the Creative Commons Attribution 4.0 License.
the Creative Commons Attribution 4.0 License.
Airborne measurements of oxygen concentration from the surface to the lower stratosphere and pole to pole
Eric J. Morgan
Jonathan D. Bent
Ralph F. Keeling
Andrew S. Watt
Stephen R. Shertz
Bruce C. Daube
We have developed in situ and flask sampling systems for airborne measurements of variations in the ratio at the part per million level. We have deployed these instruments on a series of aircraft campaigns to measure the distribution of atmospheric O2 from 0–14 km and 87∘ N to 86∘ S throughout the seasonal cycle. The National Center for Atmospheric Research (NCAR) airborne oxygen instrument (AO2) uses a vacuum ultraviolet (VUV) absorption detector for O2 and also includes an infrared CO2 sensor. The VUV detector has a precision in 5 s of ±1.25 per meg (1σ) δ(), but thermal fractionation and motion effects increase this to ±2.5–4.0 per meg when sampling ambient air in flight. The NCAR/Scripps airborne flask sampler (Medusa) collects 32 cryogenically dried air samples per flight under actively controlled flow and pressure conditions. For in situ or flask O2 measurements, fractionation and surface effects can be important at the required high levels of relative precision. We describe our sampling and measurement techniques and efforts to reduce potential biases. We also present a selection of observational results highlighting the individual and combined instrument performance. These include vertical profiles, O2:CO2 correlations, and latitudinal cross sections reflecting the distinct influences of terrestrial photosynthesis, air–sea gas exchange, burning of various fuels, and stratospheric dynamics. When present, we have corrected the flask δ() measurements for fractionation during sampling or analysis with the use of the concurrent δ() measurements. We have also corrected the in situ δ() measurements for inlet fractionation and humidity effects by comparison to the corrected flask values. A comparison of -corrected Medusa flask δ() measurements to regional Scripps O2 Program station observations shows no systematic biases over 10 recent campaigns ( per meg, mean and standard deviation, n=86). For AO2, after resolving sample drying and inlet fractionation biases previously on the order of 10–100 per meg, independent AO2 δ() measurements over six more recent campaigns differ from coincident Medusa flask measurements by per meg (mean and standard deviation, n=1361) with campaign-specific means ranging from −5 to +5 per meg.
- Article
(5591 KB) - Full-text XML
-
Supplement
(4899 KB) - BibTeX
- EndNote
Atmospheric O2 observations can be a powerful tool for elucidating carbon cycle processes on multiple time and space scales because of the unique relationships between O2 and CO2 surface exchange (e.g., Keeling and Shertz, 1992; Stephens et al., 1998; Ishidoya et al., 2013a; Keeling and Manning, 2014; Nevison et al., 2015; Morgan et al., 2019). Although measuring atmospheric O2 is challenging because of the need to detect small variations against the large natural background, various in situ and flask-based techniques are now capable of achieving precision at the required 10−6 relative level (Keeling, 1988; Bender et al., 1994; Manning et al., 1999; Tohjima, 2000; Stephens et al., 2003, 2007a). In particular, airborne measurements have the potential to capture information on processes at large spatial scales and to overcome uncertainty associated with the vertical mixing of flux signals away from the surface (e.g., Gerbig et al., 2003; Stephens et al., 2007b; Graven et al., 2013; Sweeney et al., 2015).
However, aircraft pose significant limitations to instrument size, weight, and power, and are challenging platforms from which to conduct precise measurements. Cabin temperature can vary by 10 ∘C and have local vertical gradients of 5 ∘C m−1; cabin pressure can vary by 250 hPa. Furthermore, while profiling from the surface to 14 km in the tropics, ambient humidity drops from over 30 000 to less than 20 ppm, ambient temperature drops by 85 ∘C, and ambient pressure drops from 1000 to 150 hPa. To avoid fractionation of O2 relative to N2 or surface effects in the face of these and other challenges, it is generally necessary to actively control instrument flows, temperatures, and pressures, to dry the sample stream to a few ppm of H2O, and to minimize the surface area and roughness of tubing experiencing temperature, pressure, and humidity changes (Keeling et al., 1998; Langenfelds, 2002). Additional sources of measurement bias may result from fractionation at sample inlets (Blaine et al., 2006; Steinbach, 2010; Bent, 2014), thermal diffusion of gases inside calibration cylinders (Langenfelds, 2002), and leaks of cabin air reaching the inlet stream (Vay et al., 2003). Flask sampling reduces some of these challenges because flasks can generally be sampled at higher flow rates and the critical calibration and analysis steps all occur in a controlled laboratory environment. However, flask sampling may be subject to fractionation at the flask outlet during sampling (Bent, 2014) and storage effects (Keeling et al., 1998; Steinbach, 2010). In comparison, the advantages of in situ atmospheric O2 measurements are the greatly increased spatial and temporal coverage and resolution, and the lack of sample storage concerns. Measurements of atmospheric O2 have been made on flasks collected from aircraft in a number of studies (Langenfelds, 2002; Sturm et al., 2005; Steinbach, 2010; Ishidoya et al., 2012, 2014; van der Laan et al., 2014; Bent, 2014).
Here we present an airborne in situ O2 instrument that has flown on 13 campaigns since 2007 and an airborne flask sampling system that has flown on 17 campaigns since 1999 (Figs. S1 and S2 in the Supplement). We focus on data from recent campaigns. Flying on the NSF/NCAR High-performance Instrumented Airborne Platform for Environmental Research (HIAPER) Gulfstream V (GV) aircraft (UCAR/NCAR – Earth Observing Laboratory, 2005), these campains include the Stratosphere–Troposphere Analyses of Regional Transport campaign (START-08; Pan et al., 2010), five HIAPER Pole-to-Pole Observations campaigns (HIPPO 1–5, 2009–2011; Wofsy et al., 2011), and the 2016 Ratio and CO2 Airborne Southern Ocean (ORCAS) study (Stephens et al., 2018). We also include data from the Airborne Research Instrumentation Testing Opportunity (ARISTO-2015) campaign on the NSF/NCAR C-130 (UCAR/NCAR – Earth Observing Laboratory, 1994), and four Atmospheric Tomography Mission (ATom 1–4, 2016–2018) campaigns on the NASA DC-8. Selected results and methods from these instruments have been previously presented in Bent (2014), Resplandy et al. (2016), Nevison et al. (2016), Stephens et al. (2018), Asher et al. (2019), Morgan et al. (2019), and Birner et al. (2020).
The in situ NCAR airborne oxygen instrument (AO2) measures O2 concentration using a vacuum ultraviolet (VUV) absorption technique. AO2 is based on earlier shipboard (Stephens, 1999; Stephens et al., 2003) and laboratory instruments using the same technique, but has been designed specifically for airborne use to minimize motion and thermal sensitivity and with a pressure- and flow-controlled inlet system. The VUV detector in AO2 uses a low-pressure small-volume detector cell, which is possible due to the very high absorption cross section for O2 in the VUV. The small cell allows rapid switching between sample and reference which, combined with the strong absorption, provide unparalleled signal-to-noise ratio and rapid time response. We tested an early prototype in situ instrument on the NSF/NCAR C-130 during the Instrument Development and Education in Airborne Science (IDEAS-1 and IDEAS-2, 2002) campaigns. AO2 first made research quality measurements on the University of Wyoming King Air during the 2007 Airborne Carbon in the Mountains Experiment (ACME-07; Desai et al., 2011),
The NCAR/Scripps Medusa airborne flask sampler was designed to collect cryogenically dried air samples under controlled pressure and flow conditions. The drying and pressure and flow control are necessary to minimize fractionation of the collected air during sampling and to reduce surface effects from both the flasks and sample tubing. The Medusa flasks are maintained at 1 atm pressure and a few ppm of H2O at all times from preparation and shipping through sampling and analysis. In addition, the flasks are contained in an insulated enclosure to minimize thermal fractionation effects during sampling. An earlier 16 flask version of the sampler flew on the University of North Dakota (UND) Citation II aircraft during the CO2 Budget and Rectification and Airborne Study (COBRA-1999test, COBRA-2000 and COBRA-2003; Stephens et al., 2000; Kort et al., 2008) and during IDEAS-1. This version also flew on the NSF/NCAR C-130 during ACME-04, but collected smaller samples for 13C of CO2 and not O2 measurements (Sun et al., 2010). We repackaged Medusa for START-08 and then increased the sampling capacity to 32 flasks for HIPPO-1.
Here we describe the AO2 (Sect. 2) and Medusa (Sect. 3) configurations and operational procedures as flown during the most recent ORCAS and ATom campaigns and list significant past configuration changes in Table S2 in the Supplement. For AO2, we focus on aspects specific to airborne deployment and other modifications from the instrument described by Stephens et al. (2003). Additional Medusa details can be found in Bent (2014). In Sect. 4, we discuss potential sources of measurement bias and our efforts to minimize them. We confine this discussion primarily to the O2 measurements and leave discussion of potential CO2 biases for presentation elsewhere; for HIPPO CO2 instrument intercomparisons, see Santoni et al. (2014) and Gaubert et al. (2019). We then present a selection of measured vertical profiles, O2:CO2 correlations, and latitude–altitude cross sections (Sect. 5) that highlight the resolution of the measurements and their ability to distinguish the influences of specific processes.
2.1 Instrument description
The AO2 gas handling system depicted in Fig. 1 consists of a pump box, a cylinder box, an analyzer box, an inlet, and a cryotrap. See Table S1 in the Supplement for selected vendor and part numbers. We describe AO2 here in the general order of the sample air moving through the system. During ATom 2–4, AO2 sampled from an aft-facing 3.2 mm OD, 2.2 mm ID electropolished stainless steel inlet inside of a HIAPER modular inlet (HIMIL) pylon 47.5 cm from the aircraft skin. The HIMIL is a cigar-shaped tube with a 6.4 mm ID conical knife edge forward inlet, a 22 mm ID cylindrical bore, and a 9.5 mm ID outlet, and is designed to slow the relative air speed to minimize acceleration effects at the internal 3.2 mm inlet to the instrument. The HIMIL contains the AO2 and Medusa sample inlet tubing, an open tube connected to a pressure sensor, and an unused sample tube. The AO2 inlet is the aftmost of these. Except where noted, all tubing exposed to sample air in AO2 is 3.2 mm OD, 2.2 mm ID electropolished Sulfinert-treated stainless steel to minimize surface adsorption and desorption effects.
Immediately inside the aircraft from the inlet, a manual three-way valve selects air from either the inlet or a line purge cylinder. Directly following this selection, a proportional solenoid valve actively controls the pressure in the line to the instrument rack and at the inlet to an upstream vacuum pump. The pump uses Teflon-coated diaphragms and Teflon valve plates sealed by o-rings to custom aluminum heads, the latter used to minimize volume. Before entering the pump box, we filter sample air using a 3 µm pore by 47 mm diameter mixed cellulose ester filter in a stainless steel holder. The feedback controller for the inlet solenoid valve is referenced to an absolute pressure sensor downstream of the pump and maintains a pump outlet pressure of 1050±7 hPa (1σ at 0.4 Hz) over the full range of flight altitudes. The sample air is then cryogenically dried with a 1.6 cm ID by 20.5 cm long electropolished stainless steel trap immersed in a dry ice and Fluorinert slurry at −78.5 ∘C to a depth of 18 cm at the start of a flight. At the pump outlet pressure of 1050 hPa this results in a saturation vapor concentration of 1.5 ppm. The air enters the trap at the top and exits through a 3.2 mm OD, 2.2 mm ID dip tube extending near the bottom of the trap. We use 3 mm glass beads in the lower 10 cm of the trap to minimize volume below the area of most ice accumulation and to restrict the free passage of any ice particles that might break loose, resulting in an approximate trap volume of 22 mL.
