METHOD FOR PREPARING BIOCHAR AND HYDROGEN BY UTILIZING ANAEROBIC FERMENTATION BYPRODUCTS

Abstract

A method for preparing biochar and hydrogen by utilizing anaerobic fermentation byproducts, the method including: (1) mixing a first straw, seeding sludge and distilled water, and then carrying out anaerobic fermentation to obtain a mixed product after fermentation; (2) performing separation on the mixed product to obtain a second straw and biogas slurry; and (3) carbonizing the second straw to obtain biochar, and collecting gas after a pressurized catalytic reaction on the biogas slurry to obtain hydrogen.

Claims

1. A method for preparing biochar and hydrogen by utilizing anaerobic fermentation byproducts, the method comprising: mixing first straw, seeding sludge, and distilled water for anaerobic fermentation to obtain a fermented mixed product; separating fermented straw from the fermented mixed product to obtain second straw; separating and recovering a biogas slurry from the fermented mixed product; carbonizing the obtained second straw to obtain the biochar; and collecting gas after a pressurized catalytic reaction of the obtained biogas slurry.

2. The method according to claim 1, wherein: the mass ratio of the seeding sludge to the first straw is (25-30):1; the mass ratio of the distilled water to the first straw is (10-20):1; the length of the first straw is 2-3 cm; the first straw is an air-dried straw; the second straw is washed and dried before the carbonization step; the mesh number of the second straw is 40-80 mesh.

3. The method according to claim 1, wherein: the anaerobic fermentation is realized in an anaerobic fermentation tank; the seeding sludge is the discharged sludge from an anaerobic fermentation tank; in the anaerobic fermentation, the fermentation temperature is 20-25° C.; the fermentation time is 7-14 days; and the materials are stirred every 10-14 hours; during the anaerobic fermentation, an anaerobic environment is realized by introducing inert gas comprising nitrogen.

4. The method according to claim 1, wherein: the carbonization step is realized in a pyrolytic carbonization device; the pyrolytic carbonization device comprises a high-temperature tube furnace; in the carbonization step, the high-temperature tube furnace has a carbonization temperature of 750-850° C. and a pyrolytic carbonization time is 50-70 min.

5. The method according to claim 1, wherein: the step of collecting gas after a pressurized catalytic reaction of the obtained biogas slurry comprises, after adding a catalyst to the biogas slurry, reacting under a pressurized condition, and then cooling and collecting gas.

6. The method according to claim 5, wherein: the concentration of the catalyst is 2-5 g/L; the reaction pressure is 1.5-5.0 MPa.

7. The method according to claim 6, wherein: the reaction pressure is 2.5-3.0 MPa.

8. The method according to claim 5, wherein: the reaction temperature is 150-250° C.; the reaction time is 2.5-3 hours.

9. The method according to claim 8, wherein: the reaction temperature is 200-250° C.; the reaction time is 3 hours.

10. The method according to claim 5, wherein: the stirring speed is 200-300 r/min.

11. The method according to claim 10, wherein: the stirring speed is 200-250 r/min.

12. The method according to claim 5, wherein a method for catalyst preparation comprises: a supported nickel-based catalyst is prepared by an equal volume impregnation method, which is reduced in a hydrogen gas atmosphere to obtain a black powdery solid comprising the catalyst.

13. The method according to claim 12, wherein the method for catalyst preparation comprises: 1) the supported nickel-based catalyst is prepared by an equal volume impregnation method: nickel nitrate is added to distilled water and stirred for 15-25 min, then a catalyst carrier is added and stirred for 15-25 min, and dried at 85-95° C. and taken out to obtain a solid A; 2) under a hydrogen gas atmosphere, the solid A obtained in step 1) is reduced at 550-650° C. for 2.5-3.5 hours to obtain a black powdery solid B comprising the catalyst, wherein the Ni content in the supported nickel-based catalyst is 15-20 wt %.

14. The method according to claim 5, wherein: the catalyst carrier is a CeO.sub.2 carrier or Al.sub.2O.sub.3 carrier, wherein the preparation method of the CeO.sub.2 carrier comprises: cerium nitrate is baked at 550-650° C. for 1.5-2.5 hours to obtain a CeO.sub.2 carrier; the biogas slurry and the catalyst are added to a reactor for reaction, the reactor comprising a micro-reactor equipped with means for heating, pressurizing and stirring; the cooling step in the cooling and collecting gas is realized by an ice bath cooling method.

