“…Another difference between the lakes during this period is that increases in the relative abundances of intact molecules from plants (e.g., lignin oligomers and phenols) and algae (i.e., chlorophylls and N compounds) are accompanied by a substantial decrease of the degraded OM pool in Lång-Älgsjön, as shown by the relative abundances of n-alkanes, n-alkenes, alka-2-ones, and (poly)aromatics, while for Dragsjön the abundances of these Py-compound classes indicative of degraded OM remain stable. [Geological Survey of Sweden, 2016], the development for the conventional OM variables is characteristic for recently deglaciated lakes [Engstrom et al, 2000;Fritz and Anderson, 2013] and can be linked to the establishment and development of catchment vegetation, reduced catchment erosion, and increased in-lake productivity [e.g., Reuss et al, 2010;Ilyashuk et al, 2013;Chmiel et al, 2015;Meyer-Jacob et al, 2015;Rantala et al, 2015b]. Declines in δ 13 C may be the result of increased aquatic respiration and supply of δ 13 C-depleated plant OM but can also represent a reduced influence of inorganic C (IC) from glacial debris [Hammarlund, 1993;Wolfe et al, 1999].…”