CN112845494A - Method for preparing sewage treatment material by utilizing agricultural waste - Google Patents

Method for preparing sewage treatment material by utilizing agricultural waste Download PDF

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Publication number
CN112845494A
CN112845494A CN202011406580.6A CN202011406580A CN112845494A CN 112845494 A CN112845494 A CN 112845494A CN 202011406580 A CN202011406580 A CN 202011406580A CN 112845494 A CN112845494 A CN 112845494A
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China
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treatment material
sewage treatment
preparing
agricultural waste
waste
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CN202011406580.6A
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Chinese (zh)
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秦赢赢
邹国栋
曹卫东
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Nanjing Sko Volt New Materials Co ltd
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Nanjing Sko Volt New Materials Co ltd
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    • BPERFORMING OPERATIONS; TRANSPORTING
    • B09DISPOSAL OF SOLID WASTE; RECLAMATION OF CONTAMINATED SOIL
    • B09BDISPOSAL OF SOLID WASTE NOT OTHERWISE PROVIDED FOR
    • B09B3/00Destroying solid waste or transforming solid waste into something useful or harmless
    • B09B3/40Destroying solid waste or transforming solid waste into something useful or harmless involving thermal treatment, e.g. evaporation
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/46Treatment of water, waste water, or sewage by electrochemical methods
    • C02F1/461Treatment of water, waste water, or sewage by electrochemical methods by electrolysis
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/46Treatment of water, waste water, or sewage by electrochemical methods
    • C02F1/461Treatment of water, waste water, or sewage by electrochemical methods by electrolysis
    • C02F1/46104Devices therefor; Their operating or servicing
    • C02F1/46176Galvanic cells

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  • Chemical & Material Sciences (AREA)
  • Environmental & Geological Engineering (AREA)
  • Engineering & Computer Science (AREA)
  • Electrochemistry (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • General Chemical & Material Sciences (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Hydrology & Water Resources (AREA)
  • Water Supply & Treatment (AREA)
  • Organic Chemistry (AREA)
  • Thermal Sciences (AREA)
  • Physics & Mathematics (AREA)
  • Processing Of Solid Wastes (AREA)

Abstract

The invention discloses a method for preparing a sewage treatment material by utilizing agricultural waste, which comprises the following steps: step 1) heating agricultural waste to 200 ℃ in nitrogen, and keeping for 2 h; 2) soaking the dehydrated waste in an iron salt solution for 8 hours, draining the liquid and drying; 3) sintering the material body in nitrogen at 1200 ℃ for 6h, cooling to room temperature and taking out; 4) the body was kept under nitrogen.