15. A biochar prepared by the method according to claim 1, wherein the specific surface area of the biochar is 240-288 m.sup.2/g.

16. A method comprising: performing anaerobic fermentation of a mixture of straw, seeding sludge, and distilled water to obtain a fermented mixed product; and carbonizing fermented straw separated from the fermented mixed product, to produce biochar.

17. The method of claim 16, further comprising collecting gas from a pressurized catalytic reaction of biogas slurry separated from the fermented mixed product.

18. The method of claim 16, wherein: the mass ratio of the seeding sludge to the straw is (25-30):1; the mass ratio of the distilled water to the straw is (10-20):1; the length of the straw is 2-3 cm.

19. The method of claim 16, wherein: the carbonizing is realized in a pyrolytic carbonization device comprising a high-temperature tube furnace; in the carbonizing, the high-temperature tube furnace has a carbonization temperature of 750-850° C. and a pyrolytic carbonization time is 50-70 min.

20. A biochar prepared by the method according to claim 16, wherein the specific surface area of the biochar is 240-288 m.sup.2/g.

Description

BRIEF DESCRIPTION OF THE DRAWINGS

[0012] FIG. 1 is a process flow chart of an example of the present disclosure;

[0013] FIG. 2 is a Fourier transform infrared spectrum of the straw before and after the anaerobic fermentation treatment in Example 1 of the present disclosure;

[0014] FIG. 3 is an X-ray diffraction pattern of the straw before and after the anaerobic fermentation treatment in Example 1 of the present disclosure;

[0015] FIG. 4 is a scanning electron micrograph of the straw before and after the anaerobic fermentation treatment in Example 1 of the present disclosure;

[0016] FIG. 5 is a flow chart of the high-temperature tube furnace pyrolytic device in Example 1 of the present disclosure;

[0017] FIG. 6 is a scanning electron micrograph of the straw biochar before and after the anaerobic fermentation treatment in Example 1 of the present disclosure;

[0018] FIG. 7 is a flow chart of biogas slurry derived from anaerobic fermentation to produce hydrogen in an example of the present disclosure.

[0019] List of Reference numbers: 1—crucible, 2—the first high-temperature resistant ceramic pipe plug, 3—the second high-temperature resistant ceramic pipe plug, 4—stainless steel pushrod, 5—mass flowmeter, 6—high-temperature tube furnace, 7—temperature control system, 8—condenser, 9—filter, 10—pyrolytic gas purification system.

DESCRIPTION OF EMBODIMENTS

[0020] The present disclosure discloses a method for preparing biochar and hydrogen by utilizing anaerobic fermentation byproducts, comprising:

[0021] mixing a first straw, seeding sludge, and distilled water for anaerobic fermentation to obtain a fermented mixed product;

[0022] separating the fermented straw from the mixed product to obtain a second straw; and separating and recovering a biogas slurry from the mixed product;

[0023] carbonizing the obtained second straw to obtain the biochar; and collecting the gas, i.e., the hydrogen, after a pressurized catalytic reaction of the obtained biogas slurry.

[0024] Preferably, the mass ratio of the first straw to the seeding sludge is (25-30):1.

[0025] Preferably, the mass ratio of the first straw to the distilled water is (10-20):1.

[0026] Preferably, the length of the first straw is 2-3 cm.

[0027] Preferably, the first straw is an air-dried straw.

[0028] Preferably, the second straw is washed and dried before the carbonization step.

[0029] Preferably, the mesh number of the second straw is 40-80 mesh.

[0030] Preferably, the anaerobic fermentation is realized in an anaerobic fermentation tank.

[0031] Preferably, the seeding sludge is a discharged sludge from the anaerobic fermentation tank.

[0032] Preferably, in the anaerobic fermentation step, the fermentation temperature is 20-25° C.; the fermentation time is 7-14 days; and the materials are stirred every 10-14 hours.

[0033] Preferably, during the anaerobic fermentation, the anaerobic environment is realized by introducing inert gases.