After compression and drying, the sample air is selected to either be measured or purged by a solenoid manifold that can also select one of several calibration gases to be measured or purged. These calibration gases include a high-span (high O2 and low CO2 concentration), a low-span (low O2 and high CO2 concentration), a long-term reference, and a working tank. All calibration gases are composed of ambient air dried to less than 1 ppm H2O. The working tank runs continuously as a reference and can also be selected for measurement to be used as an additional CO2 calibration; for O2, the working tank is only used for diagnostic purposes as there is potential for fractionation in splitting the flow in the cylinder box manifold. The calibration gases are contained in high-pressure, 4.7 L fiber-wrapped aluminum cylinders, horizontally mounted in a block of foam insulation 5 cm thick at the outside walls. Two-stage brass regulators on each calibration gas cylinder are adjusted to match the delivery pressure of the inlet sample pump during preflight, but as they are referenced to cabin pressure, the absolute delivery pressure of the regulators varies in flight.
The inlet line purge gas is in a similar cylinder but mounted vertically outside of the insulated cylinder box and uses a similar regulator but with a lower delivery pressure of 70 hPa above cabin. During ACME-07, prior to Research Flight 10 on START-08, and during HIPPO-3, we used a coiled 6.4 mm diameter electropolished stainless steel moisture trap held at approximately 1 ∘C as a preliminary drying stage. Out of concerns for surface effects, and because the aircraft spent the most time sampling very dry air, this trap has not been used since (Table S2 in the Supplement).
The working tank and the selected sample or calibration gas, which we refer to as the span gas, are next pulled through the analyzer box by a downstream vacuum pump with sufficient capacity to operate the detector cell at <100 hPa. Both airstreams first pass, in sequence, an absolute pressure sensor, a proportional solenoid valve, a mass flow meter, and a 13 hPa full-scale differential pressure sensor referenced to a common 500 mL insulated volume maintained at 400 hPa. The feedback controllers for these solenoid valves actively match this pressure to within ±1.5 Pa (1σ at 0.4 Hz). The span gas is then measured for CO2 by a single cell non-dispersive infrared CO2 H2O sensor. We replaced the CO2 sensor internal plastic tubing with 3.2 mm OD stainless steel, but to avoid ground loops through the sensor, we inserted PFA union fittings inline to break electrical conductivity. The two streams are then cryogenically dried, the second time for the sample gas and as a precaution for calibration and working tank gases, in 3.2 mm OD, 2.2 mm ID by 120 cm long coiled tubes immersed in the dry ice slurry. At 400 hPa, the saturation vapor concentration in these traps is 3.8 ppm H2O. While this is wetter than saturation for the first-stage trap and calibration gas, we include it because the first-stage sample trap may not dry to saturation owing to residence time or diffusion limitations, and the span gases may pick up a small amount of water permeating through the seals in the CO2 sensor (see Sect. 4.5 below). The second-stage span gas trap is intended to remove any of this water, and we include a trap on the working tank line both for consistency and as an added precaution.
After the coiled tube traps, the gases reach a changeover valve manifold with two rapid-switching, long-life, miniature three-way solenoid valves configured to work as a low-volume four-way changeover valve. These valves alternately select the span or working tank gas to either be measured by the VUV detector cell or vented through a bypass line. On the VUV detector line, a 0.2 mm sapphire jewel orifice immediately upstream of the cell acts as a critical flow orifice and reduces the pressure to 95 hPa as it passes through the cell. A proportional solenoid valve downstream of the cell controls this pressure to within ±0.009 Pa (1σ at 0.4 Hz) by referencing a 1.3 hPa full-scale differential pressure sensor to a second 500 mL insulated volume. Between the changeover valve and the orifice we use 1.0 mm ID tubing to minimize sweepout times. A manual needle valve is located on the bypass line to match the combined flow impedance of the VUV detector line. The flow through the instrument is nominally 100 sccm, set by the sapphire orifice and the upstream reference pressure. Solenoid valves and pressure gauges allow the reference volume pressures to be monitored and adjusted if necessary between flights or for testing.
The VUV source consists of a Xe resonance lamp with a MgF2 window powered by a 15 W 180 MHz radio frequency oscillator, which emits strongly at 147 nm and more weakly at 129 nm (Okabe, 1964). The detector is a CsI photocathode with a MgF2 window and peak output of 100 nA. The analyzer box and O2 sensor have essentially the same configuration as the shipboard instrument described in Stephens (1999) and Stephens et al. (2003) with a few key differences. The airborne instrument, and our laboratory system, now use a sealed Xe lamp instead of the original flow through design. In addition to the MgF2 windows on the lamp and detector, we have also employed a sapphire window in front of the detector on the aircraft instrument to eliminate the secondary Xe line at 129 nm. Earlier tests using a sapphire window fused to the lamp body with a proprietary coating, showed large humidity effects that we previously speculated might have resulted from water adsorption on the sapphire coating. These effects no longer appear to be as significant, either because of the use of an uncoated sapphire window or because the earlier problems may have been a result of inadequate drying. However, to further minimize concerns we place an additional MgF2 disc on the sample cell side of this sapphire disc. We also use a 1 mm thick aluminum aperture disc with a 6.4 mm diameter hole between this MgF2 window and the sample cell to avoid damaging the CsI photocathode with too much light. The VUV absorption cell is thus defined on one side by the detector window and aperture disc and on the other by the lamp window and is a 4.3 mm long by 13 mm diameter cylinder with a 5.3 mm path length accounting for the aperture.
Figure 2 shows the relationship between detector voltage and cell pressure with this configuration, along with predicted noise contributions from thermal and shot noise. Using sapphire to exclude the 129 nm line in a region of weaker O2 absorption allows the instrument to be run at higher cell pressures and greater absorption factors. The 95 hPa cell pressure corresponds to an optical depth of 3.8, or absorption of 98 % of the light, and a scaling factor of 3.0 between changes in δ() and relative changes in the signal (ΔV V). This factor differs from 3.8 because the conversion between relative changes in mole fraction and δ() includes division by (1-X) (see Eq. 4 in Keeling et al., 1998). We amplify and convert the resulting detector current of approximately 80 nA with a low noise op amp and 1.25×108 ohm resistor (Stephens et al., 2003) and measure it using a 24-bit analogue-to-digital converter. As indicated in Fig. 2, there is a tradeoff between absorbing more light to achieve greater sensitivity and the increase in shot noise with the reduced number of photons reaching the detector. The current limits defined by the photocathode and op amp configuration are also relevant. Figure 2 also shows the typical noise from the instrument running calibration gas without switching in the lab, which indicates that the detector is within a factor of 2.4 of the shot and Johnson noise limit and that the predicted noise is not particularly sensitive to the choice of cell pressure between 80 and 120 hPa.
Our aircraft and lab systems also do not have the beam splitter and second detector described in Stephens et al. (2003) because we found that measurement noise could not be reduced by referencing to the unabsorbed beam, either because lamp output is not a dominant source of noise or plasma variations were imaged differently by the two detectors. We correct for the imperfect control of cell pressure on short timescales using the measured pressure differential between the cell and reference volume. We also employ a second identical 1.3 hPa full-scale differential pressure sensor with both ports plumbed together to correct for acceleration effects on the primary sensor (Fig. 1). These sensors have acceleration sensitivities of approximately 0.1 Pa s2 m−1. We orient all pressure sensors parallel to the longitudinal axis of the aircraft to minimize the impact of vertical and horizontal accelerations during turbulence, but they do experience changes in the longitudinal component of gravity with aircraft pitch, and longitudinal accelerations during intentional yaw maneuvers, or on takeoff or landing (Sect. 4.6.5).
AO2 control and data acquisition is done by an embedded computer and analogue-to-digital converters in each box. In addition to the primary sensor measurements, for diagnostic purposes, AO2 logs 16 temperatures, 12 pressures, and four flows at 0.4 to 10 Hz.
2.2 Measurement approach and precision
To achieve the high levels of precision desired, AO2 switches between sample gas and working tank gas approximately every 2.3 s, more than a factor of 2 faster than the earlier shipboard instrument (Stephens et al., 2003). The AO2 measurement is then based on the amplitude of the resulting square wave as defined by the bidirectional difference in signals between a particular jog and an average of the prior and subsequent jogs. This yields a statistically independent measurement every 4.6 s (hereafter rounded to 5 s), though we report partially overlapping differences every 2.3 s. The switching time is set by the amount of time the instrument needs to record 20 detector voltages at 10 Hz and then housekeeping variables between switches. Figure 3 shows the 5 s square wave signal averaged over the calibration and sample periods under different drying conditions. The low volume of the switching solenoid valves, the detector cell, and the intervening tubing, and the low cell pressure result in very fast cell flushing times on the order of 0.02 s. The instrument records a number of housekeeping signals over the first 0.3 s after switching and by the time it records the VUV detector signal again the cell has almost completely swept out. As a result, artifacts due to incomplete sweepout are small. The difference in slopes between the working tank and span segments of the square wave is only marginally influenced by the magnitude of the difference in concentration between the two gases, and we do not exclude any data following the changeover valve switch. However, the slope difference between working tank and span segments can provide an important diagnostic of several other possible issues, including delays in pressure equilibration from small cross-port leaks in the changeover valve or differences in humidity or hydrocarbons leading to chemical interactions with optical surfaces under intense VUV (see Sect. 4.5 below).
Atmospheric oxygen is quantified as the ratio of the relative abundance of O2 to the relative abundance of N2 in units of per meg (Keeling and Shertz, 1992; Keeling and Manning, 2014), i.e.,
where 1 per meg represents a one-millionth change in the ratio relative to an arbitrary reference. For the Scripps O2 Program O2 scale, this reference is a suite of high-pressure cylinders maintained at Scripps. An analogous definition to Eq. (1) is used to report measurements of the ratio. In addition to δ() and CO2, we also report values for the derived tracer atmospheric potential oxygen (APO; Stephens et al., 1998):
where 1.1 is the estimated stoichiometric ratio of long-term terrestrial biosphere O2 and CO2 exchange, and X is the mole fraction of O2 in dry air as defined by the Scripps O2 Program O2 scale. APO is designed to be conservative with respect to terrestrial photosynthesis and respiration, to only have a small fossil-fuel sink, and to primarily reflect δ() and CO2 exchange with the oceans. Although 1.05 is likely a better O2:CO2 ratio for canceling short-term terrestrial influences (Stephens et al., 2007a; Battle et al., 2019), we continue to use 1.1 here for consistency with past studies and encourage sensitivity tests over a range of possible O2:CO2 ratios.
Figure 4 shows instrument noise as a function of hypothetical switching time based on 40 min of calibration gas analysis with no actual valve switching in the lab. This figure includes the two-sample Allan standard deviation, as well as the standard deviation of the bidirectional three-sample differences we use, the latter of which has a broad minimum of 1.25 per meg between simulated switching times of 2 and 3 s. The slope of the rise in noise for shorter intervals suggests that there would be no improvement from switching faster. Figure 4 also shows typical noise values from the instrument while running calibration gas with switching and while measuring ambient air with stable concentration, both during field conditions. Although at times AO2 noise while running calibration gas is 1.25 per meg or better (1σ in 5 s), the value shown here of 1.6 per meg is more consistently achievable. For example, the median of the 5 s noise levels within all individual calibration gas intervals was 1.5 per meg for ATom-3, and 1.7 for ATom-4. Our correction of imperfect cell pressure control based on the downstream 1.3 hPa differential pressure sensor has a negligible effect for the lab conditions shown in Fig. 4 but can reduce the noise in turbulent flight conditions by a factor of 5 or more.
