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不同矿化度水对煤的甲烷解吸影响的试验研究

Experimental study on influence of water with different salinity on methane desorption performance of coal seam

  • 摘要: 为了研究水分及其矿化度对煤样甲烷解吸的影响,以平顶山矿区己16-17煤样为例,开展了干燥和不同矿化度(0、2、5、15 g/L)饱和水条件下煤样的等温解吸试验,探讨了不同矿化度水对煤解吸性能的影响。结果表明:不同矿化度水的存在,大幅减小了煤的甲烷解吸初速度、解吸总时间和甲烷解吸总量;不同程度地增加了各时间段甲烷解吸量占解吸总量的比例,但该比例的增幅随平衡压力的增大而呈现不同程度的下降;但对煤的甲烷解吸拟合规律影响不大。对于不同矿化度饱和水煤样,不同平衡压力下,各煤样前期解吸速度衰减都较快;相同平衡压力下,随矿化度的增大,各煤样甲烷解吸的初期速度、解吸总时间和解吸总量均呈现先增大后减小的规律,解吸总量最大时矿化度约为2.5 g/L;此后,解吸总量逐步减小,减小幅度逐步降低,当矿化度为15 g/L时,煤样的甲烷解吸总量甚至低于0 g/L饱和水煤样;甲烷解吸总量不会一直下降,当矿化度大于20 g/L时,其对甲烷解吸总量的变化无明显作用。研究认为水分子除了竞争占据甲烷分子的吸附点位外,还多层吸附于煤表面占据甲烷吸附通道,进一步减少了煤对甲烷的吸附量;当水分增至饱和时,多余水分会以游离态赋存于煤粒间大孔隙中,在一定温压条件下,甲烷可以溶解到这部分水中,增加了煤对甲烷的“吸附”量,因此,饱和水煤体等温吸附甲烷的量主要包括甲烷在煤孔、裂隙水中的极限溶解量和在剩余孔隙中的极限吸附量2个部分,矿化度水中无机盐离子则影响前者,且通过水合作用和间隙填充这2种竞争机制来影响甲烷的溶解和扩散;总体而言,不同矿化度饱和水煤体解吸时,水中无机盐离子的水合作用利于增强甲烷分子在煤孔、裂隙游离水中的扩散运移能力,而间隙填充则相反。在低温条件(小于85 ℃)下,水合作用占据主导,因此,矿化度较低时,促进甲烷在煤孔、裂隙游离水中的扩散运移;矿化度较高时,则会减小孔、裂隙游离水的有效间隙度而降低气体扩散运移能力,但存在一个极限值,超过该值后矿化度对煤的甲烷解吸总量的影响不大。

     

    Abstract: In order to study the influence of moisture and salinity on methane desorption of coal samples, taking the coal samples from the hex16-17 coal seam in Pingdingshan mining area as an example,an isothermal desorption experiment was carried out on coal samples with different salinity (0,2,5,15 g/L) under the condition of dry and saturated water, and the influence of water with different salinity on coalLMdesorption performance was discussed. The results show that the existence of water with different salinities greatly reduces the initial rate of coal methane desorption, the total desorption time, and the total amount of methane desorption; it increases the proportion of methane desorption in each time period to the total desorption to varying degrees, but the increase of this ratio decreases with the increase of equilibrium pressure; however, it has little effect on the fitting law of coal desorption of methane. For saturated coal watersamples with different salinities, the desorption rate of each coal sample in the early stage decays rapidly under different balance pressure. Under same equilibrium pressure, with the increase of salinity, the initial methane desorption velocities in early stage and total desorption times and desorption amounts of the different coal sample increase first and then decrease. When the total desorption is at its maximum, the salinity is about 2.5 g/L; After that, the total desorption is gradually reduced, and the degree of decrease amplitude is gradually reduced. When the salinity is at 15 g/L, coal sample methane desorption amount is even lower than that of the coal sample saturated pure water, however, the total amount of methane desorption in saturated coal samples with different salinity will not always decrease; when the salinity is greater than 20 g/L, the total amount of methane desorption will be less than 0 g/L. The change in the amount has no obvious effect. The reason is that it is different from previous cognition that in addition to competing to occupy the adsorption sites of methane, water molecules also adsorb on the surface of coal in multiple layers to occupy methane adsorption channels, which further reduces the amount of methane adsorption by coal. When it reaches saturation, excess water will be stored in the large pores between coal particles in a free state; under certain temperature and pressure conditions, methane can be dissolved in this part of the water, increasing the amount of coal′s "adsorption" of methane.Therefore, the amount of methane adsorbed by coal isotherm mainly includes two parts: the limit dissolved amount of methane in coal pores and fissure water and the limit adsorption amount in remaining pores. Inorganic salt ions in the salinity water affect the former, and through hydration and gap filling these two competition mechanismaffect the dissolution and diffusion of methane. In general, when desorption of saturated coal with different salinity was carried out, the hydration of inorganic salt ions in the water was conducive to enhancing the diffusion ability of methane molecules in the free water of coal holes and cracks, while gap filling was the opposite. Under low temperature (less than 85 ℃), hydration dominates,therefore, when the salinity is low, it promotes the diffusion and transport of methane in the free water of coal holes and cracks. When the salinity is high, the effective clearance degree of free water in pores and crevasses will be reduced and the gas diffusion ability will be reduced. However, there is a limit that the excess of the salinity has little influence on the total desorption amount of coal samples.

     

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