荒漠土壤产脲酶菌诱导碳酸钙沉淀固沙优化与效果分析

    Optimization the sand-fixation via calcium carbonate precipitation induced by urea-producing bacteria and its effects in desert soils

    • 摘要: 产脲酶菌诱导碳酸钙已广泛应用于土壤固化,但存在环境适应性差的缺陷。该研究使用荒漠土壤产脲酶菌,结合室内试验和响应面法优化反应条件,通过野外试验分析固沙效果,以期解决荒漠地区产脲酶菌诱导碳酸钙固沙的技术问题。结果表明:1)影响碳酸钙沉积的主要因子是温度、时间、pH值、菌液和胶结液配比,优化条件为34.47 ℃、71.68 h、pH值7.73、配比74.94%,此时钙沉积率最高,为42.33%。2)最优条件下诱导形成的碳酸钙呈立方体形、菱形、球形和无定形等多晶态,分布在沙粒表面或镶嵌在沙粒中。3)优化后固沙效果明显增强,风沙土颗粒显著增大(P<0.05),固结层硬度和厚度分别提升5倍和10倍,所有时间段内风蚀可蚀性因子均降低,24 h降幅最大,由0.91降至0.66。该技术是防沙治沙的新方法,野外应用需确定施用时间,采用洒水、覆盖、适当破碎等措施,营造适宜条件提升固沙效果的同时避免土壤板结问题。

       

      Abstract: Microbially induced calcium carbonate precipitation (MICP) is one widespread approach to soil clay improvement in sustainable biological engineering in the world. The green and efficient approach can also greatly contribute to a series of environmental and ecological challenges. Among them, urea-producing bacteria can be used to induce calcium carbonate precipitation for better soil consolidation. Bacterially generated urease enzymes can decompose the urea to further promote the binding of Ca2+ and CO32-. Therefore, the calcium carbonate precipitation can be expected to apply to desertification combating. However, the urea-producing bacteria can be limited to environmental adaptability and weak function in a harsh desert environment. Many technical bottlenecks are urgent issues for the sand-fixation using calcium carbonate precipitation induced by urea-producing bacteria. It is a high demand to develop native urea-producing bacteria. In the preliminary research, the strain of Sporosarcina pasteurii was identified from the aeolian soils in the Mu Us desert. In this research, the optimal reaction conditions were determined to verify the sand-fixation effect in the desert soil after optimization. A series of single-factor experiments were designed during 0-72 h with the different experimental gradients by pH (7, 8, 9, and 10), bacterial inoculum (1%, 2%, 3%, 4%, and 5%), the ratio of bacterial and cementing solution (25%, 50%, and 75%), and temperature (30, 35, and 40 ℃). The initial urease activity and calcium deposition rate were tested using the response surface method. The optimal reaction factors and conditions were then determined from the six factors (reaction time, pH, bacterial inoculum, the ratio of bacterial and cementing solution, reaction temperature, and initial urease activity). The sand-fixation experiments were carried out on the aeolian soil from the Mu Us desert under optimized conditions. Mineral morphologies and properties were then characterized by the scanning electron microscope (SEM). The thickness and hardness of the soil consolidated layer, soil particle distribution, soil organic matter and calcium carbonate content were measured to calculate the erodibility factor (EF) under soil wind erosion. The results showed that: 1) The main reaction drivers of calcium carbonate precipitation were determined as the reaction temperature, reaction time, pH value, as well as the ratio of bacterial and cementing solution. An optimal combination of conditions was achieved at 34.47 ℃, 71.68 h, pH 7.73, and 74.94% ratio. In this condition, the maximum rate of calcium deposition was 42.33%. 2) The calcium carbonate precipitation was obtained in the polycrystalline phase composition with the cubic, rhombic, spherical, and amorphous under the optimized conditions. Diverse calcium carbonate precipitation was formed on the surface of sand grains, or embedded in the sand grains. 3) Sand-fixation by induced calcium carbonate precipitation was significantly enhanced after optimization. The number of sand particles increased significantly (P<0.05), and the thickness and hardness of the soil consolidated layer increased by 5 and 10 times, respectively. The contents of organic matter and calcium carbonate increased significantly, whereas, the wind erodibility factor decreased in all times, which has the maximum reduction from 0.91 to 0.66 in 24 h. Therefore, the urea-producing bacteria-induced calcium carbonate precipitation can serve as the new effective and favorable sand fixation for desertification combating in the future. It is still necessary to develop the distribution of simultaneous ecological restoration, in order to gradually promote this new technology in large-scale field experiments. Consequently, in the field application, the sand fixation effect can be enhanced to further determine the application time and water under suitable conditions and the soil compaction will be avoided by appropriately breaking.

       

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