global measurement of nitrous oxide and its stable isotopes … poster... · 2018. 7. 4. ·...

1
8. ABBREVIATED REFERENCES Mohn, J., B. Tuzson, A. Manninen, N. Yoshida, S. Toyoda, W.A. Brand, and L. Emmenegger. 2012. Site selective real-time measurements of atmospheric N2O isotopomers by laser spectroscopy. Atmos. Meas. Tech. Discuss., 5:813-838. Park, S., P. Croteau, K. A. Boering, D. M. Etheridge, D. Ferretti, P. J. Fraser, K-R. Kim, P. B. Krummel, R. L. Langenfelds, T. D. van Ommen, L. P. Steele, and C. M. Trudinger. 2012. Trends and seasonal cycles in the isotopic composition of nitrous oxide since 1940. Nat. Geosci.,5:261:265. Pérez, T., S. E. Trumbore, S. C. Tyler, P. A. Matson, and I. Ortiz-Monasterio. 2001. Identifying the agricultural imprint on the global N2O budget using stable isotopes. J. Geophys. Res., 106:9869–78. Rahn, T., and M. Wahlen. 2000. A reassessment of the global isotopic budget of atmospheric nitrous oxide. Global Biogeochem. Cycles, 14(2): 537-543. Sutka, R. L., N. E. Ostrom, P. H. Ostrom, J. A. Breznak, H. Gandhi, A. J. Pitt, and F. Li. 2006. Distinguishing nitrous oxide production from nitrification and denitrification on the basis of isotopomer abundances. Applied and Environmental Microbiology, 72: 638-644. Toyoda, S. and N. Yoshida. 1999. Determination of nitrogen isotopomers of nitrous oxide on a modified isotope ratio mass spectrometer. Anal. Chem., 71: 4711-4718. 1. INTRODUCTION Global Measurement of Nitrous Oxide and its Stable Isotopes using Cavity Ring-down Spectroscopy Amy E. Steiker1, Alan R. Townsend1, James W.C. White1 1 Institute of Arctic and Alpine Research, University of Colorado, UCB 450, Boulder, CO, 80309, USA University of Colorado Boulder 2. MEASURED SITES FROM NOAA CCGG FLASK NETWORK 3. PICARRO G5101-i Analyzer 6. DISCUSSION 7. CONCLUSIONS AND FUTURE WORK * Nitrous oxide (N 2 O), a greenhouse gas with ~300 times the global warming potential of CO 2 , is currently increasing at a rate of ~0.26% yr -1 , mainly due to increased microbial production from fertilized agricultural systems. A better understanding of the controls over N 2 O production is essential to more effective mitigation policies. * Due to the complexity of microorganism processes within soil, the spatiotemporal effects of fertilizer on N 2 O production at a high resolution remain largely unconstrained. Advances in the use of stable isotope techniques can aid in determining the sources and mechanisms involved in soil N 2 O emission. Determining the intramolecular, or site-specific, position of 15 N (β position 15 N 14 N 16 O versus α position 14 N 15 N 16 O) is a more robust tool for unraveling the biological and physical controls over atmospheric N 2 O. The position-specific 15 N is measured as site preference (SP), which is defined as [δ 15 Nα - δ 15 Nβ]. Unlike total δ 15 N-N 2 O, it has been shown that SP values are independent of the substrate’s isotopic composition in microbial processes, with SP values of ~33‰ and ~0‰ for nitrification-derived N 2 O versus denitrification-derived N 2 O, respectively. * A subset of sites from the NOAA Global Monitoring Division (GMD) Cooperative Sampling Network is being measured using Picarro’s new G5101-i analyzer capable of simultaneous N 2 O concentration, δ 15 Nα, and δ 15 Nβ measurement in order to describe the global distribution of N 2 O and its isotopes on a seasonal level, and to refine current models of the global N 2 O cycle. *Precision of unflagged samples averages 0.1 ppb for mole-fractions and 0.5‰ for both δ 15 Nα and δ 15 Nβ. Precision determined by calculating standard deviation of 100 second rolling means of each sample. *N 2 O concentration measurements beginning to capture northen hemisphere agricultural signal, yielding high