Pati Sarah G, Brunner Lara M, Ley Martin, Hofstetter Thomas B
Department of Environmental Geosciences, Centre for Microbiology and Environmental Systems Science, University of Vienna, Vienna 1090, Austria.
Department of Environmental Sciences, University of Basel, Basel 4056, Switzerland.
ACS Environ Au. 2025 Jan 22;5(2):220-229. doi: 10.1021/acsenvironau.4c00107. eCollection 2025 Mar 19.
Oxygen isotope ratios of O are important tracers for assessing biological activity in biogeochemical processes in aquatic environments. In fact, changes in the O/O and O/O ratios of O have been successfully implemented as measures for quantifying photosynthetic O production and biological O respiration. Despite evidence for light-dependent O consumption in sunlit surface waters, however, photochemical O loss processes have so far been neglected in the stable isotope-based evaluation of oxygen cycling. Here, we established the magnitude of the O isotope fractionation for abiotic photochemical O elimination through formation of singlet O, O, and the ensuing oxygenation and oxidation reactions with organic compounds through experiments with rose bengal as the O sensitizer and three different amino acids and furfuryl alcohol as chemical quenchers. Based on the kinetic analysis of light-dependent O removal in the presence of different quenchers, we rationalize the observable O isotope fractionation of O and the corresponding, apparent O kinetic isotope effects (O-AKIE) with a pre-equilibrium model for the reversible formation of O and its irreversible oxygenation reactions with organic compounds. While O-AKIEs of oxygenation reactions amount to 1.03, the O isotope fractionation of O decreased to unity with increasing ratio of the rates of oxygenation reaction of O vs O decay to ground state oxygen, O. Our findings imply that O isotope fractionation through photochemical O consumption with isotope enrichment factors, O-ϵ, of up to -30‰ can match contributions from biological respiration at typical dissolved organic matter concentrations of lakes, rivers, and oceans and should, therefore, be included in future evaluations of biogeochemical O cycling.
氧的氧同位素比率是评估水生环境生物地球化学过程中生物活性的重要示踪剂。事实上,氧的O/O和O/O比率变化已成功用作量化光合产氧和生物氧呼吸的指标。然而,尽管有证据表明在阳光照射的表层水体中存在光依赖的氧消耗,但在基于稳定同位素的氧循环评估中,光化学氧损失过程迄今一直被忽视。在此,我们通过以孟加拉玫瑰红作为氧敏化剂,三种不同氨基酸和糠醇作为化学猝灭剂进行实验,确定了通过单线态氧、O的形成以及随后与有机化合物的氧合和氧化反应实现非生物光化学氧消除的氧同位素分馏程度。基于在不同猝灭剂存在下光依赖氧去除的动力学分析,我们用一个关于O的可逆形成及其与有机化合物的不可逆氧合反应的预平衡模型,解释了可观测的O的氧同位素分馏以及相应的表观氧动力学同位素效应(O-AKIE)。虽然氧合反应的O-AKIE达到1.03,但随着O与O衰变回基态氧的氧合反应速率之比增加,O的氧同位素分馏降至单位值。我们的研究结果表明,通过光化学氧消耗实现的氧同位素分馏,其同位素富集因子O-ϵ高达-30‰,在湖泊、河流和海洋典型溶解有机物浓度下可与生物呼吸的贡献相匹配,因此应纳入未来生物地球化学氧循环的评估中。