Description

Method for preparing sewage treatment material by utilizing agricultural waste
Technical Field
The invention belongs to the field of environment-friendly materials, and relates to a method for preparing a sewage treatment material by using agricultural waste.
Background
The iron-carbon micro-electrolysis method is also called as an internal electrolysis method, which utilizes the reaction principle of a Fe/C primary battery, integrates the functions of electrochemical oxidation reduction, electrochemical electricity on the electric enrichment of flocs, the condensation of electrochemical reaction products, the adsorption of new flocs, bed filtration and the like, and realizes the effective treatment of wastewater. Has the advantages of wide application range, good treatment effect, long service life, low cost, convenient operation and maintenance and the like, and has the meaning of treating wastes with processes of wastes against one another. At present, the iron-carbon micro-electrolysis technology is widely applied to treatment of waste water such as printing and dyeing, pesticides/pharmacy, heavy metals, petrochemical industry, oil content and the like and landfill leachate, and achieves good effect.
Disclosure of Invention
The technical problem to be solved is as follows: a large amount of waste materials such as straws, crop waste residues and the like can be generated in crop production, the conventional incineration treatment often causes resource waste and environmental pollution, and the method for preparing the water treatment material based on the iron-carbon micro-electrolysis technology by using the straws and the waste residues in agricultural production has social significance of changing waste into valuable.
The technical scheme is as follows:
a method for preparing a sewage treatment material by utilizing agricultural waste comprises the following steps:
(1) heating agricultural waste to 200 ℃ in nitrogen, and keeping for 2h for dehydration;
(2) soaking the dehydrated waste in an iron salt solution for 8 hours, draining the liquid and drying;
(3) sintering the material body in nitrogen at 1200 ℃ for 4h, cooling to room temperature and taking out;
(4) the body was kept under nitrogen.
Further, the agricultural waste in the step (1) is corn straw, sorghum straw, bagasse or other crop waste with a porous structure.
Further, the heating temperature in the step (1) is 180-.
Further, the ferric salt in the step (2) is one or a combination of ferric chloride and ferrous chloride, and the concentration of the ferric salt solution is 5-10%.
Further, in the step (3), the sintering condition is that the heating rate is 150 ℃/h between 50 ℃ and 200 ℃, the temperature is kept for 1h at 200 ℃, the heating rate is 200 ℃/h between 200 ℃ and 1200 ℃, and the sintered product is cooled to the room temperature along with the furnace after being sintered for 4h at 1200 ℃.
The sewage treatment material prepared by the method for preparing the sewage treatment material by utilizing the agricultural waste can be used for COD reduction and decoloration treatment of sewage with COD less than 1000mg/L, and the treatment method comprises the steps of adding the water treatment material according to 0.5-5% of the total amount of the sewage, adjusting the pH to 4-6, stirring for 8 hours, naturally settling for 1 hour, and filtering out a settled product.
Drawings
FIG. 1 is a graph showing the change in COD of a sewage material treated in the first example.
FIG. 2 is a graph showing changes in COD of sewage materials treated in examples 1 to 3 and comparative examples 1 to 4.
Advantageous effects
The method utilizes the agricultural waste to produce the sewage treatment material, has the advantages of low cost, energy conservation and environmental protection, integrates the dual effects of oxidation and electrolysis, and has remarkable advantage for removing COD in the sewage.
Detailed Description
The first embodiment is as follows:
(1) removing soil from 10kg of corn straws, putting the corn straws into a muffle furnace, introducing nitrogen, heating to 200 ℃, and keeping for 2 hours for dehydration;
(2) soaking the dehydrated corn straws in 50L of 5% ferric chloride solution for 8h, draining the liquid and drying;
(3) putting the straws into a muffle furnace, introducing nitrogen for heating, keeping the temperature at 200 ℃ for 1h at the temperature rise rate of 150 ℃/h between 50 ℃ and 200 ℃, keeping the temperature at 200 ℃ for 200 ℃/h at the temperature rise rate of 200 ℃/h between 200 ℃ and 1200 ℃, sintering for 4h at 1200 ℃, and cooling to room temperature along with the furnace;
(4) filling nitrogen into the material body and preserving the material body for later use.
Example two:
(1) removing soil from 10kg of corn straws, putting the corn straws into a muffle furnace, introducing nitrogen, heating to 200 ℃, and keeping for 2 hours for dehydration;
(2) soaking the dehydrated corn straws in 50L of 8% ferric chloride solution for 8h, draining the liquid and drying;
(3) putting the straws into a muffle furnace, introducing nitrogen for heating, keeping the temperature at 200 ℃ for 1h at the temperature rise rate of 150 ℃/h between 50 ℃ and 200 ℃, keeping the temperature at 200 ℃ for 200 ℃/h at the temperature rise rate of 200 ℃/h between 200 ℃ and 1200 ℃, sintering for 4h at 1200 ℃, and cooling to room temperature along with the furnace;
(4) filling nitrogen into the material body and preserving the material body for later use.
Example three:
(1) removing soil from 10kg of corn straws, putting the corn straws into a muffle furnace, introducing nitrogen, heating to 200 ℃, and keeping for 2 hours for dehydration;
