Voigt, Carolina; van Delden, Lona; Marushchak, Maija E; Biasi, Christina; Abbott, Benjamin W; Elberling, Bo; Siciliano, Steven D; Sonnentag, Oliver; Stewart, Katherine J; Yang, Yuanhe; Martikainen, Pertti J (2020): Nitrous oxide fluxes from permafrost regions [dataset]. PANGAEA, https://doi.org/10.1594/PANGAEA.919217
Always quote citation above when using data! You can download the citation in several formats below.
Abstract:
This dataset is a synthesis of published nitrous oxide (N2O) fluxes from permafrost-affected soils in Arctic, Antarctic, and Alpine permafrost regions. The data includes mean N2O flux rates measured under field (in situ) conditions and in intact plant-soil systems (mesocosms) under near-field conditions. The dataset further includes explanatory environmental parameters such as meteorological data, soil physical-chemical properties, as well as site and experimental information. Data has been synthesized from published studies (see 'Further details'), and in some cases the authors of published studies have been contacted for additional site-level information. The dataset includes studies published until 2019.
We encourage linking additional N2O flux data from unpublished and future studies with similar metadata structure to this dataset, to produce a comprehensive, findable database for N2O fluxes from permafrost regions.
Supplement to:
Voigt, Carolina; Marushchak, Maija E; Abbott, Benjamin W; Biasi, Christina; Elberling, Bo; Siciliano, Steven D; Sonnentag, Oliver; Stewart, Katherine J; Yang, Yuanhe; Martikainen, Pertti J (2020): Nitrous oxide emissions from permafrost-affected soils. Nature Reviews Earth and Environment, https://doi.org/10.1038/s43017-020-0063-9
Further details:
Altshuler, Ianina; Ronholm, Jennifer; Layton, Alice; Onstott, T C; Greer, Charles W; Whyte, Lyle G (2019): Denitrifiers, nitrogen-fixing bacteria and N2O soil gas flux in high Arctic ice-wedge polygon cryosols. FEMS Microbiology Ecology, 95(5), https://doi.org/10.1093/femsec/fiz049
Bao, Tao; Zhu, Renbin; Wang, Pei; Ye, Wenjuan; Ma, Dawei; Xu, Hua (2018): Potential effects of ultraviolet radiation reduction on tundra nitrous oxide and methane fluxes in maritime Antarctica. Scientific Reports, 8(1), https://doi.org/10.1038/s41598-018-21881-1
Brummell, Martin E; Farrell, Richard E; Hardy, Sarah P; Siciliano, Steven D (2014): Greenhouse gas production and consumption in High Arctic deserts. Soil Biology and Biochemistry, 68, 158-165, https://doi.org/10.1016/j.soilbio.2013.09.034
Brummell, Martin E; Farrell, Richard E; Siciliano, Steven D (2012): Greenhouse gas soil production and surface fluxes at a high arctic polar oasis. Soil Biology and Biochemistry, 52, 1-12, https://doi.org/10.1016/j.soilbio.2012.03.019
Cao, Yingfang; Ke, Xun; Guo, Xiaowei; Cao, Guangmin; Du, Yangong (2018): Nitrous Oxide Emission Rates over 10 Years in an Alpine Meadow on the Tibetan Plateau. Polish Journal of Environmental Studies, 27(3), 1353-1358, https://doi.org/10.15244/pjoes/76795
Chang, Ruiying; Wang, Genxu; Yang, Yuanhe; Chen, Xu (2017): Experimental warming increased soil nitrogen sink in the Tibetan permafrost. Journal of Geophysical Research: Biogeosciences, 122(7), 1870-1879, https://doi.org/10.1002/2017JG003827
Chen, Q; Zhu, Renbin; Wang, Qing; Xu, Hua (2014): Methane and nitrous oxide fluxes from four tundra ecotopes in Ny-Ålesund of the High Arctic. Journal of Environmental Sciences, 26(7), 1403-1410, https://doi.org/10.1016/j.jes.2014.05.005
Chen, Xu; Wang, Genxu; Zhang, Tao; Mao, Tianxu; Wei, Da; Hu, Zhaoyong; Song, C (2017): Effects of warming and nitrogen fertilization on GHG flux in the permafrost region of an alpine meadow. Atmospheric Environment, 157, 111-124, https://doi.org/10.1016/j.atmosenv.2017.03.024
Christensen, Torben R; Michelsen, Anders; Jonasson, Sven E (1999): Exchange of CH4 and N2O in a subarctic heath soil: effects of inorganic N and P and amino acid addition. Soil Biology and Biochemistry, 31(4), 637-641, https://doi.org/10.1016/S0038-0717(98)00166-7
Cui, Qian; Song, C; Wang, Xianwei; Shi, Fuxi; Yu, Xueyang; Tan, Wenwen (2018): Effects of warming on N2O fluxes in a boreal peatland of Permafrost region, Northeast China. Science of the Total Environment, 616-617, 427-434, https://doi.org/10.1016/j.scitotenv.2017.10.246
Dinsmore, Kerry J; Drewer, Julia; Levy, Peter E; George, Ejin; Lohila, Annalea; Aurela, Mika; Skiba, Ute Maria (2017): Growing season CH4 and N2O fluxes from a subarctic landscape in northern Finland; from chamber to landscape scale. Biogeosciences, 14(4), 799-815, https://doi.org/10.5194/bg-14-799-2017
Du, Yangong; Cui, Yingguang; Xu, Xingliang; Liang, Dongying; Long, Ruijun; Cao, Guangmin (2008): Nitrous oxide emissions from two alpine meadows in the Qinghai–Tibetan Plateau. Plant and Soil, 311(1-2), 245-254, https://doi.org/10.1007/s11104-008-9727-9
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Du, Yangong; Guo, Xiaowei; Cao, Guangmin; Wang, Bin; Pan, Guoyan; Liu, De Li (2016): Simulation and prediction of nitrous oxide emission by the water and nitrogen management model on the Tibetan plateau. Biochemical Systematics and Ecology, 65, 49-56, https://doi.org/10.1016/j.bse.2016.02.002
Elberling, Bo; Christiansen, Hanne Hvidtfeldt; Hansen, Birger Ulf (2010): High nitrous oxide production from thawing permafrost. Nature Geoscience, 3(5), 332-335, https://doi.org/10.1038/ngeo803
Gao, Weifeng; Yao, Yunlong; Liang, Hong; Song, L; Sheng, Houcai; Cai, Tijiu; Gao, Dawen (2019): Emissions of nitrous oxide from continuous permafrost region in the Daxing'an Mountains, Northeast China. Atmospheric Environment, 198, 34-45, https://doi.org/10.1016/j.atmosenv.2018.10.045
Gil, Jenie; Pérez, Tibisay; Boering, K; Martikainen, Pertti J; Biasi, Christina (2017): Mechanisms responsible for high N2O emissions from subarctic permafrost peatlands studied via stable isotope techniques. Global Biogeochemical Cycles, 31(1), 172-189, https://doi.org/10.1002/2015GB005370
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Jiang, Chunming; Yu, G; Fang, Huajun; Cao, Guangmin; Li, Y (2010): Short-term effect of increasing nitrogen deposition on CO2, CH4 and N2O fluxes in an alpine meadow on the Qinghai-Tibetan Plateau, China. Atmospheric Environment, 44(24), 2920-2926, https://doi.org/10.1016/j.atmosenv.2010.03.030
Kato, Tomomichi; Hirota, Marina; Tang, Y; Wada, Eitaro (2011): Spatial variability of CH4 and N2O fluxes in alpine ecosystems on the Qinghai–Tibetan Plateau. Atmospheric Environment, 45(31), 5632-5639, https://doi.org/10.1016/j.atmosenv.2011.03.010
Kato, Tomomichi; Toyoda, Sakae; Yoshida, Naohiro; Tang, Y; Wada, Eitaro (2013): Isotopomer and isotopologue signatures of N2O produced in alpine ecosystems on the Qinghai-Tibetan Plateau. Rapid Communications in Mass Spectrometry, 27(13), 1517-1526, https://doi.org/10.1002/rcm.6595
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Köster, Egle; Köster, Kajar; Berninger, Frank; Aaltonen, Heidi; Zhou, Xuan; Pumpanen, Jukka (2017): Carbon dioxide, methane and nitrous oxide fluxes from a fire chronosequence in subarctic boreal forests of Canada. Science of the Total Environment, 601-602, 895-905, https://doi.org/10.1016/j.scitotenv.2017.05.246
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Li, Fengjiang; Zhu, Renbin; Bao, Tao; Wang, Qing; Xu, Hua (2016): Sunlight stimulates methane uptake and nitrous oxide emission from the High Arctic tundra. Science of the Total Environment, 572, 1150-1160, https://doi.org/10.1016/j.scitotenv.2016.08.026
Li, Y; Dong, Shikui; Liu, Shiliang; Zhou, Huakun; Gao, Qingzhu; Cao, Guangmin; Wang, Xuexia; Su, Xukun; Zhang, Yong; Tang, Lin; Zhao, Haidi; Wu, Xiaoyu (2015): Seasonal changes of CO2, CH4 and N2O fluxes in different types of alpine grassland in the Qinghai-Tibetan Plateau of China. Soil Biology and Biochemistry, 80, 306-314, https://doi.org/10.1016/j.soilbio.2014.10.026
Lin, X; Wang, S; Ma, Xiuzhi; Xu, Guangping; Luo, Caiyun; Li, Y; Jiang, Gaoming; Xie, Z (2009): Fluxes of CO2, CH4, and N2O in an alpine meadow affected by yak excreta on the Qinghai-Tibetan plateau during summer grazing periods. Soil Biology and Biochemistry, 41(4), 718-725, https://doi.org/10.1016/j.soilbio.2009.01.007
Liu, Xingren; Zhang, Qingwen; Li, Sijia; Zhang, Leiming; Ren, Jianqiang (2017): Simulated NH 4+-N Deposition Inhibits CH4 Uptake and Promotes N2O Emission in the Meadow Steppe of Inner Mongolia, China. Pedosphere, 27(2), 306-317, https://doi.org/10.1016/S1002-0160(17)60318-7
Ma, Wai K; Schautz, Alexandra; Fishback, Lee-Ann E; Bedard-Haughn, Angela; Farrell, Richard E; Siciliano, Steven D (2007): Assessing the potential of ammonia oxidizing bacteria to produce nitrous oxide in soils of a high arctic lowland ecosystem on Devon Island, Canada. Soil Biology and Biochemistry, 39(8), 2001-2013, https://doi.org/10.1016/j.soilbio.2007.03.001
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Morishita, T; Matsuura, Yojiro; Kajimoto, Takuya; Osawa, Akira; Zyryanova, Olga A; Prokushkin, Anatoly S (2014): CH4 and N2O dynamics of a Larix gmelinii forest in a continuous permafrost region of central Siberia during the growing season. Polar Science, 8(2), 156-165, https://doi.org/10.1016/j.polar.2014.01.004
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Coverage:
Median Latitude: 41.597664 * Median Longitude: 144.646352 * South-bound Latitude: -78.020000 * West-bound Longitude: 11.930000 * North-bound Latitude: 82.580000 * East-bound Longitude: -20.500000
Date/Time Start: 1991-07-22T00:00:00 * Date/Time End: 2016-09-30T00:00:00
Event(s):
Abisko_N2O * Latitude: 68.330000 * Longitude: 20.850000 * Date/Time Start: 1996-07-03T00:00:00 * Date/Time End: 1996-08-28T00:00:00 * Location: Sweden
Comment:
If not reported, water-filled pore space (WFPS) was calculated as follows: WFPS (%) = VWC/(1-BD/PD)*100, where VWC is the volumetric water content, BD is the bulk density, and PD is the particle density. If BD was not reported, BD was estimated from the SOM content using functions developed for Arctic soils (Hossain et al, 2015) as follows: 0.075+1.301*EXP(-0.06*SOM) for mineral soils, and 0.043*0+4.258*EXP(-0.047*SOM) for organic soils. If not reported, SOM via loss on ignition was derived from the soil carbon content as follows: SOM (%) = C content*2. If the resulting SOM value was >100%, SOM (%) = C content*1.724. PD can be derived as follows (Okruszko, 1971): PD = 0.011*(100-SOM)+1.451 (see references Okruszko, 1971 and Hossain et al, 2015).
The term "topsoil" depends on the exact depths the soil characteristics are reported in the individual publications, but generally the soil layer of 0–10cm was used.
Column "SOC" includes mostly total soil C content (reported in the majority of studies), and on some occasions total organic C.
Parameter(s):
# | Name | Short Name | Unit | Principal Investigator | Method/Device | Comment |
---|---|---|---|---|---|---|
1 | Event label | Event | Voigt, Carolina | |||
2 | Sample code/label | Sample label | Voigt, Carolina | |||
3 | Nitrous oxide, flux, in mass nitrous oxide | N2O flux | µg/m2/day | Voigt, Carolina | ||
4 | Permafrost extent | Permafrost ext | Voigt, Carolina | permafrost coverage | ||
5 | Zone | Zone | Voigt, Carolina | permafrost region | ||
6 | Ecosystem | Ecosystem | Voigt, Carolina | ecosystem type | ||
7 | Vegetation type | Vegetation type | Voigt, Carolina | vegetation coverage | ||
8 | Location | Location | Voigt, Carolina | description of landcover mass | ||
9 | Country | Country | Voigt, Carolina | country the measurement was taken in | ||
10 | Area/locality | Area | Voigt, Carolina | subregion | ||
11 | Site | Site | Voigt, Carolina | |||
12 | LATITUDE | Latitude | Voigt, Carolina | Geocode | ||
13 | LONGITUDE | Longitude | Voigt, Carolina | Geocode | ||
14 | Number of measurement seasons | N meas seasons | # | Voigt, Carolina | number of measurement seasons included in the flux estimate | |
15 | Year of observation | Year obs | a AD | Voigt, Carolina | year the measurement period started | |
16 | Month | Month | Voigt, Carolina | month the measurement period started | ||
17 | Day | Day | Voigt, Carolina | day the measurement period started | ||
18 | Year of observation | Year obs | a AD | Voigt, Carolina | year the measurement period ended | |
19 | Month | Month | Voigt, Carolina | month the measurement period ended | ||
20 | Day | Day | Voigt, Carolina | day the measurement period ended | ||
21 | Organic carbon, soil | SOC | % | Voigt, Carolina | Carbon content in topsoil | |
22 | Nitrogen, soil | SN | % | Voigt, Carolina | Nitrogen content in topsoil | |
23 | Carbon/Nitrogen ratio | C/N | Voigt, Carolina | C/N ratio in topsoil | ||
24 | Ammonium | NH4 | mg/kg | Voigt, Carolina | Ammonium content in topsoil, mass nitrogen per mass dry weight of soil (mg NH4-N per kg DW) | |
25 | Nitrate | NO3 | mg/kg | Voigt, Carolina | Nitrate content in topsoil, mass nitrogen per mass dry weight of soil (mg NH4-N per kg DW) | |
26 | pH, soil | pH soil | Voigt, Carolina | pH in topsoil | ||
27 | Soil organic matter | Soil OM | % | Voigt, Carolina | ||
28 | Density, active layer, bulk | BD act layer | g/cm3 | Voigt, Carolina | bulk density of topsoil/active layer | |
29 | Soil moisture | Soil moisture | % | Voigt, Carolina | ||
30 | Soil water content, gravimetric | grav SWC | g/g | Voigt, Carolina | gravimetric water content reported in g H2O per g dry weight of soil | |
31 | Soil water content, volumetric | vol SWC | m3/m3 | Voigt, Carolina | ||
32 | Water holding capacity | WHC | % | Voigt, Carolina | ||
33 | Water filled pore space | WFPS | % | Voigt, Carolina | ||
34 | Water filled pore space, calculated | WFPS calc | % | Voigt, Carolina | calculated water-filled pore space if not reported in papers, based on other soil moisture parameters | |
35 | Temperature, air, annual mean | MAAT | °C | Voigt, Carolina | mean annual air temperature at study site | |
36 | Temperature, air | TTT | °C | Voigt, Carolina | actual air temperature during measurement period | |
37 | Temperature, soil | T soil | °C | Voigt, Carolina | actual soil temperature during measurement period | |
38 | Precipitation, annual mean | MAP | mm | Voigt, Carolina | ||
39 | Thaw depth of active layer, mean | Thaw depth mean | cm | Voigt, Carolina | mean thaw depth during growing season | |
40 | Thaw depth of active layer, maximum | Thaw depth max | cm | Voigt, Carolina | maximum thaw / active layer depth | |
41 | Type of study | Study type | Voigt, Carolina | study type | ||
42 | Hemeroby/disturbance | Hemeroby/disturbance | Voigt, Carolina | |||
43 | Experimental treatment | Exp treat | Voigt, Carolina | experimental manipulation | ||
44 | Disturbance Type | Disturbance Type | Voigt, Carolina | |||
45 | Number of measurements | n | # | Voigt, Carolina | number of N2O flux measurements included in the N2O estimate in n2o.flux | |
46 | Replicates | Repl | # | Voigt, Carolina | replicate collars per landcover class used in n2o.flux estimate | |
47 | Original value | Orig val | Voigt, Carolina | original value of N2O flux reported in publication | ||
48 | Original unit | Orig unit | Voigt, Carolina | original unit of N2O flux reported in publication | ||
49 | Analytical method | Method | Voigt, Carolina | measurement method (GC/static=manual syringe sampling followed by GC analysis; portable gas analyzer=direct flux measurement with dynamic chamber; snow/soil gradient=flux calculated from concentration gradient) | ||
50 | Type of chamber | Chamber type | Voigt, Carolina | chamber type | ||
51 | Time in minutes | Time | min | Voigt, Carolina | ||
52 | Time in minutes | Time | min | Voigt, Carolina | maximum closure time of chamber during measurement | |
53 | Number of points | Points | # | Voigt, Carolina | concentration time points measured during measurement | |
54 | Presence/absence | Presence/absence | Voigt, Carolina | CO2 fluxes reported in the same paper | ||
55 | Presence/absence | Presence/absence | Voigt, Carolina | CH4 fluxes reported in the same paper | ||
