CN107176798A - A kind of production method and application that biological cement is prepared based on low price calcium ion - Google Patents
A kind of production method and application that biological cement is prepared based on low price calcium ion Download PDFInfo
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- 238000004519 manufacturing process Methods 0.000 title claims abstract description 16
- BHPQYMZQTOCNFJ-UHFFFAOYSA-N Calcium cation Chemical compound [Ca+2] BHPQYMZQTOCNFJ-UHFFFAOYSA-N 0.000 title claims abstract description 14
- 229910001424 calcium ion Inorganic materials 0.000 title claims abstract description 14
- 239000004568 cement Substances 0.000 title description 9
- QTBSBXVTEAMEQO-UHFFFAOYSA-N Acetic acid Chemical compound CC(O)=O QTBSBXVTEAMEQO-UHFFFAOYSA-N 0.000 claims abstract description 39
- 241000193830 Bacillus <bacterium> Species 0.000 claims abstract description 23
- 239000011575 calcium Substances 0.000 claims abstract description 22
- 229910052791 calcium Inorganic materials 0.000 claims abstract description 22
- 108010046334 Urease Proteins 0.000 claims abstract description 21
- 238000002360 preparation method Methods 0.000 claims abstract description 21
- 239000002154 agricultural waste Substances 0.000 claims abstract description 18
- XSQUKJJJFZCRTK-UHFFFAOYSA-N Urea Chemical compound NC(N)=O XSQUKJJJFZCRTK-UHFFFAOYSA-N 0.000 claims abstract description 17
- 239000004202 carbamide Substances 0.000 claims abstract description 17
- 238000000034 method Methods 0.000 claims abstract description 17
- 239000002699 waste material Substances 0.000 claims abstract description 13
- 239000002994 raw material Substances 0.000 claims abstract description 10
- 235000019738 Limestone Nutrition 0.000 claims abstract description 7
- 239000006028 limestone Substances 0.000 claims abstract description 7
- 239000000843 powder Substances 0.000 claims abstract description 7
- 238000000197 pyrolysis Methods 0.000 claims abstract description 5
- 239000000243 solution Substances 0.000 claims description 38
- 239000004576 sand Substances 0.000 claims description 31
- OYPRJOBELJOOCE-UHFFFAOYSA-N Calcium Chemical compound [Ca] OYPRJOBELJOOCE-UHFFFAOYSA-N 0.000 claims description 21
- 239000007788 liquid Substances 0.000 claims description 21
- 230000001580 bacterial effect Effects 0.000 claims description 7
- 239000002245 particle Substances 0.000 claims description 7
- VSGNNIFQASZAOI-UHFFFAOYSA-L calcium acetate Chemical compound [Ca+2].CC([O-])=O.CC([O-])=O VSGNNIFQASZAOI-UHFFFAOYSA-L 0.000 claims description 6
- 239000001639 calcium acetate Substances 0.000 claims description 6
- 235000011092 calcium acetate Nutrition 0.000 claims description 6
- 229960005147 calcium acetate Drugs 0.000 claims description 6
- 239000010902 straw Substances 0.000 claims description 6
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Chemical compound O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims description 6
- 241000894006 Bacteria Species 0.000 claims description 5
- 235000013339 cereals Nutrition 0.000 claims description 5
- 239000007791 liquid phase Substances 0.000 claims description 5
- 238000002156 mixing Methods 0.000 claims description 5
- 240000007594 Oryza sativa Species 0.000 claims description 4
- 235000007164 Oryza sativa Nutrition 0.000 claims description 4
- 240000008042 Zea mays Species 0.000 claims description 4
- 235000005824 Zea mays ssp. parviglumis Nutrition 0.000 claims description 4
- 235000002017 Zea mays subsp mays Nutrition 0.000 claims description 4
- 235000005822 corn Nutrition 0.000 claims description 4
- 239000012153 distilled water Substances 0.000 claims description 4
- 239000001963 growth medium Substances 0.000 claims description 4
- 230000003287 optical effect Effects 0.000 claims description 4
- 235000009566 rice Nutrition 0.000 claims description 4
- 241000193469 Clostridium pasteurianum Species 0.000 claims description 3
- BFNBIHQBYMNNAN-UHFFFAOYSA-N ammonium sulfate Chemical compound N.N.OS(O)(=O)=O BFNBIHQBYMNNAN-UHFFFAOYSA-N 0.000 claims description 3
- 229910052921 ammonium sulfate Inorganic materials 0.000 claims description 3
- 235000011130 ammonium sulphate Nutrition 0.000 claims description 3
- 229940041514 candida albicans extract Drugs 0.000 claims description 3
- 239000012299 nitrogen atmosphere Substances 0.000 claims description 3
- LENZDBCJOHFCAS-UHFFFAOYSA-N tris Chemical compound OCC(N)(CO)CO LENZDBCJOHFCAS-UHFFFAOYSA-N 0.000 claims description 3
- 239000012138 yeast extract Substances 0.000 claims description 3
- 241000609240 Ambelania acida Species 0.000 claims description 2
- 229920000742 Cotton Polymers 0.000 claims description 2