summer N 2 O emissions. *We expect to see a seasonal cycle in N 2 O isotopomers due to stratospheric mixing in the spring of each hemisphere (causing an enrichment in total δ 15 N and SP) and heightened ocean and soil microbial activity in the summer and fall of each hemisphere (causing an increase in N 2 O concentration as well as a depletion in total δ 15 N). *Antarctic data consistent in enrichment of δ 15 N seen in the spring of each hemisphere due to stratospheric mixing. *Data show correlation between higher N 2 O concentration and more depleted δ 15 N (p<<0.05), consistent with previously determined global temporal trends. However, no correlation present between N 2 O concentration and SP. *The early stages of this project show the potential to not only better constrain the global N 2 O budget, but also better detect seasonal and interannual trends in N 2 O sources and sinks, specifically helping to partition shifts in nitrification versus denitrification processes. *More measurements are needed both temporally and spatially in order to detect these signals. In particular, seasonal variability of site-specific δ 15 N (± ~0.4‰) should be detectable given the instrument precision once a larger dataset is compiled. *International standards for N 2 O isotopomers are needed in order for accurate inter-laboratory comparison. Currently several efforts are being made to create commercially available standards. Our internal standards are being calibrated to the Toyoda and Yoshida scale, and future calibration work includes the development of a whole air standard for laser-based use. *CRDS holds several advantages over traditional IRMS methods including field deployablility, ease of use, continuous/simultaneous measurement of N 2 O concentration and 15 N isotopes, and no need for back-calculation of NO + fragment using IRMS. !" $"% &'( )*+,-*'. /0- 1+'*2'-2 34// 5566 7.'89 ANTARCTIC (66.56°S - 90°S) ARCTIC (66.56°N- 90°N) N. HEM (23.5°N - 66.5°N) S. HEM (23.5°S - 66.5°S) TROPICS (23.5°S - 23.5°N) 5. RESULTS 4. SAMPLING SYSTEM * Sampling line includes a beaded glass water trap submerged in -62°C ethanol bath in order to remove water * Sampling line is evacuated until pressure < 0.02 mBar; then sample is introduced and measured for 5 minutes * Samples are measured against internal standard cylinder containing ambient air filled at Niwot Ridge. Standards are measured for 10 minutes after 4 consecutive samples. A “trap” cylinder (known unknown QAQC sample) is also measured every 8 samples to ensure measurement accuracy. * Samples are corrected to an internal standard using concentration calibration from NOAA/ESRL and rough isotopic calibration from the Biogeochemistry and Paleoproteomics Lab at Michigan State University. * Sample flag limits are > 1 ppb different from NOAA/ESRL halocarbons flask program data and > 1‰ flask pair difference for δ 15 N, δ 15 α, and δ 15 Nβ. Picarro’s innovative technology employs Cavity Ring Down Spectroscopy (CRDS), where a small cavity is filled with light from a laser beam, and is then shut off, causing the light to decay exponentially. This “ring-down” is performed both with the laser tuned for and against N 2 O. The gas concentration is then calculated from the difference in these ring-down times. Since energy absorbance is a function of the size and shape of a molecule, N 2 O stable isotopes and isotopomers can both be measured using this approach. This particular analyzer employs a unique quantum cascade laser capable of the mid-infrared wavelength detection needed for N 2 O without the need for liquid nitrogen cooling. Abbreviated Specs * ~4 second sampling interval * 0.3 to 2 ppm N 2 O sampling concentration * 30 sccm flow rate * 300 to 1000 Torr sampling pressure