(2) soaking the dehydrated corn straws in 50L of 10% ferric chloride solution for 8h, draining the liquid and drying;
(3) putting the straws into a muffle furnace, introducing nitrogen for heating, keeping the temperature at 200 ℃ for 1h at the temperature rise rate of 150 ℃/h between 50 ℃ and 200 ℃, keeping the temperature at 200 ℃ for 200 ℃/h at the temperature rise rate of 200 ℃/h between 200 ℃ and 1200 ℃, sintering for 4h at 1200 ℃, and cooling to room temperature along with the furnace;
(4) filling nitrogen into the material body and preserving the material body for later use.
Example four:
(1) removing soil from 10kg of corn straws, putting the corn straws into a muffle furnace, introducing nitrogen, heating to 200 ℃, and keeping for 2 hours for dehydration;
(2) soaking the dehydrated corn straws in 50L of 5% ferrous chloride solution for 8h, draining the liquid and drying;
(3) putting the straws into a muffle furnace, introducing nitrogen for heating, keeping the temperature at 200 ℃ for 1h at the temperature rise rate of 150 ℃/h between 50 ℃ and 200 ℃, keeping the temperature at 200 ℃ for 200 ℃/h at the temperature rise rate of 200 ℃/h between 200 ℃ and 1200 ℃, sintering for 4h at 1200 ℃, and cooling to room temperature along with the furnace;
(4) filling nitrogen into the material body and preserving the material body for later use.
Example five:
(1) putting 10kg of bagasse into a muffle furnace, introducing nitrogen, heating to 200 ℃, and keeping for 2 hours for dehydration;
(2) soaking the dewatered bagasse in 30L 5% ferric chloride solution for 8 hr, draining off liquid and drying;
(3) putting bagasse into a muffle furnace, introducing nitrogen gas for heating, keeping the temperature at 200 ℃ for 1h at the temperature rise rate of 150 ℃/h between 50 ℃ and 200 ℃, keeping the temperature at 200 ℃ for 200 ℃/h at the temperature rise rate of 200 ℃/h between 200 ℃ and 1200 ℃, sintering for 4h at 1200 ℃, and cooling to room temperature along with the furnace;
(4) filling nitrogen into the material body and preserving the material body for later use.
Comparative example one:
(1) removing soil from 10kg of corn straws, putting the corn straws into a muffle furnace, introducing nitrogen, heating to 200 ℃, and keeping for 2 hours for dehydration;
(2) soaking the dehydrated corn straws in 50L of 1% ferric chloride solution for 8h, draining the liquid and drying;
(3) putting the straws into a muffle furnace, introducing nitrogen for heating, keeping the temperature at 200 ℃ for 1h at the temperature rise rate of 150 ℃/h between 50 ℃ and 200 ℃, keeping the temperature at 200 ℃ for 200 ℃/h at the temperature rise rate of 200 ℃/h between 200 ℃ and 1200 ℃, sintering for 4h at 1200 ℃, and cooling to room temperature along with the furnace;
(4) filling nitrogen into the material body and preserving the material body for later use.
Comparative example two:
(1) removing soil from 10kg of corn straws, putting the corn straws into a muffle furnace, introducing nitrogen, heating to 200 ℃, and keeping for 2 hours for dehydration;
(2) soaking the dehydrated corn straws in 50L of 3% ferric chloride solution for 8h, draining the liquid and drying;
(3) putting the straws into a muffle furnace, introducing nitrogen for heating, keeping the temperature at 200 ℃ for 1h at the temperature rise rate of 150 ℃/h between 50 ℃ and 200 ℃, keeping the temperature at 200 ℃ for 200 ℃/h at the temperature rise rate of 200 ℃/h between 200 ℃ and 1200 ℃, sintering for 4h at 1200 ℃, and cooling to room temperature along with the furnace;
(4) filling nitrogen into the material body and preserving the material body for later use.
Comparative example three:
(1) removing soil from 10kg of corn straws, putting the corn straws into a muffle furnace, introducing nitrogen, heating to 200 ℃, and keeping for 2 hours for dehydration;
(2) soaking the dehydrated corn stalks in 50L of 12% ferric chloride solution for 8h, draining the liquid and drying;
(3) putting the straws into a muffle furnace, introducing nitrogen for heating, keeping the temperature at 200 ℃ for 1h at the temperature rise rate of 150 ℃/h between 50 ℃ and 200 ℃, keeping the temperature at 200 ℃ for 200 ℃/h at the temperature rise rate of 200 ℃/h between 200 ℃ and 1200 ℃, sintering for 4h at 1200 ℃, and cooling to room temperature along with the furnace;
(4) filling nitrogen into the material body and preserving the material body for later use.
Comparative example four:
(1) removing soil from 10kg of corn straws, putting the corn straws into a muffle furnace, introducing nitrogen, heating to 200 ℃, and keeping for 2 hours for dehydration;
(2) mixing the dehydrated corn straws with iron filings with equal weight;
(3) filling nitrogen into the material body and preserving the material body for later use.
Experiment 1: the experiment of example 1 was carried out, the water sample was 830mg/L of wastewater from a certain dyeing mill, after flocculation and sedimentation, 1L of wastewater was taken from each of 3 experimental groups, 15g of material was added, the pH was adjusted to 3, 5 and 7 with sulfuric acid, stirring was continued, and the change of COD in the water sample was recorded for 1-8 hours, the results are shown in FIG. 1.
Experiment 2: the experiments of examples 1-3 and comparative examples 1-4 were carried out, the water samples were the same as those of experiment 1, 1L of wastewater was taken from each of 7 experimental groups, 15g of the material was added, the pH was adjusted to 4 with sulfuric acid, stirring was continued, and the change in COD of the water sample was recorded for 1-8 hours, and the results are shown in FIG. 2.