[0034] Preferably, the inert gas comprises nitrogen.

[0035] Preferably, the carbonization step is realized in a pyrolytic carbonization device.

[0036] Preferably, the pyrolytic carbonization device comprises a high-temperature tube furnace.

[0037] Preferably, in the carbonization step, the high-temperature tube furnace has a carbonization temperature of 750-850° C. and a pyrolytic carbonization time of 50-70 min.

[0038] The present disclosure also discloses the biochar prepared by the above method, characterized in that, the specific surface area of the biochar is 240-288 m.sup.2/g.

[0039] Preferably, the step of collecting gas after a pressurized catalytic reaction of the obtained biogas slurry specifically comprises: after adding a catalyst to the biogas slurry, reacting under pressurized conditions, then cooling and collecting gas.

[0040] Preferably, the concentration of the catalyst is 2-5 g/L.

[0041] Preferably, the reaction pressure is 1.5-5.0 MPa, more preferably 2.5-3.0 MPa.

[0042] Preferably, the reaction temperature is 150-250° C., more preferably 200-250° C.

[0043] Preferably, the stirring speed is 200-300 r/min, more preferably 200-250 r/min.

[0044] Preferably, the reaction time is 2.5-3 h, more preferably 3 h.

[0045] Preferably, the preparation method of the catalyst is as follows: a supported nickel-based catalyst is prepared by an equal volume impregnation method, which is reduced in a hydrogen atmosphere to obtain a black powdery solid, i.e., the catalyst.

[0046] Preferably, the preparation method of the catalyst specifically comprises the following steps:

[0047] 1) the supported nickel-based catalyst is prepared by an equal volume impregnation method as follows: nickel nitrate is added to distilled water and stirred for 15-25 min, then a catalyst carrier is added and stirred for 15-25 min, which is dried at 85-95° C. and taken out to obtain solid A;

[0048] 2) under a hydrogen atmosphere, the solid A obtained in step 1) is reduced at 550-650° C. for 2.5-3.5 hours to obtain a black powdery solid B, i.e., the catalyst;

[0049] Preferably, the Ni content in the supported nickel-based catalyst is 15-20 wt %.

[0050] Preferably, the catalyst carrier is a CeO.sub.2 carrier or Al.sub.2O.sub.3 carrier.

[0051] Preferably, the preparation method of CeO.sub.2 carrier is as follows: cerium nitrate is baked at 550-650° C. for 1.5-2.5 hours to obtain a CeO.sub.2 carrier.

[0052] Preferably, the biogas slurry and the catalyst are added to the reactor for reaction.

[0053] Preferably, the reactor is a micro-reactor equipped with means for heating, pressurizing and stirring.

[0054] Preferably, the cooling step in the cooling and collecting gas is realized by an ice bath cooling method.

[0055] In an exemplary embodiment, a method for preparing biochar and hydrogen by utilizing anaerobic fermentation byproducts in the present disclosure is as follows: the naturally air-dried straw is coarsely pulverized into 2-3 cm; the straw, seeding sludge at a mass ratio of seeding sludge to straw of (25-30):1, and distilled water at a mass ratio of distilled water to straw of (10-20):1 are uniformly mixed, and poured into a fermentation tank, and then nitrogen gas is purged to ensure anaerobic conditions; the fermentation tank is placed in a room temperature environment for 7-14 days, and regularly stirred; the fermented mixed materials are sieved and washed to recover the fermented straw; sieve residue is precipitated and separated by centrifugation, and the biogas slurry is collected; the straw powders are obtained by drying and pulverization, and placed in a pyrolytic furnace for carbonization to obtain the biochar; 100 mL of the biogas slurry is placed in a reactor, and the reactor is sealed after adding the catalyst and a magnetic rotor; nitrogen gas is introduced to exhaust the air and the pressure is adjusted to 2.5-3.0 MPa, the temperature is 200-250° C., and the stirring speed reaches 200-300 r/min; after reacting for 3 hours, the reactor is placed in an ice bath to cool to the room temperature, and the non-condensable gas obtained at the gas outlet is a gas phase product containing hydrogen.

