CN109954747B - A method for decomposing garbage containing iron and wood using bio-sludge - Google Patents
A method for decomposing garbage containing iron and wood using bio-sludge Download PDFInfo
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- CN109954747B CN109954747B CN201910336293.3A CN201910336293A CN109954747B CN 109954747 B CN109954747 B CN 109954747B CN 201910336293 A CN201910336293 A CN 201910336293A CN 109954747 B CN109954747 B CN 109954747B
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- XEEYBQQBJWHFJM-UHFFFAOYSA-N Iron Chemical compound [Fe] XEEYBQQBJWHFJM-UHFFFAOYSA-N 0.000 title claims abstract description 60
- 239000010802 sludge Substances 0.000 title claims abstract description 40
- 229910052742 iron Inorganic materials 0.000 title claims abstract description 29
- 238000000034 method Methods 0.000 title claims abstract description 26
- 239000002023 wood Substances 0.000 title claims abstract description 23
- 239000000149 chemical water pollutant Substances 0.000 claims abstract description 36
- 238000006731 degradation reaction Methods 0.000 claims abstract description 15
- 239000002699 waste material Substances 0.000 claims abstract description 13
- 239000002028 Biomass Substances 0.000 claims description 26
- KRKNYBCHXYNGOX-UHFFFAOYSA-N citric acid Chemical compound OC(=O)CC(O)(C(O)=O)CC(O)=O KRKNYBCHXYNGOX-UHFFFAOYSA-N 0.000 claims description 24
- 241000233866 Fungi Species 0.000 claims description 21
- 239000003610 charcoal Substances 0.000 claims description 17
- 230000000813 microbial effect Effects 0.000 claims description 16
- 241000221198 Basidiomycota Species 0.000 claims description 12
- 239000000203 mixture Substances 0.000 claims description 12
- 239000002245 particle Substances 0.000 claims description 7
- 238000002791 soaking Methods 0.000 claims description 7
- 238000005507 spraying Methods 0.000 claims description 4
- 239000003795 chemical substances by application Substances 0.000 claims 4
- 230000000593 degrading effect Effects 0.000 claims 1
- 238000003756 stirring Methods 0.000 claims 1
- 239000002068 microbial inoculum Substances 0.000 abstract description 18
- 230000015556 catabolic process Effects 0.000 abstract description 7
- 238000002360 preparation method Methods 0.000 abstract description 7
- 239000002054 inoculum Substances 0.000 description 12
- 241000219095 Vitis Species 0.000 description 2
- 235000009754 Vitis X bourquina Nutrition 0.000 description 2
- 235000012333 Vitis X labruscana Nutrition 0.000 description 2
- 235000014787 Vitis vinifera Nutrition 0.000 description 2
- 239000005416 organic matter Substances 0.000 description 2
- 230000004075 alteration Effects 0.000 description 1
- 238000010276 construction Methods 0.000 description 1
- 230000007812 deficiency Effects 0.000 description 1
- 238000013461 design Methods 0.000 description 1
- 238000011161 development Methods 0.000 description 1
- 238000002474 experimental method Methods 0.000 description 1
- 238000012986 modification Methods 0.000 description 1
- 230000004048 modification Effects 0.000 description 1
- 238000006467 substitution reaction Methods 0.000 description 1
Classifications
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B09—DISPOSAL OF SOLID WASTE; RECLAMATION OF CONTAMINATED SOIL
- B09B—DISPOSAL OF SOLID WASTE NOT OTHERWISE PROVIDED FOR
- B09B3/00—Destroying solid waste or transforming solid waste into something useful or harmless
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- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02W—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
