2015
DOI: 10.1007/s11367-015-0950-3
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Modern analysis of an ancient integrated farming arrangement: life cycle assessment of a mulberry dyke and pond system

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Cited by 26 publications
(16 citation statements)
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“…The pond conditions in the IAA systems, which were used as a proxy for methane emissions in this study, came closest to those found in the mixed mangrove concurrent systems (Astudillo et al 2015). However, emissions are highly influenced by farming practices (including aeration, feed use, co-stocked species, and fertilization) and environmental conditions (including salinity, oxygen levels, and temperature) (Alongi 2005;Howe et al 2009;Penha-Lopes et al 2010;Astudillo et al 2015). For example, the presence of sulfates in mangrove systems would limit the activity of methanogenesis (Howe et al 2009), thereby lowering the methane emissions for the mixed mangrove system compared to the IAA system.…”
Section: Case Study Resultsmentioning
confidence: 58%
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“…The pond conditions in the IAA systems, which were used as a proxy for methane emissions in this study, came closest to those found in the mixed mangrove concurrent systems (Astudillo et al 2015). However, emissions are highly influenced by farming practices (including aeration, feed use, co-stocked species, and fertilization) and environmental conditions (including salinity, oxygen levels, and temperature) (Alongi 2005;Howe et al 2009;Penha-Lopes et al 2010;Astudillo et al 2015). For example, the presence of sulfates in mangrove systems would limit the activity of methanogenesis (Howe et al 2009), thereby lowering the methane emissions for the mixed mangrove system compared to the IAA system.…”
Section: Case Study Resultsmentioning
confidence: 58%
“…Moreover, satellite imagery only dated back to the year 2000, and the images only provide rough estimates of vegetation types, while most As mentioned before, research on methane emissions resulting from land use of mangrove area is rather limited and most research on methane fluxes focus on integrated rice-fish ponds (Frei and Becker 2005;Datta et al 2009) or other human disturbances of mangroves (i.e., Konnerup et al 2014). The pond conditions in the IAA systems, which were used as a proxy for methane emissions in this study, came closest to those found in the mixed mangrove concurrent systems (Astudillo et al 2015). However, emissions are highly influenced by farming practices (including aeration, feed use, co-stocked species, and fertilization) and environmental conditions (including salinity, oxygen levels, and temperature) (Alongi 2005;Howe et al 2009;Penha-Lopes et al 2010;Astudillo et al 2015).…”
Section: Case Study Resultsmentioning
confidence: 76%
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“…The unit process dataset for the LCA was supplemented with methane emissions from freshwater ponds, assuming 533 kg ha −1 yr −1 (coefficient of variation (CV)=0.4; lognormal distribution) (Astudillo et al 2015). Emissions resulting from land use and land-use change of mangroves were derived from Järviö et al (2018), assuming 129 tonnes CO 2 eq.…”
Section: Secondary Datamentioning
confidence: 99%