage remains unchanged, an adsorption saturation state was reached, and the red mud-based sewage treatment agent was dried for later use; and(II) preparation of the red mud-based ceramsite concrete: in mass percent, 25% of solid waste complex micro-powder after acidification treatment, 30% of water, 55% of the red mud-based sewage treatment agent obtained in step (I), Portland cement accounting for 12% of the mass of the solid waste complex, carbide slag ultrafine powder (900 meshes) accounting for 3.5% of the mass of the solid waste complex, and a polycarboxylic acid water reducer accounting for 0.8% of the mass of the solid waste complex were weighed, then the solid waste complex micro-powder, the red mud-based sewage treatment agent, the Portland cement, the carbide slag ultrafine powder and the polycarboxylic acid water reducer were put into a forced stirrer first so as to be stirred, then water was poured into the forced stirrer, the obtained mixture was stirred to form a pulp coating layer on the surface of the red mud-based sewage treatment agent, and natural curing was performed for 24 h to obtain the red mud-based ceramsite concrete.

Sixth Embodiment

1. A preparation method of a red mud-based sewage treatment agent includes the following steps:(1) in mass percent, red mud, coal gangue and iron tailings were respectively dried and ground and then sieved with a 400-mesh sieve to obtain red mud micro-powder, coal gangue micro-powder and iron tailings micro-powder, and the red mud micro-powder, the coal gangue micro-powder and the iron tailings micro-powder were mixed in a mass ratio of 6:3:1 to obtain a solid waste complex;(2) simulated industrial tail gas (mass concentration of carbon dioxide was about 16%) was used to perform acidification treatment on the solid waste complex obtained in step (1) for 4 h under the conditions that the temperature was 200° C., the humidity was 100% and the pressure was 2.0 MPa, and after the acidification treatment was completed, the solid waste complex was dried and ground and then sieved with a 400-mesh sieve to obtain a modified solid waste complex; and(3) in mass percent, 90% of the modified solid waste complex obtained in step (2), 1.0% of a naphthalene water reducer, 2.0% of sodium carbonate, 2.0% of ultrafine zeolite (900 meshes) and 5.0% of sodium dodecylsulfonate were mixed uniformly for pulping according to a water-cement ratio of 0.2, then granulating was performed in a granulating machine, and after the granulating was completed, natural curing was performed for 24 h to prepare a spherical red mud-based sewage treatment agent with a diameter 36-40 mm.

2. A preparation method of a red mud-based ceramsite concrete includes the following steps:(I) the red mud-based sewage treatment agent prepared in step (3) of the present embodiment was placed in sewage to adsorb pollutants, after the concentration of the pollutants in the sewage remains unchanged, an adsorption saturation state was reached, and the red mud-based sewage treatment agent was dried for later use; and(II) preparation of the red mud-based ceramsite concrete: in mass percent, 18% of solid waste complex micro-powder after acidification treatment, 17% of water, 65% of the red mud-based sewage treatment agent obtained in step (I), sodium silicate accounting for 15% of the mass of the solid waste complex, sulphoaluminate cement accounting for 1.0% of the mass of the solid waste complex, and a polycarboxylic acid water reducer accounting for 0.6% of the mass of the solid waste complex were weighed, then the solid waste complex micro-powder, the red mud-based sewage treatment agent, the sodium silicate, the sulphoaluminate cement and the polycarboxylic acid water reducer were put into a forced stirrer first so as to be stirred, then water was poured into the forced stirrer, the obtained mixture was stirred to form a pulp coating layer on the surface of the red mud-based sewage treatment agent, and natural curing was performed for 24 h to obtain the red mud-based ceramsite concrete.

Seventh Embodiment

1. A preparation method of a red mud-based sewage treatment agent includes the following steps:(1) in mass percent, red mud and blast furnace slag were respectively dried and ground and then sieved with a 400-mesh sieve to obtain red mud micro-powder and blast furnace slag micro-powder, and the red mud micro-powder and the blast furnace slag micro-powder were mixed in a mass ratio of 6:4 to obtain a solid waste complex; and(2) in mass percent, 90% of the solid waste complex obtained in step (1), 0.4% of a polycarboxylic acid water reducer, 4.0% of sodium silicate, 2.0% of ultrafine zeolite (900 meshes) and 3.6% of cetyl ammonium bromide were mixed uniformly for pulping according to a water-cement ratio of 0.35, then granulating was performed in a granulating machine, and after the granulating was completed, natural curing was performed for 24 h to prepare a spherical red mud-based sewage treatment agent with a diameter 5-8 mm.

Eighth Embodiment

1. A preparation method of a red mud-based sewage treatment agent includes the following steps:(1) in mass percent, red mud, coal gangue and iron tailings were respectively dried and ground and then sieved with a 400-mesh sieve to obtain red mud micro-powder, coal gangue micro-powder and iron tailings micro-powder, and the red mud micro-powder, the coal gangue micro-powder and the iron tailings micro-powder were mixed in a mass ratio of 6:3:1 to obtain a solid waste complex; and(2) in mass percent, 90% of the solid waste complex obtained in step (1), 0.4% of a naphthalene water reducer, 4.0% of sodium hydroxide, 2% of ultrafine zeolite (900 meshes) and 3.6% of sodium dodecylsulfonate were mixed uniformly for pulping according to a water-cement ratio of 0.3, then granulating was performed in a granulating machine, and after the granulating was completed, natural curing was performed for 24 h to prepare a spherical red mud-based sewage treatment agent with a diameter 10-13 mm.