- Y02W30/00—Technologies for solid waste management
- Y02W30/50—Reuse, recycling or recovery technologies
- Y02W30/78—Recycling of wood or furniture waste
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- Engineering & Computer Science (AREA)
- Environmental & Geological Engineering (AREA)
- Treatment Of Sludge (AREA)
- Processing Of Solid Wastes (AREA)
Abstract
本发明涉及一种垃圾处理方法的技术领域，具体公开了一种利用生物泥分解含有铁和木头的垃圾的方法，包括如下步骤：步骤一、生物泥的制备：将质量比为1:1‑1:5的池塘污泥和制碱废渣混合，得到生物泥；步骤二、将生物泥加入到垃圾中，搅拌均匀后堆放进行降解，保持垃圾堆的湿润状态，生物泥和垃圾的质量比为1:1‑1:5；步骤三、降解过程中收集垃圾渗滤液，并将垃圾渗滤液加入第二微生物菌剂后再次喷洒到垃圾堆，循环1‑3次，本发明通过利用池塘污泥和制碱废渣得到的生物泥对垃圾中的木头和铁屑进行有效分解，最终避免垃圾中的木头以及铁屑对环境的二次污染问题，实现了对垃圾的有效处理。The invention relates to the technical field of a garbage disposal method, and specifically discloses a method for decomposing garbage containing iron and wood by using biological mud, comprising the following steps: Step 1, preparation of biological mud: the mass ratio is 1:1- The 1:5 pond sludge is mixed with the alkali-making waste residue to obtain bio-sludge; step 2, the bio-sludge is added to the garbage, stirred evenly, and then stacked for degradation to maintain the wet state of the garbage heap. The mass ratio of bio-sludge to garbage is 1:1-1:5; in step 3, the landfill leachate is collected during the degradation process, and the landfill leachate is added to the second microbial inoculum and then sprayed to the garbage heap again, and the cycle is 1-3 times. The bio-sludge obtained from the alkali-making waste residue effectively decomposes the wood and iron filings in the garbage, and finally avoids the secondary pollution of the wood and iron filings in the garbage to the environment, and realizes the effective treatment of the garbage.
Description
技术领域technical field
本发明涉及一种垃圾处理方法的技术领域，尤其是一种利用生物泥分解含有铁和木头的垃圾的方法。The invention relates to the technical field of a garbage disposal method, in particular to a method for decomposing garbage containing iron and wood by utilizing biological mud.
背景技术Background technique
随着社会的发展，现在人们越来越重视生态文明的建设。对各类垃圾，尤其是含有难以分解的木头和铁质的垃圾高效处理已引起人们的高度重视。目前对垃圾分类主要是注重人工进行自动分类，但是有些垃圾中还是包含了或多或少的铁和木头，因此目前并没有一种很好的方法来分解垃圾中的铁和木头，最终导致垃圾分解困难，且后期对垃圾的处理也不得当，直接将垃圾作为废料或者直接焚烧，堆放，而由于垃圾中还掺杂了少量的木头、铁屑或小铁块，最终影响环境的二次污染，因此如何设计一款能够有效对垃圾中的木头以及铁屑进行分解的方法尤为重要。With the development of society, people are paying more and more attention to the construction of ecological civilization. Efficient treatment of various types of garbage, especially those containing hard-to-decompose wood and iron, has attracted great attention. At present, garbage classification mainly focuses on manual automatic classification, but some garbage still contains more or less iron and wood. Therefore, there is currently no good way to decompose iron and wood in garbage, which eventually leads to garbage. It is difficult to decompose, and the disposal of garbage in the later stage is also inappropriate. The garbage is directly used as waste or directly incinerated and stacked. Since the garbage is also mixed with a small amount of wood, iron filings or small iron blocks, it will eventually affect the secondary pollution of the environment. , so how to design a method that can effectively decompose the wood and iron filings in the garbage is particularly important.
发明内容SUMMARY OF THE INVENTION
本发明的目的是为了解决上述现有技术的不足而提供一种利用生物泥分解含有铁和木头的垃圾的方法。The purpose of the present invention is to provide a method for decomposing garbage containing iron and wood by utilizing bio-sludge in order to solve the above-mentioned deficiencies of the prior art.