We find similar noise levels whether switching or not switching the changeover valve between working tank and a calibration gas, or between working tank and span gas when the trap is warm, indicating that pressure and flow fluctuations from the actual switching do not add noise. Rather, the slight increase in noise for calibration gases in flight relative to lab conditions is likely a result of aircraft motion and slight drift within the flight calibration intervals. However, the switching of the changeover valve does introduce extra noise when running either long-term surveillance gas or sample air through the first-stage trap when it is cold, suggesting an interaction between flow perturbations and thermal diffusion in the trap (Keeling et al., 1998). Thus, our typically achieved precision when measuring ambient air in stable conditions is 2.5–4.0 per meg, 1σ in 5 s. Figure 5 shows O2 and CO2 signals over the course of an entire flight, including several hours of preflight and 15 min of postflight inlet line purge analysis. For the 36 min high altitude period between 22:23 and 23:00 in Fig. 5, the variability in δ() is ±3.5 per meg (1σ for 5 s samples) and as low as ±2.5 per meg for similar periods on other flights (e.g., Fig. S3 in the Supplement). For comparison, 2.5 per meg is equal to a change of 0.4 ppm in O2 mole fraction or the addition of 0.5 micromoles of O2 to 1 mole of air (Keeling et al., 1998; Kozlova et al., 2008). This variability averages as white noise and with statistically independent samples every 5 s, the precision on a 1 min average is approximately ±0.7–1.1 per meg while measuring ambient air and 0.4 per meg for calibration gas.
2.3 In-flight calibration strategy
The AO2 high-pressure reference cylinders are equipped with brass valve manifolds sealed with silver-coated c-rings. These manifolds have needle valves going to either a fill and laboratory analysis port or a regulator for use in flight, a burst disc, and a 20 cm dip tube to minimize thermal fractionation in withdrawn air (Keeling et al., 2007). These dip tubes were one of 6.4 mm OD, 4.6 mm ID stainless steel; 3.2 mm OD, 1.4 mm ID nickel; or 0.16 mm OD, 1.0 mm ID electroformed nickel supported by a perforated 6.4 mm stainless steel tube. We fill these cylinders to 200 bar with ambient air from larger cylinders filled by NOAA/GML at Niwot Ridge, CO. We then adjust the O2 and CO2 concentrations in these cylinders and calibrate them against laboratory references traceable to both the Scripps O2 Program O2 scale, as defined on 16 March 2020, and the WMO X2007 CO2 scale. We measure each flight cylinder in the lab over a period of several weeks both before and after a field deployment to detect and account for any drift (Sect. 4.6.1).
Approximately every 50 min during flight, we measure the high- and low-span cylinders for 2.5 min each, alternating their order each time to detect any flushing issues (Fig. 5). We measure the working tank against itself for 2.5 min for an additional CO2 calibration point every other calibration cycle and we measure the long-term reference for 2.5 min as a system diagnostic every third calibration cycle. Before each calibration gas is measured, we purge it at our sample flow of 100 mL min−1 for 2.5 min. We exclude 60 s of data after every switch to a calibration gas or back to sample and average the remaining data for each calibration period. Allowing for these transitions, a two-point calibration excludes 6 min of ambient air measurement and a four-point calibration excludes 11 min.
Starting with HIPPO-3, we added a fifth cylinder of air to purge the inlet line during pre- and postflight periods to prevent ingesting aircraft exhaust and to dry inlet lines during preflight (Sects. 4.3 and 4.5). Starting with ORCAS, we also used this purge air to flush and dry inlet tubing during maintenance days. This cylinder is mounted vertically and external to the insulated cylinder box. We load dry ice in the dewar approximately 2.5 h before takeoff and then start the working tank and inlet line purge gases flowing and turn on the VUV lamp 2 h before takeoff to warm up and dry out the instrument. During the hour immediately before takeoff, we run our calibration sequence four times at 15 min intervals to flush the regulators and dry out the calibration manifold and tubing.
2.4 Data processing
Similar to the processing of shipboard data described in Stephens et al. (2003), the amplitude of the 5 s switching signal is proportional to the mole fraction of O2 in the sample gas and forms the basis of the AO2 measurement (Fig. 5). For O2, we calculate a linear fit for each paired high-span–low-span calibration cycle to apparent mole fraction (Stephens et al., 2003) and interpolate these fit parameters linearly in time to ambient air or long-term reference measurements. For CO2, we first calculate a quadratic fit to calibration cycles that also include the working tank gas and interpolate and apply these parameters to cycles with only high-span and low-span gases before calculating secondary linear fits for these cycles and interpolating to sample and long-term reference measurements. After calculating apparent mole fractions of O2 for the entire flight, we convert these to δ() and correct for dilution using the concurrent calibrated measurements of CO2 (see Eq. 4 in Stephens et al., 2003). After the preflight period, the O2 calibration as defined by the linear fit to high- and low-span cylinder measurements is very stable, with typical drift rates of less than 5 per meg per hour and less than 15 per meg over an 8–10 h flight. For Fig. 5, the standard deviation of the 13 in-flight high-span calibration gas measurements is ±2.5 per meg.
We shift our measurements in time using inlet lags empirically determined from the switches to and from inlet line purge cylinder gas before and after each flight, plus a minor additional pressure-dependent lag for the remaining portion of the inlet upstream of this valve. At our present sample flow rate and trap volume, the total inlet lag is approximately 50 s with a ±10 s smoothing window attributable to shear and turbulence induced mixing in the tubing and traps. This lag time was 10 s shorter with the small diameter trap used prior to ARISTO-2015 and varied by a similar amount, owing to differences in flow and inlet lengths across campaigns.
On specific flights and campaigns, we make additional corrections to the AO2 data as described in Sects. 4.2, 4.3, 4.4, and 4.5.
3.1 Sampler description
The Medusa gas handling system is shown in Fig. 6. Medusa consists of two identical insulated flask boxes, each of which holds 16 flasks, a control box that houses most of the pressure control system and the system computer, a valve box that holds two additional multi-position gas handling valves, two external pumps, an inlet, a purge cylinder, and a stainless steel dewar. See Table S1 in the Supplement for selected vendor and part numbers. Medusa shares the same HIMIL pylon with AO2 but samples from a 6.4 mm OD, 4.6 mm ID aft-facing electropolished stainless steel inlet tube, which is in the second position behind a fourth unused inlet tube of the same size. Air is drawn from the inlet into the system by an upstream vacuum pump modified in the same way as for AO2, while a pressure controller located immediately inside the aircraft maintains a constant pressure upstream of the pump. Similar to AO2, between the inlet and this first control valve, a manual three-way valve allows the system to sample from a purge gas cylinder containing dried natural air. In the case of Medusa, this inlet purge cylinder was added prior to ORCAS. Between the pressure controller and the pump, the sample air is filtered by a 30 µm pore by 47 mm diameter polypropylene filter in a stainless steel holder. After passing through the upstream pump, the sample air is dried in series by two 2.2 cm ID by 23 cm long electropolished stainless steel traps immersed in a similar dry ice and Fluorinert slurry as for AO2. We use 3 mm glass beads in the lower 10 cm of these traps, resulting in approximate trap volumes of 54 mL. We actively heat the inlet to the upstream trap to a temperature of 4.5 ∘C to prevent water freezing out before reaching the trap itself and obstructing flow. When the ambient dew point is greater than 4.5 ∘C, water will start to condense at this location, but as it is only several centimeters directly above the trap, we expect any formed drops to migrate into the cold trap. The dried air is then directed to the inlet of one of the 32 flasks by a series of rotary multiposition valves. A second pump and pressure controller downstream of the flask outlets controls flask pressure to approximately 1 atm. Medusa includes a single-cell CO2 H2O sensor downstream of the flasks to provide diagnostics of flask drying and mixing, and detection of potential cabin-air leaks. All Medusa tubing is electropolished 6.4 mm OD, 4.6 mm ID stainless steel or flexible ethylene copolymer lined tubing. Flexible tubing includes approximately 50 cm of flexible lines of 6.4 mm OD, 4.3 mm ID upstream and downstream of each flask; approximately 1 m lines of the same interconnecting the valve and control boxes; and 60 cm of 9.5 mm OD, 6.4 mm ID upstream of the first pump to reduce intake impedance. Medusa collects air samples into 1.5 L (30 cm long by 8 cm diameter) borosilicate glass flasks that are contained within a block of foam insulation 3 cm thick at the outside walls, with the stopcocks and tubing connections protruding from the foam. The sample air enters the flask at the exposed end and exits the flasks via a 24 cm dip tube extending into the flask with the intent to minimize thermal fractionation effects and improve flushing (see Sect. 4.1). The stopcocks use Viton o-rings lightly coated with vacuum grease to minimize permeation effects and flask breakage (Keeling et al., 1998).
Pressure sensors on the bypass line and immediately upstream of the first multi-position valve and a manual proportional valve between the valve and control boxes allow for balancing and monitoring system pressures. A manual on/off valve on the inlet line facilitates leak checking. The return lines from each flask include 10 µm stainless steel screens to protect the multi-position valves from the potential introduction of foreign debris during flask swapping. The flow rate through the system is set by the upstream and downstream pressure set points, selected from a range of predetermined options to maximize flow while maintaining approximately 1 atm in the flask and the upstream controller pressure set point below ambient. At the maximum altitudes of the GV and DC-8, we typically use an upstream set point of 146 hPa with a flow rate of approximately 1550 mL min−1 and at the lowest altitudes we typically use an upstream set point of 226 hPa, which produces a flow rate of approximately 2700 mL min−1. After switching between pressure settings, we allow 10 min for the system to stabilize before sampling when switching to the lowest flow and 5 min when switching to the highest flow.
Before each campaign, we purge the flasks in the laboratory with 5 volumes of cryogenically dried cylinder air at ambient CO2 and O2 levels and store them with an internal pressure of 1 atm. Then, before each flight, we purge them for 1 min on the high flow setting in the sampler with line purge cylinder air. Before sampling, we flush the flasks with a minimum of 5 volumes of sample air before moving to the next position. At the time of sample collection, the system temporarily switches flow to a bypass loop with matched impedance, while a rotary valve isolates the air within the sampled flask and connecting tubing. At a later time, nominally several minutes to an hour, the onboard operator manually closes the flask stopcocks to preserve the sample. We record system pressures, flows, and diagnostic CO2 and H2O at 1 Hz. After each flight we disconnect and remove the upstream trap, using normally closed quick connect fittings. During maintenance days, we exchange flasks, install a dry upstream cryotrap, and pressure test all connections for leaks.
3.2 Flask analysis
Sampled flasks are shipped to Scripps Institution of Oceanography for analysis. We try to minimize the temperature range to which flasks are exposed before analysis, but this is not always possible and hence flasks can be exposed to a variety of environments before they reach the lab. Flasks are typically analyzed within 3 months of collection, with a median storage time for all flasks of 80 d. The flask analysis includes measurements of CO2 on a non-dispersive infrared analyzer (LI-COR 6252) and of δ() and δ() on a sector-magnet mass spectrometer (Micromass IsoPrime; Keeling et al., 2004), followed by extracting CO2 for subsequent isotopologue measurements. We do not find any evidence of storage effects in δ(), δ(), or CO2 over these timescales. We measure the extracted CO2 for 13C and 18O on an Optima mass spectrometer (Guenther et al., 2001) and recapture and preserve the CO2 for eventual measurement of 14C. The single-flask 1σ precision for the δ() and CO2 measurements are ±3 per meg and ±0.15 ppm, respectively (Keeling et al., 2004). The CO2, δ() and δ() measurements are done by first withdrawing 150 mL of air over 5 min out of the flask while replacing this lost volume with a purge gas with known concentrations and artificially low CO2. The flasks are contained in an insulated box during analysis to minimize temperature fluctuations. If the flasks are to be measured subsequently for stable carbon isotopes, we correct for the dilution with purge gas by remeasuring the CO2 content after the flasks have equilibrated overnight (Kort et al., 2008; Bent, 2014). This second CO2 analysis is done on a 90 mL subsample without replacement. We extract all remaining CO2 for the 13C, 18O, and 14C measurements.