- 241000192023 Sarcina Species 0.000 claims description 2
- 239000007983 Tris buffer Substances 0.000 claims description 2
- 241000209140 Triticum Species 0.000 claims description 2
- 235000021307 Triticum Nutrition 0.000 claims description 2
- 238000002835 absorbance Methods 0.000 claims description 2
- 239000010905 bagasse Substances 0.000 claims description 2
- 239000010459 dolomite Substances 0.000 claims description 2
- 229910000514 dolomite Inorganic materials 0.000 claims description 2
- 235000013399 edible fruits Nutrition 0.000 claims description 2
- 239000010903 husk Substances 0.000 claims description 2
- 238000000465 moulding Methods 0.000 claims description 2
- 239000013049 sediment Substances 0.000 claims description 2
- 239000002023 wood Substances 0.000 claims description 2
- 229910021532 Calcite Inorganic materials 0.000 abstract description 10
- 238000001556 precipitation Methods 0.000 abstract description 9
- 238000005516 engineering process Methods 0.000 abstract description 8
- 239000006227 byproduct Substances 0.000 abstract description 5
- 238000011161 development Methods 0.000 abstract description 5
- 244000005700 microbiome Species 0.000 abstract description 5
- 238000005065 mining Methods 0.000 abstract description 5
- 239000002028 Biomass Substances 0.000 abstract description 3
- 230000009286 beneficial effect Effects 0.000 abstract description 2
- VTYYLEPIZMXCLO-UHFFFAOYSA-L Calcium carbonate Chemical compound [Ca+2].[O-]C([O-])=O VTYYLEPIZMXCLO-UHFFFAOYSA-L 0.000 description 16
- UXVMQQNJUSDDNG-UHFFFAOYSA-L Calcium chloride Chemical compound [Cl-].[Cl-].[Ca+2] UXVMQQNJUSDDNG-UHFFFAOYSA-L 0.000 description 9
- 239000001110 calcium chloride Substances 0.000 description 9
- 229910001628 calcium chloride Inorganic materials 0.000 description 9
- 229910000019 calcium carbonate Inorganic materials 0.000 description 8
- 235000010216 calcium carbonate Nutrition 0.000 description 8
- 239000000203 mixture Substances 0.000 description 7
- HEMHJVSKTPXQMS-UHFFFAOYSA-M Sodium hydroxide Chemical compound [OH-].[Na+] HEMHJVSKTPXQMS-UHFFFAOYSA-M 0.000 description 6
- 230000000813 microbial effect Effects 0.000 description 6
- 238000002441 X-ray diffraction Methods 0.000 description 5
- 239000002244 precipitate Substances 0.000 description 5
- 230000008569 process Effects 0.000 description 5
- ZCCIPPOKBCJFDN-UHFFFAOYSA-N calcium nitrate Chemical compound [Ca+2].[O-][N+]([O-])=O.[O-][N+]([O-])=O ZCCIPPOKBCJFDN-UHFFFAOYSA-N 0.000 description 4
- 210000003278 egg shell Anatomy 0.000 description 4
- 239000000463 material Substances 0.000 description 4
- 238000004064 recycling Methods 0.000 description 4
- 239000004566 building material Substances 0.000 description 3
- 159000000007 calcium salts Chemical class 0.000 description 3
- 238000006243 chemical reaction Methods 0.000 description 3
- 238000002485 combustion reaction Methods 0.000 description 3
- 239000013078 crystal Substances 0.000 description 3
- 238000003912 environmental pollution Methods 0.000 description 3
- MWUXSHHQAYIFBG-UHFFFAOYSA-N nitrogen oxide Inorganic materials O=[N] MWUXSHHQAYIFBG-UHFFFAOYSA-N 0.000 description 3
- 239000000047 product Substances 0.000 description 3
- 238000001878 scanning electron micrograph Methods 0.000 description 3
- 241001494479 Pecora Species 0.000 description 2
- 244000046052 Phaseolus vulgaris Species 0.000 description 2
- 235000010627 Phaseolus vulgaris Nutrition 0.000 description 2
- RAHZWNYVWXNFOC-UHFFFAOYSA-N Sulphur dioxide Chemical compound O=S=O RAHZWNYVWXNFOC-UHFFFAOYSA-N 0.000 description 2
- 239000003153 chemical reaction reagent Substances 0.000 description 2
- 238000010276 construction Methods 0.000 description 2
- 230000007547 defect Effects 0.000 description 2
- 230000008021 deposition Effects 0.000 description 2
- 238000010586 diagram Methods 0.000 description 2
- 239000003921 oil Substances 0.000 description 2
- 238000003756 stirring Methods 0.000 description 2
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 description 1
- BVKZGUZCCUSVTD-UHFFFAOYSA-L Carbonate Chemical compound [O-]C([O-])=O BVKZGUZCCUSVTD-UHFFFAOYSA-L 0.000 description 1
- 102000002322 Egg Proteins Human genes 0.000 description 1
- 108010000912 Egg Proteins Proteins 0.000 description 1
- 241000196324 Embryophyta Species 0.000 description 1
- 101000965313 Legionella pneumophila subsp. pneumophila (strain Philadelphia 1 / ATCC 33152 / DSM 7513) Aconitate hydratase A Proteins 0.000 description 1
- 239000011398 Portland cement Substances 0.000 description 1
- 241000193395 Sporosarcina pasteurii Species 0.000 description 1
- 230000003213 activating effect Effects 0.000 description 1
- 239000012298 atmosphere Substances 0.000 description 1
