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Dalya Hazar Kalonya



            larger area (e.g., Africa). It is estimated that pastures store at least 10% of
            the global carbon storage in the soil (Anderson, 1991; Eswaran et al, 1993).
            Pastures are known to be important carbon sinks with a capacity of 200-300
            billion-ton (Pg) CO2 (Batjes and Sombroek, 1997). Even the smallest changes
            in the carbon absorption inputs of pastures will lead to more extensive and
            durable carbon capture (Scurlock and Hall, 1998).
               The interaction between climate  change and pasture biochemistry
            attracts relatively less attention than forest areas in literature. Their effects on
            temperatures, water and food have recently been understood relatively well,
            but it has been possible to assess only the results of the interactions between
            long-term  CO2  fertilization  and  global  carbon  cycles  (Hall  and  Scurlock,
            1991). Pastures are usually seen as static areas. However, although seemingly
            infertile and/or semi-decertified, the loss in carbon absorption of pastures can
            be compensated through transforming marginal forest areas into wet/semi-
            wet pastures, that is, potential carbon sinks. Therefore, different meadow-
            pastures need different decisions of use according to their features (Schimel
            et al, 1990; Thornley et al, 1991).
               Meadows and pastures are major agents of global carbon cycle owing to
            their underground carbon storage, seasonal burns and regrowth, and tree-
            grass dynamics. Although their carbon storage, efficiency and cycle periods
            are  largely  unspecified,  based  on  current  observations,  it  can  be  said  that
            pastures annually capture around 0,5 Pg of CO2. Due to climate change, and
            the ensuing potential droughts, future absorption levels are uncertain, yet
            through effective land management practices, this value is estimated to go
            up to around –/+2 Pg CO2 (Scurlock and Hall, 1998).
               US Environment Protection Agency (EPA) announced that in 2019, the world
            total greenhouse gas emission reached an equivalent (eq.) of 6,558 million-ton
            CO2. 10% of it thought to result from agricultural sector (EPA, 2021). Of the
            agricultural sector-based emissions, 39% comes from enteric fermentation,
            20% comes from animal-based fertilizers, 13% from artificial fertilizers, 10%
            from wet-rice cultivation, 6% from fertilizer management, 5% from the burning
            of agricultural waste in open areas, 4% from product remains, and 2% from
            other reasons (FAO, 2018). It is known that the most important source of
            nitrous oxide is (N2O) is the mineral fertilizers embedded in agricultural land.
            According to IPCC (2015) reports, agricultural sector accounts for 12% of the
            total anthropogenic emissions worldwide, 60% of the total N2O emissions,
            and 50% of the total methane (CH4) emissions (Ağaçayak and Öztürk, 2017).
               Especially in the last decade, greenhouse gas emissions based on
            agricultural sector seem to have increased a great deal in Türkiye. According
            to 1990-2019 Greenhouse gas emission statistics, the total gas emissions




            134 Journal of Environment, Urbanization and Climate,
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