[0056] The specific surface area of the biochar obtained from the biomass after the anaerobic fermentation treatment of the present disclosure reaches 240-288 m.sup.2/g. Compared with the initial straw, the specific surface area of biochar is increased by 31-79 m.sup.2/g, effectively improving the performance of the biochar. The prepared biochar can be directly used in the fields of soil fertility improvement, carbon sink increase and emission reduction, and environmental pollution restoration.

[0057] The seeding sludge of the present disclosure is discharged sludge from the anaerobic fermentation tank under normal operation.

[0058] The pyrolytic carbonization device of the present disclosure includes but is not limited to a high-temperature tube furnace, and may be other high-temperature devices that can realize pyrolysis.

[0059] The high-temperature tube furnace of the present disclosure has a carbonization temperature of 800° C. However, this temperature can be adjusted during the actual application, as long as the pyrolytic carbonization of straw can be realized.

[0060] The pyrolytic carbonization time of the present disclosure is 60 min. This time can be appropriately adjusted according to actual requirements, and can be based on no release of combustible components in the pyrolytic gas to ensure complete pyrolysis.

[0061] The biogas slurry used in the present disclosure includes, but is not limited to, straw and liquid phase byproducts obtained by anaerobic fermentation of sludge.

[0062] The supported nickel-based catalyst carrier for hydrogen production from biogas slurry in the present disclosure includes but is not limited to CeO.sub.2 or Al.sub.2O.sub.3. Any carrier with high specific surface area, high thermal stability, or the like can be adopted as the catalyst carrier used in the present disclosure, for example, molecular sieve, activated carbon carrier, etc.

[0063] The loading amount of the active component Ni in the supported nickel-based catalyst for hydrogen production from biogas slurry of the present disclosure is in the range of 15-20 wt %. If the loading amount is too low, the number of the metal active sites is insufficient, and thus the reaction rate is low. If the loading amount is too high, it will lead to metal agglomeration, and thus the catalytic activity is low. The catalyst dosage is 2-5 g/L; if the dosage is too low, it is not enough to exert the catalytic effect, and if the dosage is too high, it will increase the cost.

[0064] The reactor for hydrogen production from biogas slurry of the present disclosure is a micro-reactor equipped with means for heating, pressurizing and stirring.

[0065] The reaction pressure for hydrogen production from biogas slurry in the present disclosure is in the range of 2.5-3.0 MPa. When the pressure is below 2.5 MPa, the saturated vapor pressure of the biogas slurry will be easily reached to gasify the raw material. When the pressure is above 3.0 MPa, side reactions increase, which is detrimental to H.sub.2 generation.

[0066] The catalytic reaction temperature for hydrogen production from biogas slurry in the present disclosure is in the range of 200-250° C. When the temperature is below 200° C., the organic nitrogen in the biogas slurry is easily reacted with water to produce ammonia. When the temperature is above 250° C., the water-gas shift reaction is increased, the hydrogen content and selectivity are decreased, CO2 content is increased, and energy consumption is increased.

[0067] In another exemplary embodiment, a method for preparing biochar and hydrogen by utilizing anaerobic fermentation byproducts in the present disclosure comprises the following steps:

[0068] 1) Coarse pulverization of straw: the naturally air-dried straw is coarsely pulverized, and the straw with a length of about 2-3 cm is used for subsequent treatment;

[0069] 2) Anaerobic fermentation treatment: the straw pulverized in step 1) and seeding sludge at a mass ratio of seeding sludge to straw of (25-30):1 are uniformly mixed and poured into a fermentation tank, and distilled water at a mass ratio of distilled water to straw of (10-20):1 is added, and the mixed materials are stirred well. A nitrogen pipe is submerged into the bottom of the fermentation tank to purge for 3-5 min to ensure an anaerobic environment. There is a biogas outlet on the top of the fermentation tank. An exit pipe is submerged into water to prevent the air from flowing back into the fermentation tank. The fermentation tank is placed in an environment of normal temperature 20-25° C. for 7-14 days, and the fermented materials are stirred approximately every 12 hours to prevent slagging and floating;

[0070] 3) Recovery of fermented straw: the mixed materials after the fermentation treatment in step 2) are screened, and the oversized materials are rinsed repeatedly with tap water until the washed solution is transparent and colorless to obtain the pretreated straw;