Calibration gases for the mass spectrometer are introduced from the laboratory interferometer system via a tee and we correct the Medusa flask measurements for empirically determined offsets owing to fractionation at this tee of +6.4 and +8.5 per meg for δ() and δ(), respectively. The direction of flow during analysis is in through the dip tube to be consistent with Scripps O2 Program network flasks. The flasks are mounted horizontally during analysis with half of the flasks having their dip tubes upwards and the other half rotated 180 degrees with their dip tubes downwards. We are able to detect gravitational fractionation effects during analysis with flasks with lower outlets having enhanced concentrations of the heavier species and vice versa. We apply empirical corrections for this effect of ±0.8 and ±2.4 per meg for δ() and δ(), respectively.
3.3 Data processing
Laboratory tests indicate that mixing of air in the flasks during sampling is well approximated by an e-folding time equal to the flask volume divided by the flow rate. The characteristic mixing time for the Medusa flasks is approximately 33 s at the highest flow rate and 60 s at the lowest flow rate. We estimate the combined inlet and cold trap lag time for Medusa from volume/flow to be 7 s at the highest flow setting and 13 s at the lowest flow setting. To compare the flask measurements to state parameters and other chemical measurements sampled at higher frequency, we use a weighting kernel for each flask that is based upon the measured flow rate, tubing lags, and sampling start and end times (Kort et al., 2008; Bent, 2014):
where w(t) is the weighting of any 1 s time increment t between the switch to the sampled flask and the switch to the next flask, tf, and τ is the flushing time in seconds, i.e., the flask volume divided by the mean flow during the sampling period. w(t) is scaled so that it sums to 1 for all non-missing values over a given sampling interval. These weighting kernels are reported along with the final Medusa data.
Despite careful attention in the field and lab, it is possible for flasks to experience leaks during the various stages of sampling, shipping, storage, and analysis. The analysis system at Scripps has automated checks to reject flasks with obvious anomalies in fill pressure or other parameters. In addition, we manually identify and flag flasks with CO2, δ(), and δ() measurements well out of range of expectations from the concurrent CO2 measurements made by AO2 and other instruments, δ() from AO2, and background δ() values. Of the 4004 flasks sampled in the 12 most recent campaigns, 209 were flagged during analysis at Scripps and an additional 109 were manually flagged after analysis.
All flask measurements are referenced to a hierarchy of calibration cylinders to measure them on the Scripps O2 Program O2 and CO2 scales (Keeling et al., 1998, 2007). The NCAR primary cylinders, measured both by Scripps and NOAA, allow us to establish a link between the Scripps O2 Program CO2 scale and the WMO CO2 scale in order to report the flask measurements on the WMO scale in campaign merge products and to use common scales in comparison with AO2 measurements.
Making measurements at the 10−6 relative level is challenging and the developments of AO2 and Medusa have included discovering and resolving a series of potential measurement artifacts, as described in the sections below. While we now have established practices to eliminate or minimize all of these effects, in some cases it has been necessary to develop empirical corrections for recognized systematic biases. The most significant of these effects have been those associated with inlet fractionation (Sect. 4.2) and inadequate drying of AO2 sample air (Sect. 4.5). We have also identified subtler effects associated with thermal fractionation in Medusa flasks (Sect. 4.1), regulator and tubing surface conditioning (Sect. 4.3), and systematic differences between measurements on climbs and descents (Sect. 4.4). When necessary, we calculate adjustments for bias effects as described in Sects. 4.1.1, 4.2.1, 4.3.1, 4.4.1, and 4.5.1. We discuss other potential sources of bias that have fortunately not required any adjustments in Sect. 4.6 and independent checks on measurement bias in Sect. 4.7. In all reported AO2 and Medusa data products we include both the raw and adjusted measurements to support assessment of their impacts on various conclusions and use of the unadjusted data when that is more appropriate.
4.1 Fractionation of flask samples
Thermal or pressure-driven diffusive gradients can play a role in separating Ar, O2, and N2 under various conditions (Keeling et al., 1998). This is a concern for flask sampling if temperature gradients exist at the point where molecules are committed to exiting the flask, e.g., at the dip tube tip when flowing out through the dip tube or at the stopcock if flowing in through the dip tube. Figure S4 in the Supplement shows vertical profiles of δ() measurements on Medusa flasks from all campaigns. Observed decreases in δ() in the stratosphere are consistent with estimates of gravitational diffusion (Ishidoya et al., 2008, 2013b; Bent, 2014; Birner et al., 2020; Jin et al., 2021), but we expect vertical δ() gradients in the troposphere to be constant within a few per meg (Bent, 2014). During HIPPO, the tropospheric δ() scatter about the campaign mean vertical gradient of approximately ±20 per meg (1σ) is considerably larger than the synoptic or spatial variations observed at surface stations (Keeling et al., 2004) and we attribute most of this to fractionation at the flask outlets during sampling. Figure S5 in the Supplement shows Medusa flask δ() versus APO for each campaign along with reference lines for expected slopes for thermal and pressure fractionation of flask samples at 1 atm (Keeling et al., 2004). Except in the lower stratosphere, we expect only small changes in δ() and with slopes versus APO less than 2, so we use this figure to rule out large effects. Figure S6 in the Supplement similarly shows Medusa flask δ() versus normalized Medusa–AO2 APO differences, which we expect to be a more sensitive indicator of fractionation. The sign of the tropospheric Medusa δ() versus Medusa–AO2 APO difference relationship during START-08, HIPPO, and ORCAS on the GV suggest a fractionation effect on Medusa samples. Other evidence of much larger inlet fractionation for AO2 than Medusa (Sect. 4.2) suggests this is less likely an inlet effect and more likely a flask sampling effect. Though some of the larger δ() excursions are correlated with APO in Fig. S5 in the Supplement, the Medusa–AO2 APO differences and N2O values in Fig. S6 in the Supplement suggest these are of natural stratospheric origin (Birner et al., 2020).
Although we cannot exclude a contribution from pressure-driven fractionation, because pressures are actively controlled and more consistent during sampling, we conclude that thermal gradients in the flasks are the most likely cause of this scatter. During HIPPO, δ() scatter was greater for flasks collected in the lower Medusa box closer to the GV cabin air vents. These flasks also had lower mean δ() values (Bent, 2014). If this were a thermal fractionation effect, it could result from the flask dip tube being cold in comparison to the surrounding flask air. On the DC-8 during the ATom campaigns, when the Medusa rack was inboard and away from any air conditioning vents, the δ() scatter was reduced by a factor of 2 (Figs. S4, S5, and S6 in the Supplement) and the lower box difference was eliminated. On the GV during ORCAS, we added a metal plate to the side of the rack to partially block the cold cabin air vents and the δ() scatter was reduced, but the lower box still had a low bias. Also, during START-08 and HIPPO-1 we connected half of the flasks with flow into rather than out of the dip tubes and these flasks showed greater scatter in δ(). It is also possible that the use of the Medusa inlet line purge cylinder starting with ORCAS contributed to the reduction in δ() scatter during ORCAS and ATom by reducing surface effects associated with drying of tubing early in flight. We have examined the dependency of δ() on the length of time between isolating a flask with the rotary valve and manually closing the stopcocks and do not find any relationship, suggesting fractionation is not occurring during this time.
4.1.1 Adjustments for thermal fractionation
We correct the Medusa δ() measurements for apparent thermal fractionation effects by adjusting the measured δ() values according to the expected relationship with δ() for thermal fractionation and report both original and corrected values. This correction is similar to that done in previous studies (Battle et al., 2006; Steinbach, 2010; Ishidoya et al., 2014; Bent, 2014). We use a constant reference value of 15 per meg δ() in the troposphere, which is the approximate global surface annual mean from the Scripps O2 Program network (Table S3 in the Supplement). In the stratosphere, we adjust this reference δ() value by a linear fit between δ() and detrended N2O, a proxy for age of air, with an intercept at the tropopause transition (Bent, 2014). We use N2O measurements from the Harvard Quantum Cascade Laser Spectrometer (QCLS, Santoni et al., 2014) and the NOAA PAN and Trace Hydrohalocarbon ExpeRiment (PANTHER, ATom-1 only) instruments. The corrected δ() values are then defined as
and by extension
establishing new tracers, δ()∗ and APO∗, that are largely insensitive to thermally induced fractionation of flask samples.
This approach also corrects for any thermal fractionation effects during analysis, which would be indistinguishable from those during sampling. Adjusting to a constant tropospheric vertical profile in δ() also mostly compensates for potential inlet fractionation effects as discussed in Sect. 4.2. Figure 7 shows the vertical distribution of the original δ() and corrected δ()∗ values from Medusa flasks during all campaigns. The median δ() offset from the combined tropospheric value and stratospheric N2O relationship was per meg (1σ), resulting in a median adjustment to Medusa δ() of per meg. For the three campaigns ATom 2–4, the median δ() adjustments are per meg (Table S3 in the Supplement).
This method of correcting for δ() fractionation effects using δ() ignores the real boundary-layer seasonal cycles in δ() of up to ±10 per meg amplitude and likely annual mean meridional δ() gradients on the order of 5 per meg (Keeling et al., 2004; Battle et al., 2003; Bent, 2014). Thus, scientific applications of Ar-corrected Medusa data, or of versions of AO2 data that are adjusted based upon comparison to Ar-corrected Medusa data, need to consider these additional influences. For example, Bent (2014) removed the estimated contribution of seasonal Ar variations to APO∗ from AO2 in an analysis of Southern Ocean O2 exchange and Resplandy et al. (2016) used latitudinal gradients of APO from AO2 adjusted to non-Ar-corrected Medusa data in order to constrain interhemispheric ocean heat exchange.
4.2 Inlet fractionation
Pressure gradients also have the potential to diffusively separate O2 and Ar relative to N2 at aircraft inlets (Keeling et al., 1998). Steinbach (2010) proposed a model for aircraft inlet fractionation resulting from pressure gradients perpendicular to streamlines at the inlet, whereby forward-facing inlets would preferentially sample heavier molecules at high aircraft velocity and vice versa for aft-facing inlets. We expect diffusive fractionation effects to be greater by a factor of 3 for δ() than for δ() because of the greater mass difference (Keeling et al., 1998, 2004). Aircraft inlet fractionation will likely also be dependent on other factors such as ambient pressure, ram pressure, inlet shape, inlet flow rate, inlet tubing wall thickness, and angle of attack. We assessed these effects with several different configurations of aircraft and inlet design, starting with COBRA test flights in 1999. These have included sampling at variable speeds, angles of attack, and flow rates, and switching between aft and forward inlets during stable flight conditions. These tests for COBRA using a forward-facing 9.5 mm inlet tube, during the IDEAS campaign switching between forward and aft 3.2 and 6.4 mm diameter inlet tubes, and for START-08 or HIPPO using a HIMIL, were inconclusive. However, vertical gradients in δ() (Fig. S4 in the Supplement) and in AO2–Medusa δ() differences (Fig. 8) do suggest non-negligible inlet fractionation for the HIMIL. Furthermore, when using aft and side-facing non-diffusing inlets during ORCAS and ATom-1, we observed much more dramatic fractionation effects.