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Page 1: Global Measurement of Nitrous Oxide and its Stable Isotopes … poster... · 2018. 7. 4. · Microbiology, 72: 638-644. Toyoda, S. and N. Yoshida. 1999. Determination of nitrogen

8. ABBREVIATED REFERENCES

Mohn, J., B. Tuzson, A. Manninen, N. Yoshida, S. Toyoda, W.A. Brand, and L. Emmenegger. 2012. Site selective real-time measurements of atmospheric N2O isotopomers by laser spectroscopy. Atmos. Meas. Tech. Discuss., 5:813-838.

Park, S., P. Croteau, K. A. Boering, D. M. Etheridge, D. Ferretti, P. J. Fraser, K-R. Kim, P. B. Krummel, R. L. Langenfelds, T. D. van Ommen, L. P. Steele, and C. M. Trudinger. 2012. Trends and seasonal cycles in the isotopic composition of nitrous oxide since 1940. Nat. Geosci.,5:261:265.

Pérez, T., S. E. Trumbore, S. C. Tyler, P. A. Matson, and I. Ortiz-Monasterio. 2001. Identifying the agricultural imprint on the global N2O budget using stable isotopes. J. Geophys. Res., 106:9869–78.

Rahn, T., and M. Wahlen. 2000. A reassessment of the global isotopic budget of atmospheric nitrous oxide. Global Biogeochem. Cycles, 14(2): 537-543.

Sutka, R. L., N. E. Ostrom, P. H. Ostrom, J. A. Breznak, H. Gandhi, A. J. Pitt, and F. Li. 2006. Distinguishing nitrous oxide production from nitrification and denitrification on the basis of isotopomer abundances. Applied and Environmental Microbiology, 72: 638-644.

Toyoda, S. and N. Yoshida. 1999. Determination of nitrogen isotopomers of nitrous oxide on a modified isotope ratio mass spectrometer. Anal. Chem., 71: 4711-4718.

1. INTRODUCTION

Global Measurement of Nitrous Oxide and its Stable Isotopes using Cavity Ring-down SpectroscopyAmy E. Steiker1, Alan R. Townsend1, James W.C. White1

1 Institute of Arctic and Alpine Research, University of Colorado, UCB 450, Boulder, CO, 80309, USA

University of Colorado Boulder

2. MEASURED SITES FROM NOAA CCGG FLASK NETWORK

3. PICARRO G5101-i Analyzer

6. DISCUSSION

7. CONCLUSIONS AND FUTURE WORK

* Nitrous oxide (N2O), a greenhouse gas with ~300 times the global warming potential of CO

2,

is currently increasing at a rate of ~0.26% yr -1, mainly due to increased microbial production from fertilized agricultural systems. A better understanding of the controls over N

2O

production is essential to more effective mitigation policies. * Due to the complexity of microorganism processes within soil, the spatiotemporal effects of fertilizer on N

2O production at a high resolution remain largely unconstrained. Advances

in the use of stable isotope techniques can aid in determining the sources and mechanisms involved in soil N

2O emission. Determining the intramolecular, or site-specific, position of 15N

(β position 15N14N16O versus α position 14N15N16O) is a more robust tool for unraveling the biological and physical controls over atmospheric N

2O. The position-specific 15N is measured

as site preference (SP), which is defined as [δ15Nα - δ15Nβ]. Unlike total δ15N-N2O, it has been

shown that SP values are independent of the substrate’s isotopic composition in microbial processes, with SP values of ~33‰ and ~0‰ for nitrification-derived N

2O versus

denitrification-derived N2O, respectively.

* A subset of sites from the NOAA Global Monitoring Division (GMD) Cooperative Sampling Network is being measured using Picarro’s new G5101-i analyzer capable of simultaneous N

2O concentration, δ15Nα, and δ15Nβ measurement in order to describe the global

distribution of N2O and its isotopes on a seasonal level, and to refine current models of the

global N2O cycle.

*Precision of unflagged samples averages 0.1 ppb for mole-fractions and 0.5‰ for both δ15Nα and δ15Nβ. Precision determined by calculating standard deviation of 100 second rolling means of each sample.

*N2O concentration measurements beginning to capture northen hemisphere

agricultural signal, yielding high summer N2O emissions.

*We expect to see a seasonal cycle in N2O isotopomers due to stratospheric

mixing in the spring of each hemisphere (causing an enrichment in total δ15N and SP) and heightened ocean and soil microbial activity in the summer and fall of each hemisphere (causing an increase in N

2O concentration as well as a

depletion in total δ15N).

*Antarctic data consistent in enrichment of δ15N seen in the spring of each hemisphere due to stratospheric mixing.

*Data show correlation between higher N2O concentration and more depleted

δ15N (p<<0.05), consistent with previously determined global temporal trends. However, no correlation present between N

2O concentration and SP.

*The early stages of this project show the potential to not only better constrain the global N

2O budget, but also better detect seasonal and interannual trends in

N2O sources and sinks, specifically helping to partition shifts in nitrification

versus denitrification processes.