56 | Publication of data | Publ data | Voigt, Carolina | |||
57 | Reference of data | Ref data | Voigt, Carolina | reference for publication with N2O flux data |
License:
Creative Commons Attribution 4.0 International (CC-BY-4.0)
Size:
10302 data points
Data
1 Event | 2 Sample label | 3 N2O flux [µg/m2/day] | 4 Permafrost ext (permafrost coverage) | 5 Zone (permafrost region) | 6 Ecosystem (ecosystem type) | 7 Vegetation type (vegetation coverage) | 8 Location (description of landcover mass) | 9 Country (country the measurement was t...) | 10 Area (subregion) | 11 Site | 12 Latitude | 13 Longitude | 14 N meas seasons [#] (number of measurement seasons...) | 15 Year obs [a AD] (year the measurement period s...) | 16 Month (month the measurement period ...) | 17 Day (day the measurement period st...) | 18 Year obs [a AD] (year the measurement period e...) | 19 Month (month the measurement period ...) | 20 Day (day the measurement period ended) | 21 SOC [%] (Carbon content in topsoil) | 22 SN [%] (Nitrogen content in topsoil) | 23 C/N (C/N ratio in topsoil) | 24 NH4 [mg/kg] (Ammonium content in topsoil, ...) | 25 NO3 [mg/kg] (Nitrate content in topsoil, m...) | 26 pH soil (pH in topsoil) | 27 Soil OM [%] | 28 BD act layer [g/cm3] (bulk density of topsoil/activ...) | 29 Soil moisture [%] | 30 grav SWC [g/g] (gravimetric water content rep...) | 31 vol SWC [m3/m3] | 32 WHC [%] | 33 WFPS [%] | 34 WFPS calc [%] (calculated water-filled pore ...) | 35 MAAT [°C] (mean annual air temperature a...) | 36 TTT [°C] (actual air temperature during...) | 37 T soil [°C] (actual soil temperature durin...) | 38 MAP [mm] | 39 Thaw depth mean [cm] (mean thaw depth during growin...) | 40 Thaw depth max [cm] (maximum thaw / active layer d...) | 41 Study type (study type) | 42 Hemeroby/disturbance | 43 Exp treat (experimental manipulation) | 44 Disturbance Type | 45 n [#] (number of N2O flux measuremen...) | 46 Repl [#] (replicate collars per landcov...) | 47 Orig val (original value of N2O flux re...) | 48 Orig unit (original unit of N2O flux rep...) | 49 Method (measurement method (GC/static...) | 50 Chamber type (chamber type) | 51 Time [min] | 52 Time [min] (maximum closure time of chamb...) | 53 Points [#] (concentration time points mea...) | 54 Presence/absence (CO2 fluxes reported in the sa...) | 55 Presence/absence (CH4 fluxes reported in the sa...) | 56 Publ data | 57 Ref data (reference for publication wit...) |
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Ardley_Island_N2O | AN-Ard-2011-01 | 4.80 | antarctic | Antarctic | Wetland | Vegetated | Western coastal lowland tundra marsh | Antarctica | maritime Antarctica | Ardley Island | -62.22 | -58.93 | 1 | 2011 | 12 | 1 | 2012 | 2 | 21 | 2.26 | 0.27 | 8.40 | 9.84 | 15.61 | 6.5 | 85.80 | 100.000 | -2.5 | 1.6 | 4.1 | 630 | In situ | No | No | none | 8 | 3 | 0.20 | µg N2O/m2/h | GC/static | transparent | 20 | 3 | no | yes | yes | Bao T et al. 2018 | |||||||||
Ardley_Island_N2O | AN-Ard-2007-01 | 998.40 | antarctic | Antarctic | Wetland | Vegetated | Tundra dry marsh (DM); Mosses and algae dominate the vegetation in the poorly drained tundra areas | Antarctica | maritime Antarctica | Ardley Island | -62.22 | -58.93 | 1 | 2008 | 1 | 21 | 2008 | 2 | 8 | 22.91 | 2.23 | 10.20 | 131.31 | 4.23 | 6.0 | 24.90 | 5.686 | -2.2 | 0.9 | 425 | In situ | Yes | No | Birds | 10 | 3 | 41.60 | µg N2O/m2/h | GC/static | transparent | 20 | 3 | yes | yes | yes | Zhu R et al. 2014 | ||||||||||
Ardley_Island_N2O | AN-Ard-2007-02 | 52.80 | antarctic | Antarctic | Wetland | Vegetated | Tundra mesic marsh (MM); Mosses and algae dominate the vegetation in the poorly drained tundra areas | Antarctica | maritime Antarctica | Ardley Island | -62.22 | -58.93 | 1 | 2008 | 1 | 21 | 2008 | 2 | 8 | 25.50 | 1.96 | 13.20 | 89.30 | 4.03 | 6.0 | 45.23 | 12.055 | -2.2 | 0.9 | 425 | In situ | Yes | No | Birds | 10 | 3 | 2.20 | µg N2O/m2/h | GC/static | transparent | 20 | 3 | yes | yes | yes | Zhu R et al. 2014 | ||||||||||
Ardley_Island_N2O | AN-Ard-2007-03 | 56.40 | antarctic | Antarctic | Upland | Vegetated | Upland tundra with lichens and mosses (UT); mosses (Bryum Pseudotriquetrum and Bryum muelthenbeckii) and lichens (Usnea sp.) | Antarctica | maritime Antarctica | Ardley Island | -62.05 | -58.25 | 1 | 2007 | 11 | 25 | 2008 | 2 | 8 | 1.17 | 0.10 | 12.00 | 1.20 | 0.51 | 6.6 | 17.60 | 49.274 | -2.2 | 0.9 | 425 | In situ | No | No | none | 12 | 3 | 2.35 | µg N2O/m2/h | GC/static | transparent | 20 | 3 | yes | yes | yes | Zhu R et al. 2014 | ||||||||||
Ardley_Island_N2O | AN-Ard-2007-04 | -72.00 | antarctic | Antarctic | Wetland | Vegetated | Tundra waterlogged marsh (WM); Mosses and algae dominate the vegetation in the poorly drained tundra areas. | Antarctica | maritime Antarctica | Ardley Island | -62.22 | -58.93 | 1 | 2008 | 1 | 21 | 2008 | 2 | 8 | 22.77 | 2.09 | 12.00 | 175.05 | 3.73 | 5.9 | 90.00 | 100 | 100.000 | -2.2 | 0.9 | 425 | In situ | Yes | No | Birds | 10 | 3 | -3.00 | µg N2O/m2/h | GC/static | transparent | 20 | 3 | yes | yes | yes | Zhu R et al. 2014 | |||||||||
Ardley_Island_N2O | AN-Ard-2011-07 | 267.60 | antarctic | Antarctic | Upland | Vegetated | Upland tundra with lichens and mosses (UT); mosses (Bryum Pseudotriquetrum and Bryum muelthenbeckii) and lichens (Usnea sp.) | Antarctica | maritime Antarctica | Ardley Island | -62.05 | -58.25 | 1 | 2012 | 1 | 16 | 2012 | 2 | 8 | 1.17 | 0.10 | 12.00 | 1.20 | 0.51 | 6.6 | 17.60 | 49.274 | -2.2 | 1.7 | 425 | In situ | No | No | none | 9 | 3 | 11.15 | µg N2O/m2/h | GC/static | transparent | 20 | 3 | yes | yes | yes | Zhu R et al. 2014 | ||||||||||
Ardley_Island_N2O | AN-Ard-2011-08 | -646.80 | antarctic | Antarctic | Wetland | Vegetated | Tundra waterlogged marsh (WM); Mosses and algae dominate the vegetation in the poorly drained tundra areas. | Antarctica | maritime Antarctica | Ardley Island | -62.22 | -58.93 | 1 | 2011 | 12 | 24 | 2012 | 2 | 5 | 22.77 | 2.09 | 12.00 | 175.05 | 3.73 | 5.9 | 90.00 | 100 | 100.000 | -2.2 | 1.7 | 425 | In situ | Yes | No | Birds | 8 | 3 | -26.95 | µg N2O/m2/h | GC/static | transparent | 20 | 3 | yes | yes | yes | Zhu R et al. 2014 | |||||||||
Ardley_Island_N2O | AN-Ard-2011-02 | 292.80 | antarctic | Antarctic | Wetland | Vegetated | Western coastal lowland tundra marsh | Antarctica | maritime Antarctica | Ardley Island | -62.22 | -58.93 | 1 | 2011 | 12 | 1 | 2012 | 2 | 21 | 2.24 | 0.23 | 9.70 | 8.97 | 31.92 | 6.7 | 81.00 | 100.000 | -2.5 | 1.6 | 4.1 | 630 | In situ | Yes | Yes | Light reduction | 8 | 3 | 12.20 | µg N2O/m2/h | GC/static | semi-transparent | 20 | 3 | no | yes | yes | Bao T et al. 2018 | |||||||||
Ardley_Island_N2O | AN-Ard-2011-03 | 580.80 | antarctic | Antarctic | Wetland | Vegetated | Western coastal lowland tundra marsh | Antarctica | maritime Antarctica | Ardley Island | -62.22 | -58.93 | 1 | 2011 | 12 | 1 | 2012 | 2 | 21 | 1.86 | 0.24 | 7.80 | 7.47 | 13.26 | 6.7 | 84.80 | 100.000 | -2.5 | 1.6 | 4.1 | 630 | In situ | Yes | Yes | Light reduction | 8 | 3 | 24.20 | µg N2O/m2/h | GC/static | semi-transparent | 20 | 3 | no | yes | yes | Bao T et al. 2018 | |||||||||
Ardley_Island_N2O | AN-Ard-2011-04 | -76.80 | antarctic | Antarctic | Wetland | Vegetated | Eastern coastal lowland tundra with penguin nesting sites | Antarctica | maritime Antarctica | Ardley Island | -62.22 | -58.92 | 1 | 2011 | 12 | 1 | 2012 | 2 | 21 | 16.56 | 2.05 | 8.10 | 43.62 | 74.89 | 5.2 | 83.80 | 24.012 | -2.5 | 1.6 | 4.1 | 630 | In situ | Yes | No | Birds | 8 | 3 | -3.20 | µg N2O/m2/h | GC/static | transparent | 20 | 3 | no | yes | yes | Bao T et al. 2018 | |||||||||
Ardley_Island_N2O | AN-Ard-2011-05 | 331.20 | antarctic | Antarctic | Wetland | Vegetated | Eastern coastal lowland tundra with penguin nesting sites | Antarctica | maritime Antarctica | Ardley Island | -62.22 | -58.92 | 1 | 2011 | 12 | 1 | 2012 | 2 | 21 | 13.90 | 2.08 | 6.70 | 31.93 | 44.67 | 4.9 | 82.30 | 30.758 | -2.5 | 1.6 | 4.1 | 630 | In situ | Yes | Yes | Birds, Light reduction | 8 | 3 | 13.80 | µg N2O/m2/h | GC/static | semi-transparent | 20 | 3 | no | yes | yes | Bao T et al. 2018 | |||||||||
Ardley_Island_N2O | AN-Ard-2011-06 | 708.00 | antarctic | Antarctic | Wetland | Vegetated | Eastern coastal lowland tundra with penguin nesting sites | Antarctica | maritime Antarctica | Ardley Island | -62.22 | -58.92 | 1 | 2011 | 12 | 1 | 2012 | 2 | 21 | 17.59 | 2.36 | 7.50 | 83.59 | 151.65 | 4.5 | 86.90 | 22.648 | -2.5 | 1.6 | 4.1 | 630 | In situ | Yes | Yes | Birds, Light reduction | 8 | 3 | 29.50 | µg N2O/m2/h | GC/static | semi-transparent | 20 | 3 | no | yes | yes | Bao T et al. 2018 | |||||||||
Ardley_Island_N2O | AN-Ard-2013-01 | -12.00 | antarctic | Antarctic | Wetland | Vegetated | Western coastal lowland tundra marsh | Antarctica | maritime Antarctica | Ardley Island | -62.22 | -58.93 | 1 | 2014 | 2 | 14 | 2014 | 3 | 14 | 2.26 | 0.27 | 8.40 | 9.84 | 15.61 | 6.5 | 85.80 | 100.000 | -2.5 | 1.3 | 4.3 | 630 | In situ | No | No | none | 8 | 3 | -0.50 | µg N2O/m2/h | GC/static | transparent | 20 | 3 | no | yes | yes | Bao T et al. 2018 | |||||||||
Ardley_Island_N2O | AN-Ard-2013-02 | 115.20 | antarctic | Antarctic | Wetland | Vegetated | Western coastal lowland tundra marsh | Antarctica | maritime Antarctica | Ardley Island | -62.22 | -58.93 | 1 | 2014 | 2 | 14 | 2014 | 3 | 14 | 2.24 | 0.23 | 9.70 | 8.97 | 31.92 | 6.7 | 81.00 | 100.000 | -2.5 | 1.3 | 4.3 | 630 | In situ | Yes | Yes | Light reduction | 8 | 3 | 4.80 | µg N2O/m2/h | GC/static | semi-transparent | 20 | 3 | no | yes | yes | Bao T et al. 2018 | |||||||||
Ardley_Island_N2O | AN-Ard-2013-03 | 192.00 | antarctic | Antarctic | Wetland | Vegetated | Western coastal lowland tundra marsh | Antarctica | maritime Antarctica | Ardley Island | -62.22 | -58.93 | 1 | 2014 | 2 | 14 | 2014 | 3 | 14 | 1.86 | 0.24 | 7.80 | 7.47 | 13.26 | 6.7 | 84.80 | 100.000 | -2.5 | 1.3 | 4.3 | 630 | In situ | Yes | Yes | Light reduction | 8 | 3 | 8.00 | µg N2O/m2/h | GC/static | semi-transparent | 20 | 3 | no | yes | yes | Bao T et al. 2018 | |||||||||
Ardley_Island_N2O | AN-Ard-2014-01 | -69.60 | antarctic | Antarctic | Wetland | Vegetated | Western coastal lowland tundra marsh | Antarctica | maritime Antarctica | Ardley Island | -62.22 | -58.93 | 1 | 2014 | 12 | 1 | 2015 | 2 | 21 | 2.26 | 0.27 | 8.40 | 9.84 | 15.61 | 6.5 | 85.80 | 100.000 | -2.5 | 1.7 | 5.4 | 630 | In situ | No | No | none | 8 | 3 | -2.90 | µg N2O/m2/h | GC/static | transparent | 20 | 3 | no | yes | yes | Bao T et al. 2018 | |||||||||
Ardley_Island_N2O | AN-Ard-2014-02 | 55.20 | antarctic | Antarctic | Wetland | Vegetated | Western coastal lowland tundra marsh | Antarctica | maritime Antarctica | Ardley Island | -62.22 | -58.93 | 1 | 2014 | 12 | 1 | 2015 | 2 | 21 | 2.24 | 0.23 | 9.70 | 8.97 | 31.92 | 6.7 | 81.00 | 100.000 | -2.5 | 1.7 | 5.4 | 630 | In situ | Yes | Yes | Light reduction | 8 | 3 | 2.30 | µg N2O/m2/h | GC/static | semi-transparent | 20 | 3 | no | yes | yes | Bao T et al. 2018 | |||||||||
Ardley_Island_N2O | AN-Ard-2014-03 | 331.20 | antarctic | Antarctic | Wetland | Vegetated | Western coastal lowland tundra marsh | Antarctica | maritime Antarctica | Ardley Island | -62.22 | -58.93 | 1 | 2014 | 12 | 1 | 2015 | 2 | 21 | 1.86 | 0.24 | 7.80 | 7.47 | 13.26 | 6.7 | 84.80 | 100.000 | -2.5 | 1.7 | 5.4 | 630 | In situ | Yes | Yes | Light reduction | 8 | 3 | 13.80 | µg N2O/m2/h | GC/static | semi-transparent | 20 | 3 | no | yes | yes | Bao T et al. 2018 | |||||||||
Fildes_Peninsula_N2O | AN-Fil-1999-01 | 2152.80 | antarctic | Antarctic | Wetland | Vegetated | same site as Zhu et al 2014, lichen moss tundra near coast, penguin colonies | Antarctica | maritime Antarctica | Fildes Peninsula | -62.22 | -58.93 | 2 | 1999 | 1 | 21 | 2000 | 3 | 23 | 22.67 | 16.48 | 1.40 | 6.1 | -2.2 | 425 | In situ | Yes | No | Birds | 18 | 89.70 | ug N2O/m2/h | GC/static | transparent | 60 | 4 | no | yes | yes | Sun L et al. 2002 | ||||||||||||||||
Fildes_Peninsula_N2O | AN-Fil-1999-02 | 24.00 | antarctic | Antarctic | Wetland | Vegetated | same site as Zhu et al 2014, lichen moss tundra near coast, moss dominated | Antarctica | maritime Antarctica | Fildes Peninsula | -62.22 | -58.93 | 2 | 1999 | 1 | 21 | 2000 | 3 | 23 | 15.48 | 0.70 | 22.10 | 6.0 | -2.2 | 425 | In situ | No | No | none | 20 | 1.00 | ug N2O/m2/h | GC/static | transparent | 60 | 4 | no | yes | yes | Sun L et al. 2002 | ||||||||||||||||
Fildes_Peninsula_N2O | AN-Fil-1999-03 | 28.80 | antarctic | Antarctic | Upland | Partly vegetated | same site as Zhu et al 2014, lichen moss tundra near coast, lichen dominated | Antarctica | maritime Antarctica | Fildes Peninsula | -62.22 | -58.93 | 2 | 1999 | 1 | 21 | 2000 | 3 | 23 | 5.48 | 0.22 | 24.90 | 6.0 | -2.2 | 425 | In situ | No | No | none | 10 | 1.20 | ug N2O/m2/h | GC/static | transparent | 60 | 4 | no | yes | yes | Sun L et al. 2002 | ||||||||||||||||
Fildes_Peninsula_N2O | AN-Fil-2014-01 | -72.00 | antarctic | Antarctic | Upland | Vegetated | Upland, lichen-moss community | Antarctica | maritime Antarctica | Fildes Peninsula | -61.85 | -58.95 | 1 | 2014 | 12 | 1 | 2015 | 2 | 21 | 1.86 | 0.08 | 9.40 | 1.26 | 0.53 | 7.3 | 45.70 | 91.791 | -2.5 | 1.7 | 5.4 | 630 | In situ | No | No | none | 6 | 3 | -3.00 | µg N2O/m2/h | GC/static | transparent | 20 | 3 | no | yes | yes | Bao T et al. 2018 | |||||||||
Fildes_Peninsula_N2O | AN-Fil-2014-02 | 45.60 | antarctic | Antarctic | Upland | Vegetated | Upland, lichen-moss community | Antarctica | maritime Antarctica | Fildes Peninsula | -61.85 | -58.95 | 1 | 2014 | 12 | 1 | 2015 | 2 | 21 | 1.25 | 0.08 | 11.50 | 1.13 | 0.48 | 7.1 | 44.90 | 100.000 | -2.5 | 1.7 | 5.4 | 630 | In situ | Yes | Yes | Light reduction | 6 | 3 | 1.90 | µg N2O/m2/h | GC/static | semi-transparent | 20 | 3 | no | yes | yes | Bao T et al. 2018 | |||||||||
Fildes_Peninsula_N2O | AN-Fil-2014-03 | 211.20 | antarctic | Antarctic | Upland | Vegetated | Upland, lichen-moss community | Antarctica | maritime Antarctica | Fildes Peninsula | -61.85 | -58.95 | 1 | 2014 | 12 | 1 | 2015 | 2 | 21 | 1.08 | 0.12 | 8.50 | 1.17 | 0.44 | 6.8 | 42.80 | 100.000 | -2.5 | 1.7 | 5.4 | 630 | In situ | Yes | Yes | Light reduction | 6 | 3 | 8.80 | µg N2O/m2/h | GC/static | semi-transparent | 20 | 3 | no | yes | yes | Bao T et al. 2018 | |||||||||
Garwood_Valley_N2O | AN-Gav-2003-01 | 556.30 | antarctic | Antarctic | Upland | Bare | 6 m from lake edge (A) | Antarctica | maritime Antarctica | Garwood Valley | -78.02 | 163.88 | 1 | 2003 | 1 | 24 | 2003 | 1 | 29 | 4.10 | 8.82 | 14.10 | 7.3 | 0.34 | 52.609 | -10.0 | 2.3 | 100 | 11.50 | In situ | No | No | none | 6 | 1 | 0.01 | µmol/m2/min | GC/static | 12 | 3 | yes | yes | yes | Gregorich EG et al. 2006 | ||||||||||||
Garwood_Valley_N2O | AN-Gav-2003-02 | 1136.01 | antarctic | Antarctic | Upland | Bare | directly on a strand line of lacustrine detritus 4 m from lake edge (B) | Antarctica | maritime Antarctica | Garwood Valley | -78.02 | 163.88 | 1 | 2003 | 1 | 24 | 2003 | 1 | 29 | 1.90 | 4.87 | 42.20 | 7.3 | 0.36 | 64.594 | -10.0 | 1.7 | 100 | 11.50 | In situ | No | No | none | 6 | 1 | 0.02 | µmol/m2/min | GC/static | 12 | 3 | yes | yes | yes | Gregorich EG et al. 2006 | ||||||||||||
Garwood_Valley_N2O | AN-Gav-2003-03 | 364.39 | antarctic | Antarctic | Upland | Bare | area of living and dried mat about 2 m from the lake edge (C) | Antarctica | maritime Antarctica | Garwood Valley | -78.02 | 163.88 | 1 | 2003 | 1 | 24 | 2003 | 1 | 29 | 12.00 | 8.61 | 45.90 | 7.3 | 0.46 | 55.260 | -10.0 | 0.9 | 100 | 11.50 | In situ | No | No | none | 6 | 1 | 0.01 | µmol/m2/min | GC/static | 12 | 3 | yes | yes | yes | Gregorich EG et al. 2006 | ||||||||||||
Garwood_Valley_N2O | AN-Gav-2005-01 | 2236.00 | antarctic | Antarctic | Upland | Bare | 6 m from lake edge (A) | Antarctica | maritime Antarctica | Garwood Valley | -78.02 | 163.88 | 1 | 2005 | 1 | 24 | 2005 | 1 | 30 | 4.10 | 8.82 | 14.10 | 7.3 | 0.32 | 49.514 | -10.0 | 1.9 | 100 | 11.50 | In situ | No | No | none | 7 | 1 | 0.04 | µmol/m2/min | GC/static | 12 | 3 | yes | yes | yes | Gregorich EG et al. 2006 | ||||||||||||