One-dimensional model calculations of the balance between gravitational separation and tropospheric mixing suggest the mean vertical distribution of δ() should be constant to within 2 per meg below 9 km (Bent, 2014). Furthermore, marine boundary layer seasonal variations in δ() are relatively small at 10–20 per meg amplitude (Keeling et al., 2004) and would lead to vertical gradients of opposite sign in different seasons. We suspect the consistently observed tropospheric δ() gradients of approximately −2 per meg km−1 for the HIPPO campaigns and +2 per meg km−1 for ATom-1 shown in Fig. S4 in the Supplement resulted from inlet fractionation. The sign of the HIPPO gradients combined with the greater relative air speeds at higher altitude suggest preferential sampling of lighter N2 molecules at the aft-facing tube inside the HIMIL rather than at the forward-facing entrance to the HIMIL. The relative airspeed inside the diffusing HIMIL pylon is considerably slower than outside and the flow is laminar.
Motivated by concerns over the potential for cabin air to contaminate the sample stream through outward leaks more forward on the aircraft (Sect. 4.6.3), during ARISTO-2015 we evaluated a new fin HIMIL inlet design consisting of aft-facing 7.9 mm OD, 6.5 mm ID tubes extending 40 cm from the fuselage supported by (and with all but 5 mm contained within) a fin-shaped aerodynamic pylon. ARISTO-2015 was conducted on the NCAR C-130. To evaluate the new inlet design, we switched between the new fin and a standard diffusing type HIMIL at ambient pressures between 400 and 800 hPa and airspeeds of 110 to 160 m s−1. Comparisons of Medusa flasks taken with the two inlets showed differences of (fin minus diffusing) (standard error) and (standard error) per meg for δ() and APO, respectively. The fin minus diffusing HIMIL APO differences from AO2 were of the same sign and similar magnitude below 5 km, but 2–4 times larger from 5–8 km. Based on the sign of these differences being consistent with greater aft-facing inlet fractionation by the diffusing HIMIL, we decided to use a single fin HIMIL for both AO2 and Medusa on ORCAS and ATom-1.
However, during ORCAS, AO2 measurements between ambient pressures of 200 and 400 hPa and true air speeds >215 m s−1 showed a trough of low δ() values in comparison to Medusa flasks by up to 40 per meg at 300 hPa and occasional 1 min excursions of up to ±50 per meg. High altitude Medusa flask δ() values from ORCAS did not appear anomalous in comparison to other campaigns (Birner et al., 2020), suggesting the negative features seen in AO2 data were not realistic. This also points to a fractionation effect on a very small scale near the tip of the inlet that may have been more rapidly flushed by the greater Medusa sampling flow. The full set of ORCAS Medusa results and comparisons to AO2 were not available in time to detect and address this issue before ATom-1, so the same fin HIMIL was again employed.
During ATom-1, the fin HIMIL was located 94 cm above the DC-8 wing and 4.5 m directly behind a 24 cm diameter aerosol collection inlet (Guo et al., 2020). On ATom-1 test flights, we observed abrupt decreases of up to 200 per meg in δ() measured by AO2 at ambient pressures <300 hPa and true air speeds >208 m s−1 that were coincident with abrupt drops in pressure at our inlet of up to 140 hPa (Fig. S7 in the Supplement). The precise mechanism for these large perturbations to the flow at our inlet, whether caused by proximity to the wing or the large aerosol inlet, as well as for the impact on measured δ() at the AO2 inlet is not entirely clear. Investigators sampling at this same location on the DC-8 on previous campaigns anecdotally reported similar pressure effects and collaborators on ATom sampling 1.8 m behind the aerosol inlet and more forward above the wing observed similar pressure effects that were dependent on small changes in the distance of their inlet from the fuselage.
During the southbound Pacific flights of ATom-1, we modified our inlet several times in attempts to address the fractionation issue. An attempt to enhance turbulence at the inlet by modifying the inlet edge made the effect more variable and of opposite sign, with excursions up to +200 per meg in δ() at high altitude. Inserting a 3.2 mm OD, 2.2 mm ID tube through and extending 5 cm aft of the existing 7.9 mm inlet tube resulted in larger negative excursions of up to −300 per meg in δ() at high altitude. Bending this 3.2 mm OD extension to sample 2.5 cm outboard from the pylon and side facing was much worse; when climbing through ambient pressure of 350 hPa and sampling from this side-facing inlet, we observed abrupt fractionation of δ() by −1400 per meg and fractionation of CO2 by −2 ppm, in the expected ratio for mass-dependent fractionation (Fig. S8 in the Supplement; Keeling et al., 1998). Because we had two inlets connected by a three-way valve on all these flights, we were able to switch back to our original inlet as soon as we discovered these attempted improvements were not successful. Finally, before the northbound Atlantic portion of ATom-1, we found that by bending the trailing 3.2 mm tube 180∘ into a forward-facing inlet, we were able to eliminate the abrupt δ() depletions and had only a relatively consistent pressure-dependent offset with Medusa (Fig. 8). Despite a relative improvement in performance with this forward inlet, several times during the remainder of ATom-1 we experienced an obstructed inlet and intermittent flow after flying through liquid water clouds and thus still prefer aft-facing inlets in general.
On ATom-2, we went back to using a diffusing HIMIL, but with a modified design to further reduce the potential for cabin air leaks, and mounted the inlet such that the intake was 18 cm higher and 19 cm further from the fuselage. These changes eliminated the dramatic pressure and AO2 δ() effects seen on ATom-1. Since moving the inlet location and returning to a diffusing HIMIL for ATom 2–4, we have done further speed tests and switching between inlet sizes and orientations inside the HIMIL tube and do not observe any signs of inlet fractionation in these tests. However, we still observe negative deviations of 5–10 per meg in high altitude AO2 minus Medusa δ() differences at ambient pressures <400 hPa (Fig. 8) during these campaigns, which may still result from AO2 inlet fractionation sampling at this location on the DC-8. With AO2 we also observed oscillations of up to ±15 per meg during pitch maneuvers done for testing purposes during ATom 2–4. These pitch effects could either be related to unresolved inlet fractionation or to the dynamic inlet pressure and humidity effects described below (Sect. 4.4).
While Medusa flask samples in general show less evidence of fractionation than AO2 measurements on ORCAS and ATom-1, we do find evidence of systematic offsets in Medusa δ() across all campaigns between the various inlets and configurations used. Comparing the mean boundary layer Medusa flask δ() values from each campaign (Fig. S4 in the Supplement) shows an approximate range of 0 to 30 per meg, with the mean of the HIPPO campaigns (3.7±3.0 per meg, n=5) being lower than ATom 2–4 (12.9±2.2 per meg, n=3) and both of these being lower than ORCAS and ATom-1 using the fin HIMIL (28.0 and 29.2 per meg, respectively) (Table S3 in the Supplement).
The indication from ARISTO-2015 on the C-130 that the diffusing HIMIL fractionated more than the fin HIMIL despite the fin HIMIL clearly fractionating more on the GV and DC-8 remains unresolved. Possible explanations include the differing air speeds of these aircraft or different orientations of the inlets to the relative wind flow. A systematic study of inlet fractionation in a high-speed wind tunnel would be a valuable contribution to the airborne greenhouse and related gas measurement field. That the HIMIL design works as well as it does for δ() and δ() sampling may be attributable to its heritage as an aerosol inlet. It was designed to reduce the well-known tendency of aircraft inlets to differentially sample heavy and light aerosol particles (e.g., Belyaev and Levin, 1974), a potentially analogous effect to our observed separation of heavy versus light molecules. While a forward-facing inlet also appeared to reduce fractionation effects on the UND Citation II during COBRA, the forward inlet on the second half of ATom-1 showed modest positive fractionation and forward inlets also come with the increased risk of ingesting liquid water, insects, or other debris.
4.2.1 Adjustments and data filtering for inlet fractionation
For Medusa, an adjustment for inlet fractionation in the troposphere is mostly included in the calculation of δ()∗ described above (Sect. 4.1.1) since we can not distinguish deviations in δ() caused by thermal or pressure-gradient fractionation. The expected mass-dependent relationship between δ() and δ() for the inlet fractionation effect proposed by Steinbach (2010) is 3.0. However, the error in using the thermal 3.77 ratio for the inlet effect is only 1.5 per meg in δ() over a typical HIPPO 10 km vertical gradient. For stratospheric Medusa samples, we adjust for an estimated inlet fractionation effect based on a linear extrapolation of the tropospheric δ() fit to pressure (Bent, 2014). This adjustment is done before the fit between δ() and N2O in generating the stratospheric portion of the reference δ() profile (Sect. 4.1.1). Although the δ() vertical gradients and scatter on ATom 2–4 suggest that thermal and inlet fractionation were minor effects (Figs. S4, S5, S6 in the Supplement), we calculate Medusa δ()∗ for consistency with other campaigns. We have not implemented the δ()∗ calculation for COBRA Medusa samples.
For AO2 on ORCAS, we filter out data between ambient pressures of 200 and 400 hPa when the airspeed was greater than 215 m s−1, based on up to 40 per meg negative deviations with respect to Medusa under these conditions. This filter removed 19 % of the available data from ORCAS but removed none of the lower altitude data that are of particular interest for this Southern Ocean gas exchange study. For the first half of ATom-1, we filter a subset of the data on research flights 2, 4, and 5 collected with unsuccessful inlet modifications. For all of the first half of ATom-1 flights using the aft-facing 7.9 mm inlet, we filter data when the airspeed was greater than 208 m s−1, based on the up to 200 per meg negative deviations with respect to Medusa under these conditions. These filters removed 27 % of the available data from ATom-1. For the second northbound half of ATom-1, using the forward-facing 3.2 mm inlet, we apply flight-specific linear pressure-dependent corrections to AO2 δ() values based on differences to Medusa that are on average 0 per meg at 1000 hPa and −27 per meg at 200 hPa (Fig. 8). For this correction, we compare to Medusa δ()∗ values. The δ()∗ calculation largely addresses scatter, systematic offsets, and vertical gradients owing to thermal and pressure fractionation effects. In some cases it may be desirable to correct only for some of these effects. For example, one could apply a single offset for each campaign with a constant vertical gradient, which would largely address the inlet fractionation offsets while still leaving the original scatter and avoid contributions from real δ() variations.
4.3 AO2 regulator flushing and tubing conditioning
The two-stage cylinder pressure regulators we employ are commonly used for high-precision laboratory δ() and CO2 measurements but have elastomer seals and are recognized to require flushing before producing stable readings. The volume of air required for flushing depends on the length of time the regulators have been stagnant but can be several liters or more if it has been several days. We start cycling through calibration gases an hour or more before takeoff. The high- and low-span gases typically get purged and analyzed six times during preflight, using a total of 3 L of gas. During this warm-up period, we often observe increasing δ() and CO2 readings for the calibration gases. We speculate that these trends result from drying of either the regulator seals or tubing surfaces, causing O2 and CO2 to adsorb or absorb in place of the removed H2O. Both H2O and O2 adsorb to stainless steel, but H2O adsorbs preferentially and prevents O2 adsorption (Buckley, 1968). N2 does not adsorb to steel at ambient temperatures (Armbruster and Austin, 1944). Such an effect would produce negative biases in both gases and be most pronounced initially, when the rate of drying was greatest, and decrease as the drying proceeded and slowed. Negative biases for calibration gases would result in positive biases for ambient air measurements and thus this effect could lead to AO2 δ() biases that trended downwards during flight. Conversely, if the AO2 trap were inadequately drying sample air, the tubing downstream of the calibration-sample selection valve could be wetting while measuring ambient air and drying while measuring calibration gas. This might bias the ambient air measurements high for δ() with more complex time-of-flight dependencies, depending on how dry this tubing was initially. A feature of the AO2–Medusa comparisons during HIPPO was δ() differences that trended downwards during flight (Fig. S9 in the Supplement), with magnitudes ranging from −2 to −5 per meg h−1. During HIPPO, we ran calibration gases starting 45 min instead of 1 h before takeoff and our trap swapping procedures may have allowed wet ambient air into the system on maintenance days. Furthermore, our first and second-stage traps were not drying efficiently (see Sect. 4.5). This time-of-flight dependency has been improved since ORCAS (Fig. S9 in the Supplement), with dry purge gas flushing of the inlet system on maintenance days, more preflight regulator flushing, trap swapping procedures that prevent ambient air introduction, and better drying efficiency. Prior to ORCAS, we only used calibration gas measurements after takeoff. Notably, the time-of-flight AO2 δ() dependencies during HIPPO, or during other campaigns, do not appear to be related to cylinder drift. We measure and log temperature at six points inside the AO2 cylinder box and do not find correlations across flights with trends in either temperature or temperature gradients in the box.