- 239000011230 binding agent Substances 0.000 description 1
- 238000009395 breeding Methods 0.000 description 1
- 230000001488 breeding effect Effects 0.000 description 1
- AXCZMVOFGPJBDE-UHFFFAOYSA-L calcium dihydroxide Chemical compound [OH-].[OH-].[Ca+2] AXCZMVOFGPJBDE-UHFFFAOYSA-L 0.000 description 1
- 239000000920 calcium hydroxide Substances 0.000 description 1
- 229910001861 calcium hydroxide Inorganic materials 0.000 description 1
- 229910052799 carbon Inorganic materials 0.000 description 1
- BVKZGUZCCUSVTD-UHFFFAOYSA-N carbonic acid Chemical compound OC(O)=O BVKZGUZCCUSVTD-UHFFFAOYSA-N 0.000 description 1
- 230000008859 change Effects 0.000 description 1
- 239000010779 crude oil Substances 0.000 description 1
- 238000000354 decomposition reaction Methods 0.000 description 1
- 239000008367 deionised water Substances 0.000 description 1
- 229910021641 deionized water Inorganic materials 0.000 description 1
- 230000000694 effects Effects 0.000 description 1
- 238000005265 energy consumption Methods 0.000 description 1
- 230000007613 environmental effect Effects 0.000 description 1
- 238000000605 extraction Methods 0.000 description 1
- 239000003673 groundwater Substances 0.000 description 1
- 229930195733 hydrocarbon Natural products 0.000 description 1
- 150000002430 hydrocarbons Chemical class 0.000 description 1
- 230000006698 induction Effects 0.000 description 1
- 230000007246 mechanism Effects 0.000 description 1
- 239000002609 medium Substances 0.000 description 1
- 238000012545 processing Methods 0.000 description 1
- 230000001737 promoting effect Effects 0.000 description 1
- 239000000376 reactant Substances 0.000 description 1
- 230000008439 repair process Effects 0.000 description 1
- 238000011160 research Methods 0.000 description 1
- 238000009991 scouring Methods 0.000 description 1
- 239000000779 smoke Substances 0.000 description 1
- 239000002910 solid waste Substances 0.000 description 1
- 230000006641 stabilisation Effects 0.000 description 1
- 238000011105 stabilization Methods 0.000 description 1
- 239000000126 substance Substances 0.000 description 1
- 239000000758 substrate Substances 0.000 description 1
- 239000006228 supernatant Substances 0.000 description 1
- 238000012360 testing method Methods 0.000 description 1
- 239000000052 vinegar Substances 0.000 description 1
- 235000021419 vinegar Nutrition 0.000 description 1
Classifications
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- C—CHEMISTRY; METALLURGY
- C04—CEMENTS; CONCRETE; ARTIFICIAL STONE; CERAMICS; REFRACTORIES
- C04B—LIME, MAGNESIA; SLAG; CEMENTS; COMPOSITIONS THEREOF, e.g. MORTARS, CONCRETE OR LIKE BUILDING MATERIALS; ARTIFICIAL STONE; CERAMICS; REFRACTORIES; TREATMENT OF NATURAL STONE
- C04B12/00—Cements not provided for in groups C04B7/00 - C04B11/00
Landscapes
- Chemical & Material Sciences (AREA)
- Engineering & Computer Science (AREA)
- Ceramic Engineering (AREA)
- Materials Engineering (AREA)
- Structural Engineering (AREA)
- Organic Chemistry (AREA)
- Micro-Organisms Or Cultivation Processes Thereof (AREA)
- Processing Of Solid Wastes (AREA)
Abstract
本发明公开了一种基于低价钙离子制备生物水泥的生产方法和应用,即利用矿业废弃物中的石灰石粉末与农业废弃物快速热解生产生物质油的副产物乙酸进行反应,生成可溶性钙离子作为制备生物水泥关键原料‑钙源,以代替传统方法中高成本的工业级CaCl2,然后与能分泌脲酶分解尿素的芽孢杆菌、尿素溶液混合反应制成生物水泥。本发明制备的生物水泥强度高、成本低、原料来源广,实现了可持续、环保发展理念,有利于促进微生物诱导的方解石沉淀技术在实际工程中的应用与推广。
The invention discloses a production method and application for preparing biocement based on low-priced calcium ions, that is, using limestone powder in mining waste to react with acetic acid, a by-product of rapid pyrolysis of agricultural waste to produce biomass oil, to generate soluble calcium Ions are used as the key raw material for the preparation of biocement-calcium source to replace the high-cost industrial grade CaCl 2 in the traditional method, and then mixed with Bacillus and urea solution that can secrete urease to decompose urea to make biocement. The biocement prepared by the invention has high strength, low cost and wide source of raw materials, realizes the concept of sustainable and environment-friendly development, and is beneficial to promote the application and popularization of the microorganism-induced calcite precipitation technology in actual engineering.
Description
技术领域technical field
本发明涉及到一种基于低价钙离子制备生物水泥的生产方法和应用,即在传统微生物诱导方解石沉淀技术基础上,利用农业、矿业废物作为原料生产生物水泥基材料,具体属于生物建筑材料技术领域。The invention relates to a production method and application of bio-cement based on low-priced calcium ions, that is, on the basis of traditional microorganism-induced calcite precipitation technology, agricultural and mining wastes are used as raw materials to produce bio-cement-based materials, specifically belonging to bio-building material technology field.