[0071] 4) Collection of fermented biogas slurry: the undersized materials of the mixed materials after the fermentation treatment in step 3) are precipitated and centrifuged. The centrifuged supernatant is obtained as the biogas slurry;

[0072] 5) Drying and pulverization of straw: the washed straw is placed in an oven at 55-60° C. for 48 hours, then pulverized and sieved to obtain the straw with 40-80 mesh for use;

[0073] 6) Carbonization of straw: the straw pulverized and sieved in step 4) is placed in a pyrolytic furnace for carbonization, and the reaction is performed until no combustible components are released in the pyrolytic gas, and naturally cooled to the room temperature to obtain the straw biochar;

[0074] 7) Preparation of catalyst for hydrogen production from biogas slurry: the supported nickel-based catalyst is prepared by an equal volume impregnation method as follows: nickel nitrate is added to distilled water and stirred for 15-25 min, then a catalyst carrier is added and stirred for 15-25 min, which is dried at 85-95° C. and taken out to obtain solid A;

[0075] 8) Hydrogen reduction of the catalyst for hydrogen production from biogas slurry: under a hydrogen atmosphere, the solid A obtained in step 7) is reduced at 550-650° C. for 2.5-3.5 hours to obtain a black powdery solid B, i.e., the catalyst;

[0076] wherein the Ni amount is 15-20 wt %, and the carrier may be CeO.sub.2 and Al.sub.2O.sub.3, etc.; and a black powdery catalyst is obtained after reduction under a hydrogen atmosphere.

[0077] 9) Catalytic and pressurized hydrogen production from biogas slurry: the reactor is sealed after adding the biogas slurry, the catalyst in step 7) and a magnetic rotor; then nitrogen is introduced to exhaust the air, and the pressure is adjusted to 2.5-3.0 MPa, the reaction temperature is 200-250° C., the stirring speed is 200-300 r/min, and the reaction time is 3 hours;

[0078] 10) Product collection of hydrogen from biogas slurry: after stopping the heating and stirring, the reactor is placed in an ice bath to cool to room temperature, and the non-condensable gas obtained at the gas outlet is the gas phase products containing hydrogen.

EXAMPLES

[0079] The technical solutions of the present disclosure will be further explained herein below through specific examples with reference to the accompanying drawings. It should be noted that the following specific examples are merely illustrative, and the protection scope of the present disclosure is not limited thereto.

[0080] The chemical reagents and raw materials used in the following examples are all commercially available or self-made by well-known preparation methods.

Example 1

[0081] A method for preparing biochar and hydrogen by utilizing anaerobic fermentation byproducts adopted the process flow as shown in FIG. 1.

[0082] 1) Coarse pulverization of straw: 500 g of the naturally air-dried corn straw was coarsely pulverized, and the straw with a length of about 2 cm was taken for use;

[0083] 2) Anaerobic fermentation treatment: 15 kg of the seeding sludge (the mass ratio of seeding sludge to straw being 30:1) and the coarsely pulverized straw were uniformly mixed and poured into a fermentation tank, and then 10 kg of the distilled water (the mass ratio of distilled water to straw mass being 20:1) was added, and the mixed materials were stirred well; a nitrogen gas pipe was submerged into the bottom of the fermentation tank to purge for 3 min to ensure an anaerobic environment; and there was a biogas outlet on the top of the fermentation tank, and an exit pipe was submerged into water to prevent the air from flowing back into the fermentation tank. The fermentation tank was placed in an environment of 25° C. for 14 days, and the fermented materials were stirred every 12 hours to prevent slagging and floating;

[0084] 3) Recovery of fermented straw: the mixed materials after the fermentation pretreatment in step 2) were screened, and the oversize materials were rinsed repeatedly with tap water until the washed solution was transparent and colorless to obtain the treated straw;

[0085] 4) Collection of fermented biogas slurry: the undersized materials of the mixed materials after the fermentation treatment in step 3) were precipitated and centrifuged. The centrifuged supernatant was obtained as the biogas slurry;

