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references.bib
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@InCollection{liuBaselineProjectedFuture2014,
title = {Baseline and {{Projected Future Carbon Storage}}, {{Carbon Sequestration}}, and {{Greenhouse-Gas Fluxes}} in {{Terrestrial Ecosystems}} of the {{Eastern United States}}},
author = {Shuguang Liu and Jinxun Liu and Yiping Wu and Claudia Young and Jeremy Werner and Devendra Dahal and Jennifer Oeding and Gail Schmidt},
date = {2014},
series = {Professional {{Paper}}},
langid = {english},
}
@Article{selhorstNetCarbonSequestration2013,
title = {Net {{Carbon Sequestration Potential}} and {{Emissions}} in {{Home Lawn Turfgrasses}} of the {{United States}}},
author = {Adam Selhorst and Rattan Lal},
date = {2013-01},
journaltitle = {Environmental Management},
shortjournal = {Environmental Management},
volume = {51},
number = {1},
pages = {198--208},
issn = {0364-152X, 1432-1009},
doi = {10.1007/s00267-012-9967-6},
url = {http://link.springer.com/10.1007/s00267-012-9967-6},
urldate = {2024-05-09},
abstract = {Soil analyses were conducted on home lawns across diverse ecoregions of the U.S. to determine the soil organic carbon (SOC) sink capacity of turfgrass soils. Establishment of lawns sequestered SOC over time. Due to variations in ecoregions, sequestration rates varied among sites from 0.9 Mg carbon (C) ha-1 year-1 to 5.4 Mg C ha-1 year-1. Potential SOC sink capacity also varied among sites ranging from 20.8 ± 1.0–96.3 ± 6.0 Mg C ha-1. Average sequestration rate and sink capacity for all sites sampled were 2.8 ± 0.3 Mg C ha-1 year-1 and 45.8 ± 3.5 Mg C ha-1, respectively. Additionally, the hidden carbon costs (HCC) due to lawn mowing (189.7 kg Ce (carbon equivalent) ha-1 year-1) and fertilizer use (63.6 kg Ce ha-1 year-1) for all sites totaled 254.3 kg Ce ha-1 year-1. Considering home lawn SOC sink capacity and HCC, mean home lawn sequestration was completely negated 184 years post establishment. The potential SOC sink capacity of home lawns in the U.S. was estimated at 496.3 Tg C, with HCC of between 2,504.1 Gg Ce year-1 under low management regimes and 7551.4 Gg Ce year-1 under high management. This leads to a carbon-positive system for between 66 and 199 years in U.S. home lawns. More efficient and reduction of C-intensive maintenance practices could increase the overall sequestration longevity of home lawns and improve their climate change mitigation potential.},
langid = {english},
}
@Article{nahlikCarbonStorageUS2016,
title = {Carbon Storage in {{US}} Wetlands},
author = {A. M. Nahlik and M. S. Fennessy},
date = {2016-12-13},
journaltitle = {Nature Communications},
shortjournal = {Nat Commun},
volume = {7},
number = {1},
pages = {13835},
publisher = {Nature Publishing Group},
issn = {2041-1723},
doi = {10.1038/ncomms13835},
url = {https://www.nature.com/articles/ncomms13835},
urldate = {2024-02-26},
abstract = {Wetland soils contain some of the highest stores of soil carbon in the biosphere. However, there is little understanding of the quantity and distribution of carbon stored in our remaining wetlands or of the potential effects of human disturbance on these stocks. Here we use field data from the 2011 National Wetland Condition Assessment to provide unbiased estimates of soil carbon stocks for wetlands at regional and national scales. We find that wetlands in the conterminous United States store a total of 11.52\,PgC, much of which is within soils deeper than 30\,cm. Freshwater inland wetlands, in part due to their substantial areal extent, hold nearly ten-fold more carbon than tidal saltwater sites—indicating their importance in regional carbon storage. Our data suggest a possible relationship between carbon stocks and anthropogenic disturbance. These data highlight the need to protect wetlands to mitigate the risk of avoidable contributions to climate change.},
issue = {1},
langid = {english},
keywords = {Carbon cycle,Wetlands ecology},
}