为了实现上述目的，本发明所设计的一种利用生物泥分解含有铁和木头的垃圾的方法，包括如下步骤：In order to achieve the above-mentioned purpose, a method for decomposing garbage containing iron and wood by utilizing biological mud designed by the present invention comprises the following steps:
一种利用生物泥分解含有铁和木头的垃圾的方法，包括如下步骤：A method for decomposing garbage containing iron and wood by utilizing bio-sludge, comprising the following steps:
步骤一、生物泥的制备：将质量比为1:1-1:5的池塘污泥和制碱废渣混合，得到生物泥；Step 1, preparation of biological sludge: mixing pond sludge with a mass ratio of 1:1-1:5 and alkali-making waste residue to obtain biological sludge;
步骤二、将生物泥加入到垃圾中，搅拌均匀后堆放进行降解，保持垃圾堆的湿润状态，生物泥和垃圾的质量比为1:1-1:5；Step 2, adding the bio-sludge to the garbage, mixing it evenly and stacking it for degradation, keeping the garbage heap in a wet state, and the mass ratio of the bio-sludge and the garbage is 1:1-1:5;
步骤三、降解过程中收集垃圾渗滤液，并将垃圾渗滤液加入第二微生物菌剂后再次喷洒到垃圾堆，循环1-6次。Step 3: Collecting the landfill leachate during the degradation process, adding the landfill leachate to the second microbial inoculant, and then spraying the landfill leachate to the landfill again for 1-6 cycles.
步骤一和步骤二之间还包括：将生物泥进行改性，具体的：将生物泥中加入第一微生物菌剂和改性生物质炭。Between step 1 and step 2, the method further includes: modifying the biological mud, specifically: adding the first microbial inoculant and the modified biomass char to the biological mud.
所述改性生物质炭是将生物质炭颗粒浸泡于柠檬酸中超声振动1-5天后取出得到的。The modified biomass charcoal is obtained by soaking the biomass charcoal particles in citric acid for 1-5 days after ultrasonic vibration.
所述第一微生物菌剂为担子菌。The first microbial inoculum is a basidiomycete.
所述第二微生物菌剂为白腐菌、褐腐菌和软腐菌的混合物。The second microbial inoculum is a mixture of white rot fungi, brown rot fungi and soft rot fungi.
还包括步骤四，收集垃圾渗滤液，对收集垃圾渗滤液中的铁进行回收。It also includes a fourth step of collecting landfill leachate and recovering iron in the collected landfill leachate.
本发明的一种利用生物泥分解含有铁和木头的垃圾的方法，通过利用池塘污泥和制碱废渣得到的生物泥，对垃圾中进行处理，不仅可以使垃圾中的有机质等进行有效的分解，而且可以对垃圾中的木头和铁屑进行分解，最终避免垃圾中的木头以及铁屑对环境的二次污染问题。The present invention provides a method for decomposing garbage containing iron and wood by using biological sludge. By using the biological sludge obtained from pond sludge and alkali-making waste residue, the garbage can be treated, which can not only effectively decompose the organic matter in the garbage, etc. , and can decompose the wood and iron chips in the garbage, and finally avoid the secondary pollution of the wood and iron chips in the garbage to the environment.
具体实施方式Detailed ways
下面结合实施例对实施例创造作进一步说明。The creation of the embodiment will be further described below in conjunction with the embodiment.
实施例1。Example 1.
一种利用生物泥分解含有铁和木头的垃圾的方法，包括如下步骤：A method for decomposing garbage containing iron and wood by utilizing bio-sludge, comprising the following steps:
步骤一、生物泥的制备：将质量比为1:1的池塘污泥和制碱废渣混合，得到生物泥；Step 1, preparation of biological sludge: mixing pond sludge with a mass ratio of 1:1 and alkali-making waste residue to obtain biological sludge;
步骤二、将生物泥加入到垃圾中，搅拌均匀后堆放进行降解，保持垃圾堆的湿润状态，生物泥和垃圾的质量比为1:1；Step 2: Add the bio-sludge to the garbage, mix it evenly, stack it for degradation, keep the garbage heap wet, and the mass ratio of the bio-sludge to the garbage is 1:1;
步骤三、降解过程中收集垃圾渗滤液，并将垃圾渗滤液加入第二微生物菌剂后再次喷洒到垃圾堆，循环1次。Step 3: Collecting the landfill leachate during the degradation process, adding the landfill leachate to the second microbial inoculant, and then spraying the landfill leachate to the landfill again for one cycle.
