| 序号 | 专利名 | 申请号 | 申请日 | 公开（公告）号 | 公开（公告）日 | 发明人 |
|---|---|---|---|---|---|---|
| 61 | 一种垃圾焚烧生产水泥的方法和装置 | CN201110027258.7 | 2011-01-26 | CN102173614A | 2011-09-07 | 贾会平 |
| 本发明提供一种垃圾焚烧生产水泥的方法和装置，装置包括原料制备系统、进料设备、预分解器、分解器、煅烧炉和冷却器，煅烧炉上部设有2～8个垃圾粉料喷嘴。水泥原料进行破碎、均化、配料、磨粉后制成球团。生活垃圾干燥、破碎后用气体输送至煅烧炉中燃烧，煅烧球团或隔烟加热的方式煅烧球团。垃圾燃烧后产生的炉渣直接进入煅烧的水泥原料中或经垃圾炉渣出口到熟料配料/磨粉过程作水泥熟料的混合材料。本发明利用垃圾焚烧产生的热量直接加热煅烧水泥原料，既有效处理了垃圾，又合理利用了垃圾焚烧放出的热能，变废为宝，有利于环保。垃圾炉渣掺入水泥材料中，解决了废渣填埋占地问题和对环境的污染问题。 | ||||||
| 62 | 一种利用CFBC脱硫灰生产的粉煤灰硅酸盐水泥 | CN200910184133.8 | 2009-08-25 | CN101643328A | 2010-02-10 | 付晓茹; 黎飞虎; 方华; 张慧 |
| 本发明公开了一种利用CFBC脱硫灰生产的粉煤灰硅酸盐水泥，其组份和重量比是：CFBC脱硫灰15％-50％，硅酸盐水泥熟料44％-83％，石膏2％-6％。其中制备32.5级粉煤灰硅酸盐水泥，各组份的重量比是：CFBC脱硫灰30％-50％，硅酸盐水泥熟料44％-68％，石膏2％-6％。制备42.5级粉煤灰硅酸盐水泥，各组份的重量比是：CFBC脱硫灰15％-30％，硅酸盐水泥熟料64％-83％，石膏2％-6％。本发明所提供的粉煤灰硅酸盐水泥CFBC脱硫灰掺量高，不仅可解决CFBC脱硫灰利用率低，资源浪费的问题，同时还可以提供一种新的水泥生产工艺；另外本发明的粉煤灰硅酸盐水泥生产工艺简单、成本较低，便于推广使用，有巨大的经济效益、社会效益和环境效益。 | ||||||
| 63 | 一种资源化利用城市垃圾焚烧飞灰的方法 | CN200510026152.X | 2005-05-25 | CN100486926C | 2009-05-13 | 施惠生 |
| 本发明提供一种资源化利用城市垃圾焚烧飞灰烧制含氯、硫水泥熟料的方法。利用城市垃圾焚烧飞灰烧制含氯、硫水泥熟料，可以有效地将垃圾焚烧飞灰中的重金属物质结合在水泥熟料矿物中，并能保证焚烧飞灰中重金属不易从水化体系中浸出，从而确保其安全使用；所述的含氯、硫水泥熟料的烧成温度在1000-1300℃之间；同时还可以减少氯、硫等的挥发及其造成的二次环境污染。本发明具有显著的社会效益和经济效益。 | ||||||
| 64 | 生活垃圾分拣后残余灰渣直接用于生产水泥的方法 | CN200710054732.9 | 2007-07-06 | CN101337776A | 2009-01-07 | 杨力远; 马军涛; 马光义; 田永生 |
| 本发明涉及一种生活垃圾分拣后残余灰渣直接用于生产水泥的方法，包括以下步骤：(1)生活垃圾的分拣；(2)分拣残渣的除臭灭菌；(3)灰渣的陈化；(4)确定灰渣的掺入量；(5)入窑煅烧；(6)煅烧所得熟料与石膏配合入水泥磨，制成水泥。采用本发明的方法具有以下效果：(1)直接将生活垃圾分拣残渣用作水泥生产，可以变废为宝，节省了宝贵的粘土资源和煤炭资源；(2)减少了掩埋、焚烧生活垃圾设备所需要的大量资金，降低了生活垃圾处理成本；(3)可以有效地清除生活垃圾处理过程中的有害成分，保证清洁生产和排放达标；(4)对水泥产品的质量不会产生任何有害影响。经过反复试验，生活垃圾分拣后的残余灰渣可以直接投入水泥窑中进行生产，节省了大量的投资，而且对水泥的产品质量没有任何影响。 | ||||||
| 65 | 水泥熟料及其制备方法 | CN200810069676.0 | 2008-05-14 | CN101274824A | 2008-10-01 | 万朝均; 彭小芹; 李利; 袁启涛; 张廷雷; 刘立军; 李腾; 陈衡 |
| 本发明属水泥熟料及水泥熟料制备技术领域，尤其是以废弃碎石混凝土为主要原料的水泥熟料及其制备方法，原料组成按重量百分含量是：废弃碎石混凝土37.0％～77.0％；石灰岩21.0％～52.0％；砂岩 0.5％～8.5％；硫酸渣 1.0％～4.5％。制备时将废弃碎石混凝土干燥、破碎、筛分，得粒径为5～20mm的颗粒，与石灰岩、砂岩及硫酸渣配合，按传统工艺制备成水泥熟料。本发明中所得水泥熟料制备的水泥，其强度等级可达52.5级，可作为制备混凝土的胶凝材料使用。废弃碎石混凝土在水泥熟料原料中的比例可接近80％，利用率很高，为废弃混凝土的资源化找到了一条很好的利用途径。 | ||||||
| 66 | 粉煤灰基矿物聚合水泥生产方法及所制备的材料 | CN200510077649.4 | 2005-06-22 | CN1884172A | 2006-12-27 | 王栋民; 陈良程 |
| 粉煤灰基矿物聚合材料是利用粉煤灰中玻璃体的活性，选择特定组成和配方的矿物聚合剂对其进行活性激发，使其中的铝硅玻璃体发生解聚，然后在一定条件下再聚合而生成的无机聚合材料。利用粉煤灰基矿物聚合材料部分或大部取代水泥熟料来制备水泥，形成粉煤灰基矿物聚合水泥。本发明给出粉煤灰基矿物聚合水泥的生产方法，采用该方法可以制备一系列材料：粉煤灰基矿聚材料、粉煤灰掺和料、粉煤灰基矿聚水泥、粉煤灰水泥、复合硅酸盐水泥和砌筑水泥。 | ||||||
| 67 | 一种资源化利用城市垃圾焚烧飞灰的方法 | CN200510026152.X | 2005-05-25 | CN1868955A | 2006-11-29 | 施惠生 |