[0086] 5) Drying and pulverization of straw: the washed straw was placed in an oven at 60° C. for drying, and the dried straw was pulverized and sieved to obtain the straw with 40-80 mesh for characterization and carbonization; the Fourier transform infrared spectra, the X-ray diffraction pattern, and the scanning electron micrograph of the pretreated straw were shown in FIG. 2, FIG. 3, and FIG. 4, respectively. As shown in FIG. 2, the absorption strength of cellulose and hemicellulose was weakened at 1723 cm.sup.−1, 1379 cm.sup.−1, 1161 cm.sup.−1, and 899 cm.sup.−1, and the lignin stretching vibration peaks were enhanced at 1601 cm.sup.−1, 1515 cm.sup.−1, and 1247 cm.sup.−1, indicating that the mild anaerobic fermentation pretreatment improved the organic composition of the straw, reduced the contents of cellulose and hemicellulose, and enriched the lignin. It demonstrated that the anaerobic fermentation pretreatment improved the organic composition of the biomass, reducing the generation of volatile products (tar) from the source during the carbonization, and reduced the risk of biochar pore blockage by tar; as shown in FIG. 3, the diffraction intensity representing the ordered structure of the straw at 2θ≈22°-23° became weaker, the diffraction peak became broader, and the randomness of the straw structure was enhanced after pretreatment; as shown in FIG. 4, the straw structure was loose and the pores were obvious after pretreatment, which helped to strengthen the mass and heat transfer effects during the carbonization, promoted the rapid escape of volatiles, and left abundant pores, so as to produce biochar with high specific surface area;

[0087] 6) Carbonization of straw: the high-temperature tube furnace in FIG. 5 was used for the pyrolytic carbonization of the straw. The straw pulverized and sieved in step 4) was placed in the quartz crucible 1, and the crucible was placed at one end of the high-temperature tube furnace 6. The first high-temperature resistant ceramic pipe plug 2 and the second high-temperature resistant ceramic pipe plug 3 were respectively placed at both ends of the crucible, wherein the first high-temperature resistant ceramic pipe plug 2 was used to isolate the heating zone of the high-temperature tube furnace 6, and the second high-temperature resistant ceramic pipe plug 3 was connected with the stainless steel pushrod 4. The high-temperature tube furnace 6 was closed and initiated, the mass flowmeter 5 was used to control the nitrogen flow rate to 200 mL/min, and the temperature control system 7 was adjusted such that the furnace body of the high-temperature tube furnace 6 was heated to the required pyrolytic temperature of 800° C. in a nitrogen atmosphere. The stainless steel pushrod 4 was used to push the second high-temperature resistant ceramic pipe plug 3 and the crucible to the heating zone of the high-temperature tube furnace 6, followed by constant temperature pyrolysis for 60 min and natural cooling to the room temperature to obtain the biochar. The pyrolytic gas is flowed through the condenser 8, filter 9, and pyrolytic gas purification system 10, and then was collected, burned, and discharged. The scanning electron micrograph of the biochar was shown in FIG. 6. It can be seen that the pore structure of the straw biochar was more abundant after the mild fermentation pretreatment. The specific surface area of the prepared biochar was tested with an automatic specific surface area analyzer, and the specific values were shown in Table 1;

[0088] 7) Preparation of catalyst for hydrogen production from biogas slurry and hydrogen reduction: a Ni/Al.sub.2O.sub.3 catalyst with a Ni loading amount of 15 wt % was prepared by an equal volume impregnation method, which was reduced under a hydrogen atmosphere to obtain a black powdery catalyst;

[0089] 8) Catalytic and pressurized hydrogen production from biogas slurry: 0.2 g of catalyst and 100 mL of biogas slurry were placed in the reactor, and then the reactor was sealed; nitrogen was introduced to exhaust the air and the pressure was adjusted to 2.5 MPa, the temperature was heated to 250° C., the stirring speed was 250 r/min, and the reaction time was 3 hours;

[0090] 9) Products collection of hydrogen from biogas slurry: after stopping the heating and stirring, the reactor was placed in an ice bath to cool to the room temperature, and the non-condensable gas obtained at the gas outlet was the gas phase products containing hydrogen. The composition and the contents of the gas product were shown in Table 2.