*More measurements are needed both temporally and spatially in order to detect these signals. In particular, seasonal variability of site-specific δ15N (± ~0.4‰) should be detectable given the instrument precision once a larger dataset is compiled.

*International standards for N2O isotopomers are needed in order for accurate

inter-laboratory comparison. Currently several efforts are being made to create commercially available standards. Our internal standards are being calibrated to the Toyoda and Yoshida scale, and future calibration work includes the development of a whole air standard for laser-based use.

*CRDS holds several advantages over traditional IRMS methods including field deployablility, ease of use, continuous/simultaneous measurement of N

2O

concentration and 15N isotopes, and no need for back-calculation of NO+ fragment using IRMS.

�e World's Leading Instruments forCarbon and Water Cycle Measurements

©2012 PICARRO, INC. · 3105 Patrick Henry Drive, Santa Clara, CA 95054 · T 408.962.3900 · E [email protected] · W www.picarro.com

Guaranteed Performance Specifications

Target Species Precision 1-σ 10 min avg 100 sec avg

Concentration Range (ppm N2O in Air)

N2O (Concentration) < 0.05 ppb < 0.1 ppb 0.3 - 2 (optional extended mode to 20)

δ15N, δ15Nα, δ15Nβ < 0.5 ‰ < 1 ‰ 0.3 - 2 (optional extended mode to 20)

System Specifications

Measurement Technique

Time-based, CRDS

Measurement Interval

< 10 seconds

Outputs RS-232, Ethernet, USB

Fittings ¼” Swagelok®

Dimension (two box system)

17” w x 20” d x 12” h (43 x 51 x 32 cm)

Weight 95 lbs (43 kg)

Technology Advantage: Operating in the Mid IR,

Picarro’s unique cavity ring-down spectroscopy (CRDS)

provides unsurpassed performance by leveraging the

sensitivity of time-based measurement with the precision

produced by an optical path length over 8 km.

Practical Design: Picarro’s small, 48 cc measurement

cell ensures better stability, lower noise, and improved

capability to handle small samples. It also enables the most

compact design of any N2O isotope analyzer.

Precise Control: In order to produce highly linear

and low drift measurements over months of operation,

pressure and temperature are controlled to better than

±0.005 ºC and ±0.0002 atm. In conjunction, our patented

wavelength monitor ensures absolute spectral position is

accurately maintained.

Easy Configuration: Choose to automatically send data

at regular intervals via Ethernet or optional modem, or

stream data in real-time. Users can easily connect and

control the analyzer using the provided or other remote

login software.

PICARRO G5101-i N2O Concentration and Isotopes Analyzer

δ15N including site specific isotopomers

Continuous, Precise, Stable

Operating Conditions

Sample Temperature -10 to 45 °C

Sample Flow Rate < 50 sccm at 760 Torr, no filtration

required

Sample Pressure 300 to 1000 Torr (40 to 133 kPa)

Sample Humidity 0-2 % v H2O (18°C dew point)

non-condensing

Temperature 15 to 35 °C (operating)

-10 to 50 °C (storage)

Humidity (ambient) < 99% R.H. non-condensing

!"#$"%#&'(#

)*+,-*'.#/0-#1+'*2'-2#

34//#5566#7.'89##

ANTARCTIC (66.56°S - 90°S)

color name color name

darkgreen

darkgrey

darkkhaki

darkmagenta

darkolivegreen

darkolivegreen1

deepskyblue

deepskyblue1

deepskyblue2

deepskyblue3

deepskyblue4

dimgray

color name color name

orangered

orangered1

orangered2

orangered3

orangered4

orchid

orchid1

orchid2

orchid3

orchid4

palegoldenrod

palegreen

palegreen1

palegreen2

palegreen3

palegreen4

paleturquoise

paleturquoise1

paleturquoise2

paleturquoise3

paleturquoise4

palevioletred

palevioletred1

palevioletred2

palevioletred3

plum2

plum3

plum4

powderblue

purple

purple1

purple2

purple3

purple4

red

red1

red2

red3

red4

rosybrown

rosybrown1

rosybrown2

rosybrown3

rosybrown4

royalblue

royalblue1

royalblue2

royalblue3

royalblue4

saddlebrown

ARCTIC (66.56°N- 90°N)

