Faculty of Agricultural and Environmental Sciences, University of Rostock, Justus-von-Liebig-Weg 6, 18059 Rostock, Germany.
Department of Ecoscience, Aarhus University, C.F. Møllers Allé 4-6, 8000 Aarhus, Denmark; Department of Ecohydrology and Biogeochemistry, Leibniz-Institute of Freshwater Ecology and Inland Fisheries, Müggelseedamm 301, 12587 Berlin, Germany.
Sci Total Environ. 2023 May 1;871:161979. doi: 10.1016/j.scitotenv.2023.161979. Epub 2023 Feb 3.
Climate change may increase the overall susceptibility of peatlands to fire. Smoldering fires in peatlands can cause substantial emissions of greenhouse gases. It is, however, less clear how smoldering affects the soil pore water quality. In this study, soil samples were collected from agricultural fen and disturbed bog study sites in Germany and Lithuania to quantify the effect of peat burning on pore water composition. The samples were air dried and smoldered under ignition temperature (approximately 200 °C) with different durations (0, 2, 5, and 10 h). Pore water samples were extracted from the soil to determine dissolved organic carbon (DOC) concentrations, dissolved organic matter (DOM) fractions, fluoride, extractable organically bound fluorine (EOF), and sulfate concentrations. The results showed that soil smoldering changes the peat pore water chemistry and that changes differ between fens and bogs. The smoldering duration is likewise influential. For fen grasslands, 2 and 5 h of smoldering of peat caused a >10-fold increase in DOC (up to 1600 mg L) and EOF concentrations. The fluoride (up to 60 mg L) and sulfate concentrations substantially exceeded WHO drinking water guidelines. In contrast, the temperature treatment decreased the DOC concentrations of samples from raised bogs by 90 %. The fluoride concentrations decreased, but sulfate concentrations increased after smoldering of the bog samples. DOC, fluoride, and sulfate concentrations of bogs varied significantly between the smoldering duration treatments. For all peat samples, the extracted DOM was dominated by humic-like substances before smoldering, but the fraction of low molecular weight substances increased after smoldering combustion. In conclusion, smoldering alters the biogeochemical processes in both peatland types and possibly impair the water quality of adjacent water resources especially in fen peat landscapes.
气候变化可能会增加泥炭地整体对火灾的易感性。泥炭地闷烧火灾会导致大量温室气体排放。然而,泥炭闷烧如何影响土壤孔隙水质量则不太清楚。在这项研究中,从德国和立陶宛的农业湿地和干扰泥沼研究点采集了土壤样本,以量化泥炭燃烧对孔隙水组成的影响。这些样本在风干后,在点火温度(约 200°C)下闷烧不同时间(0、2、5 和 10 小时)。从土壤中提取孔隙水样本,以确定溶解有机碳(DOC)浓度、溶解有机质(DOM)分数、氟化物、可提取有机结合氟(EOF)和硫酸盐浓度。结果表明,土壤闷烧会改变泥炭孔隙水化学性质,湿地和泥沼的变化不同。闷烧时间也有影响。对于湿地草地,泥炭闷烧 2 和 5 小时会导致 DOC(高达 1600mg/L)和 EOF 浓度增加 10 倍以上。氟化物(高达 60mg/L)和硫酸盐浓度大大超过世界卫生组织饮用水指南。相比之下,温度处理会使抬高泥沼样本的 DOC 浓度降低 90%。氟化物浓度下降,但闷烧后泥沼样本的硫酸盐浓度增加。在闷烧时间处理下,泥沼样本的 DOC、氟化物和硫酸盐浓度差异显著。对于所有泥炭样本,在闷烧前提取的 DOM 主要由类腐殖质物质组成,但闷烧燃烧后低分子量物质的比例增加。总之,闷烧会改变两种泥炭地类型的生物地球化学过程,并可能损害附近水资源的水质,特别是在湿地泥炭景观中。