Example 2

[0091] This example used the same raw materials and method as those in Example 1, except that the nickel-based catalyst carrier in the hydrogen production from biogas slurry was CeO.sub.2. The test data of the specific surface area for the biochar from the biogas residue as anaerobic fermentation byproducts were shown in Table 1, and the composition and the contents of the gas product of the hydrogen production from biogas slurry were shown in Table 2.

Example 3

[0092] This example used the same raw materials and method as those in Example 1, except that the catalyst dosage in the hydrogen production from biogas slurry was 0.5 g, and the reactor was heated to 200° C. The test data of the specific surface area for the biochar from the biogas residue as anaerobic fermentation byproducts were shown in Table 1, and the composition and the contents of the gas product of the hydrogen production from biogas slurry were shown in Table 2.

Example 4

[0093] This example used the same raw materials and method as those in Example 1, except that the catalyst dosage in the hydrogen gas production from biogas slurry was 0.5 g, and the reaction pressure was 2.8 MPa. The test data of the specific surface area for the biochar from the biogas residue as anaerobic fermentation byproducts were shown in Table 1, and the composition and the contents of the gas product of the hydrogen production from biogas slurry were shown in Table 2.

Example 5

[0094] This example used the same raw materials and method as those in Example 1, except that the catalyst dosage in the hydrogen production from biogas slurry was 0.5 g, and the reaction pressure of the reactor was 3.0 MPa. The test data of the specific surface area for the biochar from the biogas residue as anaerobic fermentation byproducts were shown in Table 1, and the composition and the contents of the gas product of the hydrogen production from biogas slurry were shown in Table 2.

Example 6

[0095] This example used the same raw materials and method as those in Example 1, except that the nickel-based catalyst carrier in the hydrogen gas production from biogas slurry was CeO.sub.2, the catalyst dosage was 0.5 g, and the reactor was heated to 200° C. The test data of the specific surface area for the biochar from the biogas residue as anaerobic fermentation byproducts were shown in Table 1, and the composition and the contents of the gas product of the hydrogen production from biogas slurry were shown in Table 2.

Example 7

[0096] This example used the same raw materials and method as those in Example 1, except that the nickel-based catalyst carrier in the hydrogen gas production from biogas slurry was CeO.sub.2, the catalyst dosage was 0.5 g, the reactor was heated to 225° C., and the reaction pressure of the reactor was 2.8 MPa. The test data of the specific surface area for the biochar from the biogas residue as anaerobic fermentation byproducts were shown in Table 1, and the composition and the contents of the gas product of the hydrogen production from biogas slurry were shown in Table 2.

Example 8

[0097] This example used the same raw materials and method as those in Example 1, except that the nickel-based catalyst carrier in the hydrogen gas production from biogas slurry was CeO.sub.2, the catalyst dosage was 0.5 g, and the reaction pressure of the reactor was 3.0 MPa. The test data of the specific surface area for the biochar from the biogas residue as anaerobic fermentation byproducts were shown in Table 1, and the composition and the contents of the gas product of the hydrogen production from biogas slurry were shown in Table 2.

Example 9

[0098] This example used the same raw materials and method as those in Example 1, except that the seeding sludge had a mass of 13.75 kg (the mass ratio of seeding sludge to straw being 27.5:1), the distilled water had a mass of 7.5 kg (the mass ratio of distilled water to straw being 15:1), and the fermentation pretreatment period was 10 days.

[0099] The test data of the specific surface area for the biochar from the biogas residue as anaerobic fermentation byproducts were shown in Table 1.

Example 10

[0100] This example used the same raw materials and method as those in Example 1, except that the seeding sludge had a mass of 12.5 kg (the mass ratio of seeding sludge to straw being 25:1), the distilled water had a mass of 5 kg (the mass ratio of distilled water to straw being 10:1), and the fermentation pretreatment period was 7 days.

[0101] The test data of the specific surface area for the biochar from the biogas residue as anaerobic fermentation byproducts were shown in Table 1.

[0102] Table 1 summarizes the data for the carbonization from biogas residue as anaerobic fermentation byproducts in the Examples.

TABLE-US-00001 Operating conditions Biochar properties Mass ratio of seeding Mass ratio of distilled Specific surface Item sludge to straw water to straw Period/days area (m.sup.2/g) Blank none none none 209 Examples 1-8 30 20 14 288 Example 9 27.5 15 10 255 Example 10 25 10 7 240

[0103] Table 2 summarizes the data for the hydrogen production from biogas slurry as anaerobic fermentation byproducts in the Examples.

