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曲靖盆地生物气成藏条件及主控因素分析 总被引：1，自引：0，他引：1
曲靖盆地新近系茨营组第三段的晚期生物气藏是新近系沉积之后,喜山运动时期各种成藏条件有效的时空配置的结果.在讨论曲靖盆地构造和沉积演化的基础上,综合分析了生物气源、储集层和盖层、圈闭形成以及天然气输导等成藏条件,阐述了生物气晚期聚集成藏条件的时空匹配关系.指出自第四纪以来,生物气源岩持续高效的产气作用是生物气成藏的物质保障,气藏的形成是生物气连续的补充大于逸散动态平衡的产物;背斜构造、砂岩上倾尖灭和砂岩透镜体圈闭是该区主要的圈闭类型;断裂和不整合面是沟通生物气源岩到圈闭的垂向和侧向输导通道,茨营组的连通砂岩体是生物气近距离运移的输导层.蔡家冲组大套湖相暗色泥岩的生物产气效率、断裂的垂向输导能力和圈闭的保存条件及其在时空上的动态配置是生物气晚期成藏的主控因素. 相似文献
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生物气CO_2还原途径中碳同位素分馏作用研究及应用 总被引：2，自引：0，他引：2
地质历史中,CO2/H2还原产甲烷作用对生物气的形成具有十分重要的意义。中国柴达木盆地第四系生物气主要为CO2/H2还原型生物气。笔者以CO2/H2还原生气理论为指导,进行不同初始碳同位素值和不同赋存状态碳源的生物模拟实验,研究CO2/H2还原产气过程中发生的碳同位素分馏作用。实验结果表明,产物中δ13CH4值与底物的δ13C值呈很好的正相关关系;在反应母质过量的情况下,碳源的赋存状态可以影响产物甲烷的碳同位素组成。以游离形式CO2还原产生的甲烷δ13C值,相对于以HCO3-、CO23-离子形式产生的甲烷δ13C值轻。通过柴达木盆地东部第四系生物气田实例分析,探讨了该区生物气的主要底物CO2的来源及赋存状态,对评价盆地生物气资源和有利勘探区预测有重要的参考价值。 相似文献
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松辽盆地白垩纪湖泊水体温度与古气候温度估算 总被引：2，自引：0，他引：2
湖泊沉积物沉积的第一场所是湖底,湖底温度的高低影响沉积有机质的保存,也影响湖底下部地层的温度。了解古水体温度尤其是古水底温度情况成为评估松辽盆地白垩系生物气勘探前景的必要研究内容之一。根据已有的古气候研究成果与现今气候对比,得出白垩纪松辽盆地年平均气温约为14~24℃。再根据水库温度的计算方法和利用已有的古纬度及古水深的研究成果计算得出,白垩纪松辽盆地古湖盆水体表面温度为17~25℃;水深大于20 m的深湖区,水底温度为6.2~12.5℃;湖底最深处温度为4.0~11.3℃;青山口组和嫩江组沉积时期,湖水分层明显,湖底温度季节性变化很小且温度较低,约为8℃。湖底的低温对松辽盆地白垩纪生物气勘探是有利的。 相似文献
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评价生物气生成量、生成期的元素平衡法及其应用 总被引：2，自引：0，他引：2
生物气的生成期对其成藏有至关重要的制约作用,但目前国内外尚缺少可信、有效方法来对此进行评价。针对这一难题,考虑到无论生物气的生成机理如何,都是一个有机元素之间的物质平衡过程,文章探索并建立了评价生物气生成量的元素平衡法,并利用松辽盆地大量的实际分析数据,对这一评价方法(模型)进行了标定和应用。结果表明,松辽盆地生物气的生成可能主要发生在800m以浅的埋深条件下;区内源岩生物气的生成量约为285.0×1012m3;生物气的主要生成期在嫩江组沉积末期之前。 相似文献
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莺歌海盆地海相生物气特征及生化成气模式 总被引：11，自引：2，他引：9
莺歌海盆地浅层第四系-上新统存在丰富的生物气资源,已发现生物气的组成以甲烷和氮为主、干燥系数高达0.99,甲烷碳同位素轻(-65.57‰～-63.14‰)尤其是氢同位素偏重(-172.1‰～-108.5‰)是该区生物气的重要特点.研究表明,该区第四系-上新统海相沉积有机质是生物气的基质,这套源岩的平均有机碳含量约0.4%,有机质中细菌可利用基质以粗纤维、半纤维素和蛋白质为主,特别是有机质生化代谢过程中的中间产物-氨基酸、乙酸含量异常高,揭示其正处在活跃的生化成气时期;根据模拟实验结果结合本区的地质条件,初步确定生物气生成的主带在35～65℃之间、生化成气下限深度约为85℃(对应井深约2000 m,实际埋深1900 m左右),进而建立了海相生物气的形成演化模式。 相似文献
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Shaunna Barnhart 《The Professional geographer》2013,65(3):345-353
Nepal has more than 250,000 household biogas digesters that replace firewood with methane for most cooking needs, thus conserving forest resources while reducing indoor air pollution, reducing workloads for energy procurement, and providing a fertilizer slurry by-product. Biogas is also an approved clean development mechanism that reduces carbon emissions, creating a potential revenue stream for the government from global carbon trading markets through aggregating household biogas plants into larger projects for carbon trading. This article traces the shift to biogas as a neoliberal development strategy in Nepal by exploring the connection between biogas as a household energy decision and global carbon trading. 相似文献
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Paulina Rusanowska Monika Harnisz Marcin Zieli&#x;ski Marcin D&#x;bowski Ewa Korzeniewska Marta Kisielewska Ewa Amenda 《洁净——土壤、空气、水》2020,48(2)
