WO2015007103A1 - Method for preparing retardant slurry containing coal ash for controlling fire disaster in coal field - Google Patents

Method for preparing retardant slurry containing coal ash for controlling fire disaster in coal field Download PDF

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WO2015007103A1
WO2015007103A1 PCT/CN2014/074072 CN2014074072W WO2015007103A1 WO 2015007103 A1 WO2015007103 A1 WO 2015007103A1 CN 2014074072 W CN2014074072 W CN 2014074072W WO 2015007103 A1 WO2015007103 A1 WO 2015007103A1
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Prior art keywords
coal
water
slurry
solution
fire
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PCT/CN2014/074072
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French (fr)
Chinese (zh)
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秦波涛
鲁义
张雷林
申洪敏
贾玉威
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中国矿业大学
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Priority to AU2014274500A priority Critical patent/AU2014274500B2/en
Priority to RU2014147113/03A priority patent/RU2584186C1/en
Priority to CA2872360A priority patent/CA2872360C/en
Priority to ZA2014/08006A priority patent/ZA201408006B/en
Publication of WO2015007103A1 publication Critical patent/WO2015007103A1/en

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    • EFIXED CONSTRUCTIONS
    • E21EARTH DRILLING; MINING
    • E21FSAFETY DEVICES, TRANSPORT, FILLING-UP, RESCUE, VENTILATION, OR DRAINING IN OR OF MINES OR TUNNELS
    • E21F5/00Means or methods for preventing, binding, depositing, or removing dust; Preventing explosions or fires
    • E21F5/08Rock dusting of mines; Depositing other protective substances
    • E21F5/12Composition of rock dust
    • EFIXED CONSTRUCTIONS
    • E21EARTH DRILLING; MINING
    • E21FSAFETY DEVICES, TRANSPORT, FILLING-UP, RESCUE, VENTILATION, OR DRAINING IN OR OF MINES OR TUNNELS
    • E21F5/00Means or methods for preventing, binding, depositing, or removing dust; Preventing explosions or fires
    • E21F5/02Means or methods for preventing, binding, depositing, or removing dust; Preventing explosions or fires by wetting or spraying
    • E21F5/06Fluids used for spraying
    • AHUMAN NECESSITIES
    • A62LIFE-SAVING; FIRE-FIGHTING
    • A62DCHEMICAL MEANS FOR EXTINGUISHING FIRES OR FOR COMBATING OR PROTECTING AGAINST HARMFUL CHEMICAL AGENTS; CHEMICAL MATERIALS FOR USE IN BREATHING APPARATUS
    • A62D1/00Fire-extinguishing compositions; Use of chemical substances in extinguishing fires
    • A62D1/0028Liquid extinguishing substances
    • A62D1/005Dispersions; Emulsions
    • CCHEMISTRY; METALLURGY
    • C04CEMENTS; CONCRETE; ARTIFICIAL STONE; CERAMICS; REFRACTORIES
    • C04BLIME, MAGNESIA; SLAG; CEMENTS; COMPOSITIONS THEREOF, e.g. MORTARS, CONCRETE OR LIKE BUILDING MATERIALS; ARTIFICIAL STONE; CERAMICS; REFRACTORIES; TREATMENT OF NATURAL STONE
    • C04B28/00Compositions of mortars, concrete or artificial stone, containing inorganic binders or the reaction product of an inorganic and an organic binder, e.g. polycarboxylate cements
    • C04B28/34Compositions of mortars, concrete or artificial stone, containing inorganic binders or the reaction product of an inorganic and an organic binder, e.g. polycarboxylate cements containing cold phosphate binders
    • CCHEMISTRY; METALLURGY
    • C04CEMENTS; CONCRETE; ARTIFICIAL STONE; CERAMICS; REFRACTORIES
    • C04BLIME, MAGNESIA; SLAG; CEMENTS; COMPOSITIONS THEREOF, e.g. MORTARS, CONCRETE OR LIKE BUILDING MATERIALS; ARTIFICIAL STONE; CERAMICS; REFRACTORIES; TREATMENT OF NATURAL STONE
    • C04B2111/00Mortars, concrete or artificial stone or mixtures to prepare them, characterised by specific function, property or use
    • C04B2111/20Resistance against chemical, physical or biological attack
    • C04B2111/28Fire resistance, i.e. materials resistant to accidental fires or high temperatures
    • CCHEMISTRY; METALLURGY
    • C04CEMENTS; CONCRETE; ARTIFICIAL STONE; CERAMICS; REFRACTORIES