Ninth Embodiment

A preparation method of a red mud-based ceramsite concrete includes the following steps: the red mud-based sewage treatment agent prepared in step (3) of the third embodiment was placed in sewage to adsorb pollutants, after the concentration of the pollutants in the sewage remains unchanged, an adsorption saturation state was reached, the red mud-based sewage treatment agent was dried, and then, the leaching amount of the pollution factors adsorbed in the red mud-based sewage treatment agent was tested directly.

Tenth Embodiment

A preparation method of a red mud-based ceramsite concrete includes the following steps: the red mud-based sewage treatment agent prepared in step (3) of the fourth embodiment was placed in sewage to adsorb pollutants, after the concentration of the pollutants in the sewage remains unchanged, an adsorption saturation state was reached, the red mud-based sewage treatment agent was dried, and then, the leaching amount of the pollution factors adsorbed in the red mud-based sewage treatment agent was tested directly.

Property Test

The indexes of the red mud-based sewage treatment agents and the red mud-based ceramsite concretes prepared in the first embodiment to the tenth embodiment were tested, wherein the strength was tested in accordance with the national standard GB/T 11969-2008 Test Method for Properties of Autoclaved Aerated Concrete. Results were shown in Table 2.

TABLE 2Red mud-basedsewageRed mud-based ceramsite concretetreatment agent28dCu2+Phosphate radicalcompressiveleachingProperty indexadsorption rate/%strength/MPaamount/ppmEmbodiment 198.642.254.1Embodiment 299.534.710.9Embodiment 397.236.941.2Embodiment 496.845.731.8Embodiment 598.337.293.3Embodiment 699.140.162.6Embodiment 766.8——Embodiment 863.3——Embodiment 9——28.5Embodiment 10——24.7

It can be seen from the test data in Table 1 that the red mud-based ceramsite concrete prepared in the embodiments of the present invention has excellent compressive strength, which makes the mud-based cementing material of the present invention fully suitable for manufacturing buildings. The red mud-based ceramsite concrete was not only convenient to prepare, but also can realize the large-scale utilization of solid wastes.

At the same time, it can be seen from the test results of the adsorption capacity of the red mud-based sewage treatment agents prepared in the first embodiment to the eighth embodiment for phosphate radical ions in the sewage that compared with the treatment agent that was not prepared by acidification, the treatment agent obtained after acidification treatment on solid wastes by carbon dioxide has a significantly enhanced adsorption capacity for phosphate radical ions. After analysis and research, it was found that the main reason was that the solid wastes contain a large amount of metal ions which can be converted into nano carbonates in an acidification reaction process, and these carbonates in the form of ultrafine particles were distributed in the sewage treatment agent, so that the surface area of the sewage treatment agent can be significantly increased, and the adsorption efficiency in the sewage treatment process can be increased.

In addition, the leaching amount of Cu2+adsorbed in the red mud-based ceramsite concretes prepared in the first embodiment to the sixth embodiment and the ninth and tenth embodiments was tested under the same conditions, so as to evaluate the secondary pollution indexes of the red mud-based ceramsite concrete in the later use process. It can be seen from the results in Table 1 that when the solid waste complex pulp after acidification treatment by industrial tail gas is not used for coating, the leaching amount of Cu2+was significantly increased. After re-coating, since the chemical composition of the solid waste complex was dominated by elements such as silicon, aluminum and calcium, geopolymers with a three-dimensional network structure can be formed under the action of an alkali activator, and the polymerization products treat the adsorbed pollution factors and the inherent pollutants in the solid wastes in manners of chemical bonding, physical encapsulation and the like, so as to avoid the secondary pollution of the red mud-based adsorbent and ensure the environmental friendliness of the red mud-based ceramsite concrete.

In addition, by testing the pH value of the sewage treated with the red mud-based sewage treatment agents prepared in the first embodiment to the eighth embodiment, it was found that the sewage corresponding to the seventh and eighth embodiments was significantly alkaline, and the sewage corresponding to the first embodiment to the sixth embodiment was basically neutral. After further analysis and research, it was found that this was caused by a large amount of alkaline substances contained in the red mud. In a pollutant adsorption process, the leaching liquid of the red mud changes a neutral environment of the sewage to an alkaline environment, which causes secondary pollution, so that the sewage only can be discharged after the pH was adjusted again. By means of the acidification treatment, modification of the components of the red mud was realized, and furthermore, the impacts caused by strong alkalinity of the red mud were significantly reduced.

The above descriptions are merely preferred embodiments of this application and are not intended to limit this application. For those skilled in the art, this application may have various modifications and changes. Any modification, equivalent replacement, improvement and the like made without departing from the spirit and principle of this application shall fall within the protection scope of this application.