4.3.1 Adjustments for time-of-flight-dependent biases
Because the Medusa flow rate is 15–27 times greater than for AO2 and we find no other evidence in Medusa flask measurements for time-of-flight dependencies, we attribute time-of-flight dependencies in the AO2–Medusa difference to biases in AO2 and a combination of the calibration cylinder regulator and line drying, and sample line wetting described above. Therefore, we adjust the AO2 δ() data using flight-specific linear time-dependent fits to the AO2–Medusa differences, as summarized for campaign means in Fig. S9 in the Supplement. These fits are made to differences between AO2 δ() and Medusa δ()∗. The mean impact of these linear time-of-flight adjustments for all flights is per meg h−1 (1σ). For ATom 2–4 the mean time-of-flight adjustment is per meg h−1. These adjustments remove both the apparent trend in AO2 data over a flight and also the mean difference between AO2 and Medusa for reasons described below (Sect. 4.5).
4.4 AO2 differences between ascent and descent
There are large and dynamic differences in inlet and instrument conditions when the plane is ascending versus when it is descending. These differences include: the angle of attack at the inlet; the relative air speed at the inlet; the sign of change of inlet pressure, temperature, and humidity; the angle of the instrument with respect to gravity; and the sign of change in cabin pressure. To assess the potential for bias between ascent and descent, it is useful to compare measurements from adjacent profiles.
During ACME-07 and the first half of START-08, the AO2 inlet included long sections of non-pressure-controlled 6.4 mm OD, 4.3 mm ID ethylene copolymer lined tubing (2 and 7 m, respectively). We found that as a result, the AO2 measurements were biased in proportion to the rate of change of the pressure in this tubing, with δ() biased low during descents and high during ascents by up to ±75 per meg during ACME-07 and ±200 per meg during the first half of START-08. We attribute this effect to the preferential absorption and desorption of either O2 relative to N2 or H2O relative to O2 into and out of the ethylene copolymer lining. Between the first and second phases of START-08 (before Research Flight 13) we replaced this tubing with 2.2 mm ID stainless steel tubing and moved the inlet pressure control valve from the AO2 rack to immediately inside the aircraft, which eliminated these large pressure-dependent biases. Medusa also sampled from 6.4 mm OD, 4.3 mm ID ethylene copolymer lined tubing during START-08, but with 15–27 times the flow rate of AO2 and we did not find any clear evidence of Medusa sampling biases from inlet pressure changes. To further reduce the likelihood of surface interactions, for the AO2 inlet line we switched to electropolished 2.2 mm ID stainless steel tubing before HIPPO-1 and electropolished Sulfinert treated 2.2 mm ID stainless steel tubing before HIPPO-4. For the Medusa inlet line we switched to 4.6 mm ID electropolished stainless steel tubing and moved the inlet pressure controller to immediately inside the fuselage before HIPPO-2.
Despite greatly improved performance after moving the AO2 pressure control point upstream and switching to stainless steel tubing, followed by further reductions in surface roughness, we still see small differences between δ() on ascents versus descents for AO2. As shown in Fig. S10 in the Supplement for HIPPO, ORCAS, and ATom, the magnitude of these differences are generally greatest at altitude and can be as large as −10 per meg, on average, for the first half of ATom-1 and for ATom-2. Comparisons to Medusa and with level legs at altitude suggest these biases were symmetric, with the end of the ascents biased low by 5 per meg and the start of the descents biased high by 5 per meg. HIPPO-1 showed ascent minus descent differences of opposite sign, with a peak of 5 per meg (±2.5 per meg) at mid-altitudes (Fig. S10 in the Supplement). HIPPO-2 through HIPPO-5 had campaign average ascent minus descent differences close to zero but a tendency towards negative differences at altitude consistent in sign with later campaigns. ORCAS ascents and descents were also similar at pressures greater than 600 hPa but diverged by up to 7 per meg between 400 and 600 hPa. The first and second halves of ATom-1 and ATom-2 showed the largest ascent minus descent differences, which peaked between 650 and 450 hPa at −9 to −14 per meg. Finally, the ascent minus descent differences on ATom-3 and 4 were very consistent with a peak at max altitude of −5 per meg.
Calibration gas measurements do not show this behavior so we can rule out cabin pressure or pitch effects on the AO2 instrument. Of the external changing parameters, those with greater ascent versus descent differences at altitude include angle of attack and the relative rate of change in water vapor concentration, pointing to either inlet fractionation or surface effects. Also, the effect appears to vary from flight to flight and within a flight, which could result from variable flight conditions or tubing surface conditions. However, the ascent minus descent differences in angle of attack on ATom-4 were a factor of 2 greater than on previous campaigns, with no noticeable difference on the δ() sensitivity. Finally, the effect did not reverse sign between the aft and forward inlets used in ATom-1, which might be expected for an inlet fractionation effect.
The ascent minus descent differences since HIPPO-1 are opposite in sign to the earlier ethylene copolymer lined tubing effect but are consistent in sign with the slower tubing and regulator drying effect described above (Sect. 4.3). We suspect that a similar competition between H2O and O2 on tubing surfaces is responsible (Buckley, 1968). In this scenario, on ascent as pressure and humidity decrease in the AO2 inlet upstream of the control valve and humidity decreases in the inlet and tubing upstream of the cryotrap, there would be less competition for O2 adsorption leading to a net loss of O2 from the sample air to the tubing surfaces. Conversely, as humidity and pressure increase on descent, more H2O would adsorb leading to a net desorption of O2 from the tubing surfaces to the sample air. The effect is largest at altitude despite the absolute rate of pressure and humidity changes being largest at low altitude, but this could be explained by a saturation of H2O adsorption at relatively low humidities. The colder inlet temperatures at altitude could also play a role.
4.4.1 Adjustments for ascent versus descent differences
For ACME-07 and the first half of START-08, we adjusted the AO2 data using linear fits between APO and a smoothed representation of the time rate of change in pressure at the inlet, optimized by adjusting the smoothing window. This adjustment is zero when the inlet pressure is not changing and at other times is negative or positive with a magnitude determined by the optimized fit. Although the empirical correlations for these adjustments are reasonably good (r2 values from 0.5 to 0.9), we suggest caution in detailed interpretations of the individual AO2 δ() profiles from these flights, as significant biases may remain. However, by either looking separately at results from ascents versus descents or averaging data from ascents and descents together, the impact of these biases on particular results can be identified or largely removed.
For the smaller effect seen on more recent campaigns (HIPPO, ORCAS, and ATom), we derive an empirical correction based on comparisons between subsequent profiles. For each profile, we subtract a combination of the prior and following profile, interpolating by pressure, then fit these differences with a linear relationship to pressure between 400 hPa and the surface, excluding profiles with >40 % missing data over this range. We then compute a four-profile running mean of the bias versus pressure slopes to allow for trends within a flight while avoiding real atmospheric differences on a single profile from having too much influence. Finally, we interpolate these smoothed slopes to all times in the flight and use them to calculate a correction to the flight data depending on whether the plane was climbing or descending and at what pressure altitude. For flights with few profiles, we used the average correction of the prior and following flight. While the most noticeable impact of this correction is better visualization of upper-tropospheric patterns in δ() in cross-section plots (e.g., Fig. 11), it also improves results based on vertical gradients in individual profiles. Analyses that average multiple profiles together, such as the mean vertical gradient over a flight or region, are largely unaffected, as the corrections are balanced from one profile to the next.
4.5 AO2 water and hydrocarbon effects
During the HIPPO campaigns, we used simple 40 cm long 6.4 mm OD, 4.6 mm ID u-shaped tubes for the second-stage sample air and working tank cryotraps and a narrower 9.5 mm ID for the first-stage sample air cryotrap. Over the course of the five HIPPO campaigns, the differences between AO2 and Medusa δ() measurements became steadily more negative, reaching a minimum of approximately −80 per meg during HIPPO-4 and HIPPO-5 (Fig. 8 and Fig. S9 in the Supplement), despite significant efforts between each campaign to diagnose and address these offsets. We also observed differences in the slope of subsequent working tank and span gas jogs during these campaigns on the order of 30 per meg s−1 (Fig. 3). Laboratory tests after HIPPO-5 finally confirmed that the cryotraps were not adequately drying sample gas before it entered the VUV cell. Although measurements of ppm-level H2O at our sample flow rate are challenging, our best estimate using a laboratory dew-point hygrometer is that during HIPPO-5 the second-stage trap outlet had on the order of 15 ppm of H2O when sampling outside air.
We can exclude a direct VUV absorption effect from this water because the biases were in the opposite direction from that expected for additional absorption. Less water would likely have exited the traps during calibration periods but trap and tubing surfaces would have contributed water to the dry calibration gas, resulting in transient responses in H2O over calibration sequences and we did observe transient δ() changes for several minutes after each calibration-sample and sample-calibration switch on these campaigns. Alternate wetting and drying of surfaces downstream of the calibration-sample selection manifold might be expected to lead to O2 adsorption and desorption in the other direction (Sect. 4.3); however, this also would have resulted in AO2 biases with the opposite sign of those we observed. Nonetheless, replacing the u-tube traps with longer and smaller diameter coiled traps and increasing the diameter of the first-stage trap eliminated the transients and greatly reduced the AO2–Medusa differences in ARISTO-2015 and subsequent campaigns (Fig. 8 and Fig. S9 in the Supplement), despite not having a good explanation for the cause of the bias at the time. These changes also eliminated the working tank versus span jog slope differences.
Then, between the ATom-3 and ATom-4 campaigns, two discoveries led us to hypothesize that the biases during HIPPO were likely a result of photochemical dissociation of H2O in the detector cell followed by radical interactions with optical surfaces. First, when using AO2 working tank gas from a commercial vendor that been scrubbed of all hydrocarbons compared to compressed natural sample air, the differences in the slopes of subsequent working tank and span jogs was around 20 per meg s−1 in the same direction as with wet sample gas, as opposed to zero when both gases had ambient CH4 concentrations. The second discovery came while conducting tests in the laboratory, sampling air from large polyethylene barrels used as integrating volumes. Switching to sampling barrel air led to large increases in the working tank versus span jog slope differences. Then, after switching back to sampling inlet line purge cylinder air, the measurements were biased low and both the jog slope differences and the biases persisted for at least 2 h. Either replacing the sample trap or warming it with a heat gun under vacuum for several minutes and then rechilling it eliminated the problem.
Notably, the problem of inadequate drying on HIPPO, the difference between gas with and without hydrocarbons, and the polyethylene barrel effect all manifested themselves similarly in terms of the direction of working tank versus span jog slope differences and δ() biases. Specifically, when water or excess hydrocarbons are present in the span gas relative to working tank gas, the slope of the VUV signal during span jogs is positive, indicating decreasing O2 or increasing light. The signal slope is opposite during working tank jogs and the measured δ() values for the span gas are biased low. VUV absorption by H2O or CH4 is too weak (Stephens, 1999) and of the wrong sign to explain these effects. Also, the photochemical production of another absorbing species can not explain the trends over several seconds as the residence time of the air in the sample cell is on the order of 0.02 s. However, photochemical processing of H2O and hydrocarbons in the intense VUV light may result in a “cleaning” effect on the lamp and detector optics via surface reactions with OH or other radicals. Such an effect would be consistent with the increasing signal over several seconds during span jogs leading to the appearance of less O2 in the cell. We now avoid using commercially sourced gases lacking ambient CH4. In the stratosphere, ambient CH4 depletion might also lead to biases in AO2 measurements. For the flights presented here, CH4 in the lower stratosphere was only depleted by 10 %–20 %, but this could be a greater concern deeper in the stratosphere and warrants further laboratory investigation. Also, since HIPPO, we have ensured that the traps are drying the air sufficiently and have adjusted our procedures to avoid introducing wet ambient air into the system when swapping traps between flights. We find that a saturation vapor concentration of less than 1.5 ppm appears sufficient to avoid anomalous square wave slopes, and also note that this concentration would limit potential H2O dilution effects to less than 2 per meg. Thus, for VUV measurements we recommend drying to 1.5 ppm H2O or better.