color name color name

lightpink4

lightsalmon

lightsalmon1

lightsalmon2

lightsalmon3

lightsalmon4

lightseagreen

lightskyblue

lightskyblue1

lightskyblue2

lightskyblue3

lightskyblue4

lightslateblue

lightslategray

lightslategrey

lightsteelblue

lightsteelblue1

lightsteelblue2

lightsteelblue3

lightsteelblue4

lightyellow

lightyellow1

lightyellow2

lightyellow3

lightyellow4

limegreen

linen

magenta

magenta1

magenta2

magenta3

magenta4

maroon

maroon1

maroon2

maroon3

maroon4

mediumaquamarine

mediumblue

mediumorchid1

mediumorchid2

mediumorchid3

mediumorchid4

mediumpurple

mediumpurple1

mediumpurple2

mediumpurple3

mediumpurple4

mediumseagreen

mediumslateblue

mediumspringgreen

mediumturquoise

mediumvioletred

midnightblue

mintcream

mistyrose

mistyrose1

mistyrose2

mistyrose3

mistyrose4

moccasin

navajowhite

navajowhite1

navajowhite2

navajowhite3

navajowhite4

navy

navyblue

oldlace

olivedrab

olivedrab1

olivedrab2

olivedrab3

olivedrab4

orange

orange1

orange2

orange3

N. HEM (23.5°N - 66.5°N)

color name color name

seashell4

sienna

sienna1

sienna2

sienna3

sienna4

skyblue

skyblue1

skyblue2

skyblue3

skyblue4

slateblue

tan3

tan4

thistle

thistle1

thistle2

thistle3

thistle4

tomato

tomato1

tomato2

tomato3

tomato4

S. HEM (23.5°S - 66.5°S)

color name color name

seashell4

sienna

sienna1

sienna2

sienna3

sienna4

skyblue

skyblue1

skyblue2

skyblue3

skyblue4

slateblue

slateblue1

slateblue2

slateblue3

slateblue4

slategray

slategray1

slategray2

slategray3

slategray4

slategrey

snow

snow1

snow2

snow3

snow4

springgreen

springgreen1

springgreen2

springgreen3

springgreen4

steelblue

steelblue1

steelblue2

tan3

tan4

thistle

thistle1

thistle2

thistle3

thistle4

tomato

tomato1

tomato2

tomato3

tomato4

turquoise

turquoise1

turquoise2

turquoise3

turquoise4

violet

violetred

violetred1

violetred2

violetred3

violetred4

wheat

wheat1

wheat2

wheat3

wheat4

whitesmoke

yellow

yellow1

yellow2

yellow3

yellow4

yellowgreen

TROPICS (23.5°S - 23.5°N)

5. RESULTS

4. SAMPLING SYSTEM* Sampling line includes a beaded glass water trap submerged in -62°C ethanol bath in order to remove water* Sampling line is evacuated until pressure < 0.02 mBar; then sample is introduced and measured for 5 minutes* Samples are measured against internal standard cylinder containing ambient air filled at Niwot Ridge. Standards are measured for 10 minutes after 4 consecutive samples. A “trap” cylinder (known unknown QAQC sample) is also measured every 8 samples to ensure measurement accuracy. * Samples are corrected to an internal standard using concentration calibration from NOAA/ESRL and rough isotopic calibration from the Biogeochemistry and Paleoproteomics Lab at Michigan State University. * Sample flag limits are > 1 ppb different from NOAA/ESRL halocarbons flask program data and > 1‰ flask pair difference for δ15N, δ15α, and δ15Nβ.

Picarro’s innovative technology employs Cavity Ring Down Spectroscopy (CRDS), where a small cavity is filled with light from a laser beam, and is then shut off, causing the light to decay exponentially. This “ring-down” is performed both with the laser tuned for and against N

2O.

The gas concentration is then calculated from the difference in these ring-down times. Since energy absorbance is a function of the size and shape of a molecule, N

2O stable

isotopes and isotopomers can both be measured using this approach. This particular analyzer employs a unique quantum cascade laser capable of the mid-infrared wavelength detection needed for N

2O without the need for liquid

nitrogen cooling.

Abbreviated Specs

* ~4 second sampling interval* 0.3 to 2 ppm N

2O sampling concentration

* 30 sccm flow rate* 300 to 1000 Torr sampling pressure

*Error bars contained within datapoints