Literature DB >> 22645829

Inconsistent definitions of "urban" result in different conclusions about the size of urban carbon and nitrogen stocks.

Steve M Raciti1, Lucy R Hutyra, Preeti Rao, Adrien C Finzi.   

Abstract

There is conflicting evidence about the importance of urban soils and vegetation in regional C budgets that is caused, in part, by inconsistent definitions of "urban" land use. We quantified urban ecosystem contributions to C stocks in the Boston (Massachusetts, USA) Metropolitan Statistical Area (MSA) using several alternative urban definitions. Development altered aboveground and belowground C and N stocks, and the sign and magnitude of these changes varied by land use and development intensity. Aboveground biomass (live trees, dbh > or = 5 cm) for the MSA was 7.2 +/- 0.4 kg C/m2 (mean +/- SE), reflecting a high proportion of forest cover. Vegetation C was highest in forest (11.6 +/- 0.5 kg C/m2), followed by residential (4.6 +/- 0.5 kg C/m2), and then other developed (2.0 +/- 0.4 kg C/m2) land uses. Soil C (0-10 cm depth) followed the same pattern of decreasing C concentration from forest, to residential, to other developed land uses (4.1 +/- 0.1, 4.0 +/- 0.2, and 3.3 +/- 0.2 kg C/m2, respectively). Within a land use type, urban areas (which we defined as > 25% impervious surface area [ISA] within a 1-km(2) moving window) generally contained less vegetation C, but slightly more soil C, than nonurban areas. Soil N concentrations were higher in urban areas than nonurban areas of the same land use type, except for residential areas, which had similarly high soil N concentrations. When we compared our definition of urban to other commonly used urban extents (U.S. Census Bureau, Global Rural-Urban Mapping Project [GRUMP], and the MSA itself), we found that urban soil (1 m depth) and vegetation C stocks spanned a wide range, from 14.4 +/- 0.8 to 54.5 +/- 3.4 Tg C and from 4.2 +/- 0.4 to 27.3 +/- 3.2 Tg C, respectively. Conclusions about the importance of urban soils and vegetation to regional C and N stocks are very sensitive to the definition of urban used by the investigators. Urban areas, regardless of definition, are rapidly expanding in their extent; a systematic understanding of how our development patterns influence ecosystems is necessary to inform future development choices.

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Year:  2012        PMID: 22645829     DOI: 10.1890/11-1250.1

Source DB:  PubMed          Journal:  Ecol Appl        ISSN: 1051-0761            Impact factor:   4.657


  5 in total

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Authors:  Gordon M Fitch
Journal:  Oecologia       Date:  2017-10-23       Impact factor: 3.225

2.  Density and stability of soil organic carbon beneath impervious surfaces in urban areas.

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Journal:  PLoS One       Date:  2014-10-09       Impact factor: 3.240

3.  Building houses and managing lawns could limit yard soil carbon for centuries.

Authors:  Morgan E Peach; Laura A Ogden; Eleni A Mora; Andrew J Friedland
Journal:  Carbon Balance Manag       Date:  2019-08-16

4.  Tree Productivity Enhanced with Conversion from Forest to Urban Land Covers.

Authors:  Brittain M Briber; Lucy R Hutyra; Andrew B Reinmann; Steve M Raciti; Victoria K Dearborn; Christopher E Holden; Allison L Dunn
Journal:  PLoS One       Date:  2015-08-24       Impact factor: 3.240

5.  Methane uptake in forest soils along an urban-to-rural gradient in Pearl River Delta, South China.

Authors:  Wei Zhang; Keya Wang; Yiqi Luo; Yunting Fang; Junhua Yan; Tao Zhang; Xiaomin Zhu; Hao Chen; Wantong Wang; Jiangming Mo
Journal:  Sci Rep       Date:  2014-05-30       Impact factor: 4.379

  5 in total

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