| 本发明提供一种资源化利用城市垃圾焚烧飞灰烧制含氯、硫水泥熟料的方法。利用城市垃圾焚烧飞灰烧制含氯、硫水泥熟料，可以有效地将垃圾焚烧飞灰中的重金属物质结合在水泥熟料矿物中，并能保证焚烧飞灰中重金属不易从水化体系中浸出，从而确保其安全使用；所述的含氯、硫水泥熟料的烧成温度在1000－1300℃之间；同时还可以减少氯、硫等的挥发及其造成的二次环境污染。本发明具有显著的社会效益和经济效益。 | ||||||
| 68 | 硬化组合物和硬化产物 | CN96190912.9 | 1996-08-14 | CN1161032A | 1997-10-01 | 冈元丰重; 石田泰之; 内田润 |
| 本发明涉及一种硬化组合物，特点在于，含有(A)一种矿渣组合物，含有0～37wt％的CaO、23～90wt％的SiO2、和0～40wt％的Al2O3和0.1～50wt％的一种或多种选自由氧化铁、碱性组分、含磷组分、二氧化钛、氧化锰、和氧化镁组成的组中的化合物，和/或0.1～10wt％的卤素；和(B)一种碱性激活剂。本发明还涉及通过把所说的硬化组合物与水混合得到的硬化产物。所说的硬化产物适用于各种混凝土材料，所以，可以有效地利用垃圾焚烧后的灰分、污水污泥等，并作为资源再循环。 | ||||||
| 69 | 湿磨粉煤灰制无熟料水泥及其制品 | CN94111221.7 | 1994-01-13 | CN1105344A | 1995-07-19 | 高杰生; 杜庆林 |
| 一种湿磨粉煤灰无熟料水泥，是由火电厂的湿排粉煤灰、石灰、石膏经分别磨细后充分混合，即成为一种低标号水泥(275#)，这种水泥可作为一般低标号水泥使用，如制作免烧砖、免烧砌块，也可用来制作建筑砂浆、C13#混凝土或将磨细粉煤灰掺入普通硅酸盐水泥中。其质量完全符合国家标准。 | ||||||
| 70 | 用膨润土废矿作混合材的水泥生产方法 | CN94116611.2 | 1994-10-05 | CN1104187A | 1995-06-28 | 郑荣贵; 孟忠 |
| 一种用膨润土废矿作混合材的水泥生产方法，按常规工艺流程生产熟料，在后段工序中，可加或不加活性材料粉煤灰，几乎全部用膨润土废矿作混合材，经粉碎再与熟料、石膏分别按配方计量后混合，进行粉磨、入库、包装、检验、出厂。本发明一改以高炉矿渣为主作混合料的习惯作法，一扫以煤渣、石灰渣等作代用原料造成水泥质次的作法，配合以相应的新工艺，使水泥质量得到改善，成本大大降低，易磨性好、节能，还解决了膨润土产地的废矿堆积的公害问题，社会与经济效益显著。 | ||||||
| 71 | 沸腾锅炉供热、发电、烧水泥的生产工艺 | CN89103930.9 | 1989-06-08 | CN1024461C | 1994-05-11 | 秦至刚; 蔡晋强; 康齐福; 付子诚; 王象明; 杨天豪; 陈政彬; 施正伦; 崔恩书; 郑越; 巴陵; 佟贵山; 王金元; 张玉昌; 付鸣放; 徐敏康 |
| 本发明公开了一种沸腾锅炉供热发电烧水泥的生产工艺，水泥原料中的粘土全部用燃料燃烧后的煤灰代替，其特征是要加入比一般水泥生料多的矿化剂(如石膏、萤石)同时要加入抗爆剂(如CaO、水玻璃、浓纸浆液、纯水泥)，所得水泥熟料的KH值可控制在0.65至0.88，本发明的优点是，燃料灰分转化为水泥产品，可以提高沸腾炉发电供热的经济效益，免挖农田有利于保护粘土资源降低废气中SO3浓度，有利于保护环境。 | ||||||
| 72 | 테르네사이트 제조 방법 | KR1020147005709 | 2012-07-16 | KR1020140066714A | 2014-06-02 | 불러얀,프랑크; 슈미트,덕; 벤하하,모젠 |
| 본 발명은 20 내지 95 중량%의 C 5 S 2 $ 및 15 중량% 미만의 C 4 A 3 $를 포함하는 테르네사이트 클링커의 제조, 및 수경성 및/또는 잠재 수경성 및/또는 포졸란성 물질에 대한 첨가제로서 테르네사이트의 용도에 관한 것이다. | ||||||
| 73 | 테르네사이트-벨라이트-칼슘 설포알루미네이트 클링커 제조 방법 | KR1020147005708 | 2012-07-16 | KR1020140064828A | 2014-05-28 | 불러얀,프랑크; 슈미트,덕; 벤하하,모젠 |
| 본 발명은 테르네사이트-벨라이트-칼슘 설포알루미네이트 (페라이트) 클링커 제조에 관한 것이다. 본 발명은 또한 클링커 제조를 위한 대안의 원료, 예를 들어, 낮은 유리 함량 및/또는 높은 유리 석회 함량 및/또는 높은 함량의 결정질 고온 상을 가지는 덩어리 슬래그 및 애쉬와 같이 저품질을 가지는 것을 포함한 공업 부산물 기반의 원료, 또한 유사한 화학적 조성을 가지는 천연 발생의 암석 및 암석 유리의 용도에 관한 것이다. | ||||||
| 74 | SPECIALIZED LINED LANDFILL SYSTEM FOR THE STABILIZATION AND CONTAINMENT OF DRILLING WASTES AND COAL COMBUSTION RESIDUES | US15425106 | 2017-02-06 | US20170144203A1 | 2017-05-25 | JAMES JOSEPH MANNO, JR.; JACQUELINE LILJA MANNO |
