Nierop Klaas G J, Verstraten Jacobus M
Centre for Geo-ecological Research (ICG), IBED-Physical Geography, Universiteit van Amsterdam, Nieuwe Achtergracht 166, 1018 WV Amsterdam, The Netherlands.
Rapid Commun Mass Spectrom. 2004;18(10):1081-8. doi: 10.1002/rcm.1449.
Each plant species has a unique chemical composition, and also within a given plant the various tissues differ from one another in their chemistry. These different compositions can be traced back after decay of the plant parts when they are transformed into soil organic matter (SOM). As a result, the composition of SOM reflects not only the plant origin, but also the various tissues, and the composition consequently provides an estimate of the contribution of above-ground vs. below-ground litter. From the latter distribution the extent of bioturbation (mixing of above-ground litter with the mineral soil) can be assessed. Application of thermally assisted hydrolysis and methylation (THM) using tetramethylammonium hydroxide (TMAH) and subsequent analysis by gas chromatography/mass spectrometry (GC/MS) releases all typical cutin- and suberin-derived aliphatic monomers (mono-, di- and trihydroxyalkanoic acids, alpha,omega-alkanedioic acids) as their methyl esters and/or ethers in a rapid manner. Using the distribution of omega-hydroxyalkanoic acids that are present in pine needle cutin (C(12) and C(14)) and not in root suberin, and those that are present in roots but not in needles (C(20) and C(22)), the extent of bioturbation (mixing of above-ground plant litter with the mineral soil) can be assessed. Similarly, the (9,16-dihydroxyhexadecanoic acid+9,10,18-trihydroxyoctadecanoic acid)/(C(20) + C(22) alpha,omega-alkanedioic acids) ratio reflects the degree of bioturbation. Three mineral soil profiles under Corsican pine with an A horizon that exhibited extensive bioturbation phenomena, and underlying C horizons with hardly any or no bioturbation, were investigated in order to examine the applicability of such an approach. It appeared that the A horizons contained all four mentioned omega-hydroxyalkanoic acids, while the C horizons contained virtually only the C(20) and C(22) members. The results not only suggest that bioturbation occurs in the A horizons, but also that possible illuviation or other transport mechanisms of omega-hydroxyalkanoic acids seem hardly ever or never to occur, which is a prerequisite for applying this biomarker approach in assessing degrees of bioturbation.
每种植物都有独特的化学成分,而且在同一植物内部,不同组织的化学组成也彼此不同。当植物部分腐烂并转化为土壤有机质(SOM)后,这些不同的组成成分仍可追溯。因此,土壤有机质的组成不仅反映了植物来源,还反映了不同组织,从而可以估算地上凋落物与地下凋落物的贡献。根据后者的分布情况,可以评估生物扰动(地上凋落物与矿质土壤混合)的程度。使用氢氧化四甲铵(TMAH)进行热辅助水解和甲基化(THM),随后通过气相色谱/质谱(GC/MS)分析,能够快速释放出所有典型的角质和木栓质衍生脂肪族单体(单羟基、二羟基和三羟基链烷酸、α,ω-链烷二酸)的甲酯和/或醚。利用松针角质中存在(C(12)和C(14))而根木栓质中不存在的ω-羟基链烷酸的分布,以及根中存在而针叶中不存在的ω-羟基链烷酸(C(20)和C(22))的分布,可以评估生物扰动(地上植物凋落物与矿质土壤混合)的程度。同样,(9,16-二羟基十六烷酸+9,10,18-三羟基十八烷酸)/(C(20)+C(22)α,ω-链烷二酸)的比值反映了生物扰动的程度。为了检验这种方法的适用性,对科西嘉松树下的三个矿质土壤剖面进行了研究,这些剖面的A层表现出广泛的生物扰动现象,而其下的C层几乎没有或不存在生物扰动。结果表明,A层含有上述所有四种ω-羟基链烷酸,而C层实际上只含有C(20)和C(22)成分。结果不仅表明A层发生了生物扰动,还表明ω-羟基链烷酸几乎从未或从未发生过可能的淋溶或其他迁移机制,这是应用这种生物标志物方法评估生物扰动程度的一个前提条件。