    • C04BLIME, MAGNESIA; SLAG; CEMENTS; COMPOSITIONS THEREOF, e.g. MORTARS, CONCRETE OR LIKE BUILDING MATERIALS; ARTIFICIAL STONE; CERAMICS; REFRACTORIES; TREATMENT OF NATURAL STONE
    • C04B2111/00Mortars, concrete or artificial stone or mixtures to prepare them, characterised by specific function, property or use
    • C04B2111/70Grouts, e.g. injection mixtures for cables for prestressed concrete
    • YGENERAL 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
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W30/00Technologies for solid waste management
    • Y02W30/50Reuse, recycling or recovery technologies
    • Y02W30/91Use of waste materials as fillers for mortars or concrete

Abstract

A method for preparing a retardant slurry containing coal ash for controlling the fire disaster in a coal field comprises the steps of adding coal ash, aluminium phosphate, magnesium chloride, sodium carboxymethylcellulose, sodium silicate and sodium bentonite material in water to prepare a coal ash thickening slurry having high retardation and high-temperature resistance. The prepared thickening slurry is conveyed to burning coal seams or coal fractures through a grouting pipeline by a high-pressure screw pump. After a period of time, the retardant slurry can be thickened and solidified into a soft solid form. The retardant slurry can resist a high temperature of above 1000°C, form a hard block structure after water evaporates, and hermetically cover the coal body and block the fractures. The retardant slurry containing coal ash is low in costs, safe and environmentally friendly, and has significant control effects on the fire disaster caused by spontaneous combustion of coal in the coal field, and a good application prospect.

Description

一种用于治理煤田火灾的含粉煤灰阻化浆体制备方法  Method for preparing fly ash resistant slurry for treating coal field fire
技术领域 Technical field
本发明涉及煤田火灾治理方法, 特别是一种用于治理煤田煤自燃火灾的含粉煤灰阻 化浆体的制备方法。  The invention relates to a coal field fire treatment method, in particular to a preparation method of a fly ash resistant slurry for treating a coal field spontaneous combustion fire.
背景技术 Background technique
煤炭是我国的主要能源, 在一次能源生产和消费结构中占 70%左右。 从空间布局上 看, 我国煤炭资源主要分布在西北和华北地区, 其中新疆、 内蒙、 山西、 陕西、 宁夏、 甘肃等六省区探明煤炭储量约占全国的 80%左右,是事关我国能源安全和经济发展的战略 能源基地。 随着我国煤炭工业布局的进一步西移, 上述地区的战略地位日益凸显。 然而, 这些区域由于长年干旱少雨, 煤层厚且赋存浅, 加上小煤窑的滥采乱掘, 导致煤田火灾 频发、 火区遍布, 其中以新疆、 内蒙古、 宁夏最为严重。 新疆目前共有 44处煤田火灾, 火区面积达 992万 m2, 年燃煤损失量达 552万 t, 火区威胁储量 477亿 t, 年排放温室气 体 C02达到 1238万 内蒙古乌达、 桌子山、 鄂尔多斯、 准格尔、 古拉本等几大煤田还 存在 1903万 m2的煤田火区, 其中乌达煤田火区 2009年的总面积达 475. 4万 m2, 比 2004 年增加了 40%。 宁夏现有煤田火区 394. 56万 m2, 每年直接烧失煤炭量近 100万 t, 火区 下呆滞的煤炭储量达 7872. 58万 t。煤田火灾不仅直接烧毁不可再生的煤炭资源,还间接 造成数十倍的呆滞资源不能开采, 并直接威胁煤矿的安全生产, 还造成土壤沙化、 植被 死亡、 地面塌陷, 蒸汽、 青烟、 热浪不断向地表涌出, 结晶硫磺、 煤焦油、 高温火口遍 布, 大量 C0、 C02和 S02等有毒有害气体排入空气中, 严重危害当地的生态环境和地下水 资源, 局部地方已影响到居民生存。 煤火问题已成为危害我国能源战略安全和生态和谐 发展的重大问题, 引起了世界多个国家相关学者的关注。 Coal is China's main energy source, accounting for about 70% of primary energy production and consumption structure. From the perspective of spatial layout, China's coal resources are mainly distributed in the northwest and north China. Among them, Xinjiang, Inner Mongolia, Shanxi, Shaanxi, Ningxia, Gansu and other six provinces and regions have about 80% of the country's proven coal reserves, which is related to China's energy. Strategic energy base for safety and economic development. With the further westward shift of China's coal industry layout, the strategic position of the above-mentioned regions has become increasingly prominent. However, due to the long-term drought and low rainfall in these areas, the coal seams are thick and shallow, and the indiscriminate mining of small coal mines leads to frequent fires in the coal fields and fire areas, including Xinjiang, Inner Mongolia and Ningxia. Xinjiang has a total of 44 coal fire, fire area of 9.92 million m 2, in coal-fired loss amounted to 5.52 million t, the threat of the fire district reserves 47.7 billion t, annual emissions of greenhouse gases C0 2 reached 12.38 million Wuda, Zhuozishan There are also 19.03 million m 2 coalfield fire zones in several coal fields such as Erdos, Zhungeer