Claims (6)

1. A method for preparing a sewage treatment material by utilizing agricultural wastes is characterized by comprising the following steps:
(1) heating agricultural waste to 200 ℃ in nitrogen, and keeping for 2h for dehydration;
(2) soaking the dehydrated waste in an iron salt solution for 8 hours, draining the liquid and drying;
(3) sintering the material body in nitrogen at 1200 ℃ for 4h, cooling to room temperature and taking out;
(4) the body was kept under nitrogen.
2. The method for preparing sewage treatment material using agricultural waste according to claim 1, wherein the agricultural waste in the step (1) is corn stover, sorghum straw, bagasse or other crop waste with porous structure.
3. The method for preparing sewage treatment material using agricultural waste as claimed in claim 1, wherein the heating temperature in step (1) is 180-250 ℃.
4. The method for preparing sewage treatment material by using agricultural waste material according to claim 1, wherein the iron salt in step (2) is one or a combination of ferric chloride and ferrous chloride, and the concentration of the iron salt solution is 5-10%.
5. The method for preparing a sewage treatment material using agricultural waste according to claim 1, wherein the sintering conditions in step (3) are a heating rate of 150 ℃/h between 50 ℃ and 200 ℃, a heat preservation time of 1h at 200 ℃, a heating rate of 200 ℃/h between 200 ℃ and 1200 ℃, and furnace cooling to room temperature after sintering for 4h at 1200 ℃.
6. The method for preparing a sewage treatment material using agricultural wastes according to claim 1, wherein the sewage treatment material is prepared by adding a water treatment material in an amount of 0.5-5% of the total amount of sewage, adjusting pH to 4-6, stirring for 8 hours, settling for 1 hour, and filtering the settled product.
CN202011406580.6A 2020-12-04 2020-12-04 Method for preparing sewage treatment material by utilizing agricultural waste Pending CN112845494A (en)

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CN106000416A (en) * 2016-06-03 2016-10-12 浙江科技学院 Method for preparing ozone catalyst by using agricultural waste straw as raw material and application thereof
CN106118613A (en) * 2016-06-27 2016-11-16 林春梅 A kind of environment-friendly type heat-storing material and preparation method thereof
CN106237985A (en) * 2016-08-16 2016-12-21 四川师范大学 A kind of straw base selectivity removal of mercury material and its preparation method and application
CN106467390A (en) * 2016-03-29 2017-03-01 济南圣泉集团股份有限公司 A kind of Graphene boccaro composite and its boccaro ware made, preparation method
CN109012592A (en) * 2018-08-28 2018-12-18 肖宇琛 The preparation method of charcoal compound adsorbent and to contain Cr (VI) waste water restorative procedure
CN109046247A (en) * 2018-09-08 2018-12-21 重庆大学 Strengthen the modification biological charcoal and preparation method thereof of absorption organic dyestuff
CN110518262A (en) * 2019-08-13 2019-11-29 武汉长海电力推进和化学电源有限公司 A kind of anode of microbial fuel cell material and preparation method thereof
CN111302340A (en) * 2020-04-26 2020-06-19 南京工业大学 Preparation method of biogas residue biochar

Patent Citations (12)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101905979A (en) * 2009-06-04 2010-12-08 佳木斯大学 Method for preparing carbon/carbon-silicon carbide (C/C-SiC) composite self-sealing and anti-oxidation coating
CN104003384A (en) * 2013-02-27 2014-08-27 上海化学工业区中法水务发展有限公司 Method for preparing activated carbon by using mixture of activated sludge and reed straws
CN103213984A (en) * 2013-03-25 2013-07-24 中山火炬职业技术学院 Method for preparing high thermal conductivity active carbon taking waste cotton cloth as raw material
CN105536703A (en) * 2015-12-25 2016-05-04 华中农业大学 Preparation method for magnetic biological carbon by one-step synthesis
CN106467390A (en) * 2016-03-29 2017-03-01 济南圣泉集团股份有限公司 A kind of Graphene boccaro composite and its boccaro ware made, preparation method
CN106000416A (en) * 2016-06-03 2016-10-12 浙江科技学院 Method for preparing ozone catalyst by using agricultural waste straw as raw material and application thereof
CN106118613A (en) * 2016-06-27 2016-11-16 林春梅 A kind of environment-friendly type heat-storing material and preparation method thereof
CN106237985A (en) * 2016-08-16 2016-12-21 四川师范大学 A kind of straw base selectivity removal of mercury material and its preparation method and application
CN109012592A (en) * 2018-08-28 2018-12-18 肖宇琛 The preparation method of charcoal compound adsorbent and to contain Cr (VI) waste water restorative procedure
CN109046247A (en) * 2018-09-08 2018-12-21 重庆大学 Strengthen the modification biological charcoal and preparation method thereof of absorption organic dyestuff
CN110518262A (en) * 2019-08-13 2019-11-29 武汉长海电力推进和化学电源有限公司 A kind of anode of microbial fuel cell material and preparation method thereof
CN111302340A (en) * 2020-04-26 2020-06-19 南京工业大学 Preparation method of biogas residue biochar

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Application publication date: 20210528