微藻无机碳利用在岩石风化及碳循环过程中的作用

赵丽华, 吴沿友, 谢腾祥, 李海涛. 微藻无机碳利用在岩石风化及碳循环过程中的作用[J]. 中国岩溶, 2023, 42(1): 1-18. doi: 10.11932/karst20230101
引用本文: 赵丽华, 吴沿友, 谢腾祥, 李海涛. 微藻无机碳利用在岩石风化及碳循环过程中的作用[J]. 中国岩溶, 2023, 42(1): 1-18. doi: 10.11932/karst20230101
ZHAO Lihua, WU Yanyou, XIE Tengxiang, LI Haitao. Role of carbonic utilization of microalgae on rock weathering and carbon cycle[J]. Carsologica Sinica, 2023, 42(1): 1-18. doi: 10.11932/karst20230101
Citation: ZHAO Lihua, WU Yanyou, XIE Tengxiang, LI Haitao. Role of carbonic utilization of microalgae on rock weathering and carbon cycle[J]. Carsologica Sinica, 2023, 42(1): 1-18. doi: 10.11932/karst20230101

微藻无机碳利用在岩石风化及碳循环过程中的作用

  • 基金项目: 贵州省高层次创新型人才培养项目“百层次”(黔科合人才(2015)4035号);国家自然科学基金 (U1612441);贵州科学院青年科学基金(黔科院J字 (2023) 22号)
详细信息
    作者简介: 赵丽华(1992-),女,工程师,硕士研究生,主要从事环境生物地球化学等研究工作。E-mail:18798012493@163.com
    通讯作者: 吴沿友(1966-),男,博士,研究员,博士生导师,主要从事生态环境和环境地球化学等研究工作。E-mail:wuyanyou@mail.gyig.ac.cn
  • 中图分类号: P642.25

Role of carbonic utilization of microalgae on rock weathering and carbon cycle

More Information
  • 岩溶碳汇呈现两种不同观点:(1)岩溶碳汇巨大,其机理在于岩溶区藻类及光合细菌利用碳酸氢根离子(${\rm{HCO}}_3^{-}$)实现光合作用,从动力学上加速了岩溶风化过程,促进大气CO2的溶解。(2)岩溶区碳酸盐岩的风化作用,产生${\rm{HCO}}_3^{-}$,随后产生等量的阳离子在海洋中进行碳酸盐岩的沉积作用,这仅仅体现的是碳酸盐岩的搬运作用,不能体现碳汇,在长期尺度上仅仅有硅酸盐岩风化产生净碳汇。文章抓住岩石风化产生${\rm{HCO}}_3^{-}$与微藻光合作用利用${\rm{HCO}}_3^{-}$的耦合点,分析了典型代表性水生生物——微藻在无机碳利用上对岩石风化及碳汇的影响。从微藻光合无机碳利用机制以及光合作用关键性酶-碳酸酐酶(CA)作用两方面,论证了微藻生长对岩石风化及其碳汇的的促进作用;同时论述高pH、高${\rm{HCO}}_3^{-}$的风化环境对微藻生长影响。获得以下新认识:(1)微藻通过胞外碳酸酐酶(CAex) 利用了大量${\rm{HCO}}_3^{-}$,加速岩石风化,并促使风化朝着形成${\rm{HCO}}_3^{-}$的方向进行;(2)微藻加速钙镁硅酸盐岩风化,风化溶出的Ca2+、Mg2+会促使碳酸盐岩的沉积,因此微藻加速硅酸盐岩风化形成净碳汇;(3)长时间尺度下,单纯的碳酸盐岩化学风化并不能直接产生净碳汇,但微藻对${\rm{HCO}}_3^{-}$利用使得碳酸盐岩风化朝着${\rm{HCO}}_3^{-}$转化方向进行,微藻参与碳酸钙沉积作用的同时转化无机碳为惰性有机碳,产生碳汇。故微藻通过CAex的作用,催化加速${\rm{HCO}}_3^{-}$与CO2之间的转化,形成水体${\rm{HCO}}_3^{-}$消耗的动力基础,微藻无机碳利用对岩石风化具有促进作用,从而调节大气CO2、浓度变化。基于当前研究,提出三点展望:(1)开展岩溶区区域水体系统的岩石风化、水生生物碳汇评估成为解决当前区域碳收支不平衡问题的关键;(2)查明岩石风化作用中生物作用碳转化机理及转化量,解决单纯的水化学径流法计算岩石风化碳汇精度不够问题;(3)构建光合生物参与下的新的评估方法,评估当前岩石风化在水生生物、水循环作用下的碳汇的时间尺度问题,厘清岩石风化碳汇在碳收支中的贡献。

  • 加载中
  • 图 1  地表温度(a)、大气CO2浓度(b)、大气CO2浓度增长率(c)随时间的变化(据IPCC AR6,2021[1]修编)

    Figure 1. 

    图 2  长期碳循环模型(a)、短期碳循环模型(b)(据Berner,1999修编[13]

    Figure 2. 

    图 3  不同pH条件下水体中各无机碳分量的百分含量( Larkum等,1989[76]

    Figure 3. 

    图 4  微藻CO2浓缩机制( CCM)模型(据Sültemeyer,1998[87];Li Haitao等,2019[96]修编)

    Figure 4. 