Garwood_Valley_N2O | AN-Gav-2005-02 | 1269.08 | antarctic | Antarctic | Upland | Bare | directly on a strand line of lacustrine detritus 4 m from lake edge (B) | Antarctica | maritime Antarctica | Garwood Valley | -78.02 | 163.88 | 1 | 2005 | 1 | 24 | 2005 | 1 | 30 | 1.90 | 4.87 | 42.20 | 7.3 | 0.46 | 82.537 | -10.0 | 0.9 | 100 | 11.50 | In situ | No | No | none | 7 | 1 | 0.02 | µmol/m2/min | GC/static | 12 | 3 | yes | yes | yes | Gregorich EG et al. 2006 | ||||||||||||
Garwood_Valley_N2O | AN-Gav-2005-03 | 1208.66 | antarctic | Antarctic | Upland | Bare | area of living and dried mat about 2 m from the lake edge (C) | Antarctica | maritime Antarctica | Garwood Valley | -78.02 | 163.88 | 1 | 2005 | 1 | 24 | 2005 | 1 | 30 | 12.00 | 8.61 | 45.90 | 7.3 | 0.54 | 64.871 | -10.0 | 0.9 | 100 | 11.50 | In situ | No | No | none | 7 | 1 | 0.02 | µmol/m2/min | GC/static | 12 | 3 | yes | yes | yes | Gregorich EG et al. 2006 | ||||||||||||
Alexandra_Fjord_N2O | CA-Alf-2009-01 | 657.98 | continuous | Arctic | Upland | Bare | B1 Cryptogram, herb barren | Canada | Ellesmere Island, Nunavut | Alexandra Fjord | 78.88 | -75.92 | 1 | 2009 | 6 | 2009 | 8 | 0.50 | 0.00 | 3.60 | 2.50 | 7.7 | 36 | 36.000 | -15.0 | 5.0 | 100 | 35.00 | In situ | No | No | none | 8 | 5 | 0.00 | µmol N2O/m2/s | portable gas analzyer | opaque | 10 | 10 | yes | yes | yes | Brummell ME et al. 2012 | ||||||||||||
Alexandra_Fjord_N2O | CA-Alf-2009-02 | 2346.65 | continuous | Arctic | Upland | Partly vegetated | B3 Noncarbonate mountain complex | Canada | Ellesmere Island, Nunavut | Alexandra Fjord | 78.88 | -75.92 | 1 | 2009 | 6 | 2009 | 8 | 0.35 | 0.00 | 7.80 | 1.00 | 6.5 | 53 | 53.000 | -15.0 | 5.0 | 100 | 35.00 | In situ | No | No | none | 8 | 5 | 0.00 | µmol N2O/m2/s | portable gas analzyer | opaque | 10 | 10 | yes | yes | yes | Brummell ME et al. 2012 | ||||||||||||
Alexandra_Fjord_N2O | CA-Alf-2009-03 | 2536.82 | continuous | Arctic | Upland | Vegetated | P1 Prostrate dwarf-shrub, herb tundra | Canada | Ellesmere Island, Nunavut | Alexandra Fjord | 78.88 | -75.92 | 1 | 2009 | 6 | 2009 | 8 | 0.40 | 0.12 | 3.20 | 0.10 | 2.50 | 6.6 | 79 | 79.000 | -15.0 | 5.0 | 100 | 45.00 | In situ | No | No | none | 8 | 5 | 0.00 | µmol N2O/m2/s | portable gas analzyer | opaque | 10 | 10 | yes | yes | yes | Brummell ME et al. 2012 | |||||||||||
Alexandra_Fjord_N2O | CA-Alf-2009-04 | 2628.10 | continuous | Arctic | Upland | Vegetated | P2 Prostrate/hemiprostrate dwarf-shrub tundra | Canada | Ellesmere Island, Nunavut | Alexandra Fjord | 78.88 | -75.92 | 1 | 2009 | 6 | 2009 | 8 | 0.40 | 0.00 | 3.50 | 5.40 | 6.7 | 66 | 66.000 | -15.0 | 5.0 | 100 | 55.00 | In situ | No | No | none | 8 | 5 | 0.00 | µmol N2O/m2/s | portable gas analzyer | opaque | 10 | 10 | yes | yes | yes | Brummell ME et al. 2012 | ||||||||||||
Alexandra_Fjord_N2O | CA-Alf-2009-05 | 3194.80 | continuous | Arctic | Upland | Vegetated | G3 Nontussock sedge, dwarf-shrub, moss tundra | Canada | Ellesmere Island, Nunavut | Alexandra Fjord | 78.88 | -75.92 | 1 | 2009 | 6 | 2009 | 8 | 1.67 | 0.32 | 5.20 | 15.50 | 7.50 | 5.8 | 51 | 51.000 | -15.0 | 5.0 | 100 | 35.00 | In situ | No | No | none | 8 | 5 | 0.00 | µmol N2O/m2/s | portable gas analzyer | opaque | 10 | 10 | yes | yes | yes | Brummell ME et al. 2012 | |||||||||||
Alexandra_Fjord_N2O | CA-Alf-2009-06 | -1125.79 | continuous | Arctic | Wetland | Vegetated | W1 Sedge/grass, moss wetland | Canada | Ellesmere Island, Nunavut | Alexandra Fjord | 78.88 | -75.92 | 1 | 2009 | 6 | 2009 | 8 | 0.69 | 0.18 | 3.80 | 5.60 | 2.20 | 6.4 | 92 | 92.000 | -15.0 | 5.0 | 100 | 35.00 | In situ | No | No | none | 8 | 5 | -0.00 | µmol N2O/m2/s | portable gas analzyer | opaque | 10 | 10 | yes | yes | yes | Brummell ME et al. 2012 | |||||||||||
Eagle_Plains_N2O | CA-Alf-2009-07 | 2623.10 | continuous | Arctic | Upland | Vegetated | Dwarf shrub tundra | Canada | Northwestern Canada | Eagle Plains | 78.88 | -75.77 | 1 | 2009 | 7 | 22 | 2009 | 7 | 25 | 63.00 | 27.00 | 0.37 | 56 | 56.400 | -15.0 | 5.0 | 16.3 | 100 | 50.00 | In situ | No | No | none | 45 | 0.69 | nmol/m2/s | portable gas analzyer | opaque | 10 | 10 | yes | yes | yes | Lamb EG et al. 2011 | ||||||||||||
Boniface_River_N2O | CA-Bon-1991-01 | 39.27 | discontinuous | Subarctic | Peatland | Vegetated | Bog1, WT close to surface | Canada | Quebec | Boniface River | 57.75 | -76.15 | 1 | 1991 | 7 | 22 | 1991 | 7 | 27 | 0.00 | 5.6 | 100 | 100.000 | -4.0 | 11.2 | 500 | 50.00 | In situ | No | No | none | 1 | 3 | 0.03 | mg N2O-N/m2/d | GC/static | opaque | 60 | 6 | no | yes | yes | Toda H et al. 1994 | |||||||||||||
Boniface_River_N2O | CA-Bon-1991-02 | 0.01 | discontinuous | Subarctic | Wetland | Vegetated | Black spruce forest, WT near surface | Canada | Quebec | Boniface River | 57.75 | -76.15 | 1 | 1991 | 7 | 22 | 1991 | 7 | 27 | 0.00 | 4.4 | 100 | 100.000 | -4.0 | 12.8 | 500 | In situ | No | No | none | 1 | 3 | 0.00 | mg N2O-N/m2/d | GC/static | opaque | 60 | 6 | no | yes | yes | Toda H et al. 1994 | ||||||||||||||
Boniface_River_N2O | CA-Bon-1991-03 | 23.57 | discontinuous | Subarctic | Peatland | Vegetated | Palsa, drier than bog | Canada | Quebec | Boniface River | 57.75 | -76.15 | 1 | 1991 | 7 | 22 | 1991 | 7 | 27 | -4.0 | 16.5 | 500 | 100.00 | In situ | No | No | none | 1 | 3 | 0.01 | mg N2O-N/m2/d | GC/static | opaque | 60 | 6 | no | yes | yes | Toda H et al. 1994 | |||||||||||||||||
Boniface_River_N2O | CA-Bon-1991-04 | 15.71 | discontinuous | Subarctic | Upland | Vegetated | Bush | Canada | Quebec | Boniface River | 57.75 | -76.15 | 1 | 1991 | 7 | 22 | 1991 | 7 | 27 | -4.0 | 23.1 | 500 | In situ | No | No | none | 1 | 3 | 0.01 | mg N2O-N/m2/d | GC/static | opaque | 60 | 6 | no | yes | yes | Toda H et al. 1994 | ||||||||||||||||||
Cape_Bounty_N2O | CA-Cab-2008-01 | -10.26 | continuous | Arctic | Upland | Bare | Polar desert, barren | Canada | Melville Island, Nunavut | Cape Bounty | 74.92 | -109.58 | 1 | 2008 | 6 | 2008 | 7 | 17.70 | 0.16 | -11.4 | 11.3 | 7.6 | 125 | 74.00 | In situ | No | No | none | 4 | 8 | -0.07 | ng N/m2/s | GC/static | opaque | 45 | 4 | yes | yes | yes | Wagner I et al. 2019 | ||||||||||||||||
Cape_Bounty_N2O | CA-Cab-2008-02 | 35.99 | continuous | Arctic | Upland | Vegetated | Polar desert, vegetated | Canada | Melville Island, Nunavut | Cape Bounty | 74.92 | -109.58 | 1 | 2008 | 6 | 2008 | 7 | 17.70 | 0.15 | -11.4 | 11.0 | 6.8 | 125 | 74.00 | In situ | No | No | none | 4 | 4 | 0.26 | ng N/m2/s | GC/static | opaque | 45 | 4 | yes | yes | yes | Wagner I et al. 2019 | ||||||||||||||||
Cape_Bounty_N2O | CA-Cab-2008-03 | 62.14 | continuous | Arctic | Upland | Vegetated | Mesic tundra | Canada | Melville Island, Nunavut | Cape Bounty | 74.92 | -109.58 | 1 | 2008 | 6 | 2008 | 7 | 30.60 | 0.32 | -11.4 | 9.9 | 5.7 | 125 | 66.00 | In situ | No | No | none | 4 | 8 | 0.46 | ng N/m2/s | GC/static | opaque | 45 | 4 | yes | yes | yes | Wagner I et al. 2019 | ||||||||||||||||
Cape_Bounty_N2O | CA-Cab-2008-04 | 89.08 | continuous | Arctic | Wetland | Vegetated | Wet sedge | Canada | Melville Island, Nunavut | Cape Bounty | 74.92 | -109.58 | 1 | 2008 | 6 | 2008 | 7 | 68.20 | 0.52 | -11.4 | 9.8 | 5.5 | 125 | 63.00 | In situ | No | No | none | 4 | 8 | 0.66 | ng N/m2/s | GC/static | opaque | 45 | 4 | yes | yes | yes | Wagner I et al. 2019 | ||||||||||||||||
Cape_Bounty_N2O | CA-Cab-2009-01 | -2.21 | continuous | Arctic | Upland | Bare | Polar desert, barren | Canada | Melville Island, Nunavut | Cape Bounty | 74.92 | -109.58 | 1 | 2009 | 6 | 2009 | 7 | 17.70 | 0.34 | -11.4 | 3.8 | 5.5 | 125 | 58.00 | In situ | No | No | none | 5 | 8 | -0.02 | ng N/m2/s | GC/static | opaque | 45 | 4 | yes | yes | yes | Wagner I et al. 2019 | ||||||||||||||||
Cape_Bounty_N2O | CA-Cab-2009-02 | -10.66 | continuous | Arctic | Upland | Vegetated | Polar desert, vegetated | Canada | Melville Island, Nunavut | Cape Bounty | 74.92 | -109.58 | 1 | 2009 | 6 | 2009 | 7 | 17.70 | 0.35 | -11.4 | 3.8 | 4.4 | 125 | 58.00 | In situ | No | No | none | 5 | 4 | -0.08 | ng N/m2/s | GC/static | opaque | 45 | 4 | yes | yes | yes | Wagner I et al. 2019 | ||||||||||||||||
Cape_Bounty_N2O | CA-Cab-2009-03 | 60.52 | continuous | Arctic | Upland | Vegetated | Mesic tundra | Canada | Melville Island, Nunavut | Cape Bounty | 74.92 | -109.58 | 1 | 2009 | 6 | 2009 | 7 | 30.60 | 0.44 | -11.4 | 4.3 | 4.0 | 125 | 45.00 | In situ | No | No | none | 5 | 8 | 0.45 | ng N/m2/s | GC/static | opaque | 45 | 4 | yes | yes | yes | Wagner I et al. 2019 | ||||||||||||||||
Cape_Bounty_N2O | CA-Cab-2009-04 | 101.53 | continuous | Arctic | Wetland | Vegetated | Wet sedge | Canada | Melville Island, Nunavut | Cape Bounty | 74.92 | -109.58 | 1 | 2009 | 6 | 2009 | 7 | 68.20 | 0.61 | -11.4 | 4.8 | 4.3 | 125 | 55.83 | In situ | No | No | none | 5 | 8 | 0.74 | ng N/m2/s | GC/static | opaque | 45 | 4 | yes | yes | yes | Wagner I et al. 2019 | ||||||||||||||||
Churchill_N2O | CA-Chu-2009-01 | 94.39 | continuous | Subarctic | Upland | Vegetated | Back slope with taller vegetation. Some trees such as Picea glauca and small shrubs such as Vaccinium uliginosum were particularly abundant | Canada | Hudson Bay | Churchill | 58.75 | -93.85 | 1 | 2009 | 2009 | 20.37 | 0.96 | 22.60 | 0.33 | 0.18 | 5.7 | 1.16 | 23.935 | -5.8 | 6.5 | 501 | In situ | No | No | none | 1 | 36 | 0.02 | nmol/m2/s | portable gas analzyer | opaque | 5 | 15 | yes | yes | yes | Pare MC & Bedard-Haughn A 2012 | ||||||||||||||
Churchill_N2O | CA-Chu-2009-02 | 135.39 | continuous | Subarctic | Wetland | Vegetated | Lower slope; high vegetation diversity growing on a silty and wet soil material. Carex aquatilis were found in wet parts whereas Vaccinium uliginosum was found in driest locations | Canada | Hudson Bay | Churchill | 58.75 | -93.85 | 1 | 2009 | 2009 | 33.72 | 1.81 | 20.50 | 1.13 | 0.03 | 6.7 | 3.37 | 66.909 | -5.8 | 5.8 | 501 | In situ | No | No | none | 1 | 36 | 0.04 | nmol/m2/s | portable gas analzyer | opaque | 5 | 15 | yes | yes | yes | Pare MC & Bedard-Haughn A 2012 | ||||||||||||||
Churchill_N2O | CA-Chu-2009-03 | -691.86 | continuous | Subarctic | Upland | Partly vegetated | Upper slope of the beach crests; relatively low vegetation cover as well as high gravel and rock content in the soil | Canada | Hudson Bay | Churchill | 58.75 | -93.85 | 1 | 2009 | 2009 | 5.24 | 0.31 | 18.10 | 0.13 | 0.18 | 6.3 | 0.14 | 15.725 | -5.8 | 10.4 | 501 | In situ | No | No | none | 1 | 36 | -0.18 | nmol/m2/s | portable gas analzyer | opaque | 5 | 15 | yes | yes | yes | Pare MC & Bedard-Haughn A 2012 | ||||||||||||||
Churchill_N2O | CA-Chu-2009-04 | -11.21 | continuous | Subarctic | Peatland | Vegetated | Hummock (dry peatland); lichens and evergreen plants; Empetrum nigrum | Canada | Hudson Bay | Churchill | 58.75 | -93.85 | 1 | 2009 | 2009 | 47.14 | 1.65 | 33.30 | 0.00 | 0.00 | 3.9 | 2.20 | 11.534 | -5.8 | 7.7 | 501 | In situ | No | No | none | 1 | 15 | -0.00 | nmol/m2/s | portable gas analzyer | opaque | 5 | 15 | yes | yes | yes | Pare MC & Bedard-Haughn A 2012 | ||||||||||||||
Churchill_N2O | CA-Chu-2009-05 | 278.68 | continuous | Subarctic | Peatland | Vegetated | Inter-hummock/wegde (wet peatland); dwarf birch and Carex vegetation types. Vaccinium uliginosum | Canada | Hudson Bay | Churchill | 58.75 | -93.85 | 1 | 2009 | 2009 | 39.40 | 2.75 | 15.00 | 0.66 | 0.27 | 5.9 | 2.23 | 24.945 | -5.8 | 5.9 | 501 | In situ | No | No | none | 1 | 15 | 0.07 | nmol/m2/s | portable gas analzyer | opaque | 5 | 15 | yes | yes | yes | Pare MC & Bedard-Haughn A 2012 | ||||||||||||||
Daring_Lake_N2O | CA-Dar-2008-01 | -876.36 | continuous | Arctic | Upland | Vegetated | Back slope; high vegetation diversity, including several taller shrub species, growing on sandy material. Some vascular species such as A. alpina and B. glandulosa | Canada | Northwestern Canada | Daring Lake | 64.83 | -111.63 | 1 | 2008 | 2008 | 7.21 | 0.28 | 27.90 | 0.01 | 0.02 | 3.6 | 0.57 | 47.981 | -9.0 | 13.1 | 120.00 | In situ | No | No | none | 1 | 20 | -0.23 | nmol/m2/s | portable gas analzyer | opaque | 5 | 10 | yes | yes | yes | Pare MC & Bedard-Haughn A 2012 | ||||||||||||||
Daring_Lake_N2O | CA-Dar-2008-02 | 1658.23 | continuous | Arctic | Wetland | Vegetated | Lower slopes; high vegetation diversity growing on silty and/or organicmaterials (i.e., poorly sorted sediments) sometimes associated with mud boils. Carex spp. and Eriophorium vaginatum were particularly abundant | Canada | Northwestern Canada | Daring Lake | 64.83 | -111.63 | 1 | 2008 | 2008 | 25.83 | 0.86 | 32.50 | 0.27 | 0.14 | 3.5 | 2.28 | 32.670 | -9.0 | 13.4 | 120.00 | In situ | No | No | none | 1 | 20 | 0.44 | nmol/m2/s | portable gas analzyer | opaque | 5 | 10 | yes | yes | yes | Pare MC & Bedard-Haughn A 2012 | ||||||||||||||
Daring_Lake_N2O | CA-Dar-2008-03 | 1052.03 | continuous | Arctic | Upland | Partly vegetated | Upper slopes; low vegetation cover as well as high gravel and rock contents. Lichens and Empetrum nigrum | Canada | Northwestern Canada | Daring Lake | 64.83 | -111.63 | 1 | 2008 | 2008 | 4.39 | 0.22 | 19.50 | 0.02 | 0.01 | 4.2 | 0.50 | 64.227 | -9.0 | 13.6 | 120.00 | In situ | No | No | none | 1 | 20 | 0.28 | nmol/m2/s | portable gas analzyer | opaque | 5 | 10 | yes | yes | yes | Pare MC & Bedard-Haughn A 2012 | ||||||||||||||
Dome_Desert_N2O | CA-Dom-2010-01 | 349.91 | continuous | Arctic | Upland | Partly vegetated | polar desert, less than 5% vegetation cover; alpine semi desert | Canada | Ellesmere Island, Nunavut | Dome Desert | 78.85 | -75.92 | 1 | 2010 | 7 | 20 | 2010 | 7 | 21 | 4.77 | 1.63 | 2.90 | 0.61 | 0.00 | 8.6 | 5 | 5.000 | -15.0 | 5.0 | 100 | 42.40 | In situ | No | No | none | 1 | 5 | 0.09 | nmol N2O/m2/s | portable gas analzyer | opaque | 10 | 10 | yes | yes | yes | Brummell ME et al. 2014 | |||||||||
Dome_Desert_N2O | CA-Dom-2010-02 | -562.89 | continuous | Arctic | Upland | Partly vegetated | polar desert, less than 5% vegetation cover; alpine semi desert | Canada | Ellesmere Island, Nunavut | Dome Desert | 78.85 | -75.92 | 1 | 2010 | 7 | 20 | 2010 | 7 | 21 | 4.77 | 1.63 | 2.90 | 0.61 | 0.00 | 8.6 | 5 | 5.000 | -15.0 | 5.0 | 100 | 42.40 | In situ | No | No | none | 1 | 5 | -0.15 | nmol N2O/m2/s | portable gas analzyer | transparent | 10 | 10 | yes | yes | yes | Brummell ME et al. 2014 | |||||||||
Eagle_Plains_N2O | CA-Eag-2015-01 | 92.30 | continuous | Subarctic | Upland | Vegetated | Forest, 46 years after burning | Canada | Northwestern Canada | Eagle Plains | 66.98 | -135.23 | 1 | 2015 | 7 | 2015 | 7 | 16.50 | 0.80 | 20.60 | 6.7 | 49.00 | 27.686 | -8.8 | 16.4 | 5.3 | 248 | 49.00 | In situ | Yes | No | Fire | 9 | 0.00 | mg N2O/m2/s | GC/static | opaque | 20 | 5 | yes | yes | yes | Köster E et al. 2017 | |||||||||||||
Eagle_Plains_N2O | CA-Eag-2015-02 | 59.75 | continuous | Subarctic | Upland | Vegetated | Forest, 25 years after burning | Canada | Northwestern Canada | Eagle Plains | 66.98 | -135.23 | 1 | 2015 | 7 | 2015 | 7 | 15.50 | 0.50 | 31.00 | 5.2 | 40.00 | 21.159 | -8.8 | 22.3 | 7.7 | 248 | 88.00 | In situ | Yes | No | Fire | 9 | 0.00 | mg N2O/m2/s | GC/static | opaque | 20 | 5 | yes | yes | yes | Köster E et al. 2017 | |||||||||||||
Eagle_Plains_N2O | CA-Eag-2015-03 | 121.82 | continuous | Subarctic | Upland | Vegetated | Forest, 3 years after burning | Canada | Northwestern Canada | Eagle Plains | 66.98 | -135.23 | 1 | 2015 | 7 | 2015 | 7 | 10.80 | 0.50 | 21.60 | 4.2 | 37.00 | 31.107 | -8.8 | 17.7 | 6.8 | 248 | 101.00 | In situ | Yes | No | Fire | 9 | 0.00 | mg N2O/m2/s | GC/static | opaque | 20 | 5 | yes | yes | yes | Köster E et al. 2017 | |||||||||||||
Eagle_Plains_N2O | CA-Eag-2015-04 | 138.35 | continuous | Subarctic | Upland | Vegetated | Forest, undisturbed | Canada | Northwestern Canada | Eagle Plains | 66.98 | -135.23 | 1 | 2015 | 7 | 2015 | 7 | 28.40 | 0.90 | 31.60 | 5.1 | 55.00 | 15.373 | -8.8 | 14.8 | 4.3 | 248 | 28.00 | In situ | No | No | none | 9 | 0.00 | mg N2O/m2/s | GC/static | opaque | 20 | 5 | yes | yes | yes | Köster E et al. 2017 | |||||||||||||
Expedition_Fjord_N2O | CA-Exf-2015-01 | 291.00 | continuous | Arctic | Upland | Bare | Polygonal tundra - polygon trough | Canada | Axel Heiberg Island, Nunavut | Expedition Fjord | 79.43 | -90.77 | 1 | 2015 | 7 | 2015 | 7 | 2.57 | 0.00 | 35.50 | 9.0 | 66.50 | In situ | No | No | none | 2 | 4 | 0.29 | mg N2O/m2/d | GC/static | opaque | 480 | 4 | no | no | yes | Altshuler I et al. 2019 | ||||||||||||||||||