步骤一和步骤二之间还包括：将生物泥进行改性，具体的：将生物泥中加入第一微生物菌剂和改性生物质炭。Between step 1 and step 2, the method further includes: modifying the biological mud, specifically: adding the first microbial inoculant and the modified biomass char to the biological mud.
所述改性生物质炭是将生物质炭颗粒浸泡于柠檬酸中超声振动1天后取出得到的。The modified biomass charcoal is obtained by soaking the biomass charcoal particles in citric acid for 1 day after ultrasonic vibration.
所述第一微生物菌剂为担子菌。所述的担子菌的含量为生物泥体积的0.01%，改性生物质炭为生物泥体积的0.1%。The first microbial inoculum is a basidiomycete. The content of the basidiomycetes is 0.01% of the volume of the biological mud, and the modified biomass char is 0.1% of the volume of the biological mud.
所述第二微生物菌剂为白腐菌、褐腐菌和软腐菌的混合物。所述第二微生物菌剂的含量为垃圾渗滤液总质量的0.01%。The second microbial inoculum is a mixture of white rot fungi, brown rot fungi and soft rot fungi. The content of the second microbial inoculum is 0.01% of the total mass of the landfill leachate.
还包括步骤四，收集垃圾渗滤液，对收集垃圾渗滤液中的铁进行回收。It also includes a fourth step of collecting landfill leachate and recovering iron in the collected landfill leachate.
实施例2。Example 2.
一种利用生物泥分解含有铁和木头的垃圾的方法，包括如下步骤：A method for decomposing garbage containing iron and wood by utilizing bio-sludge, comprising the following steps:
步骤一、生物泥的制备：将质量比为1:2的池塘污泥和制碱废渣混合，得到生物泥；Step 1, preparation of biological mud: mixing pond sludge with a mass ratio of 1:2 and alkali-making waste residue to obtain biological mud;
步骤二、将生物泥加入到垃圾中，搅拌均匀后堆放进行降解，保持垃圾堆的湿润状态，生物泥和垃圾的质量比为1:2；Step 2: Add the bio-sludge to the garbage, mix it evenly, stack it for degradation, keep the garbage heap wet, and the mass ratio of the bio-sludge to the garbage is 1:2;
步骤三、降解过程中收集垃圾渗滤液，并将垃圾渗滤液加入第二微生物菌剂后再次喷洒到垃圾堆，循环3次。Step 3: Collecting the landfill leachate during the degradation process, adding the landfill leachate to the second microbial inoculant, and then spraying the landfill leachate to the landfill again for three cycles.
步骤一和步骤二之间还包括：将生物泥进行改性，具体的：将生物泥中加入第一微生物菌剂和改性生物质炭。Between step 1 and step 2, the method further includes: modifying the biological mud, specifically: adding a first microbial inoculant and modified biomass charcoal to the biological mud.
所述改性生物质炭是将生物质炭颗粒浸泡于柠檬酸中超声振动2天后取出得到的。The modified biomass charcoal is obtained by soaking the biomass charcoal particles in citric acid and ultrasonically vibrating for 2 days.
所述第一微生物菌剂为担子菌。所述的担子菌的含量为生物泥体积的0.02%，改性生物质炭为生物泥体积的0.15%。The first microbial inoculum is a basidiomycete. The content of the basidiomycetes is 0.02% of the volume of the biological mud, and the modified biomass char is 0.15% of the volume of the biological mud.
所述第二微生物菌剂为白腐菌、褐腐菌和软腐菌的混合物。所述的第二微生物菌剂的含量为垃圾渗滤液总质量的0.04%。The second microbial inoculum is a mixture of white rot fungi, brown rot fungi and soft rot fungi. The content of the second microbial inoculum is 0.04% of the total mass of the landfill leachate.
还包括步骤四，收集垃圾渗滤液，对收集垃圾渗滤液中的铁进行回收。It also includes a fourth step of collecting landfill leachate and recovering iron in the collected landfill leachate.
实施例3。Example 3.
