| 序号 | 专利名 | 申请号 | 申请日 | 公开（公告）号 | 公开（公告）日 | 发明人 |
|---|---|---|---|---|---|---|
| 1 | 一种降粘型聚羧酸高性能减水剂及其制备方法 | CN201710452555.3 | 2017-06-15 | CN107265906A | 2017-10-20 | 仲以林; 陆智明; 黄凯波; 符惠玲; 巫晓鑫 |
| 一种降粘型聚羧酸高性能减水剂及其制备方法，减水剂合成原料为：低分子量嵌段改性不饱和聚氧乙烯醚共聚单体A、不饱和羧酸共聚单体B、烷基酚聚氧乙烯醚C、引发剂、还原剂、链转移剂、液碱和水；合成原料的质量比为，不饱和聚氧乙烯醚共聚单体A：不饱和羧酸共聚单体B：烷基酚聚氧乙烯醚C：引发剂：还原剂：链转移剂：液碱：水为(320～420)：(24～36)：(3～10)：(1～5)：(0.5～3)：(0.5～4)：(20～50)：(400～500)。本发明具有分散性能良好、降粘效果显著、与水泥适应性优良等特点，产品工艺简单，安全可靠，性能稳定，不含氯离子，对钢筋无锈蚀危害，对环境无污染等优点。 | ||||||
| 2 | 抗紫外线砂浆组合物 | CN200910054076.1 | 2009-06-29 | CN101648800B | 2012-07-04 | 施晓旦; 郭和森; 王养臣 |
| 本发明公开了一种抗紫外线砂浆组合物，含有400～600重量份白水泥、半水石膏50～100重量份、重质碳酸钙200～400重量份、钡钛有机复合乳液200～300重量份和光敏抗紫外线保护剂10～30重量份；所述钡钛有机复合乳液为(甲基)丙烯酸酯和(甲基)苯乙烯改性的钡钛混合物；光敏抗紫外线保护剂是由吸光染料、还原剂和氧化络合体系组成的胶溶物。本发明使砂浆内层得到保护，保护了高分子聚合物和颜料免遭紫外线的直接幅射，本发明的多功能抗紫外线砂浆组合物通过调节钡钛有机复合乳液的用量可用作多种防水涂料之用，主要用于高档住宅楼的阳台墙面和屋顶抗水砂浆之用。 | ||||||
| 3 | 热还原法炼镁联产水硬性胶凝材料的方法 | CN200610200738.8 | 2006-07-25 | CN101113081A | 2008-01-30 | 张继强; 陈黔 |
| 本发明公开的是热还原法炼镁联产水硬性胶凝材料的方法。本发明以硅铁合金和硅铝合金、或硅铁合金和金属铝配制还原剂，按常规的炼镁工艺步骤获得炼镁还原渣，将还原渣快速冷却，得到以硅酸钙和铝酸钙为主的水硬性胶凝材料，相当于国家标准32.5(R)等级强度以上水泥。本发明通过改进炼镁方法和对废渣的处理方法，可利用热还原法炼镁产生的还原渣直接生成能用于建筑使用的水硬性胶凝材料，做到了废物利用，也减少了对环境的污染和处理废渣的成本。 | ||||||
| 4 | 施工用填充材料 | CN201380041955.5 | 2013-08-05 | CN104520408A | 2015-04-15 | 饭田义宪; 金子敬祐 |
| [解决手段]一种施工用填充材料，包括固化材料、作为混合材料的微细粉末、及通过对混凝土处理设备的清洗排水中的沙子及砂砾进行分离而获得的污泥水。 | ||||||
| 5 | 建筑、筑路用快速修补材料 | CN200610028419.3 | 2006-06-30 | CN101096304B | 2011-12-07 | 张雄; 袁翔; 刘文龙 |
| 本发明涉及一种建筑用混凝土材料，特别涉及一种建筑用快速修补材料。主要解决现有修补材料通用性不够的技术问题。本发明的技术方案为：一种建筑用复合凝胶主剂，其组成成分的重量百分比为：硫铝酸盐水泥：30～50％，硅酸盐水泥：20～40％，尾矿粉：5～15％，粉煤灰：5～15％，硅灰：5～15％。本发明建筑用快速修补材料，由复合凝胶主剂、复合添加剂和复合骨料组成，根据不同的抢修用途复合凝胶主剂不变，对复合添加剂和复合骨料进行微调。本发明可适用于各种情况的建筑快速抢修抢建。 | ||||||
| 6 | 筑路、建筑用快速抢修材料 | CN200610028418.9 | 2006-06-30 | CN101096303B | 2011-09-21 | 张雄; 袁翔; 刘文龙 |
| 本发明涉及一种筑路、建筑用混凝土材料，特别涉及一种筑路、建筑用快速抢修材料。主要解决现有修补材料通用性不够的技术问题。本发明的技术方案为：一种筑路、建筑用快速抢修材料，由复合凝胶主剂、复合添加剂和复合骨料组成，复合凝胶主剂其组成成分的重量百分比为：硫铝酸盐水泥：30～50％，硅酸盐水泥：20～40％，尾矿粉：5～15％，粉煤灰：5～15％，硅灰：5～15％。本发明根据不同的抢修用途复合凝胶主剂不变，对复合添加剂和复合骨料进行微调。本发明可适用于各种情况的建筑、筑路的快速抢修抢建。 | ||||||
| 7 | 建筑、筑路用快速修补材料 | CN200610028419.3 | 2006-06-30 | CN101096304A | 2008-01-02 | 张雄; 袁翔; 刘文龙 |
| 本发明涉及一种建筑、筑路用混凝土材料，特别涉及一种建筑、筑路用快速修补材料。主要解决现有修补材料通用性不够的技术问题。本发明的技术方案为：一种建筑、筑路用复合凝胶主剂，其组成成分的重量百分比为：硫铝酸盐水泥：30～50％，硅酸盐水泥：20～40％，尾矿粉：5～15％，粉煤灰：5～15％，硅灰：5～15％。本发明建筑、筑路用快速修补材料，由复合凝胶主剂、复合添加剂和复合骨料组成，根据不同的抢修用途复合凝胶主剂不变，对复合添加剂和复合骨料进行微调。本发明可适用于各种情况的建筑、筑路的快速抢修抢建。 | ||||||
| 8 | 热还原法炼镁联产水硬性胶凝材料的方法 | CN200610200738.8 | 2006-07-25 | CN101113081B | 2012-07-25 | 张继强; 陈黔 |
| 本发明公开的是热还原法炼镁联产水硬性胶凝材料的方法。本发明以硅铁合金和硅铝合金、或硅铁合金和金属铝配制还原剂，按常规的炼镁工艺步骤获得炼镁还原渣，将还原渣快速冷却，得到以硅酸钙和铝酸钙为主的水硬性胶凝材料，相当于国家标准32.5(R)等级强度以上水泥。本发明通过改进炼镁方法和对废渣的处理方法，可利用热还原法炼镁产生的还原渣直接生成能用于建筑使用的水硬性胶凝材料，做到了废物利用，也减少了对环境的污染和处理废渣的成本。 | ||||||
| 9 | 抗紫外线砂浆组合物 | CN200910054076.1 | 2009-06-29 | CN101648800A | 2010-02-17 | 施晓旦; 郭和森; 王养臣 |
