2 research outputs found
Effect of waterlogging on carbon isotope discrimination during photosynthesis in <i>Larix gmelinii</i>
<p>Soil moisture is a major factor controlling carbon isotope discrimination (Δ<sup>13</sup>C), which has been demonstrated to decrease under dry conditions in many studies; however, few studies on Δ<sup>13</sup>C under waterlogging condition have been conducted. In this study, a pot experiment was conducted with <i>Larix gmelinii</i>, a major larch species in the east Siberian Taiga, to investigate the effect of waterlogging on Δ<sup>13</sup>C during photosynthesis. Assimilation rate and Δ<sup>13</sup>C<sub>RD</sub> (instantaneous Δ<sup>13</sup>C calculated with Rayleigh distillation equation) decreased drastically soon after waterlogging, followed by recovery in their values, which was caused by a change in stomatal conductance. Thereafter, assimilation rate decreased gradually, whereas Δ<sup>13</sup>C<sub>RD</sub> decreased more gently. These results were thought to be caused by the decrease in both stomatal conductance and carboxylation. Our results indicate that extreme wet events may cause a decrease in Δ<sup>13</sup>C, which is important information for detecting flooding events in the past using tree-ring isotope analyses and for studying impacts of flooding on plants in areas where waterlogging might occur.</p
Spatial variations in larch needle and soil δ<sup>15</sup>N at a forest–grassland boundary in northern Mongolia
<p>The spatial patterns of plant and soil δ<sup>15</sup>N and associated processes in the N cycle were investigated at a forest–grassland boundary in northern Mongolia. Needles of <i>Larix sibirica</i> Ledeb. and soils collected from two study areas were analysed to calculate the differences in δ<sup>15</sup>N between needle and soil (Δδ<sup>15</sup>N). Δδ<sup>15</sup>N showed a clear variation, ranging from −8 ‰ in the forest to −2 ‰ in the grassland boundary, and corresponded to the accumulation of organic layer. In the forest, the separation of available N produced in the soil with <sup>15</sup>N-depleted N uptake by larch and <sup>15</sup>N-enriched N immobilization by microorganisms was proposed to cause large Δδ<sup>15</sup>N, whereas in the grassland boundary, small Δδ<sup>15</sup>N was explained by the transport of the most available N into larch. The divergence of available N between larch and microorganisms in the soil, and the accumulation of diverged N in the organic layer control the variation in Δδ<sup>15</sup>N.</p