一种利用生物泥分解含有铁和木头的垃圾的方法，包括如下步骤：A method for decomposing garbage containing iron and wood by utilizing bio-sludge, comprising the following steps:
步骤一、生物泥的制备：将质量比为1:4的池塘污泥和制碱废渣混合，得到生物泥；Step 1. Preparation of biological mud: mixing pond sludge with a mass ratio of 1:4 and alkali-making waste residue to obtain biological mud;
步骤二、将生物泥加入到垃圾中，搅拌均匀后堆放进行降解，保持垃圾堆的湿润状态，生物泥和垃圾的质量比为1:4；Step 2: Add the bio-sludge to the garbage, mix it evenly, stack it for degradation, keep the garbage heap in a wet state, and the mass ratio of the bio-sludge to the garbage is 1:4;
步骤三、降解过程中收集垃圾渗滤液，并将垃圾渗滤液加入第二微生物菌剂后再次喷洒到垃圾堆，循环2次。In step 3, the landfill leachate is collected during the degradation process, and the landfill leachate is added to the second microbial inoculant and then sprayed onto the landfill again for two cycles.
步骤一和步骤二之间还包括：将生物泥进行改性，具体的：将生物泥中加入第一微生物菌剂和改性生物质炭。Between step 1 and step 2, the method further includes: modifying the biological mud, specifically: adding the first microbial inoculant and the modified biomass char to the biological mud.
所述改性生物质炭是将生物质炭颗粒浸泡于柠檬酸中超声振动3天后取出得到的。The modified biomass charcoal is obtained by soaking the biomass charcoal particles in citric acid for 3 days after ultrasonic vibration.
所述第一微生物菌剂为担子菌。所述的担子菌的含量为生物泥体积的0.03%，改性生物质炭为生物泥体积的0.2%。The first microbial inoculum is a basidiomycete. The content of the basidiomycetes is 0.03% of the volume of the biological mud, and the modified biomass char is 0.2% of the volume of the biological mud.
所述第二微生物菌剂为白腐菌、褐腐菌和软腐菌的混合物。所述第二微生物菌剂的含量为垃圾渗滤液总质量的0.02%。The second microbial inoculum is a mixture of white rot fungi, brown rot fungi and soft rot fungi. The content of the second microbial inoculum is 0.02% of the total mass of the landfill leachate.
还包括步骤四，收集垃圾渗滤液，对收集垃圾渗滤液中的铁进行回收。It also includes a fourth step of collecting landfill leachate and recovering iron in the collected landfill leachate.
实施例4。Example 4.
一种利用生物泥分解含有铁和木头的垃圾的方法，包括如下步骤：A method for decomposing garbage containing iron and wood by utilizing bio-sludge, comprising the following steps:
步骤一、生物泥的制备：将质量比为1:5的池塘污泥和制碱废渣混合，得到生物泥；Step 1, preparation of biological mud: mixing pond sludge with a mass ratio of 1:5 and alkali-making waste residue to obtain biological mud;
步骤二、将生物泥加入到垃圾中，搅拌均匀后堆放进行降解，保持垃圾堆的湿润状态，生物泥和垃圾的质量比为1:5；Step 2: Add the bio-sludge to the garbage, mix it evenly, stack it for degradation, keep the garbage heap wet, and the mass ratio of the bio-sludge to the garbage is 1:5;
步骤三、降解过程中收集垃圾渗滤液，并将垃圾渗滤液加入第二微生物菌剂后再次喷洒到垃圾堆，循环6次。In step 3, the landfill leachate is collected during the degradation process, and the landfill leachate is added to the second microbial inoculant and then sprayed to the landfill again, and the cycle is repeated 6 times.
步骤一和步骤二之间还包括：将生物泥进行改性，具体的：将生物泥中加入第一微生物菌剂和改性生物质炭。Between step 1 and step 2, the method further includes: modifying the biological mud, specifically: adding the first microbial inoculant and the modified biomass char to the biological mud.
所述改性生物质炭是将生物质炭颗粒浸泡于柠檬酸中超声振动5天后取出得到的。The modified biomass charcoal is obtained by soaking the biomass charcoal particles in citric acid for 5 days after ultrasonic vibration.
