Journals / Gaziosmanpaşa Üniversitesi Ziraat Fakültesi Dergisi / 2019 / Cilt: 36 - Sayı: 3

Dependency of Soil Organic Carbon Mineralization to Moisture and Temperature under Different Land Uses

Pages
198–205
Publication Date
2022-10-18
DOI
—
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AI Summary & Key Takeaways

AI Insight
⚡ TL;DR(Too Long; Didn't Read)

This result indicates that the amount of mineralize C in the forest soil is more sensitive to temperature, while agricultural soil is more sensitive to the increase in moisture content.

📌 3 Key Takeaways

🎯
Objective & Hypothesis:Temperature and humidity are the important environmental factors that control the decomposition of organic carbon in the soil.
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Key Findings & Data:The aim of this study is to determine the change in mineralized C content of different soils (agriculture, pasture and forest) at different temperature (20 oC and 35 oC) and humidity conditions (30% and 60% of field capacity).
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Conclusion & Impact:This result indicates that the amount of mineralize C in the forest soil is more sensitive to temperature, while agricultural soil is more sensitive to the increase in moisture content.
🔬Design:Research Article
📍Scope:Comprehensive Sample
⚙️Variables:Domain Parameters

Abstract

Temperature and humidity are the important environmental factors that control the decomposition of organic carbon in the soil. The sensitivity of the soils to temperature and moisture may vary. The aim of this study is to determine the change in mineralized C content of different soils (agriculture, pasture and forest) at different temperature (20 oC and 35 oC) and humidity conditions (30% and 60% of field capacity). This study was carried out in agriculture, forest and pasture lands in Almus district of Tokat province. In the study, soil samples were taken from 0-5, 5-15 and 15-30 cm depths by hand probe. Particle distribution, pH, lime, organic matter, total C, organic C, microbial biomass C and mineralize C were determined in the samples. Mineralize C content was determined by incubation of 30% and 60% of field capacity at 20 oC and 30 oC. Soils were generally classified as clay texture. The highest organic C was found in forest soil. Microbial biomass C showed significant change depending on land use. The difference between the land uses at 20 °C incubation was only observed at 60% of field capacity. The similar trend was also seen at 35 °C temperature. Significant differences have been observed between uses at high humidity conditions. While the increase in the amount of moisture significantly increased the amount of mineralize C in agricultural soil, the increase in temperature in forest soil was significant. This result indicates that the amount of mineralize C in the forest soil is more sensitive to temperature, while agricultural soil is more sensitive to the increase in moisture content.

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Cite This Article

GÜLER, E., KOÇYİĞİT, R., OĞUZ, İ. (2022). Dependency of Soil Organic Carbon Mineralization to Moisture and Temperature under Different Land Uses. Gaziosmanpaşa Üniversitesi Ziraat Fakültesi Dergisi, Cilt: 36 - Sayı: 3, 198–205. https://ajindex.com/articles/520817

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References (14)

  1. Arslan EI, İpek U, Aslan S, Öbek E (2009). Farklı kompostların topraktaki karbon mineralizasyonu. Anadolu Üniversitesi Bilim ve Teknoloji Dergisi, 10(2):389-395.
  2. Bouyocous GJ (1951). A recalibration of the hydrometer method for making mechanical analysis of soil. Argon. Jour, 43:434-438.
  3. Bowden RD, Newkırk KM, Rullo GM (1998). Carbon dioxide and methane fluxes by aforest soil under labratory-controlled moisture and temperature conditions. Soil Biol. Biochem. 30:1591-1597.
  4. Demirci S (2008). Farklı arazi kullanımlarında agregatlara bağlı karbon ile biyolojik karbon ve azot fraksiyonlarının belirlenmesi. Gaziosmanpaşa Üniversitesi,
  5. Fen Bilimleri Enstitüsü, Toprak Anabilim Dalı. Dinç U, Kapur S, Akça E, Özden M, Senol S, Dingil M, Öztekin E, Kızılarslanoglu HA, Keskin S (2001). History and status of soil survey programmes in Turkey and suggestions on land management. In (P. Zdruli, P. Steduto, C. Lacirignola, L. Montanarella) soil resources of southern and eastern mediterranean countries. options mediterraneennes, Serie B. n. 34. 263-273.
  6. Gudasz C, Bastviken D, Steger K, Premke K, Sobek S (2010). Temperature-controlled organic carbon mineralization in lake sediments. Macmillan Publishers Limited, vol: 466. Horwath WR, Paul EA (1994). Microbial biomass. Pages 753-773
  7. In Weaver RW, Angle S, Bottomley P, Smith D, Tabatabai S, and A. Wollum, Editors. methods of soil analysis. Part 2. Microbiological and biochemical properties. IPCC (2000). Land use change and forestry. IPCC, special report. Cambridge University Press:
  8. Cambridge. Jaiyeoba IA (2003). Changes in soil properties due to continuous cultivation in Nigerian semiarid Savannah. Soil and Tillage Research 70:91-98.
  9. Kara Ö, Bolat İ (2008). Bartın ili orman ve tarım topraklarının mikrobiyal biokütle karbon ve azotun içerikleri. Ekoloji 18: 32-40.
  10. Klute A (1986). Water retention: laboratory methods. methods of soil analysis. Part1.2nd Ed. Agronomy 9. Am. Soc. Argon., 635-660,
  11. Madison. Kutlay A, Darıcı C, Aka Sağlıker H (2010). Doğu akdeniz bölgesinde yetişen capparis spinosa l. topraklarında organik madde mineralizasyonu. 3 (3):259-263.
  12. Lal R (2003). Soil erosion and the global carbon budget. Environmental International, 29: 437-450.
  13. Mclaughlin SB and Walsh ME (1998). Evaluating enviromental consequences of producing herbaceous crops for bioenergy. Biomass and Bioenergy. 14: 317-324.
  14. Mohammed AM, Naab JB, Nartey E and Adiku SGK (2014). Carbon mineralization from plant residue-amended soils under varying moisture