| 本发明公开了一种抗紫外线砂浆组合物，含有400～600重量份白水泥、半水石膏50～100重量份、重质碳酸钙200～400重量份、钡钛有机复合乳液200～300重量份和光敏抗紫外线保护剂10～30重量份；所述钡钛有机复合乳液为(甲基)丙烯酸酯和(甲基)苯乙烯改性的钡钛混合物；光敏抗紫外线保护剂是由吸光染料、还原剂和氧化络合体系组成的胶溶物。本发明使砂浆内层得到保护，保护了高分子聚合物和颜料免遭紫外线的直接幅射，本发明的多功能抗紫外线砂浆组合物通过调节钡钛有机复合乳液的用量可用作多种防水涂料之用，主要用于高档住宅楼的阳台墙面和屋顶抗水砂浆之用。 | ||||||
| 10 | 优质改良材 | CN200910110839.X | 2009-01-13 | CN101570409A | 2009-11-04 | 田中义昭; 蔡德明 |
| 优质改良材，属建筑材料领域。其组成成分及重量百分比含量如下：天然砂10％－40％，机制加工砂10％－40％，工业废渣20％－60％。还可以包含碎石，所述碎石的含量不超过54％。还可以包含0.003％－0.5％的碱性有机化合物。通过搅拌机进行均匀混合，即可得到本发明所述的优质改良材。本发明有效抑制混凝土的碱集料反应、提高混凝土的强度、对钢筋有极好的钝化阻锈和保护作用、延长建筑物的寿命。本发明主要用于灰浆材料、地基改良材、轻量混凝土骨料、混凝土预制件材料、下水道填充材，还可以作为植被土壤改良材使用。 | ||||||
| 11 | 一种改性氯氧镁水泥制品及其制备方法 | CN200910058582.8 | 2009-03-12 | CN101492278A | 2009-07-29 | 李家贵 |
| 本发明公开了一种改性氯氧镁水泥制品及其制备方法，由下述原料制备而成：轻烧氧化镁粉(75－95％MgO)100份，氯化镁(MgCl2·6H2O)50－75份，丙烯酸类单体2－10份，水溶性强氧化剂0.1－0.8份，水溶性强还原剂0.1－0.8份，0－20份硫酸铝，硫酸与磷矿粉混合预制浆体0－20份，硫酸与含铝矿粉混合预制浆体5－20份，磷酸(85％H3PO4)0－8份，硼酸0－8份，填料20－500份，水45－90份。利用本发明配方和方法制造的氯氧镁水泥制品，无泛霜、返卤、变形现象，性能稳定，适于作建筑材料、特别是装饰性天然石材的替代品和其它材料的替代品，具有较高的应用价值和广阔的应用前景。 | ||||||
| 12 | 筑路、建筑用快速抢修材料 | CN200610028418.9 | 2006-06-30 | CN101096303A | 2008-01-02 | 张雄; 袁翔; 刘文龙 |
| 本发明涉及一种筑路、建筑用混凝土材料，特别涉及一种筑路、建筑用快速抢修材料。主要解决现有修补材料通用性不够的技术问题。本发明的技术方案为：一种筑路、建筑用快速抢修材料，由复合凝胶主剂、复合添加剂和复合骨料组成，复合凝胶主剂其组成成分的重量百分比为：硫铝酸盐水泥：30～50％，硅酸盐水泥：20～40％，尾矿粉：5～15％，粉煤灰：5～15％，硅灰：5～15％。本发明根据不同的抢修用途复合凝胶主剂不变，对复合添加剂和复合骨料进行微调。本发明可适用于各种情况的建筑、筑路的快速抢修抢建。 | ||||||
| 13 | NOVEL SULFOALUMINATE CLINKER BASED HYDRAULIC BINDER AND USE THEREOF IN A PROCESS FOR TREATING POLLUTED SOILS | US14400865 | 2013-05-13 | US20150158063A1 | 2015-06-11 | Emmanuel Moudilou; Cyril Guerandel; Bruno Le Rolland; Stephanie Delair |
| A hydraulic binder based on a sulfoaluminate clinker including the mineralogical phases ye'elimite C4A3$, mayenite C12A7, free lime CaO, and optionally belite C2S, characterized in that, in the clinker, the mineralogical phases are 20% to 50% by weight of ye'elimite C4A3$ phase, 5% to 80% by weight of mayenite C12A7 phase, and 1% to 5% by weight of free lime CaO, the weight ratio between the mayenite C12A7 and ye'elimite C4A3$ phases being between 0.1 and 10. The binder can be used to treat polluted soils, in particular soils with a leachable fraction greater than 0.4% that contains predominantly anions and/or heavy metal cations by mixing the soil with the hydraulic binder, in soil/binder weight proportions of between 1 and 40 parts of binder for 100 parts of soil. It makes it possible to stabilize soils which are polluted or to stabilize soils before dumping. | ||||||
| 14 | Method of waste stabilization with dewatered chemically bonded phosphate ceramics | US10547445 | 2004-02-26 | US07745679B2 | 2010-06-29 | Arun Wagh; Martin D. Maloney |