所述第一微生物菌剂为担子菌。所述的担子菌的含量为生物泥体积的0.01%，改性生物质炭为生物泥体积的0.5%。The first microbial inoculum is a basidiomycete. The content of the basidiomycetes is 0.01% of the volume of the biological mud, and the modified biomass char is 0.5% of the volume of the biological mud.
所述第二微生物菌剂为白腐菌、褐腐菌和软腐菌的混合物。所述的第二微生物菌剂的含量为垃圾渗滤液总质量的0.02%。The second microbial inoculum is a mixture of white rot fungi, brown rot fungi and soft rot fungi. The content of the second microbial inoculum is 0.02% of the total mass of the landfill leachate.
还包括步骤四，收集垃圾渗滤液，对收集垃圾渗滤液中的铁进行回收。It also includes a fourth step of collecting landfill leachate and recovering iron in the collected landfill leachate.
实施例5。Example 5.
一种利用生物泥分解含有铁和木头的垃圾的方法，包括如下步骤：A method for decomposing garbage containing iron and wood by utilizing bio-sludge, comprising the following steps:
步骤一、生物泥的制备：将质量比为1:4的池塘污泥和制碱废渣混合，得到生物泥；Step 1. Preparation of biological mud: mixing pond sludge with a mass ratio of 1:4 and alkali-making waste residue to obtain biological mud;
步骤二、将生物泥加入到垃圾中，搅拌均匀后堆放进行降解，保持垃圾堆的湿润状态，生物泥和垃圾的质量比为1:4；Step 2: Add the bio-sludge to the garbage, mix it evenly, stack it for degradation, keep the garbage heap in a wet state, and the mass ratio of the bio-sludge to the garbage is 1:4;
步骤三、降解过程中收集垃圾渗滤液，并将垃圾渗滤液加入第二微生物菌剂后再次喷洒到垃圾堆，循环2次。In step 3, the landfill leachate is collected during the degradation process, and the landfill leachate is added to the second microbial inoculant and then sprayed onto the landfill again for two cycles.
步骤一和步骤二之间还包括：将生物泥进行改性，具体的：将生物泥中加入第一微生物菌剂、葡萄酒酒厂的废料葡萄渣和改性生物质炭。Between step 1 and step 2, the method further includes: modifying the biological mud, specifically: adding a first microbial inoculant, waste grape pomace from a winery and modified biomass charcoal to the biological mud.
所述改性生物质炭是将生物质炭颗粒浸泡于柠檬酸中超声振动3天后取出得到。The modified biomass charcoal is obtained by soaking the biomass charcoal particles in citric acid for 3 days after ultrasonic vibration.
所述第一微生物菌剂为担子菌。所述的担子菌的含量为生物泥体积的0.05%，葡萄酒酒厂的废料葡萄渣为生物泥体积的2%，改性生物质炭为生物泥体积的0.1%。The first microbial inoculum is a basidiomycete. The content of the basidiomycetes is 0.05% of the volume of the biological mud, the waste grape pomace of the winery is 2% of the volume of the biological mud, and the modified biomass char is 0.1% of the volume of the biological mud.
所述第二微生物菌剂为质量比为1:1:1的白腐菌、褐腐菌和软腐菌的混合物。所述的第二微生物菌剂的含量为垃圾渗滤液总质量的0.02%。The second microbial inoculum is a mixture of white rot fungi, brown rot fungi and soft rot fungi with a mass ratio of 1:1:1. The content of the second microbial inoculum is 0.02% of the total mass of the landfill leachate.
还包括步骤四，收集垃圾渗滤液，对收集垃圾渗滤液中的铁进行回收。It also includes a fourth step of collecting landfill leachate and recovering iron in the collected landfill leachate.
本发明所用柠檬酸的质量浓度为20%。The mass concentration of citric acid used in the present invention is 20%.
经过实验证明，经过1-6个月后，利用上述方法获得处理过的垃圾中基本未发现木头和小铁块，其他有机质也已完全腐烂分解。Experiments have proved that after 1-6 months, basically no wood and small iron lumps are found in the treated garbage obtained by the above method, and other organic matter has also been completely decomposed.
