<p>Soil acidification has increasingly&#160;become a critical issue&#160;for sustainable production due to&#160;the excessive nitrogen&#160;(N)&#160;fertilization&#160;in agricultural systems.&#160;Application of N&#160;fertilizers&#160;and the consequent nitrification yield protons (H<sup>+</sup>), which&#160;strongly&#160;and irreversibly accelerate dissolution of soil inorganic carbon (SIC) e.g.,&#160;CaCO<sub>3</sub>, leading to CO<sub>2</sub>&#160;release in&#160;the atmosphere.&#160;Here, <sup>14</sup>C-labeled CaCO<sub>3</sub>&#160;was added to calcareous soil&#160;(0.75% CaCO<sub>3</sub>) to investigate the effects of&#160;chicken manure, urea, NH<sub>4</sub>NO<sub>3, </sub>KNO<sub>3 </sub>and<sub>&#160;</sub>(NH<sub>4</sub>)<sub>2</sub>SO<sub>4</sub>&#160;on soil acidification&#160;and to estimate the SIC contribution&#160;to CO<sub>2</sub>&#160;emission.&#160;250 mL gas-tight jars&#160;were filled with a cropland soil (pH&#160;=&#160;7.2), homogenously mixed with 1.3% Ca<sup>14</sup>CO<sub>3</sub>&#160;powder&#160;(<sup>14</sup>C&#160;activity = 11.3 kBq pot<sup>-1</sup>).&#160;Following fertilization in rates of 0.1, 0.15, 0.25 g N kg<sup>-1</sup>&#160;soil,&#160;NaOH was applied to&#160;trap the emitted CO<sub>2</sub>&#160;and to determine <sup>14</sup>C activity.&#160;CaCO<sub>3</sub>&#160;addition increased soil pH&#160;values&#160;by 0.17-0.43&#160;units. Addition of ammonium-based fertilizers ((NH<sub>4</sub>)<sub>2</sub>SO<sub>4</sub>, NH<sub>4</sub>NO<sub>3</sub>) strongly decreased pH up to 0.3 units. All fertilizers increased&#160;CO<sub>2</sub>&#160;emission (5.1%-180%) compared&#160;to the unfertilized soil after 44 days of incubation except KNO<sub>3</sub>. SIC-originated&#160;CO<sub>2</sub>&#160;due to fertilization was ranged&#160;from 2.9 to 160&#160;mg C kg<sup>-1</sup>&#160;(1.1%&#160;to 48% of total emitted CO<sub>2</sub>). Manure and urea had lowest&#160;impacts on SIC-driven CO<sub>2</sub>&#160;during&#160;the first 5&#160;days&#160;(2.9-34 mg C kg<sup>-1</sup>) irrespective&#160;of the application rate. Thereafter, the effects of fertilizers on SIC-originated&#160;CO<sub>2</sub>&#160;increased in the order:&#160;urea < manure < KNO<sub>3</sub>&#160;< NH<sub>4</sub>NO<sub>3</sub>&#160;< (NH<sub>4</sub>)<sub>2</sub>SO<sub>4</sub>. As nitrification of (NH<sub>4</sub>)<sub>2</sub>SO<sub>4</sub>&#160;yields in 4 mol H<sup>+</sup>, which neutralizes&#160;2 mol carbonates, it initially caused the highest SIC-originated&#160;CO<sub>2</sub><sub>&#160;</sub>until 9 days. Urea and NH<sub>4</sub>NO<sub>3</sub>&#160;release by nitrification 2 mol H<sup>+ </sup>per mole of fertilizer, but urea initially hydrolyses&#160;to NH<sub>4</sub>OH, which&#160;increases soil pH. So, urea addition&#160;had the minimum SIC loss as CO<sub>2</sub><sub>&#160;</sub>in the first 5 days, but starting&#160;from 16<sup>th</sup>&#160;day, CO<sub>2</sub>&#160;emission sharply increased and reached to highest&#160;values among the fertilizers. Manure increased&#160;SIC-originated&#160;CO<sub>2</sub>&#160;emission from 23<sup>rd</sup>&#160;day of incubation. Gradual and incomplete mineralization of organic N of&#160;chicken manure duration 44&#160;days explains the smallest released CO<sub>2</sub>&#160;from CaCO<sub>3</sub>&#160;and slowest acidification&#160;in the first 16 days. Furthermore, Ca<sup>2+</sup>&#160;and Mg<sup>2+</sup>&#160;in manure may be precipitated as carbonates, which decrease the SIC share in the emitted CO<sub>2</sub>.&#160;Generally, the higher the applied fertilizer amounts, the larger was the proportion of CO<sub>2</sub>&#160;released from SIC.&#160;Both the fertilizer chemistry and the application rate played significant roles in&#160;dissolution of carbonates. Summarizing, the correct selection of the type and amount of fertilizers based on soil properties and plant demand is necessary to decrease&#160;SIC-originated&#160;CO<sub>2</sub>&#160;emission to mitigate global warming, and also save various ecosystem services such as organic matter stability and increase C sequestration.</p>