| A method of stabilizing a waste in a chemically bonded phosphate ceramic (CBPC). The method consists of preparing a slurry including the waste, water, an oxide binder, and a phosphate binder. The slurry is then allowed to cure to a solid, hydrated CBPC matrix. Next, bound water within the solid, hydrated CBPC matrix is removed. Typically, the bound water is removed by applying heat to the cured CBPC matrix. Preferably, the quantity of heat applied to the cured CBPC matrix is sufficient to drive off water bound within the hydrated CBPC matrix, but not to volatalize other non-water components of the matrix, such as metals and radioactive components. Typically, a temperature range of between 100° C.-200° C. will be sufficient. In another embodiment of the invention wherein the waste and water have been mixed prior to the preparation of the slurry, a select amount of water may be evaporated from the waste and water mixture prior to preparation of the slurry. Another aspect of the invention is a direct anyhydrous CBPC fabrication method wherein water is removed from the slurry by heating and mixing the slurry while allowing the slurry to cure. Additional aspects of the invention are ceramic matrix waste forms prepared by the methods disclosed above. | ||||||
| 15 | Liquid additive for reducing water-soluble chromate | US11269350 | 2005-11-08 | US07296626B2 | 2007-11-20 | Karen Luke; Roger S. Cromwell |
| Methods for cementing and cement compositions are provided, wherein the cement composition comprises cementitious material and an aqueous suspension of zeolite and a chromate reducing agent. | ||||||
| 16 | Waste-treating material | US35577 | 1993-03-23 | US5609558A | 1997-03-11 | Taiichiro Sasae; Tomio Nishida; Masakazu Uekita; Takashi Funahashi |
| A waste-treating material which comprises cement and at least one reducing metal, effective for stabilizing industrial wastes containing harmful metals like a heavy metal and the like and cyanides. A preferred example of the reducing metal is iron. Additionally the waste-treating material may also contain at least one member selected from a group consisting of a reducing agent, aluminum sulfate, allophane, and bentonite as the auxiliary. The use of this waste-treating material makes it possible to stabilize the hazardous heavy material and the cyanides contained in the industrial wastes, thereby remarkably contributing to a stabilizing treatment of the industrial wastes. | ||||||
| 17 | Sulfoaluminate clinker based hydraulic binder and use thereof in a process for treating polluted soils | US14400865 | 2013-05-13 | US09764365B2 | 2017-09-19 | Emmanuel Moudilou; Cyril Guerandel; Bruno Le Rolland; Stephanie Delair |
