Use of Porous Glass Media for a Biofilter to Remove Odorous Compounds from an Air Stream
US-2020368683-A1 · Nov 26, 2020 · US
US11491444B2 · US · B2
| Field | Value |
|---|---|
| Publication number | US-11491444-B2 |
| Application number | US-202016747564-A |
| Country | US |
| Kind code | B2 |
| Filing date | Jan 21, 2020 |
| Priority date | Feb 15, 2019 |
| Publication date | Nov 8, 2022 |
| Grant date | Nov 8, 2022 |
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The invention discloses a preparation method and application of in-situ high-efficiency degradation carbon based material of VOCs in landfill based on waste regeneration, which comprises the following steps: air drying the agricultural and forestry wastes to a moisture content of 0.001 wt %˜20 wt %, and the agricultural and forestry wastes mainly include: straw, wheat straw, leaves, branches, weeds, crushing them to a particle size of 0-50 mm with a grinder, and then using urea or amide as modifier The nitrogen enriched biochar was prepared by mixing the crushed agricultural and forestry wastes with a mass ratio of 1:50-1:10; the nitrogen enriched biochar was prepared by retorting the nitrogen doped agricultural and forestry wastes at 300-600° C. for 20-60 min, and then cooling them rapidly; the nitrogen enriched biochar was mixed with the sewage sludge with a moisture content of 90-98 wt. % with a weight ratio of 20:1-10:1 to get the nitrogen enriched microorganism The degradation efficiency of TVOCs in landfill is 96.74%˜99.70%.
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The invention claimed is: 1. A preparation method of in-situ efficiency degradation carbon based material of VOCs in landfill based on waste regeneration, which is characterized in that the following steps are included: S01: pretreatment of raw materials: air dry the agricultural and forestry wastes to a moisture content of 0.001 wt %˜20 wt %, and crush them to a particle size of 0˜50 mm with a grinder, Then mix the organic nitrogen as a modifier with the crushed agricultural and forestry wastes in a mass ratio of 1:50˜1:10 to uniformly prepare the agricultural and forestry wastes mixed with nitrogen; S02: after 20-60 minutes of dry distillation at 300-600° C., the nitrogen doped agricultural and forestry wastes prepared in step S01 were rapidly cooled to prepare nitrogen rich biochar; S03: preparation of microbial rich nitrogen biochar: the microbial rich nitrogen biochar was prepared by mixing the nitrogen rich biochar obtained in step S02 and sewage sludge with water content of 90-98 wt. % in the proportion of 20:1-10:1 by weight; and S04: in situ degradation of VOCs in landfill site by microbial rich N-rich biochar: replace part of clay cover with microbial rich N-rich biochar obtained in step S03. 2. The preparation method as claimed in claim 1 , which is characterized in that the agricultural and forestry wastes are selected from the group consisting of straw, wheat straw, bagasse, leaves, branches and weeds. 3. The preparation method according to claim 1 , which is characterized in that the organic nitrogen modifier in step S01 is urea or amide. 4. The preparation method according to claim 1 , which is characterized in that the sewage sludge in the step S03 is the activated sludge rich in microorganisms produced in the process of urban domestic sewage or industrial sewage treatment. 5. The preparation method according to claim 1 , which is characterized in that the activated sludge contains microorganisms are selected from the group consisting of non methane nutrition bacteria, methane nutrition bacteria-i, methane nutrition bacteria-ii, aerobic heterotrophic bacteria, actinomycetes, fungi, sulfur oxidizing bacteria, and sulfate reducing bacteria. 6. The preparation method as claimed in claim 1 , which is characterized in that the nitrogen mixed agricultural and forestry wastes in step S04 are uniformly prepared by mixing the organic nitrogen as modifier and the crushed agricultural and forestry wastes in the proportion of 1:50-1:10 by mass. 7. The preparation method as claimed in claim 1 , which is characterized in that the nitrogen rich biochar rich in microorganism in step S04 replaces the clay covering layer.
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