and Gulaben. The total area of the Wuda coalfield fire zone in 2009 was 4,754,000 m 2 , an increase of 40 from 2004. %. Ningxia's existing coalfield fire zone is 394.56 million m 2 , and the amount of coal directly burned and lost is nearly 1 million tons per year. The coal reserves under the fire zone are 7872.58 million tons. Coal-fired fires not only directly burn non-renewable coal resources, but also indirectly cause dozens of times of stagnant resources to be exploited, and directly threaten the safe production of coal mines. They also cause soil desertification, vegetation death, ground collapse, steam, blue smoke, and heat waves. Surface germination, crystal sulphur, coal tar, high temperature crater, a large number of toxic and harmful gases such as C0, C0 2 and S0 2 are discharged into the air, seriously jeopardizing the local ecological environment and groundwater resources, local areas have affected the survival of residents. The problem of coal fire has become a major problem that jeopardizes China's energy strategy security and ecological harmonious development, and has attracted the attention of scholars from many countries around the world.
目前国内外煤田火区治理方法主要是剥离法、 注水与注浆法。 但剥离方法安全性较 差、 工程量较大。 由于火区燃烧形成了大量的悬空区和塌陷区, 剥离施工中所使用的推 土机和挖掘机易陷进空洞中, 会造成人员伤亡和重大经济损失; 此外, 若对地下煤火情 况判断不准, 会因剥开后造成供氧, 使煤火快速蔓延而导致火区范围扩大, 增加了灭火 的危险性与困难。 该方法对埋藏较深的煤火直接进行剥离, 工程量大、 成本高, 难以实 施; 采用爆破工程剥离火区时, 一般要求爆破温度不高于 40~60°C, 而火区爆破孔却经常 遇见 100°C以上甚至数百度的高温, 使火区爆破无法顺利进行。注水注浆配合黄土覆盖是 当前治理煤火的最主要手段。 由于水、 土这两种灭火材料较易获取, 且成本低廉, 因此 注水注浆是最经济的灭火方法; 但水浆会沿着煤岩裂隙或老窑通道往低处流, 不能对火 区均匀有效的覆盖, 需要大量钻孔和构建许多鱼鳞坑进行大量长期注水, 方可实现煤体 的逐渐降温; 由于水浆的流动通道少, 据统计 80%以上的水起不到吸热降温的作用而白白 流失; 在注水注浆过程中, 当水汇集到高温火源处时易导致水煤气爆炸, 造成人员伤亡; 同时, 在煤火下部有煤矿生产时, 注浆还易发生溃浆事故, 威胁井下煤矿安全生产。 因 此传统的注水注浆的方法还不能完全适应煤火治理的需要。 At present, the domestic coal area fire area treatment methods are mainly stripping method, water injection and grouting method. However, the peeling method is less safe and has a large amount of work. Due to the formation of a large number of suspended and collapsed areas in the fire zone, the bulldozers and excavators used in the stripping construction are likely to be trapped in the voids, causing casualties and major economic losses. In addition, if the underground coal fire situation is judged It will cause oxygen supply after stripping, which will cause the coal fire to spread rapidly and lead to the expansion of the fire area, increasing the danger and difficulty of fire extinguishing. The method directly peels off the buried coal fire, and has large engineering cost and high cost, and is difficult to implement; when the fire zone is used for blasting, the blasting temperature is generally not higher than 40-60 ° C, but the blasting hole in the fire zone is Frequently encountered high temperatures of 100 ° C or even hundreds of degrees, so that the fire area can not be blasted smoothly. Water injection grouting combined with loess cover is the most important means of controlling coal fire. Since water and soil are easy to obtain and low in cost, water injection grouting is the most economical fire extinguishing method; but the water slurry will flow along the coal rock crack or the old kiln passage to the lower part, not to the fire. Uniform and effective coverage of the area requires a large number of drilling holes and construction of many fish scale pits for a large number of long-term water injections, in order to achieve a gradual cooling of the coal body; due to the small flow path of the water slurry, according to statistics, more than 80% of the water does not absorb heat and cool down. In the process of water injection and grouting, when the water is collected at the high temperature fire source, it will easily lead to water gas explosion, causing casualties; meanwhile, when there is coal mine production in the lower part of the coal fire, grouting is also prone to slurry collapse. , threatening the safe production of underground coal mines. Therefore, the traditional method of water injection grouting can not fully meet the needs of coal fire treatment.