Expedition_Fjord_N2O | CA-Exf-2015-02 | 121.00 | continuous | Arctic | Upland | Bare | Polygonal tundra - polygon center | Canada | Axel Heiberg Island, Nunavut | Expedition Fjord | 79.43 | -90.77 | 1 | 2015 | 7 | 2015 | 7 | 2.17 | 0.00 | 13.00 | 9.0 | 66.50 | In situ | No | No | none | 2 | 4 | 0.12 | mg N2O/m2/d | GC/static | opaque | 480 | 4 | no | no | yes | Altshuler I et al. 2019 | ||||||||||||||||||
Okse_Bay_N2O | CA-Oks-2010-01 | 34.23 | continuous | Arctic | Upland | Partly vegetated | polar desert, less than 5% vegetation cover; raised beach crest with moist tundra patches | Canada | Ellesmere Island, Nunavut | Okse Bay | 77.13 | -87.65 | 1 | 2010 | 7 | 13 | 2010 | 7 | 17 | 3.32 | 0.57 | 5.80 | 2.05 | 0.41 | 7.9 | 6 | 6.200 | -15.0 | 5.0 | 100 | 49.70 | In situ | Yes | No | Birds | 1 | 5 | 0.01 | nmol N2O/m2/s | portable gas analzyer | opaque | 10 | 10 | yes | yes | yes | Brummell ME et al. 2014 | |||||||||
Okse_Bay_N2O | CA-Oks-2010-02 | 3.80 | continuous | Arctic | Upland | Partly vegetated | polar desert, less than 5% vegetation cover; raised beach crest with moist tundra patches | Canada | Ellesmere Island, Nunavut | Okse Bay | 77.13 | -87.65 | 1 | 2010 | 7 | 13 | 2010 | 7 | 17 | 3.32 | 0.57 | 5.80 | 2.05 | 0.41 | 7.9 | 6 | 6.200 | -15.0 | 5.0 | 100 | 49.70 | In situ | Yes | No | Birds | 1 | 5 | 0.00 | nmol N2O/m2/s | portable gas analzyer | transparent | 10 | 10 | yes | yes | yes | Brummell ME et al. 2014 | |||||||||
Patterson_River_N2O | CA-Pat-2010-01 | -604.73 | continuous | Arctic | Upland | Partly vegetated | polar desert, less than 5% vegetation cover; fluvial outwash plain | Canada | Ellesmere Island, Nunavut | Patterson River | 82.58 | -63.75 | 1 | 2010 | 7 | 30 | 2010 | 8 | 1 | 7.17 | 3.33 | 2.20 | 0.40 | 0.15 | 8.6 | 4 | 4.500 | -15.0 | 5.0 | 100 | 35.50 | In situ | No | No | none | 1 | 5 | -0.16 | nmol N2O/m2/s | portable gas analzyer | opaque | 10 | 10 | yes | yes | yes | Brummell ME et al. 2014 | |||||||||
Patterson_River_N2O | CA-Pat-2010-02 | -1026.90 | continuous | Arctic | Upland | Partly vegetated | polar desert, less than 5% vegetation cover; fluvial outwash plain | Canada | Ellesmere Island, Nunavut | Patterson River | 82.58 | -63.75 | 1 | 2010 | 7 | 30 | 2010 | 8 | 1 | 7.17 | 3.33 | 2.20 | 0.40 | 0.15 | 8.6 | 4 | 4.500 | -15.0 | 5.0 | 100 | 35.50 | In situ | No | No | none | 1 | 5 | -0.27 | nmol N2O/m2/s | portable gas analzyer | transparent | 10 | 10 | yes | yes | yes | Brummell ME et al. 2014 | |||||||||
Truelove_Lowland_N2O | CA-Tru-2004-01 | 9.54 | continuous | Arctic | Upland | Vegetated | Lower foreslope, Brunisolic Eutric Turbic Cryosol (LFS) | Canada | Devon Island, Nunavut | Truelove Lowland | 75.67 | -84.58 | 1 | 2004 | 6 | 16 | 2004 | 7 | 13 | 3.78 | 0.19 | 19.90 | 7.12 | 1.51 | 6.7 | 0.66 | 93.755 | -16.0 | 4.1 | 185 | In situ | No | No | none | 9 | 5 | 1.64 | g N2O-N/ha | GC/static | opaque | 135 | 4 | yes | no | yes | Ma WK et al. 2007 | ||||||||||
Truelove_Lowland_N2O | CA-Tru-2004-02 | 3.43 | continuous | Arctic | Upland | Vegetated | Raised beach crest, Regosolic static cryosol (RBC) | Canada | Devon Island, Nunavut | Truelove Lowland | 75.67 | -84.58 | 1 | 2004 | 6 | 16 | 2004 | 7 | 13 | 4.47 | 0.20 | 22.40 | 2.77 | 1.35 | 7.5 | 0.20 | 25.361 | -16.0 | 5.4 | 185 | In situ | No | No | none | 9 | 5 | 0.59 | g N2O-N/ha | GC/static | opaque | 135 | 4 | yes | no | yes | Ma WK et al. 2007 | ||||||||||
Truelove_Lowland_N2O | CA-Tru-2004-03 | 26.60 | continuous | Arctic | Wetland | Vegetated | Wed sedge meadow, Gleysolic Turbic Cryosol (WSM) | Canada | Devon Island, Nunavut | Truelove Lowland | 75.67 | -84.58 | 1 | 2004 | 6 | 16 | 2004 | 7 | 13 | 30.00 | 1.54 | 19.50 | 36.24 | 7.52 | 6.9 | 6.48 | 90 | 90.000 | -16.0 | 5.1 | 185 | In situ | No | No | none | 9 | 5 | 4.57 | g N2O-N/ha | GC/static | opaque | 135 | 4 | yes | no | yes | Ma WK et al. 2007 | |||||||||
Daxing-an_Mountains_N2O | CH-Dax-2016-01 | 977.76 | continuous | Alpine | Peatland | Vegetated | Swamp coniferous forest (LL) | China | Central Asia | Daxing'an Mountains | 53.28 | 122.10 | 1 | 2016 | 6 | 2016 | 9 | 53.41 | 3.01 | 17.20 | 4.38 | 0.86 | 4.7 | -4.9 | 8.2 | 490 | In situ | No | No | none | 8 | 3 | 40.74 | µg N2O/m2/h | GC/static | opaque | 45 | 4 | no | no | yes | Gao W et al. 2019 | ||||||||||||||
Daxing-an_Mountains_N2O | CH-Dax-2016-02 | 708.96 | continuous | Alpine | Peatland | Vegetated | Swamp coniferous forest (LC) | China | Central Asia | Daxing'an Mountains | 53.28 | 122.10 | 1 | 2016 | 6 | 2016 | 9 | 62.38 | 5.01 | 12.50 | 5.14 | 0.78 | 5.0 | 100 | 100.000 | -4.9 | 8.0 | 490 | In situ | No | No | none | 8 | 3 | 29.54 | µg N2O/m2/h | GC/static | opaque | 45 | 4 | no | no | yes | Gao W et al. 2019 | ||||||||||||
Daxing-an_Mountains_N2O | CH-Dax-2016-03 | 920.16 | continuous | Alpine | Peatland | Vegetated | Swamp coniferous forest (BC) | China | Central Asia | Daxing'an Mountains | 53.28 | 122.10 | 1 | 2016 | 6 | 2016 | 9 | 49.42 | 2.51 | 19.70 | 4.22 | 0.80 | 4.9 | 100 | 100.000 | -4.9 | 9.2 | 490 | In situ | No | No | none | 8 | 3 | 38.34 | µg N2O/m2/h | GC/static | opaque | 45 | 4 | no | no | yes | Gao W et al. 2019 | ||||||||||||
Eboling_Mountains_N2O | CH-Ebo-2016-01 | 41800.00 | sporadic | Alpine | Upland | Vegetated | Thermokarst Alpine tundra, Undisturbed; Carex L, and Kobresia Willd | China | Qinghai-Tibetan Plateau | Eboling Mountains | 38.00 | 100.91 | 1 | 2016 | 6 | 26 | 2016 | 9 | 30 | 9.35 | 1.35 | 6.90 | 1.09 | 1.05 | 6.1 | 1.30 | 0.40 | 50.801 | -0.8 | 6.8 | 8.7 | 433 | 71.00 | 99.00 | In situ | No | No | none | 3 | 12 | 0.01 | µmol/m2/s | GC/static | opaque | 15 | 4 | yes | yes | yes | Mu CC et al. 2017 | ||||||
Eboling_Mountains_N2O | CH-Ebo-2016-02 | 17800.00 | sporadic | Alpine | Upland | Vegetated | Drape patches, collapsed but vegetated with Carex L, K. Willd, Agropyron, Poa, and Koeleria; 65% of the thermokarst gully | China | Qinghai-Tibetan Plateau | Eboling Mountains | 38.00 | 100.91 | 1 | 2016 | 6 | 26 | 2016 | 9 | 30 | 9.12 | 1.32 | 6.90 | 0.66 | 8.18 | 7.2 | 0.95 | 0.40 | 51.099 | -0.8 | 6.8 | 8.4 | 433 | 66.00 | 92.00 | In situ | Yes | No | Thermokarst | 3 | 12 | 0.01 | µmol/m2/s | GC/static | opaque | 15 | 4 | yes | yes | yes | Mu CC et al. 2017 | ||||||
Eboling_Mountains_N2O | CH-Ebo-2016-03 | 67300.00 | sporadic | Alpine | Upland | Bare | Exposed patches, collapsed, bare mineral soil; 35% of the gully | China | Qinghai-Tibetan Plateau | Eboling Mountains | 38.00 | 100.91 | 1 | 2016 | 6 | 26 | 2016 | 9 | 30 | 8.81 | 1.32 | 6.70 | 0.91 | 11.10 | 7.0 | 1.00 | 0.40 | 51.518 | -0.8 | 6.8 | 6.8 | 433 | 48.00 | 68.00 | In situ | Yes | No | Thermokarst | 3 | 12 | 0.02 | µmol/m2/s | GC/static | opaque | 15 | 4 | yes | yes | yes | Mu CC et al. 2017 | ||||||
Fenghuo_Mountains_N2O | CH-Fen-2014-01 | 43.20 | discontinuous | Alpine | Upland | Vegetated | Alpine meadow | China | Qinghai-Tibetan Plateau | Fenghuo Mountains | 34.72 | 92.88 | 2 | 2014 | 5 | 15 | 2015 | 10 | 15 | 2.73 | 0.16 | 16.90 | 3.70 | 18.50 | 7.8 | 0.89 | 23.00 | 0.23 | 31.850 | -5.2 | 4.8 | 5.0 | 311 | 115.00 | In situ | No | No | none | 61 | 3 | 1.80 | µg N2O/m2/h | GC/static | opaque | 30 | 4 | yes | yes | yes | Chen X et al. 2017 | ||||||
Fenghuo_Mountains_N2O | CH-Fen-2014-02 | 264.72 | discontinuous | Alpine | Upland | Vegetated | Alpine meadow | China | Qinghai-Tibetan Plateau | Fenghuo Mountains | 34.72 | 92.88 | 2 | 2014 | 5 | 15 | 2015 | 10 | 15 | 3.12 | 0.17 | 18.90 | 4.50 | 29.20 | 7.7 | 0.87 | 17.00 | 0.17 | 22.770 | -5.2 | 9.3 | 10.2 | 311 | 115.00 | In situ | Yes | Yes | Warming | 61 | 3 | 11.03 | µg N2O/m2/h | GC/static | opaque | 30 | 4 | yes | yes | yes | Chen X et al. 2017 | ||||||
Fenghuo_Mountains_N2O | CH-Fen-2014-03 | 77.52 | discontinuous | Alpine | Upland | Vegetated | Alpine meadow | China | Qinghai-Tibetan Plateau | Fenghuo Mountains | 34.72 | 92.88 | 2 | 2014 | 5 | 15 | 2015 | 10 | 15 | 2.68 | 0.16 | 16.80 | 3.98 | 42.20 | 7.7 | 0.88 | 23.00 | 0.23 | 31.289 | -5.2 | 4.8 | 5.0 | 311 | 115.00 | In situ | Yes | Yes | N-addition | 61 | 3 | 3.23 | µg N2O/m2/h | GC/static | opaque | 30 | 4 | yes | yes | yes | Chen X et al. 2017 | ||||||
Fenghuo_Mountains_N2O | CH-Fen-2014-04 | 330.24 | discontinuous | Alpine | Upland | Vegetated | Alpine meadow | China | Qinghai-Tibetan Plateau | Fenghuo Mountains | 34.72 | 92.88 | 2 | 2014 | 5 | 15 | 2015 | 10 | 15 | 2.94 | 0.17 | 17.30 | 3.93 | 34.29 | 7.6 | 0.86 | 17.00 | 0.17 | 22.351 | -5.2 | 9.3 | 10.2 | 311 | 115.00 | In situ | Yes | Yes | Warming, N-addition | 61 | 3 | 13.76 | µg N2O/m2/h | GC/static | opaque | 30 | 4 | yes | yes | yes | Chen X et al. 2017 | ||||||
Geermu_N2O | CH-Gee-2015-01 | 28.58 | sporadic | Alpine | Upland | Vegetated | Alpine swamp meadow, vegetated by graminoids, such as Kobresia tibetica, K. royleana, and Carex atrofuscoides | China | Qinghai-Tibetan Plateau | Geermu | 37.47 | 100.28 | 1 | 2015 | 7 | 2015 | 8 | 19.40 | 1.50 | 12.90 | 1.66 | 5.6 | 0.27 | 67.60 | 64.536 | -3.3 | 8.6 | 460 | 90.00 | In situ | No | No | none | 6 | 10 | 0.03 | mg N2O/m2/d | GC/static | opaque | 40 | 5 | no | no | yes | Yang G et al. 2018 | |||||||||||
Geermu_N2O | CH-Gee-2015-02 | 231.62 | sporadic | Alpine | Upland | Vegetated | Alpine swamp meadow with recent (3 years) permafrost collapse, vegetated | China | Qinghai-Tibetan Plateau | Geermu | 37.47 | 100.28 | 1 | 2015 | 7 | 2015 | 8 | 19.40 | 1.50 | 12.90 | 2.76 | 5.5 | 0.27 | 48.60 | 29.247 | -3.3 | 8.8 | 460 | 90.00 | In situ | Yes | No | Thermokarst | 6 | 10 | 0.23 | mg N2O/m2/d | GC/static | opaque | 40 | 5 | no | no | yes | Yang G et al. 2018 | |||||||||||
Geermu_N2O | CH-Gee-2015-03 | 81.94 | sporadic | Alpine | Upland | Vegetated | Alpine swamp meadow with medium (12 years) permafrost collapse, vegetated | China | Qinghai-Tibetan Plateau | Geermu | 37.47 | 100.28 | 1 | 2015 | 7 | 2015 | 8 | 19.40 | 1.50 | 12.90 | 1.87 | 5.7 | 0.27 | 62.80 | 52.218 | -3.3 | 9.0 | 460 | 90.00 | In situ | Yes | No | Thermokarst | 6 | 10 | 0.08 | mg N2O/m2/d | GC/static | opaque | 40 | 5 | no | no | yes | Yang G et al. 2018 | |||||||||||
Geermu_N2O | CH-Gee-2015-04 | 27.58 | sporadic | Alpine | Upland | Vegetated | Alpine swamp meadow with old (20 years) permafrost collapse, vegetated | China | Qinghai-Tibetan Plateau | Geermu | 37.47 | 100.28 | 1 | 2015 | 7 | 2015 | 8 | 19.40 | 1.50 | 12.90 | 0.55 | 5.7 | 0.27 | 63.07 | 52.826 | -3.3 | 9.2 | 460 | 90.00 | In situ | Yes | No | Thermokarst | 6 | 10 | 0.03 | mg N2O/m2/d | GC/static | opaque | 40 | 5 | no | no | yes | Yang G et al. 2018 | |||||||||||
Geermu_N2O | CH-Gee-2016-01 | 23.78 | sporadic | Alpine | Upland | Vegetated | Alpine swamp meadow, vegetated by graminoids, such as Kobresia tibetica, K. royleana, and Carex atrofuscoides | China | Qinghai-Tibetan Plateau | Geermu | 37.47 | 100.28 | 1 | 2016 | 7 | 2016 | 8 | 19.40 | 1.50 | 12.90 | 1.66 | 5.6 | 0.27 | 67.60 | 64.536 | -3.3 | 8.6 | 460 | 90.00 | In situ | No | No | none | 5 | 10 | 0.02 | mg N2O/m2/d | GC/static | opaque | 40 | 5 | no | no | yes | Yang G et al. 2018 | |||||||||||
Geermu_N2O | CH-Gee-2016-02 | 157.42 | sporadic | Alpine | Upland | Vegetated | Alpine swamp meadow with recent (3 years) permafrost collapse, vegetated | China | Qinghai-Tibetan Plateau | Geermu | 37.47 | 100.28 | 1 | 2016 | 7 | 2016 | 8 | 19.40 | 1.50 | 12.90 | 2.76 | 5.5 | 0.27 | 48.60 | 29.247 | -3.3 | 8.8 | 460 | 90.00 | In situ | Yes | No | Thermokarst | 5 | 10 | 0.16 | mg N2O/m2/d | GC/static | opaque | 40 | 5 | no | no | yes | Yang G et al. 2018 | |||||||||||
Geermu_N2O | CH-Gee-2016-03 | 31.32 | sporadic | Alpine | Upland | Vegetated | Alpine swamp meadow with medium (12 years) permafrost collapse, vegetated | China | Qinghai-Tibetan Plateau | Geermu | 37.47 | 100.28 | 1 | 2016 | 7 | 2016 | 8 | 19.40 | 1.50 | 12.90 | 1.87 | 5.7 | 0.27 | 62.80 | 52.218 | -3.3 | 9.0 | 460 | 90.00 | In situ | Yes | No | Thermokarst | 5 | 10 | 0.03 | mg N2O/m2/d | GC/static | opaque | 40 | 5 | no | no | yes | Yang G et al. 2018 | |||||||||||
Geermu_N2O | CH-Gee-2016-04 | 17.11 | sporadic | Alpine | Upland | Vegetated | Alpine swamp meadow with old (20 years) permafrost collapse, vegetated | China | Qinghai-Tibetan Plateau | Geermu | 37.47 | 100.28 | 1 | 2016 | 7 | 2016 | 8 | 19.40 | 1.50 | 12.90 | 0.55 | 5.7 | 0.27 | 63.07 | 52.826 | -3.3 | 9.2 | 460 | 90.00 | In situ | Yes | No | Thermokarst | 5 | 10 | 0.02 | mg N2O/m2/d | GC/static | opaque | 40 | 5 | no | no | yes | Yang G et al. 2018 | |||||||||||
Geermu_N2O | CH-Gee-2016-05 | 3050.38 | sporadic | Alpine | Upland | Bare | Alpine swamp meadow with recent (3 years) permafrost collapse, bare | China | Qinghai-Tibetan Plateau | Geermu | 37.47 | 100.28 | 1 | 2016 | 7 | 2016 | 8 | 19.40 | 1.50 | 12.90 | 4.49 | 5.1 | 0.27 | 49.20 | 29.957 | -3.3 | 6.7 | 460 | 90.00 | In situ | Yes | No | Thermokarst | 5 | 5 | 3.05 | mg N2O/m2/d | GC/static | opaque | 40 | 5 | no | no | yes | Yang G et al. 2018 | |||||||||||
Geermu_N2O | CH-Gee-2016-06 | 65.11 | sporadic | Alpine | Upland | Bare | Alpine swamp meadow with medium (12 years) permafrost collapse, bare | China | Qinghai-Tibetan Plateau | Geermu | 37.47 | 100.28 | 1 | 2016 | 7 | 2016 | 8 | 19.40 | 1.50 | 12.90 | 0.99 | 5.6 | 0.27 | 56.58 | 40.307 | -3.3 | 6.7 | 460 | 90.00 | In situ | Yes | No | Thermokarst | 5 | 5 | 0.07 | mg N2O/m2/d | GC/static | opaque | 40 | 5 | no | no | yes | Yang G et al. 2018 | |||||||||||
Geermu_N2O | CH-Gee-2016-07 | 11.23 | sporadic | Alpine | Upland | Bare | Alpine swamp meadow with old (20 years) permafrost collapse, bare | China | Qinghai-Tibetan Plateau | Geermu | 37.47 | 100.28 | 1 | 2016 | 7 | 2016 | 8 | 19.40 | 1.50 | 12.90 | 0.30 | 5.5 | 0.27 | 62.06 | 50.596 | -3.3 | 8.2 | 460 | 90.00 | In situ | Yes | No | Thermokarst | 5 | 5 | 0.01 | mg N2O/m2/d | GC/static | opaque | 40 | 5 | no | no | yes | Yang G et al. 2018 | |||||||||||
Great_Hing-an_Mountains_N2O | CH-Ghm-2013-01 | 9.84 | continuous | Alpine | Peatland | Vegetated | Peatland, Betula fruticosa dominance | China | Central Asia | Great Hing'an Mountains | 52.94 | 122.86 | 1 | 2013 | 5 | 2013 | 10 | 47.95 | 1.93 | 24.90 | 4.2 | 25.00 | 1.616 | -3.9 | 7.0 | 452 | 75.00 | In situ | No | No | none | 11 | 3 | 0.41 | µg N2O/m2/h | GC/static | opaque | 30 | 4 | no | no | yes | Cui Q et al. 2018 | |||||||||||||
Great_Hing-an_Mountains_N2O | CH-Ghm-2013-02 | 49.68 | continuous | Alpine | Peatland | Vegetated | Peatland, Ledum palustre dominance | China | Central Asia | Great Hing'an Mountains | 52.94 | 122.86 | 1 | 2013 | 5 | 2013 | 10 | 43.96 | 1.86 | 23.60 | 4.5 | 25.00 | 2.380 | -3.9 | 7.0 | 452 | 76.00 | In situ | No | No | none | 11 | 3 | 2.07 | µg N2O/m2/h | GC/static | opaque | 30 | 4 | no | no | yes | Cui Q et al. 2018 | |||||||||||||
Great_Hing-an_Mountains_N2O | CH-Ghm-2013-03 | 185.04 | continuous | Alpine | Peatland | Vegetated | Peatland, Betula fruticosa dominance | China | Central Asia | Great Hing'an Mountains | 52.94 | 122.86 | 1 | 2013 | 5 | 2013 | 10 | 47.95 | 1.93 | 23.60 | 4.2 | 25.00 | 1.616 | -3.9 | 9.0 | 452 | 81.00 | In situ | Yes | Yes | Warming | 11 | 3 | 7.71 | µg N2O/m2/h | GC/static | opaque | 30 | 4 | no | no | yes | Cui Q et al. 2018 | |||||||||||||
Great_Hing-an_Mountains_N2O | CH-Ghm-2013-04 | 189.36 | continuous | Alpine | Peatland | Vegetated | Peatland, Ledum palustre dominance | China | Central Asia | Great Hing'an Mountains | 52.94 | 122.86 | 1 | 2013 | 5 | 2013 | 10 | 43.96 | 1.86 | 24.90 | 4.5 | 25.00 | 2.380 | -3.9 | 9.0 | 452 | 82.00 | In situ | Yes | Yes | Warming | 11 | 3 | 7.89 | µg N2O/m2/h | GC/static | opaque | 30 | 4 | no | no | yes | Cui Q et al. 2018 | |||||||||||||
Great_Hing-an_Mountains_N2O | CH-Ghm-2014-01 | 109.20 | continuous | Alpine | Peatland | Vegetated | Peatland, Betula fruticosa dominance | China | Central Asia | Great Hing'an Mountains | 52.94 | 122.86 | 1 | 2014 | 5 | 2014 | 10 | 47.95 | 1.93 | 24.90 | 4.2 | 22.00 | 1.367 | -3.9 | 15.0 | 7.0 | 452 | 75.00 | In situ | No | No | none | 12 | 3 | 4.55 | µg N2O/m2/h | GC/static | opaque | 30 | 4 | no | no | yes | Cui Q et al. 2018 | ||||||||||||