背景技术Background technique
近年来,一种环境友好型绿色建筑材料-生物水泥已经在土木工程上得到较广泛的应用。生物水泥是一种由钙盐、尿素、微生物(如脲酶菌)按一定比例混合产生的建筑材料,其机制称为微生物诱导方解石沉淀。生物水泥与常规水泥的作用相似即降低水力传导性、增加地面强度,灌浆方式也与传统水泥大致相同。目前已经有大量关于用生物水泥代替常规水泥的研究,如固体废物填埋场的建设、堤坝的稳固、地下水生物塘的建设等。此外生物水泥与传统的波兰特水泥相比有以下优点:(1)生产过程能耗少;(2)粘度低,易于注入地下;(3)颗粒尺寸小,能修复更狭小的空隙和裂缝等。In recent years, an environmentally friendly green building material - biocement has been widely used in civil engineering. Biocement is a building material produced by mixing calcium salt, urea, and microorganisms (such as urease bacteria) in a certain proportion. The mechanism is called microorganism-induced calcite precipitation. The effect of biocement is similar to that of conventional cement, that is, to reduce hydraulic conductivity and increase ground strength, and the grouting method is roughly the same as that of traditional cement. At present, there have been a lot of research on the use of biocement to replace conventional cement, such as the construction of solid waste landfills, the stabilization of dams, and the construction of groundwater biological ponds. In addition, biocement has the following advantages compared with traditional Portland cement: (1) less energy consumption in the production process; (2) low viscosity, easy to inject into the ground; (3) small particle size, can repair narrower gaps and cracks, etc. .
然而,生物水泥在实际推广应用中却存在较大挑战。常用的微生物诱导方解石沉淀工艺通常需要大量的工业级氯化钙作为钙源,但氯化钙的价格昂贵且大量使用氯化钙会对环境造成污染。因此研究者们一直致力于寻找可代替的钙源。例如,Park等报道了植物诱导方解石沉淀过程,利用羊刀豆的活性脲酶与氢氧化钙或硝酸钙混合反应生成的反应物用于砂胶结,但羊刀豆的活性脲酶的含量低,需大量种植,占用农用田地,且其提取加工成本高。Zhang等使用硝酸钙和乙酸钙作为钙源代替氯化钙。Choi等使用蛋壳和醋制成钙源,蛋壳钙含量虽丰富,但推广需要收集大量的蛋壳,蛋壳在收集的过程存在许多障碍,如蛋壳来源主要于厨余垃圾,需要耗费大量人力和时间来收集。因此上述方法在大规模推广应用上均存在一定限制条件。However, there are great challenges in the practical promotion and application of biocement. The commonly used microbial-induced calcite precipitation process usually requires a large amount of industrial-grade calcium chloride as a calcium source, but calcium chloride is expensive and the large amount of calcium chloride will pollute the environment. Therefore, researchers have been working on finding alternative calcium sources. For example, Park et al. reported the process of plant-induced calcite precipitation, using the active urease of the sheep bean and the mixed reaction of calcium hydroxide or calcium nitrate to generate the reactant for sand cementation, but the content of the active urease of the sheep bean is low, requiring a large amount of Planting, occupying agricultural fields, and its extraction and processing costs are high. Zhang et al. used calcium nitrate and calcium acetate as calcium sources instead of calcium chloride. Choi et al. used eggshells and vinegar to make calcium sources. Although eggshells are rich in calcium, a large number of eggshells need to be collected for promotion. There are many obstacles in the process of eggshell collection. A lot of manpower and time to collect. Therefore, there are certain limitations in the large-scale application of the above methods.
东南大学钱春香申请了专利《利用微生物沉积制备碳酸钙的方法》(CN200510094744.5)提出将巴氏芽孢杆菌接种在含尿素底物的培养基上后与CaCl2混合在一定条件下反应生成碳酸钙沉淀的制备方法。该专利提出利用工业级的氯化钙作为钙源,据调查工业级氯化钙成本价每吨大约950元,而传统水泥每吨成本大约400元,因此使用氯化钙为原料使生物水泥在大量推广使用存在成本昂贵的缺陷。贾强等在2015年申请了专利《一种提高碳酸钙早期沉积量的微生物灌浆方法》(CN201510113200.2)公开提出通过控制不同的反应因素来优化生物水泥的制备方法,其中提到可以用乙酸钙作钙源来进行传统生物水泥制作,为本发明提供一种从制备原料方面上改进的思路。Qian Chunxiang of Southeast University applied for a patent "Method for preparing calcium carbonate by microbial deposition" (CN200510094744.5), proposing to inoculate Bacillus pasteurianus on the medium containing urea substrate, mix it with CaCl 2 and react under certain conditions to generate carbonic acid Preparation method of calcium precipitate. The patent proposes to use industrial-grade calcium chloride as a calcium source. According to the survey, the cost price of industrial-grade calcium chloride is about 950 yuan per ton, while the cost of traditional cement is about 400 yuan per ton. Therefore, using calcium chloride as a raw material makes biocement There is a costly defect in mass promotion and use. In 2015, Jia Qiang and others applied for a patent "A Microbial Grouting Method to Increase the Early Deposition of Calcium Carbonate" (CN201510113200.2) and publicly proposed to optimize the preparation method of biocement by controlling different reaction factors, which mentioned that acetic acid can be used Calcium is used as a calcium source for traditional biocement production, which provides an improved idea for the present invention in terms of raw material preparation.