发明内容 Summary of the invention
技术问题: 本发明的目的是针对已有技术中存在的问题, 提供一种方法简单、 阻化 性能好、 耐高温、 不脱水、 价格低廉的治理煤田火灾的含粉煤灰阻化浆体制备方法。  Technical Problem: The object of the present invention is to provide a method for preparing a fly ash-containing resisting slurry for treating coal field fires with simple method, good resistance, high temperature resistance, high dehydration, and low cost in view of the problems in the prior art. method.
技术方案: 本发明的用于治理煤田火灾的含粉煤灰阻化浆体制备方法, 包括选用粉 煤灰、 磷酸铝、 氯化镁、 羧甲基纤维素钠、 水玻璃、 钠基膨润土和水, 具体制备如下: a.在水中按质量百分比加入 25%〜30%的粉煤灰、 2%〜4%的磷酸铝、 2%〜5%的氯化镁、 0. 8%~1. 5%的羧甲基纤维素钠, 充分搅拌制成混合溶液 A;  Technical Solution: The method for preparing a fly ash resistant slurry for treating a coal field fire of the present invention comprises using fly ash, aluminum phosphate, magnesium chloride, sodium carboxymethyl cellulose, water glass, sodium bentonite and water, The 8% of the carboxylic acid is added in an amount of 25% to 30% of the aluminum ash, 2% to 4% of the aluminum phosphate, 2% to 5% of the magnesium chloride, and the 8% to 1.5% of the carboxylic acid. Methyl cellulose sodium, fully stirred to make a mixed solution A;
b.在水中按质量百分比加入 3%~5%的水玻璃和 1%~2%的钠基膨润土, 充分搅拌制成 混合溶液 B;  b. Add 3%~5% water glass and 1%~2% sodium bentonite in water by mass percentage, and mix well to make mixed solution B;
c 将溶液 B加入溶液 A, 溶液 B和溶液 A按质量比 1: 2混合, 在加入的过程中充分 搅拌混合均匀。  c Add solution B to solution A, solution B and solution A are mixed at a mass ratio of 1: 2, and mix well during the addition.
有益效果: 本发明用于治理煤田火灾的含粉煤灰阻化浆体制备方法, 通过在水中加 入粉煤灰、 磷酸铝、 氯化镁、 羧甲基纤维素钠、 水玻璃、 钠基膨润土等材料充分搅拌混 合, 制备成具有高阻化及耐高温的粉煤灰稠化浆液。 将制备好的稠化浆体利用高压螺杆 泵, 通过注浆管路输送到燃烧的煤层上或煤体裂隙中。 该材料具有很强的吸热降温能力, 且耐 iooo°c以上的高温, 因此能高效扑灭与降低煤田燃烧火区的温度; 且阻化性好, 能 有效地惰化煤体表面活性结构,与现有技术相比,该阻化材料的阻化性提高 3〜5倍以上; 同时, 当含粉煤灰阻化浆体覆盖在煤层或堆积在煤体裂隙一段时间后, 成为稠化软固体, 能严密的覆盖煤体和封堵煤体裂隙, 隔绝煤氧结合, 能有效地防止火区供氧。 本发明阻 化浆体成本较低, 且安全环保, 治理煤田火灾效果显著, 具有很好的应用前景。  Advantageous Effects: The method for preparing a fly ash resistant slurry for treating a coal field fire is prepared by adding fly ash, aluminum phosphate, magnesium chloride, sodium carboxymethyl cellulose, water glass, sodium bentonite and the like to water. The mixture is thoroughly stirred and mixed to prepare a thickened slurry of fly ash having high resistance and high temperature resistance. The prepared thickened slurry is transferred to the burning coal seam or coal seam by a high pressure screw pump through a grouting line. The material has strong heat absorption and cooling ability, and is resistant to high temperatures above iooo °c, so it can effectively extinguish and reduce the temperature of the burning fire area of the coal field; and has good resistance and can effectively inertize the surface active structure of the coal. Compared with the prior art, the resistance of the resistive material is improved by 3 to 5 times; at the same time, when the fly ash-containing resisting slurry covers the coal seam or accumulates in the coal body crack for a period of time, it becomes thickened soft. The solid can tightly cover the coal body and block the coal body cracks, and isolate the coal and oxygen, which can effectively prevent oxygen supply in the fire area. The resistive slurry of the invention has low cost, safety and environmental protection, and has obvious effect in controlling coal field fire, and has good application prospect.
