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    深时成煤演化与成煤环境分析

    李勇 李锵 刘乐 丁蓉 李玉洁 许卫凯

    李勇, 李锵, 刘乐, 丁蓉, 李玉洁, 许卫凯, 2026. 深时成煤演化与成煤环境分析. 地球科学, 51(7): 2482-2498. doi: 10.3799/dqkx.2026.206
    引用本文: 李勇, 李锵, 刘乐, 丁蓉, 李玉洁, 许卫凯, 2026. 深时成煤演化与成煤环境分析. 地球科学, 51(7): 2482-2498. doi: 10.3799/dqkx.2026.206
    Li Yong, Li Qiang, Liu Le, Ding Rong, Li Yujie, Xu Weikai, 2026. Deep-Time Coal-Forming Evolution and Perspectives on Coal-Forming Environment Analysis. Earth Science, 51(7): 2482-2498. doi: 10.3799/dqkx.2026.206
    Citation: Li Yong, Li Qiang, Liu Le, Ding Rong, Li Yujie, Xu Weikai, 2026. Deep-Time Coal-Forming Evolution and Perspectives on Coal-Forming Environment Analysis. Earth Science, 51(7): 2482-2498. doi: 10.3799/dqkx.2026.206

    深时成煤演化与成煤环境分析

    doi: 10.3799/dqkx.2026.206
    基金项目: 

    国家科技重大专项项目 2025ZD1405700

    中石油煤层气有限责任公司科技项目 2026-KJ-0101

    详细信息
      作者简介:

      李勇(1988-),男,教授,博导,主要从煤层气开发地质教学和科研工作. ORCID:0000-0001-8859-156X. E-mail:liyong@cumtb.edu.cn

    • 中图分类号: P618.13

    Deep-Time Coal-Forming Evolution and Perspectives on Coal-Forming Environment Analysis

    • 摘要: 成煤环境分析是认识煤系沉积过程、恢复古环境演化和深化煤地质学理论的重要基础.系统梳理了深时成煤环境演化特征、泥炭沼泽分布及动态变化,总结了基于显微组分、显微煤岩类型、矿物-元素地球化学和生物标志物等传统成煤环境分析方法,并讨论其适用性.结果表明,深时成煤环境演化受植物演替、气候变化和沉积体系调整共同控制,不同时代成煤植物、泥炭沼泽类型及沉积背景存在明显差异;泥炭沼泽广泛发育于三角洲平原、潮坪-潟湖、河流-湖泊及冲积平原等环境,其形成和保存受供水方式、水位状态、碎屑输入及海水影响等因素共同制约.传统煤相指标在成煤环境分析中具有重要作用,但其环境意义易受植被组成、分解作用、水位波动、外源输入及成岩-煤化改造等因素影响.成煤环境分析应更加重视沉积过程约束,强化对供水方式、水位状态、碎屑输入和保存条件等主控因素的综合识别.在已有成煤环境分类认识基础上,进一步归纳了低位、中位和高位泥炭沼泽的沉积过程特征及综合判识思路.鄂尔多斯盆地实例表明,该思路有助于揭示煤层形成环境的垂向演化规律,可为成煤环境恢复和煤系沉积研究提供参考.

       

    • 图  1  深时成煤环境演化及其植物背景(改自Greb et al., 2006, 2022

      Fig.  1.  Evolution of deep-time coal-forming environments and vegetation background (modified after Greb et al., 2006, 2022)

      图  2  早期植被和沼泽环境演变(改自Greb et al., 2006, 2022

      Fig.  2.  The evolution of early vegetation and peatland environments (modified after Greb et al., 2006, 2022)

      图  3  不同沉积背景下泥炭沼泽分布

      Fig.  3.  Distribution of peat swamps in different depositional environments

      图  4  海侵、海退体系对成煤沼泽的影响(岩性柱子参考李勇等, 2024

      Fig.  4.  Effects of marine transgression and regression systems on coal-forming swamps (lithological column modified after Li et al., 2024)

      图  5  海侵-海退过程中泥炭沼泽迁移及保存模式(改自Poumot, 1989; Demchuck et al., 2004

      Fig.  5.  Migration and preservation models of peat swamps during marine transgression and regression (revised from Poumot, 1989; Demchuck et al., 2004)

      图  6  三种典型泥炭沼泽动态演化模式

      Fig.  6.  Dynamic evolutionary models of three typical peat swamps

      图  7  成煤环境分析方法

      Fig.  7.  Analysis methods of coal-forming environments

      图  8  TPI-GI图解和VI-GWI图解

      a. 据Diessel,1992;b. 据Calder et al.,1991

      Fig.  8.  TPI-GI diagram and VI-GWI diagram

      图  9  显微组分、显微煤岩类型与宏观煤岩成分含量关系对比

      Fig.  9.  Comparison of maceral composition, microlithotypes and macroscopic coal lithotype contents

      图  10  显微煤岩类型三角图

      a. 基于三大显微组分组的显微煤岩类型(组)分类三角图(据Lester et al.,2003);b. 基于相对带宽曲线划分的显微煤岩类型相三角图(据Hunt,1982);c. 煤层显微煤岩组分组的四组分泥炭相图(据Marchioni,1980

      Fig.  10.  Microlithotype ternary diagram

      图  11  泥炭沼泽术语及分类体系

      Fig.  11.  Terminology and classification system for peatlands

      图  12  鄂尔多斯盆地东北部成煤沼泽垂向演化趋势

      Fig.  12.  Vertical evolutionary trend of coal-forming swamps in the northeastern Ordos Basin

      图  13  成煤环境分析认识及发展趋势

      Fig.  13.  Insights and future trends of coal-forming environment research

      表  1  主要煤相指标及其对沉积环境指示意义

      Table  1.   Main coal facies indicators and their implications for depositional environments

      煤相指标 反映特征 指标范围 文献
      结构保存指数(TPI) (结构镜质体+丝质体+半丝质体)/(碎屑镜质体+碎屑惰质体+无结构镜质体+粗粒体) TPI越高指示植物组织保存越好或成煤植物以木本为主 Diessel, 1992
      凝胶化指数(GI) (镜质体+粗粒体)/(丝质体+半丝质体+碎屑惰质体) GI>2:覆水深;GI≤2:覆水浅 Diessel, 1992
      地下水指数(GWI) (凝胶化镜质体+团块镜质体+矿物质)/(结构镜质体1+无结构镜质体+碎屑镜质体) GWI越高,水动力越强 Calder et al., 1991
      植被指数(VI) (结构镜质体1+无结构镜质体+丝质体+半丝质体+木栓质体+树脂体)/(碎屑镜质体+碎屑惰质体+藻类体+碎屑壳质体+孢子体+角质体) VI<1:草本植物或水生植物;VI≥1:木本植物 Calder et al., 1991
      搬运指数(TI) (壳屑体+镜屑体+惰屑体+团块镜质体+树脂体+孢子体+角质体) / (丝质体+结构镜质体+基质镜质体+粗粒体) TI值越大,水动力条件越强、搬运作用越显著 马兴祥, 1988
      氧化指数(OI) (粗粒体+惰屑体)/其他有机显微组分 OI>1为氧化环境,OI<1为还原环境 马兴祥, 1988
      沼泽类型指数(STI (微壳煤+微亮煤+微暗煤+微惰屑煤+微粗粒煤+微三合煤+原煤灰分)/(微镜煤+微丝煤+微半丝煤) 停滞沼泽(STI<0.1)、过渡沼泽(0.1<STI<1)和流水沼泽(STI>1) 马兴祥, 1988
      下载: 导出CSV
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    • 收稿日期:  2026-06-17
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