我国作为一个农业大国,农业废弃物产生量极其巨大。我国农业废弃物主要来自于种植业和养殖业。据估算,我国农作物秸秆总产量为6.5×108t/a左右,且我国的农作物秸秆多采用燃烧等一次性利用方式。且燃烧过程中会产生大量氮氧化物、二氧化硫、碳氢化合物及烟尘,直接污染大气,经过太阳光照作用产生的有害物质又进一步造成二次污染。本发明在传统生物水泥的技术上利用农业秸秆废物进行快速热解生物质油的副产物乙酸作原料,一方面农业废物来源广,数量大,容易获取,成本低廉;另一方面可以利用该发明进行废物资源回收利用,降低农业废物用于燃烧处理量及减少燃烧时对环境造成的污染,达到资源循环利用,可持续环保发展的目的。As a large agricultural country, my country produces a huge amount of agricultural waste. Agricultural waste in my country mainly comes from planting and breeding. It is estimated that the total output of crop straws in China is about 6.5×10 8 t/a, and most of the crop straws in China are used for one-time use such as burning. Moreover, a large amount of nitrogen oxides, sulfur dioxide, hydrocarbons and smoke will be produced during the combustion process, directly polluting the atmosphere, and harmful substances produced by sunlight will further cause secondary pollution. The present invention utilizes the by-product acetic acid of agricultural straw waste to rapidly pyrolyze biomass oil as a raw material in the traditional biocement technology. On the one hand, the agricultural waste has a wide source, a large quantity, easy acquisition and low cost; on the other hand, the invention can be used Carry out recycling of waste resources, reduce the amount of agricultural waste used for combustion and reduce environmental pollution during combustion, and achieve the purpose of resource recycling and sustainable environmental protection development.
综上所述,目前使用的微生物诱导方解石沉淀技术生产生物水泥的原料在大规模应用的情况下不仅成本高昂,且大量使用会对环境造成污染。因此亟需寻找一种新的低成本、可持续的钙源代替工业级的氯化钙,从而实现大规模推广应用。本发明在传统微生物诱导方解石沉淀技术基础上,使用采石场废料和农业废物快速热解生产生物原油的副产物乙酸反应生产可溶性钙盐代替工业级CaCl2,生产一种新型环境友好的生物水泥,实现了资源循环利用的可持续发展,大大促进了基于微生物诱导的方解石沉淀技术在实际工程中的应用与推广。To sum up, the currently used microbial-induced calcite precipitation technology is not only costly to produce raw materials for biocement in large-scale applications, but also causes environmental pollution when used in large quantities. Therefore, it is urgent to find a new low-cost, sustainable calcium source to replace industrial-grade calcium chloride, so as to achieve large-scale application. Based on the traditional microorganism-induced calcite precipitation technology, the present invention uses quarry waste and agricultural waste to rapidly pyrolyze the by-product acetic acid to produce bio-crude oil to produce soluble calcium salt instead of industrial-grade CaCl 2 to produce a new type of environmentally friendly bio-cement , realizing the sustainable development of resource recycling, and greatly promoting the application and promotion of calcite precipitation technology based on microbial induction in practical engineering.
发明内容Contents of the invention
本发明的目的在于针对现有技术存在的缺陷,提供一种新型基于低价钙离子制备生物水泥的生产方法。利用采石场的废料与农业废物快速热解生产生物质油的副产物乙酸反应生成的可溶性钙盐代替传统的氯化钙作钙源,然后与尿素、脲酶芽孢杆菌混合,从而利用基于尿素分解的微生物诱导方解石沉淀技术生产生物水泥。The object of the present invention is to provide a novel production method for preparing biocement based on low-priced calcium ions aiming at the defects in the prior art. The soluble calcium salt produced by the acetic acid reaction of the by-product of the rapid pyrolysis of quarry waste and agricultural waste to produce biomass oil replaces the traditional calcium chloride as the calcium source, and then mixes it with urea and urease bacillus to utilize urea decomposition. Microbial-induced calcite precipitation technology for the production of biocement.
本发明提供一种基于低价钙离子制备生物水泥的生产方法和应用,所述的生产方法如下:The present invention provides a kind of production method and application based on low-priced calcium ion preparation biological cement, and described production method is as follows:
步骤(1) :脲酶芽孢杆菌菌液的培养Step (1): the cultivation of urease bacillus bacterial liquid
按照1∶0.1~1∶1000的体积比,将脲酶芽孢杆菌菌株接种于培养液中,在15~35℃下振荡培养24~72h,得到脲酶芽孢杆菌菌液;通过光密度法测定其细胞浓度。According to the volume ratio of 1:0.1~1:1000, inoculate the strain of Bacillus urease in the culture medium, culture it with shaking at 15~35°C for 24~72 hours, and obtain the Bacillus urease bacteria liquid; measure its cell concentration by optical density method .
所述的培养液配方为:酵母提取物20g/L、硫酸铵10g/L、Tris缓冲液0.13g/L,培养液pH= 9.0。The formula of the culture solution is: 20 g/L of yeast extract, 10 g/L of ammonium sulfate, 0.13 g/L of Tris buffer, and the pH of the culture solution is 9.0.