    图 5  不同时间下方解石的镁离子释放量(mg·L−1)和叶绿素a的含量(μg·L−1)(a)对照组;(b、e)莱茵衣藻;(c、f)蛋白核小球藻;(d、g)铜绿微囊藻(据Xie Tengxiang等,2017[67]

    Figure 5. 

    图 6  微藻无机碳利用与岩石风化、大气碳之间的动力关系

    Figure 6. 

    图 7  微藻对水环境中${\rm{HCO}}_3^{-}$的响应

    Figure 7. 

    图 8  流域岩石风化与微藻生长的耦合关系

    Figure 8. 

    表 1  1850-2019年全球人为累计碳收支情况(引自AR6[1,10]

    Table 1.  Global accumulated anthropogenic CO2 budget from 1850 to 2019(revised from AR6[1,10])

    碳排放量/PgC总量/PgC收支不平衡量/PgC
    排放(源)化石燃料燃烧及水泥生产445±20685±6520
    净通量土地使用240±60
    分配(汇)大气增加CO2265±5635±80
    海洋碳汇160±20
    陆地碳汇210±55
    下载: 导出CSV

    表 2  全球碳酸盐岩风化碳汇一些数据对比(据张之淦,2012[35]

    Table 2.  Comparison of global weathering carbon sink from carbonate rock (revised from Zhang Zhigan, 2012[35])

    通量/PgC·yr−1数据来源计算方法
    0.142Berner 1983[23]水化学径流法
    0.117数据引自徐胜友等,1997;据张之淦,2012外推[32,35]水化学径流法
    0.131数据引自蒋忠诚等,2011;据张之淦,2012外推[33,35]水化学径流法
    0.165数据引自邱冬生等,2004);据张之淦,2012外推[34-35]水化学径流法
    0.608Yuan,1997[36]定点磨片
    下载: 导出CSV

    表 3  微藻的碳酸氢根离子利用途径份额

    Table 3.  Proportion of bicarbonate utilization pathway to the whole carbon utilization pathway of microalgae

    NaHCO3/mmol·L−1莱茵衣藻蛋白核小球藻野外混合微藻数据来源
    \1(1.067)0.810.98赵丽华等,2016[98]
    \0.960.77/Wu等,2015[100]
    0.500.970.81/Wu等,2015[100]
    2.001(1.05)0.92/Wu等,2015[100]
    4.001(1.02)1.00(1.10)/Wu等,2015[100]
    8.001(1.10)1.00(1.29)/Wu等,2015[100]
    下载: 导出CSV

    表 4  微藻对碳酸钙碳源的利用份额(fB)(谢腾祥等,2014[104])

    Table 4.  Proportion of calcium carbonate-carbon source utilized by microalgae (Xie Tengxiang et al., 2014[104])

    藻种AZ/mmol·L−1fB
    莱茵衣藻00.02
    0.10.03
    10.08
    100.30
    蛋白核小球藻00.02
    0.10.02
    10.10
    100.15
    下载: 导出CSV

    表 5  野外湖泊微藻利用添加的碳酸氢钠与总无机碳碳源的占比(Li Haitao等,2018[96]

    Table 5.  Proportion of NaHCO3-carbon source utilized by lake microalgae (Li Haitao et al., 2018[96])

    NaHCO3/
    mmol·L−1
    AZ /mmol·L−1
    01.010.0
    1.00.06±0.030.06±0.040.03±0.03
    2.50.08±0.020.08±0.050.09±0.03
    5.00.09±0.040.17±0.050.12±0.05
    下载: 导出CSV

    表 6  碳酸酐酶加速岩石风化的数据统计

    Table 6.  Statistics of the acceleration of rock weathering by carbonic anhydrase

    岩石种类岩石风化变化情况生物种类CA种类数据来源
    白云岩 在CO2分压低于5 000 Pa实验条件下,对白云岩的溶解速率促进倍数在1.29~3.07之间 体外实验 高分子催化剂-牛碳酸酐酶 刘再华,2001[117]
    灰岩 加入CA后,在高CO2 分压时,其溶解速率可增加 10倍 体外实验 高分子催化剂-牛碳酸酐酶 刘再华,2001[117]
    灰岩 在加入AZ后,单位时间单位藻体的镁离子释放量从3.37×10−4 mg·(μg·day)−1降低至1.99×10−4 mg·(μg·day)−1 莱茵衣藻 胞外碳酸酐酶 Xie等,2014[66]
    灰岩 在加入AZ后,单位时间单位藻体的镁离子释放量从2.44×10−4 mg·(μg·day)−1降低至2.19×10−4 mg·(μg·day)−1 蛋白核小球藻 胞外碳酸酐酶 Xie等,2014[66]
    下载: 导出CSV

    表 7  不同处理下微藻的增殖倍数(摘自Wu等,2015[103]

    Table 7.  Microalgae growth with different treatments ( Wu et al., 2015[103])

    NaHCO3/
    mmol·L−1
    增值倍数
    0 mmol·L−1 AZ1.0 mmol·L−1 AZ10.0 mmol·L−1 AZ
    14.89±0.073.75±0.251.59±0.24
    2.55.27±0.523.67±0.391.93±0.30
    56.28±0.443.93±0.192.16±0.19
    206.55±0.324.46±0.282.53±0.47
    下载: 导出CSV
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出版历程
收稿日期:  2021-10-12
刊出日期:  2023-02-25

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