4.5.1 Adjustments for inadequate drying of air
For HIPPO 1–5, we made a constant adjustment to AO2 δ() for each flight based on the comparison to Medusa (Fig. 8 and Fig. S9 in the Supplement) as listed in Table S3 in the Supplement. These adjustments are in combination with the time-of-flight slope adjustments (Sect. 4.3.1) and thus have the effect of adjusting AO2 by the average offset for each flight. These comparisons are made to Medusa δ()∗.
4.6 Additional measurement considerations
In addition to the challenges described above, in this section we discuss several other aspects of high-precision airborne O2 measurements that require careful attention.
4.6.1 Propagation of AO2 calibration scales
A critical requirement for the AO2 measurements is the propagation of primary calibration scales for δ() from Scripps and for CO2 from both Scripps and NOAA/GML. Our laboratory primary cylinder suite consists of six 50 L aluminum cylinders originally filled, adjusted, and calibrated at Scripps in 2005 and calibrated at NOAA in 2006. These cylinders have been returned to Scripps and NOAA every 5 years since for reanalysis to maintain our links to the Scripps O2 Program O2 and CO2 scales and the WMO CO2 scale. Our internal laboratory scales are then defined by linear interpolation of these external measurements. Over 15 years our primaries have varied by <5 per meg δ() and <0.05 ppm CO2. We propagate these scales to secondary cylinders annually and then to our flight cylinders before and after each campaign; we show these results in Fig. S11 in the Supplement.
Stability for δ() and CO2 is often an issue in larger high-pressure cylinders (Langenfelds, 2002; Keeling et al., 2007) and even more of a concern for smaller cylinders, which could amplify fractionation effects. We initially valved our cylinders using Viton o-rings but found drifts on the order of −100 per meg over 1 year (Fig. S11 in the Supplement). Starting with HIPPO-2, we used silver-coated c-rings for all but our working tank and inlet line purge cylinders and for all cylinders after HIPPO-5. Cylinders with these silver seals are generally very stable for both δ() and CO2, with positive δ() drifts less than 5 per meg over 1 year but with a few outliers showing drifts up to +60 per meg in the first 4 months (Fig. S11 in the Supplement). The cause of these more recent outliers is unclear but may be related to inadequate drying or a faulty regulator. We now measure the humidity in each cylinder and our filling procedures routinely achieve humidities of less than 1 ppm H2O. We select our flight span and long-term reference cylinders from those showing the best stability in the lab. For all campaigns, we measure the field cylinders for several weeks in the lab immediately before and after the deployment and assume a linear drift in time between the average prior and post campaign laboratory determinations.
4.6.2 Cabin temperature and pressure effects
It is also possible for temperature variations to cause separation of gases within a cylinder and thus affect δ() values in the gas exiting the head valve (Keeling et al., 2004, 2007). We mount our cylinders horizontally in an insulated enclosure in an attempt to minimize these effects. Also, we use dip tubes to withdraw air from the middle of the cylinder, following practices established for laboratory cylinders by Keeling et al. (2007). However, the temperature changes on research aircraft can be very large and it is not practical to isolate the cylinders from more than short-term fluctuations. To support detection and diagnosis of temperature effects on our cylinders, we measure temperature at six locations within the AO2 cylinder box, distributed to detect temperature gradients in three dimensions. We have compared gradients and trends in these temperatures to the calibration gas measurements and to differences between AO2 and Medusa flask measurements for all campaigns. We are unable to identify any relationships attributable to thermally induced fractionation of the delivered cylinder air.
We also measure temperatures at various locations in the AO2 instrument and pump boxes as well as cabin pressure. The voltage output of the AO2 detector is tightly linked to the temperature of the lamp and detector housing, likely reflecting changes in lamp output, cell pressure, cell air density, and amplifier gain. However the effect of the temperature-dependent trends in raw detector voltage are generally imperceptible on the amplitude of the square wave in voltage from switching between span and working tank air.
To monitor potential cabin pressure effects, we measure the ambient pressure inside the AO2 pump box and look for correlations with reference cylinder measurements and other system diagnostics. For ORCAS, we moved the sapphire window in the AO2 detector to the lamp side rather than detector side of the cell, which resulted in the lamp being secured only by a Teflon clamp rather than also being pulled flush to the cell by the low cell pressure. As a result, when cabin pressure changed in a climb or descent, the raw detector voltage smoothly oscillated by up to 0.02 V with a period of approximately 2 min, possibly related to resonant heating and cooling of the Teflon clamp or magnet wire coiled around the lamp resulting in subtle movements in the lamp itself. These oscillations resulted in increased noise in the square wave signal, which we were able to remove by applying a loess fit (Cleveland and Devlin, 1988) to the working tank measurements, rather than straight interpolation, in calculating the amplitude of the square wave. We eliminated these oscillations before ATom-2 by returning the sapphire window to the detector side of the cell.
4.6.3 Cabin air leaks
The combination of human respiration, dry ice sublimation, and liquid nitrogen evaporation within the typical research aircraft cabin can lead to highly perturbed CO2 concentrations and ratios in the cabin air. On several flights on both the GV and DC-8, we used AO2 to measure CO2 and δ() of cabin air and saw typical values enhanced by 250 ppm CO2 and depleted by 500 per meg δ(). Even small contributions of cabin air to our sample gas, either through direct leaks in our inlet plumbing or via fuselage vents or leaks upstream of our inlet, could potentially affect our measurements (e.g., Vay et al., 2003). In addition, a leak from the cabin to the sample stream through a small orifice could further deplete δ() by contributing air fractionated through the process of Knudsen diffusion (Keeling et al., 1998).
During maintenance days and in preflight, we routinely conduct vacuum and pressure leak checks on all AO2 and Medusa plumbing to carefully monitor for and detect any system leaks. In addition, several times per flight while at high altitude, we bathe our low pressure inlet fittings with pure CO2 from a bottle of dry ice and monitor the AO2 and Medusa CO2 signals for any spikes that would indicate leaks. These procedures have proven sufficient for eliminating leaks in the instruments and the portion of the sample tubing which is inside the cabin.
However, pressurized aircraft are not airtight and, for example, potential sources of cabin air upstream of our inlet on the GV include the cabin dump valve, a separate cockpit air conditioning vent both on the lower right of the forward fuselage, a large gasket door seal on the forward left side, the nose compartment, and leaks from other instrument inlets. The DC-8 has similar concerns, including a forward lavatory vent on the left side of the fuselage. On any research aircraft, atmospheric sampling inlets must extend beyond the boundary layer of the fuselage to sample uncontaminated air. For the GV and the DC-8 the aircraft boundary layer grows from the front of the aircraft at approximately 1 and 1.2 cm per m, resulting in predicted depths of 23.5 and 11.0 cm for our AO2 inlet locations on HIPPO and ATom, respectively. During test flights on the GV during the 2005 Progressive Science campaign, pressure was measured at several locations and a range of distances from the fuselage to empirically determine the boundary layer depth. These tests indicated that the aircraft boundary layer extended to approximately 21 cm at the locations of the AO2 and Medusa inlets during HIPPO and ORCAS. Since our inlet extended 30.5 cm out from the aircraft, we expect this length was sufficient to sample undisturbed air.
Nonetheless, the growing negative AO2–Medusa δ() offsets we found over the course of HIPPO (see Sect. 4.5, Fig. 8, and Fig.S̃9 and Table S3 in the Supplement), led us to vigorously investigate potential cabin air leaks. In particular, we were concerned about potential leaks in the HIMIL itself. These might occur through the many o-rings, gaskets, or screw holes that allow for heating the inlet for other instrument applications and passage of the tubes through the pylon or through sheathed tubing used by another instrument sharing a HIMIL, as was the case for AO2 in HIPPO. However, laboratory tests on the HIMIL and further tests with pure CO2 in flight failed to confirm our suspicions, and we also did not find correlations between the offsets and cabin pressure, ambient pressure, or their difference that might suggest a leak. As described in Sect. 4.5, subsequent laboratory tests confirmed that inadequate drying and not cabin air leaks was the primarily cause.
4.6.4 AO2 pressure and flow control
Many of the challenges described above, including inlet fractionation and regulator and tubing conditioning, could be mitigated by higher flow rates. However, we have not been able to increase the flow rate without also increasing the short-term instrument noise. In laboratory tests, increasing the flow rate by increasing the upstream reference volume pressure or swapping in a larger sapphire orifice has led to 2–4 times greater noise for the 5 s measurement and typically a smaller uncorrelated increase in the noise of the pressure signal from the downstream differential pressure transducer. Also, for several flights, after increasing the flow rate slightly while on the ground, once in flight the detector signal varied rapidly by the equivalent of 100 per meg before stabilizing after flow was reduced, suggesting an instability in the pressure control. Prior to HIPPO-1, we used a 5 cm by 0.25 mm ID capillary in place of the sapphire orifice, and before ATom-3, we removed a 10 µm by 6.4 mm diameter screen that was acting as a damper between the cell and the downstream pressure transducer. Neither of these changes dramatically changed the measurement precision or its sensitivity to increased flow. Pressure and flow control at the 10−6 relative level depends on many factors, including flow restrictions, pressure transducers, fast-response proportional valves, and the tuning of the feedback control circuitry. Ongoing laboratory work will continue to explore improved pressure and flow control at higher flow rates.
4.6.5 AO2 motion sensitivity
Sensitivity of the O2 measurement to motion can arise from movement of the lamp and ballast coils, movement of components within the extended RF field of the lamp, and from acceleration effects on the proportional solenoid valves used for pressure control. We secure the lamp coils with a Teflon clamp and glue between coils, which appears to eliminate this potential source of noise. We also correct for measured deviations in pressure control, which can be large during turbulence, and this correction is effective at reducing the solenoid valve contribution. However, RF coupling has been more challenging to address.
During the first test flights of the VUV sensor during IDEAS-1 in 2002, we discovered the RF field was escaping from the lamp box and movement of the mounting plate for the lamp and detector box relative to the rest of the rack led to large motion effects. This was largely fixed by improving the shielding of the lamp box. However, throughout HIPPO a small amount of motion sensitivity persisted, with short-term noise during a typical boundary-layer leg increasing by a factor of 2–3 and more so under moderate turbulence. Then during ARISTO-2015, after we found that adding vibration isolators to the rack made the motion sensitivity worse, we discovered that by better securing the wires and cables inside the lamp box, we were able to eliminate most of the remaining motion sensitivity. As flown during ORCAS and the ATom campaigns, short-term noise during boundary-layer legs was typically indistinguishable from other portions of the flight but occasionally in moderate turbulence it was approximately a factor of 2 greater.