所述的光密度法是指以纯培养液为参比,菌液在600nm波长下测定的吸光度,细胞浓度OD600值范围为0.1~3.0;The optical density method refers to the absorbance of the bacterial liquid measured at a wavelength of 600 nm with pure culture liquid as a reference, and the cell concentration OD600 value ranges from 0.1 to 3.0;
步骤(2):农业废物的热解Step (2): Pyrolysis of agricultural waste
在氮气氛围条件下,农业废物经粉碎后在200~900℃热解1~60min,得到富含乙酸的液相产物。Under the condition of nitrogen atmosphere, the agricultural waste is pulverized and then pyrolyzed at 200-900° C. for 1-60 minutes to obtain a liquid phase product rich in acetic acid.
步骤(3):钙溶液的制备Step (3): Preparation of Calcium Solution
石灰石粉末与步骤(2)富含乙酸的液相产物按质量比1∶2~1∶12混合,在4~40℃,反应36~120h,pH控制在0.1~10,离心得到质量浓度为0.1%-99%的乙酸钙溶液。Limestone powder and the liquid phase product rich in acetic acid in step (2) are mixed at a mass ratio of 1:2~1:12, reacted at 4~40°C for 36~120h, the pH is controlled at 0.1~10, and centrifuged to obtain a mass concentration of 0.1 %-99% calcium acetate solution.
步骤(4):胶结液的制备Step (4): Preparation of cementing liquid
将步骤(3)的乙酸钙溶液与尿素溶液以相同的摩尔浓度0.1~1mol/L等体积混合,并调节pH得到胶结液。The calcium acetate solution in step (3) and the urea solution are mixed in equal volumes at the same molar concentration of 0.1-1 mol/L, and the pH is adjusted to obtain a cementing solution.
步骤(5):游离溶液中生物水泥的制备Step (5): Preparation of biocement in free solution
将步骤(1)的脲酶芽孢杆菌菌液与步骤的胶结液按1∶1~1∶100的体积比混合,再在室温下反应12h~72h后,所得的沉淀物即为生物水泥。Combine the urease bacillus liquid of step (1) with the step The cementing liquid is mixed according to the volume ratio of 1:1~1:100, and after reacting at room temperature for 12h~72h, the obtained sediment is biocement.
所述的应用如下:The applications described are as follows:
将步骤的脲酶芽孢杆菌菌液在20~25℃的室温下循环通入一个砂柱装置1~10h,又加入脲酶芽孢杆菌菌液和质量浓度为0.1~10 mol/L尿素溶液与等质量浓度的钙溶液混合制成的胶结液混合通入砂柱装置,再循环3~12h;每天重复以上操作1~2次,持续7~28天后用蒸馏水洗涤胶结砂柱,并除去砂柱装置的圆筒外层,即可得到成型胶结生物水泥。will step The urease bacillus solution was circulated into a sand column device at room temperature of 20-25°C for 1-10 hours, and the urease bacillus solution, urea solution with a mass concentration of 0.1-10 mol/L and calcium with an equal mass concentration were added. The cementing liquid made by mixing the solutions is mixed and passed into the sand column device, and recirculated for 3 to 12 hours; repeat the above operation 1 to 2 times a day, and after 7 to 28 days, wash the cemented sand column with distilled water and remove the outer cylinder of the sand column device. layer, the form-bonded biocement can be obtained.
所述的砂柱装置为直径为1~100cm,高1~300cm的PVC材质的圆筒,其中的砂粒为制备成型胶结生物水泥的原料,且粒径范围为100~275μm。The sand column device is a PVC cylinder with a diameter of 1-100 cm and a height of 1-300 cm, the sand grains in which are raw materials for preparing molding cemented biocement, and the particle size ranges from 100 to 275 μm.
所述的石灰石粉末为石灰石或白云石采石场的废料中的一种以上,粉末粒径在0.1~1000μm。The limestone powder is more than one kind of limestone or waste materials from dolomite quarries, and the particle size of the powder is 0.1-1000 μm.
所述的农业废物包括玉米秸秆、玉米芯、麦秆、水稻秸秆、稻壳、蔗渣、棉秆、木屑和果壳中的至少一种。The agricultural waste includes at least one of corn stalks, corn cobs, wheat straw, rice stalks, rice husks, bagasse, cotton stalks, wood chips and fruit shells.
所述的脲酶芽孢杆菌包括巴氏芽孢杆菌、芽孢八叠球菌。The urease bacillus includes bacillus pasteurianus and bacillus sarcina.
本发明是利用脲酶芽孢杆菌在一定条件下利用尿素进行新陈代谢或分解生成碳酸根,与农业废物副产物乙酸溶解矿业废物反应生成大量乙酸钙溶液中的可溶性钙离子反应,生成一种粘合剂即生物水泥基材料。The present invention uses urease bacillus to metabolize or decompose urea to generate carbonate under certain conditions, and reacts with agricultural waste by-product acetic acid to dissolve mining waste to generate a large amount of soluble calcium ions in calcium acetate solution to generate a binder that is biocement based material.