Methane fermentation is widely used to dispose of sewage sludge at wastewater treatment plants (WWTPs), due to production of renewable energy in the form of biogas. Antibiotics present in wastewater may accumulate in a sewage sludge. The aim of the present study is to investigate the impact of three antibiotics from different classes in three different doses on methane production from sewage sludge. For this purpose, metronidazole (MET), amoxicillin (AMO), and ciprofloxacin (CIP) are individually added to anaerobic reactors with sewage sludge collected from municipal WWTP. The antibiotics’ highest concentration (1024 mg kg?1 of AMO; 512 mg kg?1 of MET and CIP) lowers methane production and methane content in biogas. MET exerts the most marked effect and lowers methane production to 36.8 ± 3.7 mL CH4 kg?1 volatile solids. Tested antibiotics probably inhibit methanogenic archaea, which results in volatile fatty acids (VFAs) accumulation. Addition of MET results in accumulation of many kinds of VFAs with the highest concentration of acetic acid (17.52 ± 1.85 g L?1). The addition of of AMO results in accumulation of butyric acid only (253.00 ± 15.89 g L?1). However, addition of CIP results in accumulation of mainly acetic acid (7.58 ± 0.82 g L?1) and isovaleric acid (2.01 ± 0.41 g L?1). Next, synergistic effect of these antibiotics in a low concentration of 16 mg kg?1 of AMO, 8 mg kg?1 of MET, and 2 mg kg?1 of CIP is measured in semi‐continuous conditions and causes inbibition of methane production and accumulation of VFAs. 相似文献
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《中国科学D辑(英文版)》2008,(Z1)
The Sebei gasfield is the largest biogas accumulation found in China and many reservoirs and seal rocks superposed on a syndepositional anticline in Quaternary.The biogas charging and dissipating process and its distribution have been a research focus for many years.The authors suggest a diffusing and accumulating model for the biogas,as they find that the shallower the gas producer,the more methane in the biogas,and the lighter stable carbon isotope composition of methane.Based on the diffusing model,diffused biogas is quantitatively estimated for each potential sandy reservoir in the gasfield,and the gas charging quantity for the sandy reservoir is also calculated by the diffused gas quantity plus gas reserve in-place.A ratio of diffusing quantity to charging quantity is postulated to describe biogas accumulating state in a sandy reservoir,if the ratio is less than 0.6,the reservoir forms a good gas-pool and high-production layer in the gasfield,which often occurs in the reservoirs deeper than 900 m;if the ratio is greater than 0.6,a few gas accumulated in the reservoir,which frequently exists in the reservoirs shallower than 900 m.Therefore,a biogas accumulation model is built up as lateral direct charging from gas source for the sands deeper than 900 m and indirect charging from lower gas-bearing sands by diffusion at depth shallower than 900 m.With this charging and diffusion quantitative model,the authors conducted re-evaluation on each wildcat in the central area of the Qaidam Basin,and found many commercial biogas layers. 相似文献
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评价生物气生成量、生成期的碳同位素平衡法及其应用 总被引：1，自引：1，他引：0
生物气的生成期对其成藏有至关重要的制约作用,但目前国内外尚缺少可信、有效方法来对此进行评价。针对这一难题,考虑到无论生物气的生成机理如何,转化前的有机质和转化后的残余有机质及产物的13C、12C的总量应该守恒,本文探索并建立了评价生物气生成量的碳同位素平衡法,并利用松辽盆地的实际分析数据,对这一评价方法（模型）进行了标定和应用。结果表明:Ⅰ、Ⅱ、Ⅲ型有机质累计产生物成因甲烷气的量分别约为193.94 ml/g、175.64 ml/g、161.71 ml/g。区内源岩生物气的生成量约为385.4×1012 m3;生物气的主要生成期在嫩江组沉积末期之前;区内生物气的可能资源量介于11.40×1011～24.8×1011 m3之间。 相似文献