<p>Terrestrial ecosystems play a significant role in global warming by regulating CO<sub>2</sub> concentration in the atmosphere. A comprehensive understanding of carbon (C) sources and stocks in soils, as well as the driving mechanisms, are critical to reducing CO<sub>2</sub> emission from soil and thus mitigating climate change. To date, most studies have solely focused on processes involving soil organic C (SOC), but few studies have addressed the potential contribution of soil inorganic C (SIC) mostly CaCO<sub>3</sub> pool to ecosystem C fluxes. SIC can potentially be a regulator of atmospheric CO<sub>2</sub>. However, so far the effects of plant species (i.e. variations in nitrogen (N) demand and N use efficiency (NUE)) as well as soil temperature on SIC-derived CO<sub>2</sub> are unclear. We hypothesized that 1) relatively less SIC-derived CO<sub>2</sub> is expected from soils covered under plant species with lower N demand and higher NUE. We conducted a 4-month field experiment from June to October 2021 at the research station of the University of G&#246;ttingen in Deppoldshausen (51.58<sup>o</sup>N, 9.97<sup>o</sup>E) with ca. 6% CaCO<sub>3</sub> equivalent in the topsoil. We analyzed the effects of two plant species 1) wheat (high N demand and low NUE), 2) legume (low N demand and high NUE) and two N fertilization (urea) levels, 1) low (50 kg N ha<sup>-1</sup>), 2) high (200 kg N ha<sup>-1</sup>) on CO<sub>2</sub> emission out of SIC. Each treatment had four replicate plots (1&#215;1 m<sup>2</sup>), and at least a 0.5 m gap was established between plots. We measured CO<sub>2</sub> fluxes weekly by using the static chamber method. The &#948;<sup>13</sup>C natural abundance was used to determine the contribution of SIC and SOC in the emitted CO<sub>2</sub>. The total CO<sub>2</sub> emission and its &#948;<sup>13</sup>C signature increased with soil temperature, indicating that the portion (%) of SIC-derived CO<sub>2</sub> was stimulated by temperature (<sup>o</sup>C) (slope = 0.33). The portion of SIC-derived CO<sub>2</sub> stimulated by temperature increased faster under wheat than under legume (slope = 0.36 vs. 0.26), especially under high N treatment (slope = 0.65 vs. 0.54). The portion of SIC-derived CO<sub>2</sub> under wheat (13.0%) was higher than that under legume (11.3%). Moreover, the portion of SIC-derived CO<sub>2</sub> was 1.2% higher under wheat than under legume at high N fertilization level, whereas it was increased to 2.2% under low N fertilization. This indicates a significant role of plant species with different N demand and NUE on dynamics of SIC pool and its contribution in CO<sub>2</sub> emission from soil. The rate of SIC-derived CO<sub>2</sub> was comparable between wheat and legume under high N fertilization, but it was 1.6 times higher under wheat than that under legume at low N fertilization. The contribution of SIC-derived C to the atmosphere was ~63.7 g C m<sup>-2</sup> yr<sup>-1</sup> under legume with low N demand vs. ~82.1 g C m<sup>-2</sup> yr<sup>-1</sup> under wheat with high N demand. In this regard, the impacts of plant species and their N demand and NUE are important controlling factors determining the dynamics of the SIC pool in agroecosystems.</p>
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