{"title":"La dynamique du carbone dans les tourbières à Sphagnum, de la sphaigne à l'effet de serre","authors":"André-Jean Francez","doi":"10.1016/S0003-5017(00)90002-3","DOIUrl":null,"url":null,"abstract":"<div><p><em>Sphagnum</em> mires are sink ecosystems for carbon, C-fixation by photosynthesis being higher than organic decay. Total primary production is generally lower than 500 g C·m<sup>−2</sup>·yr<sup>−1</sup>, moss layer contribution reaching sometimes 80% of the whole production. Mean annual accumulation in <em>Sphagnum</em> peatlands peat is about 30 g C·m<sup>−2</sup>, which corresponds approximately to 10% of primary production. Accumulation/production ratio increases from fen to bog and varies with vegetation communities. Methane emissions in the atmosphere from mires are about 39 T g·yr<sup>−1</sup> (1 Tg = 10<sup>12</sup> g), i.e. 35% of the whole contribution of wetlands. They fluctuate with the types of mires and vegetation and reach sometimes 3 g CH<sub>4</sub>·m<sup>−2</sup>·day<sup>−1</sup>. Mires have been used for agriculture and peat mining. The consequences of drainage and other managements to practise these different uses were carbon emissions of 6 500 Mt from peat, since the beginning of the 19<sup>th</sup> century. In these conditions, fitting of carbon emissions in the atmosphere shows that disturbed mires could contribute to greenhouse effect as much as coal mining. The influence of increasing atmospheric depositions is not yet well known but seems to be site- and species-dependent. In some European regions, great area of mires have disappeared under the increasing of nitrogen and sulfur depositions. Restoration experiments of mires show that it is possible to regenerate turfigenous process but the time responses for total recovery differ with sites and degrees of disturbance.</p></div>","PeriodicalId":78387,"journal":{"name":"L' Annee biologique","volume":"39 4","pages":"Pages 205-270"},"PeriodicalIF":0.0000,"publicationDate":"2000-10-01","publicationTypes":"Journal Article","fieldsOfStudy":null,"isOpenAccess":false,"openAccessPdf":"https://sci-hub-pdf.com/10.1016/S0003-5017(00)90002-3","citationCount":"14","resultStr":null,"platform":"Semanticscholar","paperid":null,"PeriodicalName":"L' Annee biologique","FirstCategoryId":"1085","ListUrlMain":"https://www.sciencedirect.com/science/article/pii/S0003501700900023","RegionNum":0,"RegionCategory":null,"ArticlePicture":[],"TitleCN":null,"AbstractTextCN":null,"PMCID":null,"EPubDate":"","PubModel":"","JCR":"","JCRName":"","Score":null,"Total":0}
引用次数: 14
Abstract
Sphagnum mires are sink ecosystems for carbon, C-fixation by photosynthesis being higher than organic decay. Total primary production is generally lower than 500 g C·m−2·yr−1, moss layer contribution reaching sometimes 80% of the whole production. Mean annual accumulation in Sphagnum peatlands peat is about 30 g C·m−2, which corresponds approximately to 10% of primary production. Accumulation/production ratio increases from fen to bog and varies with vegetation communities. Methane emissions in the atmosphere from mires are about 39 T g·yr−1 (1 Tg = 1012 g), i.e. 35% of the whole contribution of wetlands. They fluctuate with the types of mires and vegetation and reach sometimes 3 g CH4·m−2·day−1. Mires have been used for agriculture and peat mining. The consequences of drainage and other managements to practise these different uses were carbon emissions of 6 500 Mt from peat, since the beginning of the 19th century. In these conditions, fitting of carbon emissions in the atmosphere shows that disturbed mires could contribute to greenhouse effect as much as coal mining. The influence of increasing atmospheric depositions is not yet well known but seems to be site- and species-dependent. In some European regions, great area of mires have disappeared under the increasing of nitrogen and sulfur depositions. Restoration experiments of mires show that it is possible to regenerate turfigenous process but the time responses for total recovery differ with sites and degrees of disturbance.
泥沼是碳汇生态系统,光合作用对碳的固定高于有机衰变。初级总产量一般低于500 g C·m−2·yr−1,苔藓层的贡献有时可达总产量的80%。泥炭地泥炭年平均积累量约为30 g C·m−2,约相当于初级产量的10%。积累/生产比从沼泽到沼泽增加,并随植被群落而变化。沼泽向大气中排放的甲烷约为39 Tg·yr - 1 (1 Tg = 1012 g),占湿地总排放量的35%。它们随沼泽和植被的类型而波动,有时可达3 g CH4·m−2·day−1。矿坑已被用于农业和泥炭开采。自19世纪初以来,为了实现这些不同的用途,排水和其他管理的后果是泥炭排放了6500万吨碳。在这些条件下,对大气中碳排放的拟合表明,受干扰的矿井可能与煤炭开采一样会造成温室效应。大气沉积增加的影响尚不清楚,但似乎与地点和物种有关。在欧洲一些地区,由于氮和硫沉积的增加,大面积的矿坑已经消失。泥沼恢复实验表明,泥沼恢复是可能的,但泥沼完全恢复的时间响应随场地和扰动程度的不同而不同。