以上显示和描述了本发明的基本原理和主要特征和本发明的优点，对于本领域技术人员而言，显然本发明不限于上述示范性发明的细节，而且在不背离本发明的精神或基本特征的情况下，能够以其他的具体形式实现本发明。因此，无论从哪一点来看，均应将发明看作是示范性的，而且是非限制性的，本发明的范围由所附权利要求而不是上述说明限定，因此旨在将落在权利要求的等同要件的含义和范围内的所有变化囊括在本发明内。尽管已经示出和描述了本发明的发明，对于本领域的普通技术人员而言，可以理解在不脱离本发明的原理和精神的情况下可以对这些发明进行多种变化、修改、替换和变型，本发明的范围由所附权利要求及其等同物限定。The basic principles and main features of the present invention and the advantages of the present invention have been shown and described above, and it will be apparent to those skilled in the art that the present invention is not limited to the details of the above-described exemplary invention, but without departing from the spirit or essential characteristics of the present invention. In this case, the present invention can be implemented in other specific forms. Accordingly, the invention is to be regarded in all respects as illustrative and not restrictive, the scope of the invention being defined by the appended claims rather than the foregoing description, and it is therefore intended that the scope of the invention shall fall within the scope of the claims. All changes that come within the meaning and range of equivalents are encompassed within the invention. Although the invention of the present invention has been shown and described, it will be understood by those skilled in the art that various changes, modifications, substitutions and alterations can be made hereto without departing from the principle and spirit of the invention , the scope of the invention is defined by the appended claims and their equivalents.
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Citations (7)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN1299710A (en) * | 2000-09-18 | 2001-06-20 | 韩洪波 | Digesting treatment of city domestic garbage and sludge |
| CN1868930A (en) * | 2006-06-06 | 2006-11-29 | 广东省农业科学院土壤肥料研究所 | Method of producing polyacidic soil regulating agent using offscum in alkali manufacturing and city sludge |
| CN101786786A (en) * | 2010-02-09 | 2010-07-28 | 董萍萍 | Sewage treatment and utilization method of municipal sewage treatment plant |
| CN104438283A (en) * | 2014-11-06 | 2015-03-25 | 武汉景弘环境生物科技有限公司 | Method of accelerating aerobic degradation of municipal solid garbage by using microorganisms |
| CN106583424A (en) * | 2016-12-29 | 2017-04-26 | 浙江加百列生物科技有限公司 | Resourceful treatment process for domestic organic waste |
| CN108213037A (en) * | 2017-12-12 | 2018-06-29 | 常州杰轩纺织科技有限公司 | A kind of Food waste treatment method |
| CN109536174A (en) * | 2018-12-05 | 2019-03-29 | 湖南恒凯环保科技投资有限公司 | A kind of offal treatment technique based on phosphorus, potassium element resource utilization |
-
2019
- 2019-04-25 CN CN201910336293.3A patent/CN109954747B/en active Active
Patent Citations (7)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN1299710A (en) * | 2000-09-18 | 2001-06-20 | 韩洪波 | Digesting treatment of city domestic garbage and sludge |
| CN1868930A (en) * | 2006-06-06 | 2006-11-29 | 广东省农业科学院土壤肥料研究所 | Method of producing polyacidic soil regulating agent using offscum in alkali manufacturing and city sludge |
| CN101786786A (en) * | 2010-02-09 | 2010-07-28 | 董萍萍 | Sewage treatment and utilization method of municipal sewage treatment plant |
| CN104438283A (en) * | 2014-11-06 | 2015-03-25 | 武汉景弘环境生物科技有限公司 | Method of accelerating aerobic degradation of municipal solid garbage by using microorganisms |
| CN106583424A (en) * | 2016-12-29 | 2017-04-26 | 浙江加百列生物科技有限公司 | Resourceful treatment process for domestic organic waste |
| CN108213037A (en) * | 2017-12-12 | 2018-06-29 | 常州杰轩纺织科技有限公司 | A kind of Food waste treatment method |
| CN109536174A (en) * | 2018-12-05 | 2019-03-29 | 湖南恒凯环保科技投资有限公司 | A kind of offal treatment technique based on phosphorus, potassium element resource utilization |
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