The regulatory ecosystem services in terms of carbon sequestration and translation - The regulatory ecosystem services in terms of carbon sequestration and English how to say

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The regulatory ecosystem services in terms of carbon sequestration and storage by Indian seagrass ecosystemswere coupled with their monetary values in the context of climate change mitigation in the seagrass meadows ofPalk Bay and Chilika Lagoon, two major seagrass ecosystems of India. The results showed that the meadowsacted as a net sink of atmospheric CO2; however, they may also act as a minor source of CO2 to the atmospheredepending on the degree of anthropogenic influence. The mean ecosystem productivity ranged between 6.31 and11.9 kg C ha−1d−1, which is equivalent to the capture of 8.44 and 15.9 Mg CO2 ha−1 year−1. This capturedcarbon was apportioned primarily in sediments (129 Mg Corg ha−1 in top 1 m soil), which was much higher thanthe carbon stored as above and below ground biomass (0.20–0.96 Mg Corg ha−1 and 0.30–2.90 Mg Corg ha−1,respectively). The economic valuation of regulatory ecosystem services in the form of C sequestration by anestimated 51,700 ha of total seagrass cover in India was largely dependent on the sequestration rates and theaverage social cost of carbon. The estimated values ranged between $ 1.02 million and $ 3.65 million per year. Inaddition, monetary values of the stored carbon in live biomass of Indian seagrass systems ranged between $ 0.45million and $ 3.89 million, whereas, in the top 1 m soil it ranged between $ 109 million and $ 146 million.Detailed evaluations of various ecosystem functions considering the importance of the local variables mayprovide a better monetary estimate of these regulatory services.
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The regulatory ecosystem services in terms of carbon sequestration and storage by Indian seagrass ecosystems<br>were coupled with their monetary values in the context of climate change mitigation in the seagrass meadows of<br>Palk Bay and Chilika Lagoon, two major seagrass ecosystems of India. The results showed that the meadows<br>acted as a net sink of atmospheric CO2; however, they may also act as a minor source of CO2 to the atmosphere<br>depending on the degree of anthropogenic influence. The mean ecosystem productivity ranged between 6.31 and<br>11.9 kg C ha−1d−1, which is equivalent to the capture of 8.44 and 15.9 Mg CO2 ha−1 year−1. This captured<br>carbon was apportioned primarily in sediments (129 Mg Corg ha−1 in top 1 m soil), which was much higher than<br>the carbon stored as above and below ground biomass (0.20–0.96 Mg Corg ha−1 and 0.30–2.90 Mg Corg ha−1,<br>respectively). The economic valuation of regulatory ecosystem services in the form of C sequestration by an<br>estimated 51,700 ha of total seagrass cover in India was largely dependent on the sequestration rates and the<br>average social cost of carbon. The estimated values ranged between $ 1.02 million and $ 3.65 million per year. In<br>addition, monetary values of the stored carbon in live biomass of Indian seagrass systems ranged between $ 0.45<br>million and $ 3.89 million, whereas, in the top 1 m soil it ranged between $ 109 million and $ 146 million.<br>Detailed evaluations of various ecosystem functions considering the importance of the local variables may<br>provide a better monetary estimate of these regulatory services.
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The regulatory ecosystem services in terms of carbon sequestration and storage by Indian seagrass ecosystems<br>were coupled with their monetary values in the context of climate change mitigation in the seagrass meadows of<br>Palk Bay and Chilika Lagoon, two major seagrass ecosystems of India. The results showed that the meadows<br>acted as a net sink of atmospheric CO2; however, they may also act as a minor source of CO2 to the atmosphere<br>depending on the degree of anthropogenic influence. The mean ecosystem productivity ranged between 6.31 and<br>11.9 kg C ha−1d−1, which is equivalent to the capture of 8.44 and 15.9 Mg CO2 ha−1 year−1. This captured<br>carbon was apportioned primarily in sediments (129 Mg Corg ha−1 in top 1 m soil), which was much higher than<br>the carbon stored as above and below ground biomass (0.20–0.96 Mg Corg ha−1 and 0.30–2.90 Mg Corg ha−1,<br>respectively). The economic valuation of regulatory ecosystem services in the form of C sequestration by an<br>estimated 51,700 ha of total seagrass cover in India was largely dependent on the sequestration rates and the<br>average social cost of carbon. The estimated values ranged between $ 1.02 million and $ 3.65 million per year. In<br>addition, monetary values of the stored carbon in live biomass of Indian seagrass systems ranged between $ 0.45<br>million and $ 3.89 million, whereas, in the top 1 m soil it ranged between $ 109 million and $ 146 million.<br>Detailed evaluations of various ecosystem functions considering the importance of the local variables may<br>provide a better monetary estimate of these regulatory services.
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Regulation of seaweed ecosystem on Carbonate Sequence Stratigraphy and reservoir in India<br>They are related to the monetary value of climate change to seaweed.<br>Pax Bay and chilika lagoon are two major marine ecosystems in India.<br>However, they can also be used as a source of CO2 in the atmosphere.<br>According to the degree of human impact on the ecosystem, 6.31 and<br>1.9.kg, C, 1.kg, equal to 8.44 and 15.9.mg of CO2 captured<br>Carbon is mainly distributed in sediments, such as 129 mg kohar, at the top of a soil 41, which is higher<br>Carbon is stored in aboveground and underground organisms, such as 0.20.96 mg, one and 0.30.2.90 mg, and one<br>On the economic evaluation of ecological regulation system in C sequence stratigraphy<br>The estimated total seagrass area in India is largely dependent on sequence and sequence.<br>The estimated average social cost of carbon ranges from □ 361.02 to □ 365 million years.<br>Plus the monetary value of stored carbon in the seaweed biosystem of India<br>Million and 363.89 million, at the top, it's between 10369 and 366.<br>Considering the importance of local variables, the evaluation of different ecosystem functions was detailed.<br>Provide better monetary estimates for these regulatory services.<br>
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