TABLE-US-00002 Operating conditions Example Catalyst Catalyst Temperature/ Pressure/ Stirring Reaction Gas volume ratio No. Type amount ° C. MPa rate/r/min time/h H.sub.2/% CO.sub.2/% NH.sub.3/% 1 Ni/Al.sub.2O.sub.3 0.2 250 2.5 250 3 0 8.934 91.06 2 Ni/CeO.sub.2 0.2 250 2.5 250 3 0.97 0.44 98.59 3 Ni/Al.sub.2O.sub.3 0.5 200 2.5 250 3 0 22.53 77.47 4 Ni/Al.sub.2O.sub.3 0.5 225 2.8 250 3 6.23 26.22 67.55 5 Ni/Al.sub.2O.sub.3 0.5 250 3.0 250 3 5.64 19.44 74.92 6 Ni/CeO.sub.2 0.5 200 2.5 250 3 21.53 35.03 43.44 7 Ni/CeO.sub.2 0.5 225 2.8 250 3 35.44 27.72 36.84 8 Ni/CeO.sub.2 0.5 250 3.0 250 3 9.11 25.40 65.49

[0104] The present disclosure proposes a method for preparing biochar and hydrogen from anaerobic fermentation byproducts, which is simple in operation, low in cost and environmentally friendly. Those skilled in the art can realize the present invention by appropriately changing the raw material proportions, the fermentation period during the fermentation pretreatment, the reaction temperature and the reaction pressure in hydrogen production from biogas slurry in accordance with the disclosure herein. Therefore, the method for preparing biochar and hydrogen by utilizing anaerobic fermentation byproducts in the present disclosure has at least one of the following advantages over the prior art:

[0105] 1. The present disclosure proposes the method and use for preparing biochar from the biogas residue as anaerobic fermentation solid byproducts and for preparing hydrogen from liquid byproducts, provides a new route for resource recycling and disposal of anaerobic fermentation byproducts, and provides technical references for the preparation of biochar with high specific surface area from biomass and hydrogen production from biogas slurry;

[0106] 2. The present disclosure proposes to couple the anaerobic fermentation process with the carbonization process. The anaerobic fermentation can effectively improve the composition proportion of biomass lignocellulose and breakdown the chimeric structure inside the biomass, reducing the risk of blocking the pores of biochar by the tar from the source during carbonization, and enhancing the mass and heat transfer process during carbonization, significantly improving the specific surface area of the biochar obtained from carbonization. The specific surface area of the biochar prepared by this method reaches 240-288 m.sup.2/g, significantly higher than the specific surface area (209 m.sup.2/g) of the biochar prepared by the initial biomass; the pore structure of the biochar obtained after pretreatment is more abundant, improving the use performance to a certain extent. It can be used in the fields of soil fertility improvement, carbon sink increase and emission reduction, and environmental pollution restoration, with a great potential;

[0107] 3. The present disclosure provides a method for preparing hydrogen by aqueous phase reforming of renewable biogas slurry. The method omits the vaporization step of raw materials, and directly produces hydrogen in a one-step reaction under relatively mild reaction conditions (150-250° C., 1.5-5.0 MPa), while minimizing the influence of side reactions that are easily occurred under high temperature conditions; under the optimal implementation conditions, the proportion of hydrogen in the detectable components is 35% or more; the hydrogen produced can enrich the forms of gas in the biogas industry chains and enhance the values of gas product; and the hydrogen can be used for heating or power generation on-site;

[0108] 4. The present disclosure is simple in operation, low in cost and environmentally friendly, and broadens the routes and methods for the disposal of biogas residue and biogas slurry as anaerobic fermentation byproducts.

[0109] The specific examples described above further illustrate the objectives, technical solutions, and beneficial effects of the present disclosure in detail. It should be understood that the above descriptions are merely specific examples of the present disclosure and are not intended to limit the present disclosure. Any modifications, equivalent replacements, improvements, and the like within the spirit and principle of the present disclosure shall be included in the protection scope of the present disclosure.