Great_Hing-an_Mountains_N2O | CH-Ghm-2014-02 | 79.68 | continuous | Alpine | Peatland | Vegetated | Peatland, Ledum palustre dominance | China | Central Asia | Great Hing'an Mountains | 52.94 | 122.86 | 1 | 2014 | 5 | 2014 | 10 | 43.96 | 1.86 | 23.60 | 4.5 | 22.00 | 2.014 | -3.9 | 10.0 | 6.0 | 452 | 74.00 | In situ | No | No | none | 12 | 3 | 3.32 | µg N2O/m2/h | GC/static | opaque | 30 | 4 | no | no | yes | Cui Q et al. 2018 | ||||||||||||
Great_Hing-an_Mountains_N2O | CH-Ghm-2014-03 | 224.16 | continuous | Alpine | Peatland | Vegetated | Peatland, Betula fruticosa dominance | China | Central Asia | Great Hing'an Mountains | 52.94 | 122.86 | 1 | 2014 | 5 | 2014 | 10 | 47.95 | 1.93 | 23.60 | 4.2 | 22.00 | 1.367 | -3.9 | 15.6 | 9.0 | 452 | 83.00 | In situ | Yes | Yes | Warming | 12 | 3 | 9.34 | µg N2O/m2/h | GC/static | opaque | 30 | 4 | no | no | yes | Cui Q et al. 2018 | ||||||||||||
Great_Hing-an_Mountains_N2O | CH-Ghm-2014-04 | 163.92 | continuous | Alpine | Peatland | Vegetated | Peatland, Ledum palustre dominance | China | Central Asia | Great Hing'an Mountains | 52.94 | 122.86 | 1 | 2014 | 5 | 2014 | 10 | 43.96 | 1.86 | 24.90 | 4.5 | 22.00 | 2.014 | -3.9 | 10.6 | 8.0 | 452 | 82.00 | In situ | Yes | Yes | Warming | 12 | 3 | 6.83 | µg N2O/m2/h | GC/static | opaque | 30 | 4 | no | no | yes | Cui Q et al. 2018 | ||||||||||||
Great_Hing-an_Mountains_N2O | CH-Ghm-2015-01 | 15.36 | continuous | Alpine | Peatland | Vegetated | Peatland, Betula fruticosa dominance | China | Central Asia | Great Hing'an Mountains | 52.94 | 122.86 | 1 | 2015 | 5 | 2015 | 10 | 47.95 | 1.93 | 24.90 | 4.2 | 40.00 | 3.232 | -3.9 | 11.0 | 7.0 | 452 | 73.00 | In situ | No | No | none | 16 | 3 | 0.64 | µg N2O/m2/h | GC/static | opaque | 30 | 4 | no | no | yes | Cui Q et al. 2018 | ||||||||||||
Great_Hing-an_Mountains_N2O | CH-Ghm-2015-02 | 61.92 | continuous | Alpine | Peatland | Vegetated | Peatland, Ledum palustre dominance | China | Central Asia | Great Hing'an Mountains | 52.94 | 122.86 | 1 | 2015 | 5 | 2015 | 10 | 43.96 | 1.86 | 23.60 | 4.5 | 40.00 | 4.761 | -3.9 | 13.0 | 7.0 | 452 | 72.00 | In situ | No | No | none | 14 | 3 | 2.58 | µg N2O/m2/h | GC/static | opaque | 30 | 4 | no | no | yes | Cui Q et al. 2018 | ||||||||||||
Great_Hing-an_Mountains_N2O | CH-Ghm-2015-03 | 158.88 | continuous | Alpine | Peatland | Vegetated | Peatland, Betula fruticosa dominance | China | Central Asia | Great Hing'an Mountains | 52.94 | 122.86 | 1 | 2015 | 5 | 2015 | 10 | 47.95 | 1.93 | 23.60 | 4.2 | 40.00 | 3.232 | -3.9 | 11.6 | 9.0 | 452 | 82.00 | In situ | Yes | Yes | Warming | 16 | 3 | 6.62 | µg N2O/m2/h | GC/static | opaque | 30 | 4 | no | no | yes | Cui Q et al. 2018 | ||||||||||||
Great_Hing-an_Mountains_N2O | CH-Ghm-2015-04 | 200.16 | continuous | Alpine | Peatland | Vegetated | Peatland, Ledum palustre dominance | China | Central Asia | Great Hing'an Mountains | 52.94 | 122.86 | 1 | 2015 | 5 | 2015 | 10 | 43.96 | 1.86 | 24.90 | 4.5 | 40.00 | 4.761 | -3.9 | 13.6 | 9.0 | 452 | 82.00 | In situ | Yes | Yes | Warming | 14 | 3 | 8.34 | µg N2O/m2/h | GC/static | opaque | 30 | 4 | no | no | yes | Cui Q et al. 2018 | ||||||||||||
Haibei_N2O | CH-Hai-2000-01 | 1197.60 | sporadic | Alpine | Upland | Vegetated | Alpine meadow | China | Qinghai-Tibetan Plateau | Haibei | 37.60 | 101.20 | 10 | 2000 | 5 | 2014 | 9 | 3.35 | 9.10 | 1.87 | 7.4 | 0.75 | -1.7 | 560 | In situ | No | No | none | #200 | 49.90 | µg N2O/m2/h | GC/static | opaque | 30 | 4 | no | no | yes | Cao Y et al. 2018 | |||||||||||||||||
Haibei_N2O | CH-Hai-2000-02 | 648.00 | sporadic | Alpine | Upland | Vegetated | Alpine meadow | China | Qinghai-Tibetan Plateau | Haibei | 37.60 | 101.20 | 10 | 2000 | 5 | 2014 | 9 | 3.35 | 9.10 | 1.87 | 7.4 | 0.75 | -1.7 | 560 | In situ | No | No | none | #180 | 27.00 | µg N2O/m2/h | GC/static | opaque | 30 | 4 | no | no | yes | Cao Y et al. 2018 | |||||||||||||||||
Haibei_N2O | CH-Hai-2003-01 | 1147.20 | sporadic | Alpine | Upland | Vegetated | Alpine Kobresia humilis meadow, Herbaeous, HCK | China | Qinghai-Tibetan Plateau | Haibei | 37.53 | 101.25 | 4 | 2003 | 6 | 2006 | 6 | 5.50 | 7.3 | 0.75 | 40.30 | 53.6 | 43.718 | -0.8 | 560 | In situ | Yes | No | Grazing | 86 | 3 | 47.80 | µg N2O/m2/h | GC/static | opaque | 30 | 4 | no | no | yes | Du Y et al. 2008 | |||||||||||||||
Haibei_N2O | CH-Hai-2003-02 | 739.20 | sporadic | Alpine | Upland | Bare | Alpine Kobresia humilis meadow, Bare, BSK | China | Qinghai-Tibetan Plateau | Haibei | 37.53 | 101.25 | 4 | 2003 | 6 | 2006 | 6 | 5.50 | 7.3 | 0.75 | -0.8 | 560 | In situ | Yes | Yes | Plant removal | 90 | 3 | 30.80 | µg N2O/m2/h | GC/static | opaque | 30 | 4 | no | no | yes | Du Y et al. 2008 | ||||||||||||||||||
Haibei_N2O | CH-Hai-2003-03 | 1214.40 | sporadic | Alpine | Upland | Vegetated | Potentilla fructicosa shrub meadow, Herbaeous, HCP | China | Qinghai-Tibetan Plateau | Haibei | 37.53 | 101.25 | 4 | 2003 | 6 | 2006 | 6 | 5.70 | 6.4 | 0.88 | 35.90 | 99.6 | 49.579 | -0.8 | 560 | In situ | Yes | No | Grazing | 87 | 3 | 50.60 | µg N2O/m2/h | GC/static | opaque | 30 | 4 | no | no | yes | Du Y et al. 2008 | |||||||||||||||
Haibei_N2O | CH-Hai-2003-04 | 1454.40 | sporadic | Alpine | Upland | Vegetated | Potentilla fructicosa shrub meadow, Shrubs, SCP | China | Qinghai-Tibetan Plateau | Haibei | 37.53 | 101.25 | 4 | 2003 | 6 | 2006 | 6 | 5.70 | 6.4 | 0.88 | 99.6 | -0.8 | 560 | In situ | Yes | No | Grazing | 79 | 3 | 60.60 | µg N2O/m2/h | GC/static | opaque | 30 | 4 | no | no | yes | Du Y et al. 2008 | |||||||||||||||||
Haibei_N2O | CH-Hai-2003-05 | 967.20 | sporadic | Alpine | Upland | Bare | Potentilla fructicosa shrub meadow, Bare, BSP | China | Qinghai-Tibetan Plateau | Haibei | 37.53 | 101.25 | 4 | 2003 | 6 | 2006 | 6 | 5.70 | 6.4 | 0.88 | -0.8 | 560 | In situ | Yes | Yes | Plant removal | 81 | 3 | 40.30 | µg N2O/m2/h | GC/static | opaque | 30 | 4 | no | no | yes | Du Y et al. 2008 | ||||||||||||||||||
Haibei_N2O | CH-Hai-2003-06 | 556.80 | sporadic | Alpine | Upland | Vegetated | Alpine Kobresia humilis meadow, Herbaeous, HCK | China | Qinghai-Tibetan Plateau | Haibei | 37.53 | 101.25 | 3 | 2003 | 10 | 2006 | 4 | 5.50 | 7.3 | 0.75 | 40.30 | 53.6 | 43.718 | -0.8 | 560 | In situ | Yes | No | Grazing | 42 | 3 | 23.20 | µg N2O/m2/h | GC/static | opaque | 30 | 4 | no | no | yes | Du Y et al. 2008 | |||||||||||||||
Haibei_N2O | CH-Hai-2003-07 | 660.00 | sporadic | Alpine | Upland | Bare | Alpine Kobresia humilis meadow, Bare, BSK | China | Qinghai-Tibetan Plateau | Haibei | 37.53 | 101.25 | 3 | 2003 | 10 | 2006 | 4 | 5.50 | 7.3 | 0.75 | -0.8 | 560 | In situ | Yes | Yes | Plant removal | 50 | 3 | 27.50 | µg N2O/m2/h | GC/static | opaque | 30 | 4 | no | no | yes | Du Y et al. 2008 | ||||||||||||||||||
Haibei_N2O | CH-Hai-2003-08 | 513.60 | sporadic | Alpine | Upland | Vegetated | Potentilla fructicosa shrub meadow, Herbaeous, HCP | China | Qinghai-Tibetan Plateau | Haibei | 37.53 | 101.25 | 3 | 2003 | 10 | 2006 | 4 | 5.70 | 6.4 | 0.88 | 35.90 | 99.6 | 49.579 | -0.8 | 560 | In situ | Yes | No | Grazing | 42 | 3 | 21.40 | µg N2O/m2/h | GC/static | opaque | 30 | 4 | no | no | yes | Du Y et al. 2008 | |||||||||||||||
Haibei_N2O | CH-Hai-2003-09 | 818.40 | sporadic | Alpine | Upland | Vegetated | Potentilla fructicosa shrub meadow, Shrubs, SCP | China | Qinghai-Tibetan Plateau | Haibei | 37.53 | 101.25 | 3 | 2003 | 10 | 2006 | 4 | 5.70 | 6.4 | 0.88 | 99.6 | -0.8 | 560 | In situ | Yes | No | Grazing | 49 | 3 | 34.10 | µg N2O/m2/h | GC/static | opaque | 30 | 4 | no | no | yes | Du Y et al. 2008 | |||||||||||||||||
Haibei_N2O | CH-Hai-2003-10 | 828.00 | sporadic | Alpine | Upland | Bare | Potentilla fructicosa shrub meadow, Bare, BSP | China | Qinghai-Tibetan Plateau | Haibei | 37.53 | 101.25 | 3 | 2003 | 10 | 2006 | 4 | 5.70 | 6.4 | 0.88 | -0.8 | 560 | In situ | Yes | Yes | Plant removal | 48 | 3 | 34.50 | µg N2O/m2/h | GC/static | opaque | 30 | 4 | no | no | yes | Du Y et al. 2008 | ||||||||||||||||||
Haibei_N2O | CH-Hai-2005-01 | 117.82 | discontinuous | Alpine | Peatland | Vegetated | W1 Bog | China | Qinghai-Tibetan Plateau | Haibei | 37.62 | 101.32 | 1 | 2006 | 7 | 18 | 2006 | 7 | 18 | 20.90 | 2.22 | 9.50 | 6.9 | 0.82 | 69 | 68.900 | -1.7 | 18.2 | 561 | In situ | Yes | No | Grazing | 1 | 15 | 4.91 | µg N2O/m2/h | GC/static | opaque | 60 | 5 | yes | yes | yes | Kato T et al. 2011 | |||||||||||
Haibei_N2O | CH-Hai-2005-02 | 132.24 | discontinuous | Alpine | Upland | Vegetated | Alpine meadow | China | Qinghai-Tibetan Plateau | Haibei | 37.62 | 101.32 | 1 | 2005 | 7 | 21 | 2005 | 7 | 21 | -1.7 | 561 | in situ | Yes | No | Grazing | 1 | 4 | 5.51 | µg N2O/m2/h | GC/static | opaque | 60 | 5 | yes | yes | yes | Kato T et al. 2011 | |||||||||||||||||||
Haibei_N2O | CH-Hai-2005-03 | 94.32 | discontinuous | Alpine | Upland | Vegetated | Alpine shrubland | China | Qinghai-Tibetan Plateau | Haibei | 37.62 | 101.32 | 1 | 2005 | 7 | 23 | 2005 | 7 | 23 | -1.7 | 561 | in situ | Yes | No | Grazing | 1 | 4 | 3.93 | µg N2O/m2/h | GC/static | opaque | 60 | 5 | yes | yes | yes | Kato T et al. 2011 | |||||||||||||||||||
Haibei_N2O | CH-Hai-2005-04 | 4.30 | discontinuous | Alpine | Wetland | Vegetated | Alpine wetland | China | Qinghai-Tibetan Plateau | Haibei | 37.62 | 101.32 | 1 | 2005 | 7 | 25 | 2005 | 7 | 25 | -1.7 | 561 | in situ | Yes | No | Grazing | 1 | 4 | 0.18 | µg N2O/m2/h | GC/static | opaque | 60 | 5 | yes | yes | yes | Kato T et al. 2011 | |||||||||||||||||||
Haibei_N2O | CH-Hai-2005-05 | 19.44 | sporadic | Alpine | Upland | Vegetated | Alpine meadow | China | Qinghai-Tibetan Plateau | Haibei | 37.48 | 101.20 | 1 | 2005 | 7 | 21 | 2005 | 7 | 21 | 0.40 | -1.7 | 15.0 | 561 | In situ | Yes | No | Grazing | 4 | 4 | 0.81 | µg N2O/m2/h | GC/static | opaque | 60 | 5 | yes | no | yes | Kato T et al. 2013 | |||||||||||||||||
Haibei_N2O | CH-Hai-2005-06 | 72.24 | sporadic | Alpine | Upland | Vegetated | Alpine shrubland | China | Qinghai-Tibetan Plateau | Haibei | 37.48 | 101.20 | 1 | 2005 | 7 | 23 | 2005 | 7 | 23 | 0.32 | -1.7 | 15.0 | 561 | In situ | Yes | No | Grazing | 4 | 4 | 3.01 | µg N2O/m2/h | GC/static | opaque | 60 | 5 | yes | no | yes | Kato T et al. 2013 | |||||||||||||||||
Haibei_N2O | CH-Hai-2005-07 | -25.20 | sporadic | Alpine | Wetland | Vegetated | Alpine wetland | China | Qinghai-Tibetan Plateau | Haibei | 37.48 | 101.20 | 1 | 2005 | 7 | 25 | 2005 | 7 | 25 | 0.65 | -1.7 | 15.0 | 561 | In situ | Yes | No | Grazing | 4 | 4 | -1.05 | µg N2O/m2/h | GC/static | opaque | 60 | 5 | yes | no | yes | Kato T et al. 2013 | |||||||||||||||||
Haibei_N2O | CH-Hai-2005-08 | 9192.00 | sporadic | Alpine | Upland | Vegetated | Alpine meadow; Kobresia humilis, Festuca ovina, Elymus nutans, Poa spp., Carex spp., Scripus distigmaticus, Gentiana straminea, Gentiana farreri, Leontop odiumnanum, and Potentilla nivea | China | Qinghai-Tibetan Plateau | Haibei | 37.62 | 101.20 | 1 | 2005 | 7 | 24 | 2005 | 8 | 30 | 7.30 | 22.00 | 17.20 | 6.9 | 0.88 | 58 | 58.000 | -1.7 | 9.4 | 15.2 | 580 | In situ | Yes | No | Grazing | 15 | 4 | 383.00 | µg N2O/m2/h | GC/static | opaque | 30 | 4 | yes | yes | yes | Lin X et al. 2009 | ||||||||||
Haibei_N2O | CH-Hai-2006-01 | 72.00 | discontinuous | Alpine | Upland | Vegetated | D1 Meadow | China | Qinghai-Tibetan Plateau | Haibei | 36.70 | 99.55 | 1 | 2006 | 7 | 24 | 2006 | 7 | 24 | 5.70 | 0.95 | 5.90 | 0.18 | 31 | 30.600 | -1.7 | 18.4 | 561 | In situ | Yes | No | Grazing | 1 | 4 | 3.00 | µg N2O/m2/h | GC/static | opaque | 60 | 5 | yes | yes | yes | Kato T et al. 2011 | ||||||||||||
Haibei_N2O | CH-Hai-2006-02 | 3.38 | discontinuous | Alpine | Upland | Vegetated | D2 Dry steppe | China | Qinghai-Tibetan Plateau | Haibei | 36.43 | 98.23 | 1 | 2006 | 7 | 26 | 2006 | 7 | 26 | 0.68 | 0.21 | 3.00 | 0.17 | 28 | 27.700 | -1.7 | 28.8 | 561 | In situ | Yes | No | Grazing | 1 | 4 | 0.14 | µg N2O/m2/h | GC/static | opaque | 60 | 5 | yes | yes | yes | Kato T et al. 2011 | ||||||||||||
Haibei_N2O | CH-Hai-2006-03 | 126.00 | discontinuous | Alpine | Upland | Bare | D3 Desert | China | Qinghai-Tibetan Plateau | Haibei | 36.37 | 95.03 | 1 | 2006 | 7 | 28 | 2006 | 7 | 28 | 0.09 | 0.09 | 0.70 | 0.17 | 30 | 29.600 | -1.7 | 29.9 | 561 | In situ | Yes | No | Grazing | 1 | 4 | 5.25 | µg N2O/m2/h | GC/static | opaque | 60 | 5 | yes | yes | yes | Kato T et al. 2011 | ||||||||||||
Haibei_N2O | CH-Hai-2006-04 | 11.26 | discontinuous | Alpine | Upland | Vegetated | D4 Steppe | China | Qinghai-Tibetan Plateau | Haibei | 35.78 | 94.33 | 1 | 2006 | 7 | 30 | 2006 | 7 | 30 | 0.53 | 0.20 | 2.50 | 0.03 | 6 | 6.000 | -1.7 | 25.1 | 561 | In situ | Yes | No | Grazing | 1 | 4 | 0.47 | µg N2O/m2/h | GC/static | opaque | 60 | 5 | yes | yes | yes | Kato T et al. 2011 | ||||||||||||
Haibei_N2O | CH-Hai-2006-05 | 22.51 | discontinuous | Alpine | Upland | Vegetated | D5 Sandy grassland | China | Qinghai-Tibetan Plateau | Haibei | 35.75 | 94.30 | 1 | 2006 | 7 | 30 | 2006 | 7 | 30 | 0.04 | 0.07 | 0.40 | 0.04 | 9 | 8.600 | -1.7 | 18.2 | 561 | In situ | Yes | No | Grazing | 1 | 4 | 0.94 | µg N2O/m2/h | GC/static | opaque | 60 | 5 | yes | yes | yes | Kato T et al. 2011 | ||||||||||||
Haibei_N2O | CH-Hai-2006-06 | -10.63 | discontinuous | Alpine | Upland | Vegetated | D6 Steppe | China | Qinghai-Tibetan Plateau | Haibei | 34.10 | 92.38 | 1 | 2006 | 8 | 1 | 2006 | 8 | 1 | 1.79 | 0.30 | 5.80 | 0.05 | 9 | 8.900 | -1.7 | 24.4 | 561 | In situ | Yes | No | Grazing | 1 | 4 | -0.44 | µg N2O/m2/h | GC/static | opaque | 60 | 5 | yes | yes | yes | Kato T et al. 2011 | ||||||||||||
Haibei_N2O | CH-Hai-2006-07 | -46.03 | discontinuous | Alpine | Upland | Vegetated | D7 Grassland | China | Qinghai-Tibetan Plateau | Haibei | 30.53 | 91.05 | 1 | 2006 | 8 | 4 | 2006 | 8 | 4 | 6.68 | 0.69 | 9.50 | 0.10 | 16 | 16.300 | -1.7 | 21.7 | 561 | In situ | Yes | No | Grazing | 1 | 4 | -1.92 | µg N2O/m2/h | GC/static | opaque | 60 | 5 | yes | yes | yes | Kato T et al. 2011 | ||||||||||||
Haibei_N2O | CH-Hai-2006-08 | -48.38 | discontinuous | Alpine | Upland | Vegetated | D8 Meadow | China | Qinghai-Tibetan Plateau | Haibei | 32.83 | 91.92 | 1 | 2006 | 8 | 9 | 2006 | 8 | 9 | 2.63 | 0.32 | 8.20 | 0.14 | 28 | 28.200 | -1.7 | 16.2 | 561 | In situ | Yes | No | Grazing | 1 | 4 | -2.02 | µg N2O/m2/h | GC/static | opaque | 60 | 5 | yes | yes | yes | Kato T et al. 2011 | ||||||||||||
Haibei_N2O | CH-Hai-2006-09 | -34.22 | discontinuous | Alpine | Upland | Vegetated | D9 Sandy steppe | China | Qinghai-Tibetan Plateau | Haibei | 34.33 | 92.60 | 1 | 2006 | 8 | 11 | 2006 | 8 | 11 | 0.18 | 0.02 | 23.50 | 0.03 | 5 | 5.400 | -1.7 | 30.9 | 561 | In situ | Yes | No | Grazing | 1 | 4 | -1.43 | µg N2O/m2/h | GC/static | opaque | 60 | 5 | yes | yes | yes | Kato T et al. 2011 | ||||||||||||
Haibei_N2O | CH-Hai-2006-10 | -14.62 | discontinuous | Alpine | Wetland | Vegetated | W2 Marsh | China | Qinghai-Tibetan Plateau | Haibei | 36.75 | 99.60 | 1 | 2006 | 7 | 24 | 2006 | 7 | 24 | 11.11 | 1.31 | 8.40 | 8.1 | 0.85 | 96 | 95.700 | -1.7 | 10.7 | 561 | In situ | Yes | No | Grazing | 1 | 4 | -0.61 | µg N2O/m2/h | GC/static | opaque | 60 | 5 | yes | yes | yes | Kato T et al. 2011 | |||||||||||
Haibei_N2O | CH-Hai-2006-11 | -4.49 | discontinuous | Alpine | Wetland | Vegetated | W3 Patchy marsh | China | Qinghai-Tibetan Plateau | Haibei | 36.47 | 98.27 | 1 | 2006 | 7 | 26 | 2006 | 7 | 26 | 1.76 | 0.20 | 11.60 | 7.7 | 0.61 | 95 | 95.100 | -1.7 | 11.4 | 561 | In situ | Yes | No | Grazing | 1 | 4 | -0.19 | µg N2O/m2/h | GC/static | opaque | 60 | 5 | yes | yes | yes | Kato T et al. 2011 | |||||||||||
Haibei_N2O | CH-Hai-2006-12 | -56.26 | discontinuous | Alpine | Wetland | Vegetated | W4 Salt marsh | China | Qinghai-Tibetan Plateau | Haibei | 36.60 | 95.00 | 1 | 2006 | 7 | 28 | 2006 | 7 | 28 | 3.04 | 0.44 | 6.90 | 8.3 | 0.61 | 83 | 83.200 | -1.7 | 16.5 | 561 | In situ | Yes | No | Grazing | 1 | 4 | -2.34 | µg N2O/m2/h | GC/static | opaque | 60 | 5 | yes | yes | yes | Kato T et al. 2011 | |||||||||||