本发明的有益效果:与传统生物水泥制备方法相比,其优势在于:(1)本发明解决了传统方法上原料成本高的问题,并充分利用农业废物与矿业废物生产所需的钙源,符合废物资源化利用和可持续发展的理念,提供一种新型可持续生产低廉生物水泥的制备方法;(2)充分利用农业废物,减少资源浪费以及降低农业废物因燃烧对环境造成的污染,实现资源回收利用,环境友好型发展的目的。Beneficial effects of the present invention: Compared with the traditional biocement preparation method, its advantages are: (1) The present invention solves the problem of high raw material cost in the traditional method, and fully utilizes the calcium source required for the production of agricultural waste and mining waste, In line with the concept of resource utilization of waste and sustainable development, it provides a new method for sustainable production of low-cost biocement; (2) Make full use of agricultural waste, reduce waste of resources and reduce environmental pollution caused by burning agricultural waste, to achieve Resource recycling, the purpose of environment-friendly development.
附图说明Description of drawings
图1:本发明游离溶液制备生物水泥工艺流程图;Fig. 1: Process flow chart of biocement preparation by free solution of the present invention;
图2:生物水泥的XRD图;Figure 2: XRD pattern of biocement;
图3:纯试剂碳酸钙的XRD图;Figure 3: XRD pattern of pure reagent calcium carbonate;
图4:砂柱装置原理图;Figure 4: Schematic diagram of the sand column device;
图5:成型的胶结生物水泥示意图;Figure 5: Schematic diagram of the formed cemented biocement;
图6:成型的胶结生物水泥的无侧限抗压强度与轴向应变的关系图;Figure 6: Unconfined compressive strength versus axial strain of the formed cemented biocement;
图7:成型的胶结生物水泥的劈裂抗压强度与轴向应变的关系图;Figure 7: The relationship between splitting compressive strength and axial strain of formed cemented biocement;
图8:MICP处理砂后的SEM图像;Figure 8: SEM image of sand treated by MICP;
图9:砂粒之间的空隙被CaCO3桥连SEM图像;Figure 9: SEM images of the gaps between sand grains bridged by CaCO 3 ;
图10:覆盖在砂粒表面CaCO3晶体的尺寸大小SEM图像。Figure 10: SEM images of the size of CaCO3 crystals covering the surface of sand grains.
具体实施方式detailed description
下面结合实例对本发明进行详细说明.The present invention is described in detail below in conjunction with example.
实施例1Example 1
在游离溶液制备一种基于低价钙离子制备的生物水泥Preparation of a low-valent calcium ion-based biocement in free solution
(1)NH4-YE培养液配制:称取15.75gTris盐,用去离子水稀释至1L,用1+9HCl调节pH至9,加入酵母提取物20g,硫酸铵10g,搅拌均匀,可得NH4-YE培养液;(1) Preparation of NH 4 -YE culture medium: Weigh 15.75g of Tris salt, dilute it to 1L with deionized water, adjust the pH to 9 with 1+9HCl, add 20g of yeast extract and 10g of ammonium sulfate, and stir well to obtain NH4-YE 4 -YE culture medium;
(2)脲酶芽孢杆菌菌液的制备:将脲酶芽孢杆菌ATCC 11859(SporosarcinaPasteurii)种菌活化后,取适量接种于100ml步骤(1)所制备的培养液中,并将其置于振荡箱(130rpm)30℃培养48h(使其细菌细胞浓度为OD600=0.8~1.2),得细菌液;(2) Preparation of Bacillus urease bacteria solution: After activating Bacillus urease ATCC 11859 (Sporosarcina Pasteurii) seed bacteria, inoculate an appropriate amount into 100ml of the culture solution prepared in step (1), and place it in a shaking box (130rpm ) cultured at 30°C for 48 hours (to make the bacterial cell concentration OD 600 =0.8~1.2) to obtain the bacterial liquid;
(3)乙酸的制备:在氮气氛围条件下经粉粹后的农业废物如玉米秸秆在470℃。温度条件下热解20min,所得液相产物中富含乙酸;(3) Preparation of acetic acid: pulverized agricultural waste such as corn stalks at 470°C under nitrogen atmosphere. Pyrolysis under temperature conditions for 20 minutes, the obtained liquid phase product is rich in acetic acid;
(4)钙溶液的制备:将800ml步骤(2)所获得的乙酸与100g矿业废物混合反应5天,加蒸馏水,使其混合物钙离子浓度调至为0.3mol/L,并用1mol/L的NaOH进一步调节混合物pH 至7.0~7.5。然后将溶液以4000rpm离心20分钟,得到上清液即为制备生物水泥所需的钙源;(4) Preparation of calcium solution: Mix and react 800ml of acetic acid obtained in step (2) with 100g of mining waste for 5 days, add distilled water to adjust the calcium ion concentration of the mixture to 0.3mol/L, and use 1mol/L of NaOH Further adjust the pH of the mixture to 7.0~7.5. Then the solution is centrifuged at 4000rpm for 20 minutes, and the supernatant obtained is the calcium source required for the preparation of biocement;
(5)将18.02g尿素溶解加水至1L,搅拌至充分混匀,配制成0.3mol/L;(5) Dissolve 18.02g of urea and add water to 1L, stir until fully mixed, and prepare 0.3mol/L;
(6)在游离溶液中制备生物水泥基材料:将步骤(2)所得的脲酶芽孢杆菌菌液与步骤4所得的尿素各取30ml按1:1混合,并将混合物的pH用NaOH调至7.0~7.5,在烧杯保存一天,然后加入步骤3所制备钙溶液30ml(具体操作流程见图1)。(6) Prepare biocement-based materials in free solution: Mix 30ml of the urea bacillus liquid obtained in step (2) and urea obtained in step 4 at a ratio of 1:1, and adjust the pH of the mixture to 7.0 with NaOH ~7.5, keep it in a beaker for one day, and then add 30ml of the calcium solution prepared in step 3 (see Figure 1 for the specific operation process).
