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Influence of drill mud on the microbial communities of sandstone rocks and well fluids at the Ketzin pilot site for CO_{2} storage

机译:钻探泥浆对Ketzin试点CO_ {2}封存的砂岩岩石和井液微生物群落的影响

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摘要

At a pilot site for CO_{2} storage in Ketzin (Germany), a drastic decrease in injectivity occurred in a well intended for injection. This was attributed to an obstruction of the pore throats due to microbial degradation of the organic drill mud and subsequent iron sulfide (FeS) precipitation in the highly saline brine (240 g L^{-1}). To better understand the biogeochemical processes, the response of the autochthonous microbial community to drill mud exposure was investigated. Pristine cores of two aquifers with different salinity were incubated under simulated in situ conditions (50 bar, 40 °C and 45 bar, 25 °C, respectively) and CO_{2} atmosphere. For the first time, rock cores obtained from the CO_{2} plume of the storage formation were investigated. The influence of acetate as a biodegradation product of drill mud polymers and the effectiveness of a biocide were additionally tested. Increased microbial diversities were observed in all long-term (8-20 weeks) incubations, even including biocide. Biofilm-like structures and small round-shaped minerals of probable microbiological origin were found. The results indicate that the microbial community remains viable after long-term CO_{2} exposure. Microorganisms hydrolyzing cellulose polymers (e.g., Burkholderia spp., Variovorax spp.) biodegraded organic components of the drill mud and most likely produced low molecular weight acids. Although the effects of drill mud were less strong as observed in situ, it was demonstrated that acetate supports the growth of sulfate-reducing bacteria (i.e., Desulfotomaculum spp.). The microbial-induced precipitation of amorphous FeS reduced the injectivity in the near-well area. Therefore, when using organic drill mud, the well must be cleaned intensively to minimize the hazards of bacterial stimulation.
机译:在Ketzin(德国)的CO_ {2}储存试点中,打算注入的井中注入率急剧下降。这归因于有机钻探泥浆的微生物降解以及随后在高盐度盐水(240 g L ^ {-1})中的硫化铁(FeS)沉淀造成的孔喉阻塞。为了更好地了解生物地球化学过程,研究了土生微生物群落对泥浆暴露的响应。在模拟的原位条件下(分别为50 bar,40°C和45 bar,25°C)和CO_ {2}气氛下孵育两个盐度不同的含水层的原始岩心。首次研究了从储层的CO_ {2}羽流获得的岩心。还测试了乙酸盐作为钻探泥浆聚合物的生物降解产物的影响和杀生物剂的有效性。在所有长期(8-20周)温育中,甚至包括杀菌剂,都观察到微生物多样性增加。发现了类似生物膜的结构和可能是微生物来源的小圆形矿物。结果表明,长期暴露于CO_ {2}后,微生物群落仍保持活力。水解纤维素聚合物(例如Burkholderia spp。,Variovorax spp。)的微生物会生物降解钻探泥浆中的有机成分,最有可能产生低分子量的酸。尽管如在现场观察到的那样,钻探泥浆的作用不那么强烈,但已证明乙酸盐支持减少硫酸盐的细菌(即Desulfotomaculum spp。)的生长。微生物诱导的非晶态FeS沉淀降低了近井区域的注入性。因此,在使用有机钻探泥浆时,必须对井进行彻底清洁,以最大程度地减少细菌刺激的危害。

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