Haibei_N2O | CH-Hai-2006-13 | -24.74 | discontinuous | Alpine | Wetland | Vegetated | W5 Patchy marsh | China | Qinghai-Tibetan Plateau | Haibei | 34.12 | 92.37 | 1 | 2006 | 8 | 1 | 2006 | 8 | 1 | 4.61 | 0.57 | 8.10 | 7.9 | 0.70 | 96 | 95.800 | -1.7 | 7.4 | 561 | In situ | Yes | No | Grazing | 1 | 4 | -1.03 | µg N2O/m2/h | GC/static | opaque | 60 | 5 | yes | yes | yes | Kato T et al. 2011 | |||||||||||
Haibei_N2O | CH-Hai-2006-14 | 2.26 | discontinuous | Alpine | Peatland | Vegetated | W6 Bog | China | Qinghai-Tibetan Plateau | Haibei | 30.47 | 91.07 | 1 | 2006 | 8 | 3 | 2006 | 8 | 3 | 21.45 | 1.94 | 11.00 | 7.5 | 0.83 | 92 | 92.500 | -1.7 | 13.6 | 561 | In situ | Yes | No | Grazing | 1 | 10 | 0.09 | µg N2O/m2/h | GC/static | opaque | 60 | 5 | yes | yes | yes | Kato T et al. 2011 | |||||||||||
Haibei_N2O | CH-Hai-2006-15 | -23.62 | discontinuous | Alpine | Wetland | Vegetated | W7 Marsh | China | Qinghai-Tibetan Plateau | Haibei | 32.85 | 91.92 | 1 | 2006 | 8 | 9 | 2006 | 8 | 9 | 5.58 | 0.76 | 6.90 | 7.6 | 0.66 | 95 | 94.700 | -1.7 | 7.9 | 561 | In situ | Yes | No | Grazing | 1 | 10 | -0.98 | µg N2O/m2/h | GC/static | opaque | 60 | 5 | yes | yes | yes | Kato T et al. 2011 | |||||||||||
Haibei_N2O | CH-Hai-2006-16 | 6.24 | sporadic | Alpine | Wetland | Vegetated | Alpine wetland | China | Qinghai-Tibetan Plateau | Haibei | 37.48 | 101.20 | 1 | 2006 | 3 | 8 | 2006 | 3 | 8 | -1.7 | -2.0 | 561 | In situ | Yes | No | Grazing | 4 | 2 | 0.26 | µg N2O/m2/h | GC/static | opaque | 90 | 5 | yes | no | yes | Kato T et al. 2013 | ||||||||||||||||||
Haibei_N2O | CH-Hai-2006-17 | 31.20 | sporadic | Alpine | Upland | Vegetated | Alpine meadow | China | Qinghai-Tibetan Plateau | Haibei | 37.48 | 101.20 | 1 | 2006 | 3 | 4 | 2006 | 3 | 4 | -1.7 | -2.0 | 561 | In situ | Yes | No | Grazing | 4 | 2 | 1.30 | µg N2O/m2/h | GC/static | opaque | 90 | 5 | yes | no | yes | Kato T et al. 2013 | ||||||||||||||||||
Haibei_N2O | CH-Hai-2006-18 | 198.96 | sporadic | Alpine | Upland | Vegetated | Alpine shrubland | China | Qinghai-Tibetan Plateau | Haibei | 37.48 | 101.20 | 1 | 2006 | 3 | 6 | 2006 | 3 | 6 | -1.7 | -2.0 | 561 | In situ | Yes | No | Grazing | 4 | 2 | 8.29 | µg N2O/m2/h | GC/static | opaque | 90 | 5 | yes | no | yes | Kato T et al. 2013 | ||||||||||||||||||
Haibei_N2O | CH-Hai-2006-19 | 1296.00 | sporadic | Alpine | Upland | Vegetated | Alpine meadow; Kobresia humilis, Festuca ovina, Elymus nutans, Poa spp., Carex spp., Scripus distigmaticus, Gentiana straminea, Gentiana farreri, Leontop odiumnanum, and Potentilla nivea | China | Qinghai-Tibetan Plateau | Haibei | 37.62 | 101.20 | 1 | 2006 | 8 | 2 | 2006 | 8 | 18 | 7.30 | 1.70 | 15.70 | 6.9 | 0.88 | 52 | 52.000 | -1.7 | 8.2 | 12.8 | 580 | In situ | Yes | No | Grazing | 21 | 4 | 54.00 | µg N2O/m2/h | GC/static | opaque | 30 | 4 | yes | yes | yes | Lin X et al. 2009 | ||||||||||
Haibei_N2O | CH-Hai-2008-01 | 45.80 | sporadic | Alpine | Upland | Vegetated | Alpine meadow | China | Qinghai-Tibetan Plateau | Haibei | 37.62 | 101.20 | 1 | 2008 | 5 | 2008 | 9 | 4.28 | 0.42 | 10.20 | 12.07 | 56 | 56.000 | -1.7 | 10.3 | 9.7 | 580 | In situ | No | No | none | 20 | 3 | 12.20 | kg CO2-eq/ha | GC/static | opaque | 30 | 4 | yes | yes | yes | Jiang C et al. 2010 | |||||||||||||
Haibei_N2O | CH-Hai-2008-02 | 52.93 | sporadic | Alpine | Upland | Vegetated | Alpine meadow | China | Qinghai-Tibetan Plateau | Haibei | 37.62 | 101.20 | 1 | 2008 | 5 | 2008 | 9 | 12.07 | -1.7 | 10.3 | 9.7 | 580 | in situ | Yes | Yes | N-addition | 20 | 3 | 14.10 | kg CO2-eq/ha | GC/static | opaque | 30 | 4 | yes | yes | yes | Jiang C et al. 2010 | ||||||||||||||||||
Haibei_N2O | CH-Hai-2012-01 | 1064.16 | sporadic | Alpine | Upland | Vegetated | Alpine Kobresia humilis meadow | China | Qinghai-Tibetan Plateau | Haibei | 37.53 | 101.25 | 1 | 2012 | 6 | 2012 | 9 | 5.50 | 7.3 | 0.75 | 53.6 | -1.7 | 560 | In situ | Yes | No | Grazing | 14 | 3 | 44.34 | µg N2O/m2/h | GC/static | 30 | 4 | no | no | yes | Du Y et al. 2016a | ||||||||||||||||||
Haibei_N2O | CH-Hai-2012-02 | 1795.92 | sporadic | Alpine | Upland | Vegetated | Alpine Kobresia humilis meadow | China | Qinghai-Tibetan Plateau | Haibei | 37.53 | 101.25 | 1 | 2012 | 6 | 2012 | 9 | 0.75 | -1.7 | 560 | In situ | Yes | Yes | N-addition | 14 | 3 | 74.83 | µg N2O/m2/h | GC/static | 30 | 4 | no | no | yes | Du Y et al. 2016a | |||||||||||||||||||||
Haibei_N2O | CH-Hai-2012-03 | 1637.76 | sporadic | Alpine | Upland | Vegetated | Alpine Kobresia humilis meadow | China | Qinghai-Tibetan Plateau | Haibei | 37.53 | 101.25 | 1 | 2012 | 6 | 2012 | 9 | 0.75 | -1.7 | 560 | In situ | Yes | Yes | Water addition | 14 | 3 | 68.24 | µg N2O/m2/h | GC/static | 30 | 4 | no | no | yes | Du Y et al. 2016a | |||||||||||||||||||||
Haibei_N2O | CH-Hai-2012-04 | 1537.92 | sporadic | Alpine | Upland | Vegetated | Alpine Kobresia humilis meadow | China | Qinghai-Tibetan Plateau | Haibei | 37.53 | 101.25 | 1 | 2012 | 6 | 2012 | 9 | 0.75 | -1.7 | 560 | In situ | Yes | Yes | N-addition, Water addition | 14 | 3 | 64.08 | µg N2O/m2/h | GC/static | 30 | 4 | no | no | yes | Du Y et al. 2016a | |||||||||||||||||||||
Haibei_N2O | CH-Hai-2013-01 | 688.66 | sporadic | Alpine | Upland | Vegetated | Alpine Kobresia humilis meadow | China | Qinghai-Tibetan Plateau | Haibei | 37.53 | 101.25 | 1 | 2013 | 1 | 2013 | 12 | 3.12 | 0.93 | 3.40 | 3.80 | 2.30 | 8.4 | 5.36 | 0.75 | -1.7 | 560 | In situ | Yes | No | Grazing | 30 | 3 | 1.60 | kg N/ha | GC/static | opaque | 30 | 4 | no | no | yes | Du Y et al. 2016b | |||||||||||||
Haibei_N2O | CH-Hai-2013-02 | 736.00 | sporadic | Alpine | Upland | Vegetated | Alpine Kobresia humilis meadow | China | Qinghai-Tibetan Plateau | Haibei | 37.53 | 101.25 | 1 | 2014 | 1 | 2014 | 12 | 3.12 | 0.93 | 3.40 | 3.80 | 2.30 | 8.4 | 5.36 | 0.75 | -1.7 | 560 | In situ | Yes | No | Grazing | 31 | 3 | 1.71 | kg N/ha | GC/static | opaque | 30 | 4 | no | no | yes | Du Y et al. 2016b | |||||||||||||
Haibei_N2O | CH-Hai-2013-03 | 25.85 | sporadic | Alpine | Upland | Vegetated | Alpine desert-steppe | China | Qinghai-Tibetan Plateau | Haibei | 35.88 | 94.55 | 1 | 2013 | 5 | 2013 | 10 | 0.40 | 0.04 | 9.90 | 3.08 | 1.66 | 8.8 | 1.29 | 4.05 | 11.054 | -4.2 | 42 | In situ | No | No | none | 3 | 25.85 | µg N2O/m2/d | GC/static | opaque | 25 | 6 | yes | yes | yes | Li Y et al. 2015 | |||||||||||||
Haibei_N2O | CH-Hai-2013-04 | 154.11 | sporadic | Alpine | Upland | Vegetated | Alpine meadow | China | Qinghai-Tibetan Plateau | Haibei | 37.60 | 101.20 | 1 | 2013 | 5 | 2013 | 10 | 4.69 | 0.72 | 6.50 | 8.16 | 5.89 | 7.7 | 0.77 | 19.95 | 27.997 | -1.7 | 580 | In situ | No | No | none | 3 | 154.11 | µg N2O/m2/d | GC/static | opaque | 25 | 6 | yes | yes | yes | Li Y et al. 2015 | |||||||||||||
Haibei_N2O | CH-Hai-2013-05 | 195.84 | discontinuous | Alpine | Upland | Vegetated | Alpine steppe | China | Qinghai-Tibetan Plateau | Haibei | 37.53 | 100.22 | 1 | 2013 | 5 | 2013 | 10 | 3.05 | 0.60 | 5.10 | 6.64 | 5.20 | 8.1 | 0.98 | 13.05 | 24.293 | -2.7 | 275 | In situ | No | No | none | 3 | 195.84 | µg N2O/m2/d | GC/static | opaque | 25 | 6 | yes | yes | yes | Li Y et al. 2015 | |||||||||||||
Fenghuo_Mountains_N2O | CH-Hai-2014-01 | 37.00 | sporadic | Alpine | Upland | Vegetated | Alpine Kobresia humilis meadow | China | Qinghai-Tibetan Plateau | Fenghuo Mountains | 34.73 | 92.90 | 2 | 2014 | 5 | 15 | 2015 | 8 | 15 | 3.07 | 0.26 | 11.80 | 9.49 | 18.13 | 9.1 | 5.50 | 32.40 | 76.946 | -5.3 | 5.4 | 6.4 | 270 | 115.00 | In situ | No | No | none | 61 | 4 | 37.00 | µg N2O/m2/d | GC/static | opaque | 30 | 4 | no | no | yes | Chang R et al. 2017 | |||||||
Fenghuo_Mountains_N2O | CH-Hai-2014-02 | 203.00 | sporadic | Alpine | Upland | Vegetated | Alpine Kobresia humilis meadow | China | Qinghai-Tibetan Plateau | Fenghuo Mountains | 34.73 | 92.90 | 2 | 2014 | 5 | 15 | 2015 | 8 | 15 | 2.23 | 0.24 | 9.30 | 4.43 | 6.05 | 8.6 | 5.50 | 26.30 | 66.774 | -5.3 | 9.9 | 11.9 | 270 | 115.00 | In situ | Yes | Yes | Warming | 61 | 4 | 203.00 | µg N2O/m2/d | GC/static | opaque | 30 | 4 | no | no | yes | Chang R et al. 2017 | |||||||
Luanhaizi_N2O | CH-Lua-2012-01 | -34.44 | sporadic | Alpine | Wetland | Vegetated | North-East part of the Plateau, experiencing natural high N deposition | China | Qinghai-Tibetan Plateau | Luanhaizi | 37.58 | 101.33 | 2012 | 6 | 2012 | 9 | 16.20 | 1.10 | 14.70 | 7.7 | -1.1 | 12.0 | 480 | Mesocosm | Yes | Yes | naturally high N-deposition | 15 | 5 | -3.10 | mg N2O/m2 | GC/static | opaque | 30 | 4 | yes | yes | yes | Wang H et al. 2017 | |||||||||||||||||
Luanhaizi_N2O | CH-Lua-2013-01 | -86.67 | sporadic | Alpine | Wetland | Vegetated | North-East part of the Plateau, experiencing natural high N deposition | China | Qinghai-Tibetan Plateau | Luanhaizi | 37.58 | 101.33 | 2013 | 6 | 2013 | 9 | 16.20 | 1.10 | 14.70 | 7.7 | -1.1 | 12.0 | 480 | Mesocosm | Yes | Yes | naturally high N-deposition | 9 | 5 | -7.80 | mg N2O/m2 | GC/static | opaque | 30 | 4 | yes | yes | yes | Wang H et al. 2017 | |||||||||||||||||
Inner_Mongolia_N2O | CH-Mon-2008-01 | 136.32 | isolated | Alpine | Upland | Vegetated | Meadow Steppe; S. baicalensis, Leymus chinensis, Carex pediformis, Artemisia tanacetifolia, Melissitus ruthenica, Bupleurum scorzonerifolium, and Vicia amoena | China | Central Asia | Inner Mongolia | 49.33 | 119.94 | 2 | 2008 | 5 | 2009 | 9 | 5.10 | 0.20 | 25.50 | 13.40 | 4.60 | 5.9 | 1.22 | 40 | 40.000 | -3.0 | 375 | In situ | No | No | none | 30 | 3 | 5.68 | µg N2O/m2/h | GC/static | opaque | 30 | 4 | no | yes | yes | Liu X et al. 2017 | ||||||||||||
Nagqu_N2O | CH-Nag-2015-01 | 129.60 | sporadic | Alpine | Upland | Vegetated | Dry Alpine meadow; sedges Kobresia pygmaea and the grass stipa purpurea are the main graminoids, and Potentilla acaulis and Oxytropis ochrocephala are the main forbs | China | Qinghai-Tibetan Plateau | Nagqu | 31.44 | 92.02 | 1 | 2015 | 5 | 2015 | 9 | 22.98 | 1.83 | 12.60 | 25.20 | 16.85 | 7.4 | 1.01 | 0.19 | 30 | 30.000 | -1.2 | 8.3 | 10.9 | 432 | In situ | No | No | none | 21 | 4 | 5.40 | µg N2O/m2/h | GC/static | opaque | 30 | 4 | no | no | yes | Yan Y et al. 2018 | |||||||||
Nagqu_N2O | CH-Nag-2016-01 | 108.00 | sporadic | Alpine | Upland | Vegetated | Dry Alpine meadow; sedges Kobresia pygmaea and the grass stipa purpurea are the main graminoids, and Potentilla acaulis and Oxytropis ochrocephala are the main forbs | China | Qinghai-Tibetan Plateau | Nagqu | 31.44 | 92.02 | 1 | 2016 | 5 | 2016 | 9 | 22.98 | 1.83 | 12.60 | 44.18 | 16.61 | 7.4 | 1.01 | 0.20 | 33 | 33.000 | -1.2 | 8.1 | 11.5 | 432 | In situ | No | No | none | 21 | 4 | 4.50 | µg N2O/m2/h | GC/static | opaque | 30 | 4 | no | no | yes | Yan Y et al. 2018 | |||||||||
Wudaoliang_N2O | CH-Wud-2000-01 | 19.01 | discontinuous | Alpine | Upland | Vegetated | Alpine grassland; Stipa lawn community dominated by Stipa purpurea | China | Qinghai-Tibetan Plateau | Wudaoliang | 35.22 | 93.08 | 1 | 2000 | 7 | 2001 | 7 | 0.15 | 0.04 | 3.80 | 9.0 | 3.61 | 10.802 | -5.6 | 300 | In situ | No | No | none | 12 | 3 | 0.00 | µmol N2O/m2/s1 | GC/static | opaque | 40 | 4 | no | no | yes | Pei Z et al. 2004 | |||||||||||||||
Zackenberg_N2O | DK-Zac-2008-01 | 400.00 | continuous | Arctic | Wetland | Vegetated | Wetland tundra | Denmark | Greenland | Zackenberg | 74.50 | -20.50 | 2008 | 2008 | 2.30 | 0.15 | 15.30 | 6.0 | 100 | 100.000 | -9.5 | 7.0 | 250 | 60.00 | Mesocosm | Yes | No | mesocosm | 3 | 1 | 0.40 | mg N2O/m2/d | GC/static | 1440 | no | no | yes | Elberling B et al. 2010 | ||||||||||||||||||
Zackenberg_N2O | DK-Zac-2008-02 | 3800.00 | continuous | Arctic | Wetland | Vegetated | Wetland tundra | Denmark | Greenland | Zackenberg | 74.50 | -20.50 | 2008 | 2008 | 2.30 | 0.15 | 15.30 | 6.0 | 100 | 100.000 | -9.5 | 7.0 | 250 | 60.00 | Mesocosm | Yes | Yes | Permafrost thaw | 3 | 1 | 3.80 | mg N2O/m2/d | GC/static | 1440 | no | no | yes | Elberling B et al. 2010 | ||||||||||||||||||
Zackenberg_N2O | DK-Zac-2008-03 | 34000.00 | continuous | Arctic | Wetland | Vegetated | Wetland tundra | Denmark | Greenland | Zackenberg | 74.50 | -20.50 | 2008 | 2008 | 2.30 | 0.15 | 15.30 | 6.0 | 100 | 100.000 | -9.5 | 7.0 | 250 | 60.00 | Mesocosm | Yes | Yes | Permafrost thaw, N-addition, Water addition | 3 | 1 | 34.00 | mg N2O/m2/d | GC/static | 1440 | no | no | yes | Elberling B et al. 2010 | ||||||||||||||||||
Kilpisjaervi_N2O | FI-Kil-2012-01 | 560.00 | discontinuous | Subarctic | Peatland | Bare | Palsa, bare, dry | Finland | Northern Scandinavia | Kilpisjärvi | 68.89 | 21.05 | 2012 | 2012 | 48.47 | 1.67 | 30.30 | 66.00 | 5.40 | 3.5 | 92.00 | 0.18 | 70.30 | 55 | 55.000 | -1.9 | 10.0 | 487 | 65.00 | Mesocosm | Yes | No | mesocosm | 26 | 4 | 0.56 | mg N2O/m2/d | GC/static | transparent | 30 | 4 | yes | yes | yes | Voigt C et al. 2017a, Voigt et al. 2019 | |||||||||||
Kilpisjaervi_N2O | FI-Kil-2012-02 | 140.00 | discontinuous | Subarctic | Peatland | Vegetated | Palsa, vegetated, dry | Finland | Northern Scandinavia | Kilpisjärvi | 68.89 | 21.05 | 2012 | 2012 | 47.64 | 1.74 | 27.70 | 58.00 | 4.80 | 3.8 | 92.00 | 0.18 | 75.77 | 57 | 56.900 | -1.9 | 10.0 | 487 | 65.00 | Mesocosm | Yes | No | mesocosm | 32 | 4 | 0.14 | mg N2O/m2/d | GC/static | transparent | 30 | 4 | yes | yes | yes | Voigt C et al. 2017a, Voigt et al. 2019 | |||||||||||
Kilpisjaervi_N2O | FI-Kil-2012-03 | 200.00 | discontinuous | Subarctic | Peatland | Bare | Palsa, bare, wet | Finland | Northern Scandinavia | Kilpisjärvi | 68.89 | 21.05 | 2012 | 2012 | 48.24 | 1.82 | 30.50 | 58.00 | 2.10 | 3.9 | 0.17 | 82.89 | 92 | 91.900 | -1.9 | 10.0 | 487 | 65.00 | Mesocosm | Yes | Yes | Water addition | 30 | 4 | 0.20 | mg N2O/m2/d | GC/static | transparent | 30 | 4 | yes | yes | yes | Voigt C et al. 2017a, Voigt et al. 2019 | ||||||||||||
Kilpisjaervi_N2O | FI-Kil-2012-04 | 80.00 | discontinuous | Subarctic | Peatland | Vegetated | Palsa, vegetated, wet | Finland | Northern Scandinavia | Kilpisjärvi | 68.89 | 21.05 | 2012 | 2012 | 47.25 | 1.98 | 24.40 | 61.00 | 2.00 | 3.7 | 0.17 | 83.40 | 86 | 86.000 | -1.9 | 10.0 | 487 | 65.00 | Mesocosm | Yes | Yes | Water addition | 30 | 4 | 0.08 | mg N2O/m2/d | GC/static | transparent | 30 | 4 | yes | yes | yes | Voigt C et al. 2017a, Voigt et al. 2019 | ||||||||||||
Sodankylae_N2O | FI-Sod-2012-01 | 61.46 | none | Subarctic | Peatland | Vegetated | Fen | Finland | Northern Scandinavia | Sodankylä | 67.37 | 26.65 | 1 | 2012 | 7 | 12 | 2012 | 8 | 2 | -0.4 | 527 | In situ | No | No | none | 10 | 39 | 1.63 | µg N/m2/h | GC/static | opaque | 45 | 4 | no | yes | yes | Dinsmore KJ et al. 2017 | |||||||||||||||||||
Sodankylae_N2O | FI-Sod-2012-02 | 28.28 | none | Subarctic | Upland | Vegetated | Scots pine forest | Finland | Northern Scandinavia | Sodankylä | 67.37 | 26.63 | 1 | 2012 | 7 | 12 | 2012 | 8 | 2 | -0.4 | 527 | In situ | No | No | none | 10 | 21 | 0.75 | µg N/m2/h | GC/static | opaque | 45 | 4 | no | yes | yes | Dinsmore KJ et al. 2017 | |||||||||||||||||||
Utsjoki_N2O | FI-Uts-2009-01 | 2600.00 | discontinuous | Subarctic | Peatland | Bare | Palsa, bare | Finland | Northern Scandinavia | Utsjoki | 69.58 | 26.18 | 1 | 2009 | 8 | 2009 | 8 | 53.00 | 2.00 | 25.00 | 65.00 | 51.00 | 3.5 | 94.00 | 0.20 | 70.40 | 33 | 33.000 | -1.7 | 19.1 | 414 | 45.00 | In situ | No | No | none | 1 | 21 | 2.60 | mg N2O/m2/d | GC/static | opaque | 30 | 5 | no | no | yes | Maruschchak ME et al. 2011 | ||||||||
Utsjoki_N2O | FI-Uts-2009-02 | 0.01 | discontinuous | Subarctic | Upland | Bare | Mineral soil, frost boil | Finland | Northern Scandinavia | Utsjoki | 69.58 | 26.18 | 1 | 2009 | 8 | 2009 | 8 | 0.70 | 0.04 | 15.00 | 1.20 | 0.00 | 6.1 | 4.30 | 1.54 | 19.80 | 98.776 | -1.7 | 18.4 | 414 | >60.00 | In situ | No | No | none | 1 | 3 | 0.00 | mg N2O/m2/d | GC/static | opaque | 30 | 5 | no | no | yes | Maruschchak ME et al. 2011 | |||||||||
Utsjoki_N2O | FI-Uts-2009-03 | 200.00 | discontinuous | Subarctic | Peatland | Vegetated | Palsa, vegetated | Finland | Northern Scandinavia | Utsjoki | 69.58 | 26.18 | 1 | 2009 | 8 | 2009 | 8 | 53.00 | 2.10 | 26.00 | 7.80 | 3.70 | 3.5 | 96.00 | 0.21 | 59.20 | 17 | 17.000 | -1.7 | 18.1 | 414 | 53.00 | In situ | No | No | none | 1 | 6 | 0.20 | mg N2O/m2/d | GC/static | opaque | 30 | 5 | no | no | yes | Maruschchak ME et al. 2011 | ||||||||