(7)将所的沉淀用FG/C滤纸过滤,并在115℃下干燥1天,然后使用X射线衍射(XRD)分析被干燥后的沉淀。该沉淀的XRD图(见图2)与纯试剂级的碳酸钙的XRD 图(图3)完全匹配,结果证实沉淀物为碳酸钙。(7) The resulting precipitate was filtered with FG/C filter paper, and dried at 115° C. for 1 day, and then the dried precipitate was analyzed using X-ray diffraction (XRD). The XRD pattern of this precipitate (see Figure 2) perfectly matched the XRD pattern of pure reagent grade calcium carbonate (Figure 3), and the results confirmed that the precipitate was calcium carbonate.
实施例2Example 2
在砂柱装置中制备一种基于低价钙离子制备的生物水泥Preparation of a biocement based on low-valent calcium ions in a sand column device
砂柱装置如图4所示,直径为5cm,长10cm的PVC圆柱筒,将密度为1.20g/cm砂置于筒内,圆筒上下两端各置一片百洁布作过滤器,然后将PVC圆筒放置在填充有砾石的漏斗上,并用烧杯收集渗过砂柱的溶液,然后将其通过泵循环到柱的顶端;The sand column device is shown in Figure 4. A PVC cylinder with a diameter of 5 cm and a length of 10 cm is placed in the cylinder with a density of 1.20 g/cm sand, and a piece of scouring pad is placed at the upper and lower ends of the cylinder as a filter, and then the A PVC cylinder is placed on a funnel filled with gravel, and a beaker is used to collect the solution seeping through the sand column, which is then circulated to the top of the column through a pump;
(2)胶结液的制备:尿素溶液(0.3mol/L)与实例1步骤(3)制备的钙溶液(0.3mol/L)等体积混合制成的胶结液;(2) Preparation of cementing liquid: cementing liquid prepared by mixing equal volumes of urea solution (0.3mol/L) and calcium solution (0.3mol/L) prepared in step (3) of Example 1;
(3)取实例1步骤(2)的脲酶芽孢杆菌菌液80ml置于烧杯再通过泵循环至砂柱顶部,循环3h。然后换新鲜的30ml的菌液与300ml步骤2制备的胶结液混合通过砂柱装置循环9h。上述循环步骤每天重复两次,持续7天,碳酸钙开始在柱中沉淀,再循环上述步骤3天。总共处理10天。用蒸馏水洗涤胶结后的砂柱,并除去圆筒外层,得到成型的胶结生物水泥砂柱如图5所示;(3) Take 80ml of the urease bacillus bacteria solution in step (2) of Example 1, put it in a beaker and circulate it to the top of the sand column through a pump for 3 hours. Then change fresh 30ml of bacterial solution and mix with 300ml of cementing liquid prepared in step 2 and circulate through the sand column device for 9h. The above cycle steps were repeated twice a day for 7 days, calcium carbonate started to precipitate in the column, and the above steps were recirculated for 3 days. A total of 10 days were processed. Wash the cemented sand column with distilled water, and remove the outer layer of the cylinder to obtain the formed cemented biocement sand column as shown in Figure 5;
(4)将步骤(3)所得的成型的胶结生物水泥砂柱进行无侧限抗压强度(USC)和劈裂抗压强力(TS)测验,成型的胶结生物水泥的USC和TS强度随碳酸钙含量增加而增加(如图6与图7。已知USC/US强度比来表示生物水泥砂柱的脆性,其比值越高,材料越脆。步骤(3)制备出的生物水泥砂柱的强度比随碳酸钙含量增加而增加。(4) Test the unconfined compressive strength (USC) and splitting compressive strength (TS) of the formed cemented biocement sand column obtained in step (3). The USC and TS strengths of the formed cemented biocement vary with the The calcium content increases (as shown in Figure 6 and Figure 7. The USC/US strength ratio is known to indicate the brittleness of the biocement sand column, and the higher the ratio, the more brittle the material. The biocement sand column prepared in step (3) The strength ratio increases with increasing calcium carbonate content.
(5)通过SEM扫描电镜观察成型的胶结生物水泥的微观结构图像,可以看出砂粒表明覆盖着CaCO3(图8),且砂粒之间的空隙被CaCO3桥连如图9所示。且覆盖在砂粒表面CaCO3晶体的尺寸约为5~20um(图10),与之前报道用CaCl2作碳源诱导生成的方解石晶体尺寸大小相差无几。(5) Observing the microstructure image of the formed cemented biocement through SEM scanning electron microscope, it can be seen that the sand particles are covered with CaCO 3 (Fig. 8), and the gaps between the sand particles are bridged by CaCO 3 as shown in Fig. 9. And the size of CaCO 3 crystals covering the surface of sand grains is about 5-20um (Figure 10), which is almost the same size as the size of calcite crystals induced by CaCl 2 as carbon source reported previously.
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