具体实施方式 detailed description
本发明用于治理煤田火灾的含粉煤灰阻化浆体制备方法, 采用粉煤灰、 磷酸铝、 氯 化镁、 羧甲基纤维素钠、 水玻璃、 钠基膨润土和水材料, 其制备过程如下:  The preparation method of the fly ash-resistant slurry for treating coal field fires adopts fly ash, aluminum phosphate, magnesium chloride, sodium carboxymethyl cellulose, water glass, sodium bentonite and water materials, and the preparation process thereof is as follows :
a.在水中加入质量百分比为 25%〜30%的粉煤灰、质量百分比为 2%〜4%的磷酸铝、质 量百分比为 2%〜5%的氯化镁、 质量百分比为 0. 8%~1. 5%的羧甲基纤维素钠, 充分搅拌制 成混合溶液 A; 8%~1。 8%~1。 8%~1 8%~1%%%%%%%% 5% sodium carboxymethylcellulose, fully stirred Mixing solution A;
b.在水中加入质量百分比为 3%~5%的水玻璃和质量百分比为 1%~2%的钠基膨润土, 充分搅拌形成混合溶液 B;  b. Add water 3%~5% water glass and 1%~2% sodium bentonite in water, stir well to form mixed solution B;
c 将溶液 B加入溶液 A, 溶液 B和溶液 A按质量比 1: 2混合, 在加入的过程中充分 搅拌混合均匀, 约 5分钟左右形成含粉煤灰的阻化浆体。  c Add solution B to solution A. Solution B and solution A are mixed at a mass ratio of 1:2. Stir well and mix well during the addition. A resist slurry containing fly ash is formed in about 5 minutes.
如果需要稠化的速度快一些, 则 B溶液的两种材料质量比按较大值取; 如果需要稠 化速度慢一些, 则 B溶液的两种材料质量比按较小值取。  If the speed of thickening is required to be faster, the mass ratio of the two materials of the B solution is taken as a larger value; if the thickening speed is required to be slower, the mass ratio of the two materials of the B solution is taken to a smaller value.
实施例一、 先在 1000 kg水中加入 250 kg粉煤灰、 20kg磷酸铝、 20kg氯化镁和 8kg 羧甲基纤维素钠, 充分搅拌混合均匀, 制备成浓度为 23%的混合溶液; 其次, 在 500kg 水中加入 15kg水玻璃和 5kg钠基膨润土,充分搅拌均匀制备成浓度为 3. 8%的混合溶液; 将两种溶液混合, 充分搅拌均匀, 约 5分钟左右, 配制形成含粉煤灰的新型阻化浆体。  Example 1 First, add 250 kg of fly ash, 20 kg of aluminum phosphate, 20 kg of magnesium chloride and 8 kg of sodium carboxymethylcellulose in 1000 kg of water, stir well and mix well to prepare a mixed solution with a concentration of 23%; secondly, at 500 kg Adding 15kg of water glass and 5kg of sodium bentonite to the water, mixing well to prepare a mixed solution with a concentration of 3.8%; mixing the two solutions, stirring well, about 5 minutes, forming a new type of resistance containing fly ash Slurry.