| Systems and methods of the present invention include a method for the treatment of drilling wastes and coal combustion residues, comprising combining at least a first drilling waste with coal combustion residues to form a paste, combining at least a second drilling waste with coal combustion residues to form a compactable fill, and placing the paste and the compactable fill in a landfill. Other embodiments include a method of treating drilling wastes and coal combustion residues, comprising combining at least one drilling waste with a coal combustion residue to form a paste. Further embodiments include containing the paste within at least one geotextile container. Still further embodiments include placing the geotextile container in a landfill. | ||||||
| 75 | GEOPOLYMER CEMENT | US14441976 | 2013-11-13 | US20150321954A1 | 2015-11-12 | Desmond Peter CHALMERS; Paul Gregory KIDD; Peter David SLEEP |
| A solid component activator for use in a geopolymer cement containing a silico-aluminate material comprising a mixture of sodium silicate and sodium carbonate for activating the geopolymer cement by increasing reactivity of the silico-aluminate material in the geopolymer cement when forming geopolymer concrete. | ||||||
| 76 | Method for producing ternesite | US14239348 | 2012-07-16 | US09073785B2 | 2015-07-07 | Frank Bullerjahn; Dirk Schmitt; Mohsen Ben Haha |
| The present invention relates to the production of ternesite clinkers containing 20 to 95% by weight C5S2$ and less than 15% by weight C4A3$, and to the use of ternesite as an additive to hydraulic and/or latent hydraulic and/or pozzolanic materials. | ||||||
| 77 | Fly ash-based cementitious mixture | US14087753 | 2013-11-22 | US09023149B1 | 2015-05-05 | Kyle Scott Douglas; Dustin Marion Hulbert; Amitabha Kumar; Thomas McClure Pounds; Julie Robyn Rapoport; Michael Alexander Telischak; Susanne Rebecca Williams |
| A cementitious mixture for high-volume production of masonry products comprises a hydraulic binder accounting for 20 wt % or more of the cementitious mixture, the hydraulic binder comprising 75 to 100 wt % Class C fly ash with a CaO equivalent content of at least 15% by weight. The cementitious mixture also comprises one or more aggregates, and a set control system. | ||||||
| 78 | METHOD FOR PRODUCING TERNESITE-BELITE CALCIUM SULFOALUMINATE CLINKER | US14238872 | 2012-07-16 | US20140283712A1 | 2014-09-25 | Frank Bullerjahn; Dirk Schmitt; Mohsen Ben Haha |