Ny-Alesund_N2O | NO-Nya-2008-01 | 573.60 | continuous | Arctic | Upland | Vegetated | Seabird sanctuary tundra (SBT-H1), high seabird- activity; 2% barren surface; vegetation includes mosses, lichens and sedges | Norway | Svalbard | Ny-Alesund | 79.92 | 11.93 | 1 | 2008 | 7 | 26 | 2008 | 8 | 10 | 22.60 | 0.85 | 26.60 | 47.58 | 14.74 | 7.5 | 68.70 | 38.445 | -5.8 | 2.1 | 400 | 200.00 | In situ | Yes | No | Birds | 8 | 3 | 23.90 | µg N2O/m2/h | GC/static | transparent | 45 | 3 | no | yes | yes | Zhu R et al. 2012 | |||||||||
Ny-Alesund_N2O | NO-Nya-2008-02 | 110.40 | continuous | Arctic | Upland | Vegetated | Seabird sanctuary tundra (SBT-L1), low seabird activity. 2% barren surface; vegetation includes mosses, lichens and sedges | Norway | Svalbard | Ny-Alesund | 79.92 | 11.93 | 1 | 2008 | 7 | 26 | 2008 | 8 | 10 | 4.99 | 0.20 | 24.50 | 27.15 | 3.45 | 6.8 | 20.40 | 29.925 | -5.8 | 2.1 | 400 | 200.00 | In situ | Yes | No | Birds | 8 | 3 | 4.60 | µg N2O/m2/h | GC/static | transparent | 45 | 3 | no | yes | yes | Zhu R et al. 2012 | |||||||||
Ny-Alesund_N2O | NO-Nya-2008-03 | 172.80 | continuous | Arctic | Upland | Vegetated | Seabird sanctuary tundra (SBT-M1), medium seabird-activity; 2% barren surface; vegetation includes mosses, lichens and sedges | Norway | Svalbard | Ny-Alesund | 79.92 | 11.93 | 1 | 2008 | 7 | 26 | 2008 | 8 | 10 | 4.50 | 0.21 | 21.00 | 5.36 | 3.88 | 7.7 | 33.20 | 62.720 | -5.8 | 2.1 | 400 | 200.00 | In situ | Yes | No | Birds | 8 | 3 | 7.20 | µg N2O/m2/h | GC/static | transparent | 45 | 3 | no | yes | yes | Zhu R et al. 2012 | |||||||||
Ny-Alesund_N2O | NO-Nya-2009-01 | 8.81 | continuous | Arctic | Wetland | Vegetated | LT Lowland tundra | Norway | Svalbard | Ny-Alesund | 79.92 | 11.93 | 1 | 2009 | 7 | 13 | 2009 | 7 | 23 | 12.05 | 0.47 | 31.40 | 142.24 | 11.57 | 6.7 | 0.40 | 18.311 | -5.8 | 400 | In situ | No | No | none | 62 | 13 | 0.37 | µg N2O/m2/h | GC/static | 45 | 4 | no | yes | yes | Chen Q et al. 2014 | ||||||||||||
Ny-Alesund_N2O | NO-Nya-2009-02 | 189.60 | continuous | Arctic | Upland | Vegetated | BT Tundra, high seabird-activity | Norway | Svalbard | Ny-Alesund | 79.92 | 11.93 | 1 | 2009 | 7 | 21 | 2009 | 7 | 26 | 22.44 | 0.64 | 61.70 | 151.99 | 12.52 | 7.1 | 0.62 | 10.980 | -5.8 | 400 | In situ | Yes | No | Birds | 44 | 7 | 7.90 | µg N2O/m2/h | GC/static | 45 | 4 | no | yes | yes | Chen Q et al. 2014 | ||||||||||||
Ny-Alesund_N2O | NO-Nya-2009-03 | 1891.20 | continuous | Arctic | Upland | Vegetated | ST Tundra, anthropogenic activities (research stations) | Norway | Svalbard | Ny-Alesund | 79.92 | 11.93 | 2 | 2008 | 7 | 25 | 2009 | 7 | 24 | 32.44 | 0.93 | 34.80 | 427.95 | 13.88 | 7.2 | 0.40 | 9.067 | -5.8 | 400 | In situ | Yes | No | Anthropogenic | 20 | 7 | 78.80 | µg N2O/m2/h | GC/static | 45 | 4 | no | yes | yes | Chen Q et al. 2014 | ||||||||||||
Ny-Alesund_N2O | NO-Nya-2009-04 | 825.60 | continuous | Arctic | Upland | Vegetated | CT Tundra, abandoned coal mine | Norway | Svalbard | Ny-Alesund | 79.92 | 11.93 | 2 | 2008 | 7 | 31 | 2009 | 7 | 13 | 33.10 | 0.50 | 65.80 | 298.32 | 1.79 | 7.1 | 0.36 | 7.620 | -5.8 | 400 | In situ | Yes | No | Anthropogenic | 24 | 3 | 34.40 | µg N2O/m2/h | GC/static | 45 | 4 | no | yes | yes | Chen Q et al. 2014 | ||||||||||||
Ny-Alesund_N2O | NO-Nya-2009-05 | 76.80 | continuous | Arctic | Upland | Vegetated | Lowland tundra (L2); mosses (Salix polaris, Cerastium arcticum and Drepanocladus spp), lichens (Luzula confuse) and sedges (L. arctica and Saxifraga oppositifolia) | Norway | Svalbard | Ny-Alesund | 79.92 | 11.93 | 1 | 2009 | 7 | 18 | 2009 | 7 | 23 | 8.50 | 0.32 | 26.40 | 14.83 | 0.55 | 7.3 | 27.90 | 27.352 | -5.8 | 5.2 | 400 | 200.00 | In situ | No | No | none | 6 | 3 | 3.20 | µg N2O/m2/h | GC/static | transparent | 45 | 3 | no | yes | yes | Zhu R et al. 2012 | |||||||||
Ny-Alesund_N2O | NO-Nya-2009-06 | 667.20 | continuous | Arctic | Upland | Vegetated | Seabird sanctuary tundra (SBT-H2), high seabird- activity; 2% barren surface; vegetation includes mosses, lichens and sedges | Norway | Svalbard | Ny-Alesund | 79.92 | 11.93 | 1 | 2009 | 7 | 21 | 2009 | 7 | 26 | 17.89 | 0.64 | 28.20 | 113.87 | 16.64 | 7.2 | 78.60 | 93.193 | -5.8 | 5.2 | 400 | 200.00 | In situ | Yes | No | Birds | 6 | 3 | 27.80 | µg N2O/m2/h | GC/static | transparent | 45 | 3 | no | yes | yes | Zhu R et al. 2012 | |||||||||
Ny-Alesund_N2O | NO-Nya-2009-07 | 76.80 | continuous | Arctic | Upland | Vegetated | Seabird sanctuary tundra (SBT-L2), low seabird activity. 2% barren surface; vegetation includes mosses, lichens and sedges | Norway | Svalbard | Ny-Alesund | 79.92 | 11.93 | 1 | 2009 | 7 | 21 | 2009 | 7 | 26 | 5.46 | 0.97 | 26.20 | 14.19 | 3.29 | 6.9 | 73.40 | 100.000 | -5.8 | 5.2 | 400 | 200.00 | In situ | Yes | No | Birds | 6 | 3 | 3.20 | µg N2O/m2/h | GC/static | transparent | 45 | 3 | no | yes | yes | Zhu R et al. 2012 | |||||||||
Ny-Alesund_N2O | NO-Nya-2009-08 | 103.20 | continuous | Arctic | Upland | Vegetated | Seabird sanctuary tundra (SBT-M2), medium seabird-activity; 2% barren surface; vegetation includes mosses, lichens and sedges | Norway | Svalbard | Ny-Alesund | 79.92 | 11.93 | 1 | 2009 | 7 | 21 | 2009 | 7 | 26 | 21.95 | 1.02 | 21.60 | 16.90 | 3.16 | 7.0 | 73.40 | 50.587 | -5.8 | 5.2 | 400 | 200.00 | In situ | Yes | No | Birds | 6 | 3 | 4.30 | µg N2O/m2/h | GC/static | transparent | 45 | 3 | no | yes | yes | Zhu R et al. 2012 | |||||||||
Ny-Alesund_N2O | NO-Nya-2009-09 | 52.80 | continuous | Arctic | Upland | Vegetated | Slope tundra (SL); mosses (Salix polaris, Cerastium arcticum and Drepanocladus spp), lichens (Luzula confuse) and sedges (L. arctica and Saxifraga oppositifolia) | Norway | Svalbard | Ny-Alesund | 79.92 | 11.93 | 1 | 2009 | 7 | 18 | 2009 | 7 | 23 | 3.37 | 0.67 | 49.80 | 8.33 | 0.57 | 7.3 | 28.60 | 61.022 | -5.8 | 5.2 | 400 | 200.00 | In situ | No | No | none | 6 | 3 | 2.20 | µg N2O/m2/h | GC/static | transparent | 45 | 3 | no | yes | yes | Zhu R et al. 2012 | |||||||||
Ny-Alesund_N2O | NO-Nya-2009-10 | 57.60 | continuous | Arctic | Upland | Vegetated | Upland tundra (UL); mosses (Salix polaris, Cerastium arcticum and Drepanocladus spp), lichens (Luzula confuse) and sedges (L. arctica and Saxifraga oppositifolia) | Norway | Svalbard | Ny-Alesund | 79.92 | 11.93 | 1 | 2009 | 7 | 18 | 2009 | 7 | 23 | 3.07 | 0.50 | 61.30 | 15.22 | 3.82 | 6.8 | 50.00 | 100.000 | -5.8 | 5.2 | 400 | 200.00 | In situ | No | No | none | 6 | 3 | 2.40 | µg N2O/m2/h | GC/static | transparent | 45 | 3 | no | yes | yes | Zhu R et al. 2012 | |||||||||
Ny-Alesund_N2O | NO-Nya-2014-01 | 182.40 | continuous | Arctic | Wetland | Vegetated | Tundra, silty clay with thin organic layer, transect from waterlogged tundra marsh to upland | Norway | Svalbard | Ny-Alesund | 78.91 | 11.93 | 1 | 2014 | 7 | 3 | 2014 | 7 | 12 | 21.03 | 1.54 | 13.70 | 0.28 | 0.11 | 88.90 | 100 | 100.000 | -5.8 | 6.0 | 7.0 | 400 | 200.00 | In situ | No | No | none | 6 | 2 | 7.60 | ug N2O/m2/h | GC/static | transparent | 30 | 3 | no | yes | yes | Li F et al. 2016 | ||||||||
Ny-Alesund_N2O | NO-Nya-2014-02 | 350.40 | continuous | Arctic | Wetland | Vegetated | Tundra, silty clay with thin organic layer, transect from waterlogged tundra marsh to upland | Norway | Svalbard | Ny-Alesund | 78.91 | 11.93 | 1 | 2014 | 7 | 3 | 2014 | 7 | 12 | 5.26 | 0.39 | 13.50 | 1.00 | 0.27 | 99.50 | 100 | 100.000 | -5.8 | 6.0 | 7.0 | 400 | 200.00 | In situ | No | No | none | 6 | 2 | 14.60 | ug N2O/m2/h | GC/static | transparent | 30 | 3 | no | yes | yes | Li F et al. 2016 | ||||||||
Ny-Alesund_N2O | NO-Nya-2014-03 | 316.80 | continuous | Arctic | Wetland | Vegetated | Tundra, silty clay with thin organic layer, transect from waterlogged tundra marsh to upland | Norway | Svalbard | Ny-Alesund | 78.91 | 11.93 | 1 | 2014 | 7 | 3 | 2014 | 7 | 12 | 7.55 | 0.34 | 22.20 | 18.74 | 0.81 | 89.80 | 100 | 100.000 | -5.8 | 6.0 | 7.0 | 400 | 200.00 | In situ | No | No | none | 6 | 2 | 13.20 | ug N2O/m2/h | GC/static | transparent | 30 | 3 | no | yes | yes | Li F et al. 2016 | ||||||||
Ny-Alesund_N2O | NO-Nya-2014-04 | 177.60 | continuous | Arctic | Upland | Vegetated | Tundra, silty clay with thin organic layer, transect from waterlogged tundra marsh to upland | Norway | Svalbard | Ny-Alesund | 78.91 | 11.93 | 1 | 2014 | 7 | 3 | 2014 | 7 | 12 | 24.15 | 1.49 | 16.20 | 10.23 | 0.70 | 59.30 | 23.053 | -5.8 | 6.0 | 7.0 | 400 | 200.00 | In situ | No | No | none | 6 | 2 | 7.40 | ug N2O/m2/h | GC/static | transparent | 30 | 3 | no | yes | yes | Li F et al. 2016 | |||||||||
Ny-Alesund_N2O | NO-Nya-2014-05 | 228.00 | continuous | Arctic | Upland | Vegetated | Tundra, silty clay with thin organic layer, transect from waterlogged tundra marsh to upland | Norway | Svalbard | Ny-Alesund | 78.91 | 11.93 | 1 | 2014 | 7 | 3 | 2014 | 7 | 12 | 19.29 | 1.55 | 12.50 | 19.16 | 1.16 | 51.90 | 24.284 | -5.8 | 6.0 | 7.0 | 400 | 200.00 | In situ | No | No | none | 6 | 2 | 9.50 | ug N2O/m2/h | GC/static | transparent | 30 | 3 | no | yes | yes | Li F et al. 2016 | |||||||||
Ny-Alesund_N2O | NO-Nya-2014-06 | 19.20 | continuous | Arctic | Wetland | Vegetated | Tundra, silty clay with thin organic layer, transect from waterlogged tundra marsh to upland | Norway | Svalbard | Ny-Alesund | 78.91 | 11.93 | 1 | 2014 | 7 | 3 | 2014 | 7 | 12 | 21.03 | 1.54 | 13.70 | 0.28 | 0.11 | 88.90 | 100 | 100.000 | -5.8 | 6.0 | 7.0 | 400 | 200.00 | In situ | No | Yes | Shading | 6 | 2 | 0.80 | ug N2O/m2/h | GC/static | opaque | 30 | 3 | no | yes | yes | Li F et al. 2016 | ||||||||
Ny-Alesund_N2O | NO-Nya-2014-07 | -21.60 | continuous | Arctic | Wetland | Vegetated | Tundra, silty clay with thin organic layer, transect from waterlogged tundra marsh to upland | Norway | Svalbard | Ny-Alesund | 78.91 | 11.93 | 1 | 2014 | 7 | 3 | 2014 | 7 | 12 | 5.26 | 0.39 | 13.50 | 1.00 | 0.27 | 99.50 | 100 | 100.000 | -5.8 | 6.0 | 7.0 | 400 | 200.00 | In situ | No | Yes | Shading | 6 | 2 | -0.90 | ug N2O/m2/h | GC/static | opaque | 30 | 3 | no | yes | yes | Li F et al. 2016 | ||||||||
Ny-Alesund_N2O | NO-Nya-2014-08 | 16.80 | continuous | Arctic | Wetland | Vegetated | Tundra, silty clay with thin organic layer, transect from waterlogged tundra marsh to upland | Norway | Svalbard | Ny-Alesund | 78.91 | 11.93 | 1 | 2014 | 7 | 3 | 2014 | 7 | 12 | 7.55 | 0.34 | 22.20 | 18.74 | 0.81 | 89.80 | 100 | 100.000 | -5.8 | 6.0 | 7.0 | 400 | 200.00 | In situ | No | Yes | Shading | 6 | 2 | 0.70 | ug N2O/m2/h | GC/static | opaque | 30 | 3 | no | yes | yes | Li F et al. 2016 | ||||||||
Ny-Alesund_N2O | NO-Nya-2014-09 | 24.00 | continuous | Arctic | Upland | Vegetated | Tundra, silty clay with thin organic layer, transect from waterlogged tundra marsh to upland | Norway | Svalbard | Ny-Alesund | 78.91 | 11.93 | 1 | 2014 | 7 | 3 | 2014 | 7 | 12 | 24.15 | 1.49 | 16.20 | 10.23 | 0.70 | 59.30 | 23.053 | -5.8 | 6.0 | 7.0 | 400 | 200.00 | In situ | No | Yes | Shading | 6 | 2 | 1.00 | ug N2O/m2/h | GC/static | opaque | 30 | 3 | no | yes | yes | Li F et al. 2016 | |||||||||
Ny-Alesund_N2O | NO-Nya-2014-10 | -91.20 | continuous | Arctic | Upland | Vegetated | Tundra, silty clay with thin organic layer, transect from waterlogged tundra marsh to upland | Norway | Svalbard | Ny-Alesund | 78.91 | 11.93 | 1 | 2014 | 7 | 3 | 2014 | 7 | 12 | 19.29 | 1.55 | 12.50 | 19.16 | 1.16 | 51.90 | 24.284 | -5.8 | 6.0 | 7.0 | 400 | 200.00 | In situ | No | Yes | Shading | 6 | 2 | -3.80 | ug N2O/m2/h | GC/static | opaque | 30 | 3 | no | yes | yes | Li F et al. 2016 | |||||||||
Seida_I_N2O | RU-Sei-2007-01 | 10300.00 | discontinuous | Subarctic | Peatland | Bare | Peat plateau, bare surfaces | Russia | Western Russia | Seida I | 67.05 | 62.95 | 1 | 2007 | 7 | 3 | 2007 | 10 | 17 | 53.60 | 2.30 | 23.00 | 55.00 | 3.1 | 95.00 | 0.25 | 69.30 | 0.64 | 76 | 76.000 | -5.8 | 13.6 | 12.0 | 505 | 70.00 | In situ | No | No | none | 13 | 3 | 10.30 | mg N2O/m2/d | GC/static | opaque | 28 | 40 | 4 | no | no | yes | Maruschchak ME et al. 2011 | ||||
Seida_I_N2O | RU-Sei-2007-02 | -0.01 | discontinuous | Subarctic | Peatland | Vegetated | Floating fen, water saturated | Russia | Western Russia | Seida I | 67.05 | 62.95 | 1 | 2007 | 7 | 3 | 2007 | 10 | 17 | 45.10 | 1.60 | 43.00 | 4.9 | 90.00 | 1.00 | 100 | 100.000 | -5.8 | 13.6 | 14.1 | 505 | >120.00 | In situ | No | No | none | 9 | 9 | -0.00 | mg N2O/m2/d | GC/static | opaque | 28 | 40 | 4 | no | no | yes | Maruschchak ME et al. 2011 | |||||||
Seida_I_N2O | RU-Sei-2007-03 | 40.00 | discontinuous | Subarctic | Peatland | Vegetated | Peat plateau, vegetated | Russia | Western Russia | Seida I | 67.05 | 62.95 | 1 | 2007 | 7 | 3 | 2007 | 10 | 17 | 46.65 | 0.75 | 63.50 | 3.20 | 3.2 | 98.00 | 0.05 | 85.60 | 0.30 | 30 | 30.000 | -5.8 | 13.6 | 13.8 | 505 | 62.00 | In situ | No | No | none | 10 | 6 | 0.04 | mg N2O/m2/d | GC/static | opaque | 28 | 40 | 4 | no | no | yes | Maruschchak ME et al. 2011 | ||||
Seida_I_N2O | RU-Sei-2007-04 | 10.00 | discontinuous | Subarctic | Upland | Vegetated | Tundra heath | Russia | Western Russia | Seida I | 67.05 | 62.95 | 1 | 2007 | 7 | 3 | 2007 | 10 | 17 | 48.00 | 1.20 | 48.00 | 0.10 | 3.3 | 93.00 | 0.06 | 79.60 | 0.19 | 18 | 18.000 | -5.8 | 13.6 | 13.3 | 505 | 100.00 | In situ | No | No | none | 10 | 12 | 0.01 | mg N2O/m2/d | GC/static | opaque | 28 | 40 | 4 | no | no | yes | Maruschchak ME et al. 2011 | ||||
Seida_I_N2O | RU-Sei-2007-05 | 2190.83 | discontinuous | Subarctic | Peatland | Bare | Peat plateau, bare surfaces | Russia | Western Russia | Seida I | 67.05 | 62.95 | 1 | 2008 | 1 | 28 | 2008 | 6 | 9 | 53.60 | 2.30 | 23.00 | 3.1 | 95.00 | 0.25 | -5.8 | 505 | In situ | No | No | none | 12 | 3 | 2.19 | mg N2O/m2/d | snow gradient | no | no | yes | Maruschchak ME et al. 2011 | ||||||||||||||||
Seida_I_N2O | RU-Sei-2008-01 | 8110.00 | discontinuous | Subarctic | Peatland | Bare | Peat plateau, bare surfaces | Russia | Western Russia | Seida I | 67.05 | 62.95 | 1 | 2008 | 5 | 22 | 2008 | 10 | 2 | 54.00 | 2.20 | 24.00 | 25.40 | 13.04 | 3.3 | 95.00 | 0.25 | 69.30 | 0.59 | 70 | 70.000 | -5.8 | 12.7 | 13.0 | 505 | 62.00 | In situ | No | No | none | 11 | 3 | 8.11 | mg N2O/m2/d | GC/static | opaque | 28 | 40 | 4 | no | no | yes | Maruschchak ME et al. 2011 | |||
Seida_I_N2O | RU-Sei-2008-02 | -60.00 | discontinuous | Subarctic | Peatland | Vegetated | Floating fen, water saturated | Russia | Western Russia | Seida I | 67.05 | 62.95 | 1 | 2008 | 5 | 22 | 2008 | 10 | 2 | 45.00 | 1.60 | 43.00 | 4.8 | 90.00 | 1.00 | 100 | 100.000 | -5.8 | 12.7 | 13.5 | 505 | >120.00 | In situ | No | No | none | 12 | 9 | -0.06 | mg N2O/m2/d | GC/static | opaque | 28 | 40 | 4 | no | no | yes | Maruschchak ME et al. 2011 | |||||||
Seida_I_N2O | RU-Sei-2008-03 | 1080.00 | discontinuous | Subarctic | Peatland | Bare | Peat plateau, peat mounds | Russia | Western Russia | Seida I | 67.05 | 62.95 | 1 | 2008 | 5 | 22 | 2008 | 10 | 2 | 56.00 | 2.10 | 26.00 | 10.28 | 11.24 | 3.3 | 0.22 | 68.10 | 0.16 | 19 | 19.000 | -5.8 | 12.7 | 12.4 | 505 | 55.00 | In situ | No | No | none | 10 | 3 | 1.08 | mg N2O/m2/d | GC/static | opaque | 28 | 40 | 4 | no | no | yes | Maruschchak ME et al. 2011 | ||||
Seida_I_N2O | RU-Sei-2008-04 | 60.00 | discontinuous | Subarctic | Peatland | Vegetated | Peat plateau, vegetated | Russia | Western Russia | Seida I | 67.05 | 62.95 | 1 | 2008 | 5 | 22 | 2008 | 10 | 2 | 47.00 | 0.80 | 62.00 | 9.79 | 2.12 | 3.4 | 98.00 | 0.05 | 86.40 | 0.26 | 27 | 27.000 | -5.8 | 12.7 | 12.8 | 505 | 66.00 | In situ | No | No | none | 12 | 6 | 0.06 | mg N2O/m2/d | GC/static | opaque | 28 | 40 | 4 | no | no | yes | Maruschchak ME et al. 2011 | |||
Seida_I_N2O | RU-Sei-2008-05 | -10.00 | discontinuous | Subarctic | Upland | Vegetated | Tundra heath | Russia | Western Russia | Seida I | 67.05 | 62.95 | 1 | 2008 | 5 | 22 | 2008 | 10 | 2 | 45.00 | 1.20 | 38.00 | 21.67 | 4.29 | 3.5 | 93.00 | 0.06 | 76.50 | 0.14 | 14 | 14.000 | -5.8 | 12.7 | 11.7 | 505 | 104.00 | In situ | No | No | none | 12 | 12 | -0.01 | mg N2O/m2/d | GC/static | opaque | 28 | 40 | 4 | no | no | yes | Maruschchak ME et al. 2011 | |||