实施例二、先在 1000 kg水中加入 300 kg粉煤灰、 40kg磷酸铝、 50kg氯化镁和 15kg 羧甲基纤维素钠, 充分搅拌混合均匀, 制备成浓度为 28. 8%的混合溶液; 其次, 在 500kg 水中加入 25kg水玻璃和 10kg钠基膨润土,充分搅拌均匀制备成浓度为 6. 5%的混合溶液; 将两种溶液混合, 充分搅拌均匀, 约 5分钟左右, 配制形成含粉煤灰的新型阻化浆体。  8%的混合溶液; Secondly, first, in a 1000 kg of water, 300 kg of fly ash, 40 kg of aluminum phosphate, 50 kg of magnesium chloride, and 15 kg of sodium carboxymethyl cellulose, and stirred well, to prepare a mixed solution having a concentration of 28.8%; Adding 25kg of water glass and 10kg of sodium bentonite to 500kg of water, mixing well to prepare a mixed solution with a concentration of 6.5%; mixing the two solutions, stirring well, about 5 minutes, forming a fly ash-containing mixture A new type of resistive slurry.
实施例三、先在 1000 kg水中加入 270 kg粉煤灰、 30kg磷酸铝、 30kg氯化镁和 10kg 羧甲基纤维素钠, 充分搅拌混合均匀, 制备成浓度为 25. 4%的混合溶液; 其次, 在 500kg 水中加入 20kg水玻璃和 10kg钠基膨润土,充分搅拌均匀制备成浓度为 5. 7%的混合溶液; 将两种溶液混合, 充分搅拌均匀, 约 5分钟左右, 配制形成含粉煤灰的新型阻化浆体。  The second embodiment, a mixture of 270 kg of fly ash, 30 kg of aluminum phosphate, 30 kg of aluminum phosphate, 30 kg of magnesium chloride, and 10 kg of sodium carboxymethyl cellulose, and stirred well, to prepare a mixed solution having a concentration of 25.4%; Adding 20 kg of water glass and 10 kg of sodium bentonite to 500 kg of water, and mixing well to prepare a mixed solution having a concentration of 5.7%; mixing the two solutions, and uniformly stirring them for about 5 minutes to form a fly ash-containing mixture. A new type of resistive slurry.
将上述制备好的含粉煤灰阻化浆体分别通过螺杆泵和管道输送至燃烧的煤堆上, 煤 堆温度高达 500°C以上, 阻化浆体很快就均匀地覆盖在煤堆上, 煤堆火很快被扑灭, 煤堆 的温度迅速降低, 短时间内即可将煤堆的温度就降到常温。 对自燃高温煤体来说, 灭火 降温效果显著。  The above-mentioned prepared fly ash-containing resisting slurry is respectively transported to the burning coal pile through a screw pump and a pipeline, and the temperature of the coal pile is up to 500 ° C or more, and the resisting slurry is quickly uniformly covered on the coal pile. The coal pile fire was quickly extinguished, the temperature of the coal pile was rapidly reduced, and the temperature of the coal pile was reduced to normal temperature in a short time. For spontaneous combustion of high temperature coal, the effect of extinguishing fire is significant.

Claims

权利要求书 Claim
1. 一种用于治理煤田火灾的含粉煤灰阻化浆体制备方法, 其特征在于: 选用粉煤 灰、 磷酸铝、 氯化镁、 羧甲基纤维素钠、 水玻璃、 钠基膨润土和水材料, 制备方法包括 如下步骤: A method for preparing a fly ash resistant slurry for treating a coal field fire, characterized by: using fly ash, aluminum phosphate, magnesium chloride, sodium carboxymethyl cellulose, water glass, sodium bentonite and water The material, the preparation method comprises the following steps:
a.在水中按质量百分比加入 25%〜30%的粉煤灰、 2%〜4%的磷酸铝、 2%〜5%的氯化 镁、 0. 8%~1. 5%的羧甲基纤维素钠, 充分搅拌制成混合溶液 A;  a 8% by weight of carboxymethyl cellulose, 2% ~ 4% of aluminum phosphate, 2% ~ 5% of magnesium chloride, 0. 8% ~ 1.5% of carboxymethyl cellulose Sodium, fully stirred to make a mixed solution A;
b.在水中按质量百分比加入 3%~5%的水玻璃和 1%~2%的钠基膨润土, 充分搅拌制成混 合溶液 B;  b. Add 3%~5% water glass and 1%~2% sodium bentonite in water by mass percentage, and mix well to make mixed solution B;
c 将溶液 B加入溶液 A, 溶液 B和溶液 A按质量比 1 : 2混合, 在加入的过程中充分 搅拌混合均匀。  c Add solution B to solution A. Solution B and solution A are mixed at a mass ratio of 1: 2, and thoroughly mixed and mixed during the addition.
PCT/CN2014/074072 2013-07-17 2014-03-26 Method for preparing retardant slurry containing coal ash for controlling fire disaster in coal field WO2015007103A1 (en)

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