| The present invention relates to the production of a ternesite-belite-calcium sulfoaluminate (ferrite) clinker. The invention also relates to the use of alternative raw materials for clinker production, for example raw materials based on industrial byproducts, including those of low quality, such as lump slag and ash having a low glass content and/or a high free lime content and/or a high content of crystalline high-temperature phases, as well as naturally occurring rocks and rock glasses of comparative chemical composition. | ||||||
| 79 | Specialized lined landfill system for the stabilization and containment of drilling wastes and coal combustion residues | US13452269 | 2012-04-20 | US08807871B2 | 2014-08-19 | James Joseph Manno, Jr.; Jacqueline Lija Manno |
| Systems and methods of the present invention include a method for the treatment of drilling wastes and coal combustion residues, comprising combining at least a first drilling waste with coal combustion residues to form a paste, combining at least a second drilling waste with coal combustion residues to form a compactable fill, and placing the paste and the compactable fill in a landfill. Other embodiments include a method of treating drilling wastes and coal combustion residues, comprising combining at least one drilling waste with a coal combustion residue to form a paste. Further embodiments include containing the paste within at least one geotextile container. Still further embodiments include placing the geotextile container in a landfill. | ||||||
| 80 | Installation and method for conversion of paper residue into a mineral product | US13627480 | 2012-09-26 | US08764937B2 | 2014-07-01 | Joseph Jan Peter Biermann |
| A method and apparatus for conversion of paper residue into a mineral product uses a fluidized bed device with a distribution plate for securing an even distribution and supply of at least combustion air to the bed material and to the paper residue. An air box below the distribution plate supplies combustion air to the bed material and paper residue above the distribution plate. A heat exchanging section receives in separate parts ambient air and flue gases from the fluidized bed device for exchanging heat between flue gases and ambient air. The heat exchanging section is connected to the air box for supplying the heated ambient air to the air box for use as combustion air. A control system is employed for controlling the amount of bed material and the dimension of its particles and is arranged to monitor and maintain a process parameter within a predefined range. | ||||||
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