Seida_I_N2O | RU-Sei-2011-01 | 800.00 | discontinuous | Subarctic | Peatland | Bare | Peat plateau, bare surfaces | Russia | Western Russia | Seida I | 67.05 | 62.95 | 1 | 2011 | 7 | 7 | 2011 | 8 | 30 | 51.00 | 2.40 | 22.00 | 4.00 | 329.00 | 3.2 | 0.25 | 2.60 | 62 | 62.000 | -5.8 | 8.9 | 7.8 | 505 | 46.00 | in situ | No | No | none | 9 | 3 | 0.80 | mg N2O/m2/d | GC/static | opaque | 40 | 4 | no | no | yes | Gil J et al. 2017 | ||||||
Seida_II_N2O | RU-Sei-2012-01 | 164.00 | discontinuous | Subarctic | Peatland | Bare | Peat plateau, bare surfaces | Russia | Western Russia | Seida II | 67.05 | 62.92 | 1 | 2012 | 7 | 12 | 2012 | 8 | 22 | 50.00 | 2.60 | 19.00 | 49.00 | 118.00 | 4.0 | 94.00 | 0.19 | 35 | 35.000 | -5.6 | 12.9 | 10.7 | 510 | 46.00 | In situ | No | No | none | 7 | 5 | 0.16 | mg N2O/m2/d | GC/static | opaque | 40 | 4 | yes | yes | yes | Voigt C et al. 2017b | ||||||
Seida_II_N2O | RU-Sei-2012-02 | 563.00 | discontinuous | Subarctic | Peatland | Bare | Peat plateau, bare surfaces | Russia | Western Russia | Seida II | 67.05 | 62.92 | 1 | 2012 | 7 | 12 | 2012 | 8 | 22 | 50.00 | 2.70 | 19.00 | 42.00 | 157.00 | 3.7 | 95.00 | 0.19 | 30 | 30.000 | -5.6 | 13.8 | 11.2 | 513 | 53.00 | In situ | Yes | Yes | Warming | 7 | 5 | 0.56 | mg N2O/m2/d | GC/static | opaque | 40 | 4 | yes | yes | yes | Voigt C et al. 2017b | ||||||
Seida_II_N2O | RU-Sei-2012-03 | 0.11 | discontinuous | Subarctic | Peatland | Vegetated | Peat plateau, vegetated | Russia | Western Russia | Seida II | 67.05 | 62.92 | 1 | 2012 | 7 | 12 | 2012 | 8 | 22 | 48.00 | 1.20 | 40.00 | 40.00 | 0.80 | 3.8 | 98.00 | 0.02 | 17 | 17.000 | -5.6 | 13.1 | 9.3 | 511 | 42.00 | In situ | No | No | none | 7 | 5 | 0.00 | mg N2O/m2/d | GC/static | opaque | 40 | 4 | yes | yes | yes | Voigt C et al. 2017b | ||||||
Seida_II_N2O | RU-Sei-2012-04 | 1.44 | discontinuous | Subarctic | Peatland | Vegetated | Peat plateau, vegetated | Russia | Western Russia | Seida II | 67.05 | 62.92 | 1 | 2012 | 7 | 12 | 2012 | 8 | 22 | 48.00 | 1.20 | 42.00 | 17.00 | 1.10 | 3.9 | 97.00 | 0.02 | 16 | 16.000 | -5.6 | 13.4 | 8.6 | 514 | 46.00 | In situ | Yes | Yes | Warming | 7 | 5 | 0.00 | mg N2O/m2/d | GC/static | opaque | 40 | 4 | yes | yes | yes | Voigt C et al. 2017b | ||||||
Seida_II_N2O | RU-Sei-2012-05 | -23.07 | discontinuous | Subarctic | Upland | Vegetated | Tundra heath | Russia | Western Russia | Seida II | 67.05 | 62.92 | 1 | 2012 | 7 | 12 | 2012 | 8 | 22 | 44.00 | 1.50 | 30.00 | 30.00 | 0.60 | 4.3 | 41.00 | 0.06 | 17 | 17.000 | -5.6 | 12.9 | 9.0 | 512 | 114.00 | In situ | No | No | none | 7 | 5 | -0.02 | mg N2O/m2/d | GC/static | opaque | 40 | 4 | yes | yes | yes | Voigt C et al. 2017b | ||||||
Seida_II_N2O | RU-Sei-2012-06 | 7.79 | discontinuous | Subarctic | Upland | Vegetated | Tundra heath | Russia | Western Russia | Seida II | 67.05 | 62.92 | 1 | 2012 | 7 | 12 | 2012 | 8 | 22 | 46.00 | 1.20 | 39.00 | 23.00 | 0.70 | 4.2 | 43.00 | 0.06 | 16 | 16.000 | -5.6 | 13.5 | 8.5 | 515 | 130.00 | In situ | Yes | Yes | Warming | 7 | 5 | 0.01 | mg N2O/m2/d | GC/static | opaque | 40 | 4 | yes | yes | yes | Voigt C et al. 2017b | ||||||
Seida_II_N2O | RU-Sei-2013-01 | 772.00 | discontinuous | Subarctic | Peatland | Bare | Peat plateau, bare surfaces | Russia | Western Russia | Seida II | 67.05 | 62.92 | 1 | 2013 | 6 | 1 | 2013 | 9 | 24 | 50.00 | 2.60 | 19.00 | 94.00 | 419.00 | 4.0 | 94.00 | 0.19 | 26 | 26.000 | -5.6 | 16.2 | 12.2 | 516 | 48.00 | In situ | No | No | none | 10 | 5 | 0.77 | mg N2O/m2/d | GC/static | opaque | 40 | 4 | yes | yes | yes | Voigt C et al. 2017b | ||||||
Seida_II_N2O | RU-Sei-2013-02 | 884.00 | discontinuous | Subarctic | Peatland | Bare | Peat plateau, bare surfaces | Russia | Western Russia | Seida II | 67.05 | 62.92 | 1 | 2013 | 6 | 1 | 2013 | 9 | 24 | 50.00 | 2.70 | 19.00 | 71.00 | 308.00 | 3.7 | 95.00 | 0.19 | 23 | 23.000 | -5.6 | 18.3 | 12.9 | 519 | 49.00 | In situ | Yes | Yes | Warming | 10 | 5 | 0.88 | mg N2O/m2/d | GC/static | opaque | 40 | 4 | yes | yes | yes | Voigt C et al. 2017b | ||||||
Seida_II_N2O | RU-Sei-2013-03 | 19.78 | discontinuous | Subarctic | Peatland | Vegetated | Peat plateau, vegetated | Russia | Western Russia | Seida II | 67.05 | 62.92 | 1 | 2013 | 6 | 1 | 2013 | 9 | 24 | 48.00 | 1.20 | 40.00 | 36.00 | 3.20 | 3.8 | 98.00 | 0.02 | 16 | 16.000 | -5.6 | 16.3 | 9.8 | 517 | 46.00 | In situ | No | No | none | 10 | 5 | 0.02 | mg N2O/m2/d | GC/static | opaque | 40 | 4 | yes | yes | yes | Voigt C et al. 2017b | ||||||
Seida_II_N2O | RU-Sei-2013-04 | 98.95 | discontinuous | Subarctic | Peatland | Vegetated | Peat plateau, vegetated | Russia | Western Russia | Seida II | 67.05 | 62.92 | 1 | 2013 | 6 | 1 | 2013 | 9 | 24 | 48.00 | 1.20 | 42.00 | 26.00 | 1.30 | 3.9 | 97.00 | 0.02 | 13 | 13.000 | -5.6 | 17.0 | 10.3 | 520 | 38.00 | In situ | Yes | Yes | Warming | 10 | 5 | 0.10 | mg N2O/m2/d | GC/static | opaque | 40 | 4 | yes | yes | yes | Voigt C et al. 2017b | ||||||
Seida_II_N2O | RU-Sei-2013-05 | 5.87 | discontinuous | Subarctic | Upland | Vegetated | Tundra heath | Russia | Western Russia | Seida II | 67.05 | 62.92 | 1 | 2013 | 6 | 1 | 2013 | 9 | 24 | 44.00 | 1.50 | 30.00 | 37.00 | 0.80 | 4.3 | 41.00 | 0.06 | 11 | 11.000 | -5.6 | 16.3 | 8.9 | 518 | 122.00 | In situ | No | No | none | 10 | 5 | 0.01 | mg N2O/m2/d | GC/static | opaque | 40 | 4 | yes | yes | yes | Voigt C et al. 2017b | ||||||
Seida_II_N2O | RU-Sei-2013-06 | 28.63 | discontinuous | Subarctic | Upland | Vegetated | Tundra heath | Russia | Western Russia | Seida II | 67.05 | 62.92 | 1 | 2013 | 6 | 1 | 2013 | 9 | 24 | 46.00 | 1.20 | 39.00 | 28.00 | 1.00 | 4.2 | 43.00 | 0.06 | 11 | 11.000 | -5.6 | 17.4 | 8.8 | 521 | 117.00 | In situ | Yes | Yes | Warming | 10 | 5 | 0.03 | mg N2O/m2/d | GC/static | opaque | 40 | 4 | yes | yes | yes | Voigt C et al. 2017b | ||||||
Tura_N2O | RU-Tur-2005-01 | 7.54 | continuous | Arctic | Upland | Vegetated | larch forest | Russia | Siberia | Tura | 64.27 | 100.22 | 1 | 2005 | 6 | 2005 | 9 | 0.25 | 290 | <100.00 | In situ | No | No | none | 3 | 6 | 0.20 | µg N/m2/h | GC/static | opaque | 60 | 4 | no | yes | yes | Morishita T et al. 2014 | ||||||||||||||||||||
Tura_N2O | RU-Tur-2006-01 | 15.08 | continuous | Arctic | Upland | Vegetated | larch forest | Russia | Siberia | Tura | 64.27 | 100.22 | 1 | 2006 | 6 | 2006 | 9 | 0.29 | 288 | <100.00 | In situ | No | No | none | 2 | 6 | 0.40 | µg N/m2/h | GC/static | opaque | 60 | 4 | no | yes | yes | Morishita T et al. 2014 | ||||||||||||||||||||
Tura_N2O | RU-Tur-2007-01 | -7.54 | continuous | Arctic | Upland | Vegetated | larch forest | Russia | Siberia | Tura | 64.27 | 100.22 | 1 | 2007 | 6 | 2007 | 9 | 0.45 | 466 | <100.00 | In situ | No | No | none | 3 | 6 | -0.20 | µg N/m2/h | GC/static | opaque | 60 | 4 | no | yes | yes | Morishita T et al. 2014 | ||||||||||||||||||||
Yakutsk_N2O | RU-Yak-2004-01 | 52.38 | continuous | Subarctic | Upland | Vegetated | Thermokarst depression, Dry grassland; Gramineae (e.g., Elytrigia repens) | Russia | Siberia | Yakutsk | 62.32 | 129.50 | 1 | 2004 | 6 | 2004 | 9 | 10.40 | 0.98 | 10.60 | 25.90 | 8.60 | 6.7 | 0.72 | 0.18 | 26.040 | -10.0 | 10.2 | 12.1 | 230 | 200.00 | In situ | No | No | none | 9 | 3 | 0.04 | kg N2O-N/ha/period | GC/static | opaque | 60 | 3 | no | yes | yes | Takakai F et al. 2008 | |||||||||
Yakutsk_N2O | RU-Yak-2004-02 | 13.53 | continuous | Subarctic | Upland | Vegetated | Larch forest; 200-year-old larch (Larix gmelinii), with Vaccinium vitis idaed | Russia | Siberia | Yakutsk | 62.32 | 129.50 | 1 | 2004 | 6 | 2004 | 9 | 52.00 | 1.43 | 36.40 | 55.90 | 0.00 | 5.2 | 0.15 | 0.10 | 11.076 | -10.0 | 10.2 | 8.8 | 230 | 130.00 | In situ | No | No | none | 9 | 3 | 0.01 | kg N2O-N/ha/period | GC/static | opaque | 60 | 3 | no | yes | yes | Takakai F et al. 2008 | |||||||||
Yakutsk_N2O | RU-Yak-2004-03 | -27.83 | continuous | Subarctic | Wetland | Vegetated | Flooded wetland/pond (but not lake) | Russia | Siberia | Yakutsk | 62.32 | 129.50 | 1 | 2004 | 6 | 2004 | 9 | 15.50 | 1.46 | 10.60 | 6.3 | 1.00 | 100 | 100.000 | -10.0 | 10.2 | 13.4 | 230 | In situ | No | No | none | 9 | 3 | -0.02 | kg N2O-N/ha/period | GC/static | opaque | 60 | 3 | no | yes | yes | Takakai F et al. 2008 | ||||||||||||
Yakutsk_N2O | RU-Yak-2004-04 | 69.84 | continuous | Subarctic | Wetland | Vegetated | Thermokarst depression, Wet grassland-1; several species of Gramineae (e.g., Carex orthostachys, Glyceria lithuanica) | Russia | Siberia | Yakutsk | 62.32 | 129.50 | 1 | 2004 | 6 | 2004 | 9 | 5.99 | 0.49 | 12.40 | 30.50 | 4.00 | 7.2 | 1.08 | 0.34 | 61.419 | -10.0 | 10.2 | 7.6 | 230 | In situ | No | No | none | 9 | 3 | 0.05 | kg N2O-N/ha/period | GC/static | opaque | 60 | 3 | no | yes | yes | Takakai F et al. 2008 | ||||||||||
Yakutsk_N2O | RU-Yak-2004-05 | 232.80 | continuous | Subarctic | Wetland | Vegetated | Thermokarst depression, Wet grassland-2; several species of Gramineae (e.g., Carex orthostachys, Glyceria lithuanica) | Russia | Siberia | Yakutsk | 62.32 | 129.50 | 1 | 2004 | 6 | 2004 | 9 | 12.00 | 1.25 | 9.60 | 37.70 | 0.20 | 6.3 | 0.51 | 0.55 | 70.825 | -10.0 | 10.2 | 9.3 | 230 | In situ | No | No | none | 9 | 3 | 0.16 | kg N2O-N/ha/period | GC/static | opaque | 60 | 3 | no | yes | yes | Takakai F et al. 2008 | ||||||||||
Yakutsk_N2O | RU-Yak-2004-06 | 2473.54 | continuous | Subarctic | Wetland | Vegetated | Thermokarst depression, Wet grassland-3; several species of Gramineae (e.g., Carex orthostachys, Glyceria lithuanica) | Russia | Siberia | Yakutsk | 62.32 | 129.50 | 1 | 2004 | 6 | 2004 | 9 | 26.70 | 2.50 | 10.70 | 6.4 | 0.19 | 0.82 | 90.887 | -10.0 | 10.2 | 10.3 | 230 | In situ | No | No | none | 9 | 3 | 1.70 | kg N2O-N/ha/period | GC/static | opaque | 60 | 3 | no | yes | yes | Takakai F et al. 2008 | ||||||||||||
Yakutsk_N2O | RU-Yak-2005-01 | 138.97 | continuous | Subarctic | Upland | Vegetated | Thermokarst depression, Dry grassland; Gramineae (e.g., Elytrigia repens) | Russia | Siberia | Yakutsk | 62.32 | 129.50 | 1 | 2005 | 5 | 2005 | 9 | 10.40 | 0.98 | 10.60 | 25.90 | 8.60 | 6.7 | 0.72 | 0.26 | 37.614 | -10.0 | 12.1 | 12.1 | 230 | 200.00 | In situ | No | No | none | 11 | 3 | 0.13 | kg N2O-N/ha/period | GC/static | opaque | 60 | 3 | no | yes | yes | Takakai F et al. 2008 | |||||||||
Yakutsk_N2O | RU-Yak-2005-02 | 45.97 | continuous | Subarctic | Upland | Vegetated | Larch forest; 200-year-old larch (Larix gmelinii), with Vaccinium vitis idaed | Russia | Siberia | Yakutsk | 62.32 | 129.50 | 1 | 2005 | 5 | 2005 | 9 | 52.00 | 1.43 | 36.40 | 55.90 | 0.00 | 5.2 | 0.15 | 0.21 | 23.259 | -10.0 | 12.1 | 9.6 | 230 | 130.00 | In situ | No | No | none | 11 | 3 | 0.04 | kg N2O-N/ha/period | GC/static | opaque | 60 | 3 | no | yes | yes | Takakai F et al. 2008 | |||||||||
Yakutsk_N2O | RU-Yak-2004-03 | -36.35 | continuous | Subarctic | Wetland | Vegetated | Flooded wetland/pond (but not lake) | Russia | Siberia | Yakutsk | 62.32 | 129.50 | 1 | 2005 | 5 | 2005 | 9 | 15.50 | 1.46 | 10.60 | 6.3 | 1.00 | 100 | 100.000 | -10.0 | 10.2 | 16.6 | 230 | In situ | No | No | none | 9 | 3 | -0.03 | kg N2O-N/ha/period | GC/static | opaque | 60 | 3 | no | yes | yes | Takakai F et al. 2008 | ||||||||||||
Yakutsk_N2O | RU-Yak-2005-04 | 127.21 | continuous | Subarctic | Wetland | Vegetated | Thermokarst depression, Wet grassland-1; several species of Gramineae (e.g., Carex orthostachys, Glyceria lithuanica) | Russia | Siberia | Yakutsk | 62.32 | 129.50 | 1 | 2005 | 5 | 2005 | 9 | 5.99 | 0.49 | 12.40 | 30.50 | 4.00 | 7.2 | 1.08 | 0.50 | 90.322 | -10.0 | 12.1 | 12.1 | 230 | In situ | No | No | none | 11 | 3 | 0.12 | kg N2O-N/ha/period | GC/static | opaque | 60 | 3 | no | yes | yes | Takakai F et al. 2008 | ||||||||||
Yakutsk_N2O | RU-Yak-2005-05 | -33.14 | continuous | Subarctic | Wetland | Vegetated | Thermokarst depression, Wet grassland-2; several species of Gramineae (e.g., Carex orthostachys, Glyceria lithuanica) | Russia | Siberia | Yakutsk | 62.32 | 129.50 | 1 | 2005 | 5 | 2005 | 9 | 12.00 | 1.25 | 9.60 | 37.70 | 0.20 | 6.3 | 0.51 | 1.00 | 100.000 | -10.0 | 12.1 | 14.9 | 230 | In situ | No | No | none | 11 | 3 | -0.03 | kg N2O-N/ha/period | GC/static | opaque | 60 | 3 | no | yes | yes | Takakai F et al. 2008 | ||||||||||
Yakutsk_N2O | RU-Yak-2005-06 | -26.72 | continuous | Subarctic | Wetland | Vegetated | Thermokarst depression, Wet grassland-3; several species of Gramineae (e.g., Carex orthostachys, Glyceria lithuanica) | Russia | Siberia | Yakutsk | 62.32 | 129.50 | 1 | 2005 | 5 | 2005 | 9 | 26.70 | 2.50 | 10.70 | 6.4 | 0.19 | 1.00 | 100.000 | -10.0 | 12.1 | 16.4 | 230 | In situ | No | No | none | 11 | 3 | -0.03 | kg N2O-N/ha/period | GC/static | opaque | 60 | 3 | no | yes | yes | Takakai F et al. 2008 | ||||||||||||
Abisko_N2O | SE-Abi-1996-01 | 45.63 | sporadic | Subarctic | Upland | Vegetated | Subarctic heath dominated by Rhododendron lapponicum, Vaccinium uliginosum, Empetrum hermaphroditum and Betula nana above a subcanopy cover of mosses | Sweden | Northern Scandinavia | Abisko | 68.33 | 20.85 | 1 | 1996 | 7 | 3 | 1996 | 8 | 28 | 40.64 | 1.86 | 21.90 | 49.19 | 1.59 | 7.1 | -0.8 | 304 | In situ | No | No | none | 2 | 6 | 0.05 | mg N2O/m2/d | GC/static | opaque | 40 | 3 | no | yes | yes | Christensen TR et al. 1999 | |||||||||||||
Niwot_Ridge_N2O | US-Niw-1992-01 | 26.39 | isolated | Alpine | Upland | Vegetated | Alpine meadow, dry | United States | Rocky Mountains | Niwot Ridge | 40.05 | -105.35 | 1 | 1992 | 6 | 1992 | 8 | 0.47 | 19.00 | 14.00 | 2.00 | 0.63 | 52 | 52.000 | -1.9 | 487 | In situ | No | No | none | 7 | 5 | 0.07 | ng N /cm2/h | GC/static | opaque | 105 | 3 | no | yes | yes | Neff JC et al. 1994 | ||||||||||||||
Niwot_Ridge_N2O | US-Niw-1992-02 | 542.94 | isolated | Alpine | Upland | Vegetated | Alpine meadow, dry | United States | Rocky Mountains | Niwot Ridge | 40.05 | -105.35 | 1 | 1992 | 6 | 1992 | 8 | 0.71 | 17.90 | 49.00 | 15.00 | 0.63 | 52 | 52.000 | -1.9 | 487 | In situ | Yes | Yes | N-addition | 7 | 5 | 1.44 | ng N /cm2/h | GC/static | opaque | 105 | 3 | no | yes | yes | Neff JC et al. 1994 | ||||||||||||||
Niwot_Ridge_N2O | US-Niw-1992-03 | 30.16 | isolated | Alpine | Wetland | Vegetated | Alpine meadow, wet | United States | Rocky Mountains | Niwot Ridge | 40.05 | -105.35 | 1 | 1992 | 6 | 1992 | 8 | 1.24 | 15.60 | 75.00 | 2.00 | 1.34 | 90 | 90.000 | -1.9 | 487 | In situ | No | No | none | 7 | 5 | 0.08 | ng N /cm2/h | GC/static | opaque | 105 | 3 | no | yes | yes | Neff JC et al. 1994 | ||||||||||||||
Niwot_Ridge_N2O | US-Niw-1992-04 | 1293.25 | isolated | Alpine | Wetland | Vegetated | Alpine meadow, wet | United States | Rocky Mountains | Niwot Ridge | 40.05 | -105.35 | 1 | 1992 | 6 | 1992 | 8 | 1.11 | 15.90 | 86.00 | 12.00 | 1.34 | 90 | 90.000 | -1.9 | 487 | In situ | Yes | Yes | N-addition | 7 | 5 | 3.43 | ng N /cm2/h | GC/static | opaque | 105 | 3 | no | yes | yes | Neff JC et al. 1994 | ||||||||||||||
Niwot_Ridge_N2O | US-Niw-1993-01 | 62.84 | isolated | Alpine | Upland | Vegetated | Alpine meadow | United States | Rocky Mountains | Niwot Ridge | 40.05 | -105.35 | 1 | 1993 | 1 | 1 | 1993 | 4 | 4 | -3.8 | -7.0 | 1006 | 0.00 | In situ | No | No | none | 9 | 6 | 40.00 | µg N/m2/d | snow gradient | yes | no | yes | Williams MW et al. 1998 | ||||||||||||||||||||
Niwot_Ridge_N2O | US-Niw-1994-01 | 128.82 | isolated | Alpine | Upland | Vegetated | Alpine meadow | United States | Rocky Mountains | Niwot Ridge | 40.05 | -105.35 | 1 | 1994 | 1 | 1 | 1994 | 5 | -3.8 | -2.5 | 1006 | 0.00 | In situ | Yes | Yes | Snow fence | 11 | 9 | 82.00 | µg N/m2/d | snow gradient | yes | no | yes | Williams MW et al. 1998 | |||||||||||||||||||||
Yukon_Delta_N2O | US-Ykd-2016-01 | -319.33 | none | Arctic | Wetland | Vegetated | Coastal tundra along Bering Sea, gradient from barren tidal mud flats to wet sedge meadows dominated by Carex, to moist meadows | United States | Alaska | Yukon Delta | 61.25 | -165.62 | 1 | 2016 | 6 | 2 | 2016 | 8 | 18 | 7.0 | -1.6 | 10.0 | 430 | In situ | Yes | No | Birds, Grazing | 19 | -0.08 | nmol N2O/m2/s | portable gas analzyer | transparent | 3 | 36 | yes | yes | yes | Kelsey KC et al. 2018 |