| A hydraulic binder based on a sulfoaluminate clinker including the mineralogical phases ye'elimite C4A3$, mayenite C12A7, free lime CaO, and optionally belite C2S, characterized in that, in the clinker, the mineralogical phases are 20% to 50% by weight of ye'elimite C4A3$ phase, 5% to 80% by weight of mayenite C12A7 phase, and 1% to 5% by weight of free lime CaO, the weight ratio between the mayenite C12A7 and ye'elimite C4A3$ phases being between 0.1 and 10. The binder can be used to treat polluted soils, in particular soils with a leachable fraction greater than 0.4% that contains predominantly anions and/or heavy metal cations by mixing the soil with the hydraulic binder, in soil/binder weight proportions of between 1 and 40 parts of binder for 100 parts of soil. It makes it possible to stabilize soils which are polluted or to stabilize soils before dumping. | ||||||
| 18 | FILLER FOR CONSTRUCTION | US14419528 | 2013-08-05 | US20150210595A1 | 2015-07-30 | Yoshinori Iida; Keisuke Kaneko |
| A filler for construction includes a hardening material, a fine powder as an admixture material, and sludge water obtained by separating sand and gravel from discharged water provided by washing concrete handling equipment. | ||||||
| 19 | Liquid additive for reducing water-soluble chromate | US11269350 | 2005-11-08 | US20070101906A1 | 2007-05-10 | Karen Luke; Roger Cromwell |
| Methods for cementing and cement compositions are provided, wherein the cement composition comprises cementitious material and an aqueous suspension of zeolite and a chromate reducing agent. | ||||||
| 20 | Method of waste stabilization with dewatered chemically bonded phosphate ceramics | US10547445 | 2004-02-26 | US20060235258A1 | 2006-10-19 | Arun Wagh; Martin Maloney |
| A method of stabilizing a waste in a chemically bonded phosphate ceramic (CBPC). The method consists of preparing a slurry including the waste, water, an oxide binder, and a phosphate binder. The slurry is then allowed to cure to a solid, hydrated CBPC matrix. Next, bound water within the solid, hydrated CBPC matrix is removed. Typically, the bound water is removed by applying heat to the cured CBPC matrix. Preferably, the quantity of heat applied to the cured CBPC matrix is sufficient to drive off water bound within the hydrated CBPC matrix, but not to volatalize other non-water components of the matrix, such as metals and radioactive components. Typically, a temperature range of between 100° C.-200° C. will be sufficient. In another embodiment of the invention wherein the waste and water have been mixed prior to the preparation of the slurry, a select amount of water may be evaporated from the waste and water mixture prior to preparation of the slurry. Another aspect of the invention is a direct anyhydrous CBPC fabrication method wherein water is removed from the slurry by heating and mixing the slurry while allowing the slurry to cure. Additional aspects of the invention are ceramic matrix waste forms prepared by the methods disclosed above. | ||||||
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