4.7 Independent performance checks
To assess the propagation of laboratory calibrations to the in situ AO2 measurements and other aspects of the instrument stability, we measure the long-term surveillance cylinder multiple times during preflight and approximately every 150 min during flight. Figure S12 in the Supplement shows δ() differences between these measurements and our laboratory determinations for these cylinders. The campaign mean offsets are shown in each panel and in Table S3 in the Supplement. Across all campaigns, these differences have a mean of per meg (1σ, n=599). From ARISTO-2015 on, the mean offset is per meg (1σ, n=349) and for just ATom-3 and 4 the offset is per meg (1σ, n=157). However, during HIPPO, the long-term surveillance measurements showed systematic biases of up to ±10 per meg and −20 per meg for the first half of HIPPO-2.
Negative biases on HIPPO-4 and 5, and on the first half of HIPPO-2, can be attributed to transient slopes during the long-term surveillance measurement itself, owing to inadequate flushing of the long-term surveillance cylinder regulator and lines before measurement. Conversely, positive biases on the second half of HIPPO-2 and on HIPPO-3 likely result from a greater impact of inadequate flushing of the high- and low-span cylinders, which precede the long-term surveillance cylinder measurement. These offsets are generally smaller than those we attribute to inadequate regulator flushing and tubing drying during the HIPPO campaigns (Sect. 4.3 and 4.5) and are accounted for by the adjustments described in Sects. 4.3.1 and 4.5.1. Overall, these long-term surveillance results demonstrate that errors in our propagation of calibration scales from the laboratory to field measurements are now a relatively small component of overall AO2 δ() measurement uncertainty.
We have assessed the magnitude of any overall biases in Medusa by comparing our airborne observations from the HIPPO, ORCAS, and ATom campaigns to biweekly station flask samples collected and analyzed by the Scripps O2 Program (Keeling and Manning, 2014). We use samples from all 10 stations in the Scripps O2 Program network. Because we only occasionally flew close to stations, and only rarely on the actual day of a flask collection, we must use relatively loose coincidence criteria. We select any Medusa flasks that occur within 1000 km horizontally and 1000 m vertically of a sampling station and within 10 d of a station flask collection. Next we interpolate the station measurements in time to match the date and time when the aircraft was nearest. We then take the median of the selected Medusa measurements for each match and subtract the time-interpolated station measurements. The average results of these comparisons are tabulated for all campaigns in Table S3 in the Supplement. On the basis of APO∗, the mean offset between Medusa and station measurements for all campaigns was 0.2±8.2 per meg (1σ, n=86). This comparison is to measurements on station flasks using the same mass spectrometer as for Medusa flasks. Individual campaign means vary from −4.9 to 5.3 per meg (average n=9) with a standard deviation of ±3.3 per meg (Table S3 in the Supplement). This range in campaign means is as expected for random sampling of the full population and suggests a relatively consistent relationship over time.
With confidence in the overall quality of the Medusa flask measurements, we then evaluate AO2 measurements by comparison to coincident Medusa flasks. Figures 8 and S9 in the Supplement show these differences and Sect. 4 discusses adjustments made to account for the large offsets primarily seen during the HIPPO campaigns. Since resolving the inadequate drying issues present in HIPPO, the six-campaign mean unadjusted AO2–Medusa offset is (1σ, n=1361). Averaged over individual campaigns, the six campaign mean offsets since HIPPO range from −4.5 to 5.2 per meg (Table S3 in the Supplement).
To highlight the performance of AO2 and Medusa and their scientific potential, we present a limited set of examples from past campaigns. These include several vertical profiles, a collection of source-specific correlations between δ() and CO2, and global altitude–latitude cross sections for CO2, δ(), and APO.
5.1 Vertical profiles
Figure 9a and b shows a vertical profile measured by AO2 over an agriculturally dominated region in early summer during START-08. As indicated by potential temperature, there was a well-mixed boundary layer to approximately 2 km and the tropopause was at approximately 12 km. On this late-afternoon profile, the boundary layer showed an approximate decrease of 6 ppm CO2 and a well-correlated increase of approximately 30 per meg δ() relative to air immediately aloft. The average molar ratio for the variations below 4 km is close to 1 mole O2 : mole CO2 (Fig. 10d) and the APO profile is nearly flat (Fig. 9b), indicating a dominant influence of regional terrestrial photosynthesis in producing these signals (e.g., Stephens et al., 2007a; Battle et al., 2019). The overall gradients through the troposphere suggest the seasonal late-spring Northern Hemisphere CO2 maxima and δ() minima were eroding more slowly in the upper than lower troposphere. The jump to lower CO2 and greater δ() values in the lower stratosphere on this profile results from the relative isolation of this air from both the previous winter's Northern Hemisphere seasonal signals and longer term global trends.
Figure 9c and d shows a vertical profile measured by AO2 and Medusa over the Southern Ocean in early spring during ATom-3. In this case, the CO2 profile is nearly flat but the δ() and APO profiles show a strong depletion in the lower 3 km and greater negative excursions within 500 m of the ocean. These signals are consistent with uptake of O2 by the ocean as a result of ventilation of O2-depleted waters and cooling of surface waters over winter. The stratospheric δ() deviation for this profile is the same sign as that in Fig. 9a, reflecting both the trend and the tropospheric winter influence. The stratospheric CO2 signal is more muted, owing to the small CO2 seasonal cycle at high southern latitudes.
5.2 O2 versus CO2 correlations
In addition to natural terrestrial and ocean exchange signals, AO2 and Medusa have often sampled polluted air. Because various fossil-fuel types and terrestrial and oceanic exchanges have distinct O2:CO2 signatures (Keeling, 1988; Steinbach et al., 2011), the molar ratios observed for these events can provide a means of source identification. Figure 10 shows examples of three such events along with the agriculturally influenced profile presented in Fig. 9a. The combustion of fossil fuel exchanges more O2 per molecule of CO2 than terrestrial photosynthesis because fossil carbon is more reduced. The ratios observed for a natural gas plant, a city, and a coal plant shown in Fig. 10 are close to those expected for methane, liquid fuels, and coal (−1.89, −1.34, −1.16 observed versus −2.00, −1.43, and −1.15 expected, respectively; Keeling, 1988).
5.3 Altitude–latitude cross sections
Each month-long HIPPO and ATom campaign included flights north of Alaska to around 87∘ N, transecting the Pacific southwards to New Zealand, south to around 67∘ S, and returning north again either via the Pacific (HIPPO) or Atlantic (ATom) basin (Fig. S1 in the Supplement). During each HIPPO and ATom flight, the aircraft profiled continuously between a near-surface altitude of 150–300 m and a maximum altitude of 9–14 km. Figure 11 shows interpolated AO2 altitude–latitude cross sections overlain with Medusa observations for the southbound Pacific basin portion of ATom-4 in April–May of 2018. The CO2 cross section shows concentrations elevated by over 5 ppm throughout the entire northern extratropical troposphere, with enhancements as high as 8 ppm north of 60∘ N. This reflects the seasonal accumulation of northern extratropical CO2 emissions over winter from a combination of net terrestrial respiration and fossil fuel burning. The color scales in Fig. 11 are set to be equivalent on a molar basis and show larger northern extratropical depletions in O2 as a result of the greater than 1 oxidation ratio for fossil fuel burning and the additional ocean uptake of O2 resulting from both ventilation of northern ocean waters with accumulated respiration signatures and the cooling of surface waters.
Conversely, at southern high latitudes, ocean heating and net marine productivity lead to O2 emissions over the austral summer, which we observed as a strong accumulated O2 signal throughout the southern extratropical tropopause. Given the relative lack of land plants and industrial emissions at high southern latitudes, the observed Southern Hemisphere CO2 field was comparatively flat. APO effectively masks out terrestrial influences and suggests that approximately half of the interhemispheric gradient in δ() at this time of year is a result of air–sea fluxes. These flights also intercepted stratospheric air poleward of 60∘ N and less than 300 hPa, and in an isolated intrusion at 33∘ N and 300 hPa, with correspondingly high O3 and other stratospheric tracers (not shown).
All five HIPPO and four ATom campaigns with the exception of HIPPO-1 returned to the Arctic at the end of their northbound transects. Thus, we have collected 17 complete global altitude–latitude transects such as those shown in Fig. 11. Cross-section plots for all HIPPO, ORCAS, and ATom campaigns are presented in Figs. S13, S14, and S15 in the Supplement.
Over the past two decades, we have developed and improved airborne systems for in situ and flask-based measurements of atmospheric O2 and have deployed these on a series of 15 regional and global research campaigns. Here we have described the AO2 instrument and Medusa flask sampler to provide support for more detailed scientific studies using their collected data and to aid other investigators who may wish to undertake similar measurements. With this latter goal in mind, we have also detailed the many methodological challenges we have faced in making these high-precision measurements and how we have overcome them. Having two independent systems, with the high temporal resolution in situ measurements complemented by flasks sampled at much higher flow rates and analyzed in a controlled laboratory environment, has been critical for detecting and resolving problems in either system. Also, having measurements of δ() on the Medusa flasks has been invaluable for ruling out or detecting and correcting for potential fractionation effects.
The primary sources of potential biases in airborne measurements of, or sampling for, atmospheric O2 concentrations include (1) fractionation of O2 relative to N2 at aircraft inlets (Sect. 4.2) or flask outlets (Sect. 4.1) owing to pressure or temperature driven diffusion, respectively; (2) surface adsorption and desorption effects resulting from drying out of regulators and tubing (Sect. 4.3); or (3) changes in the pressure and humidity ramping of inlet tubing and components on ascent versus descent (Sect. 4.4). These effects may also be important for airborne measurements of CO2 and other gases but at a smaller absolute level. An additional O2 measurement concern unique to the use of intense VUV radiation in the AO2 detector appears to be the presence of varying concentrations of residual water vapor or hydrocarbons potentially leading to photochemically induced changes in optical window transmission (Sect. 4.5). As described above, we have taken measures to mitigate these potential biases and, when necessary, filter or empirically correct for them such that they do not adversely influence scientific interpretations of the measurements.
For AO2, we report a δ() precision of ±2.5–4 per meg in 5 s for sample air in flight, depending on aircraft motion, and ±1.25 per meg in 5 s for calibration gas on the ground (Sect. 2.2). Comparisons between Medusa and ground stations, and between AO2 and Medusa, show no statistically significant bias for Medusa relative to laboratory scales averaged over all global campaigns and no statistically significant bias for AO2 averaged over the six most recent campaigns (Sect. 4.7). For all global Medusa campaigns and the most recent six AO2 campaigns, campaign-mean offsets from stations and between AO2 and Medusa are all within 5 per meg. For both AO2 and Medusa, the quality of the measurements have improved steadily over time as we have learned from past experiences and modified the instruments or procedures.
We will continue our efforts to improve AO2 and Medusa along several paths. Most helpful for AO2 would be increasing the sample flow rate by a factor of 2 or more, which we anticipate would reduce inlet fractionation, surface effects, and noise from thermal gradients in the inlet cryotrap. However, this will require further development to maintain the high degree of pressure control and adequate drying at these higher flow rates, and the desire for reduced biases would need to be balanced against the drawbacks of a higher flow rate, such as more rapid filling of cryotraps and faster consumption of calibration gases. It may be possible to split the flow to allow for higher inlet flows and lower detector flows, but this would require research on how to eliminate or maintain constant fractionation at the split. The noise contribution from the inlet cryotrap might also be ameliorated with a smaller trap volume, improved flow and pressure control, or valves producing less of a transient flow pulse. It may also be possible to improve AO2 sample air drying by moving the first-stage cryotrap to immediately downstream of the inlet control valve or increasing the pressure at the second-stage trap, though these steps will also require development work to maintain fine pressure and flow control. Further research is also warranted on inlet fractionation using high-speed wind tunnel studies and tubing materials or surface treatments to minimize adsorption effects. For Medusa, an alternative design that packaged sets of flasks with automated distribution valves and motorized stopcocks could greatly reduce the required labor associated with swapping and leak testing flasks in the field, albeit at greater cost.
While airborne measurements of atmospheric O2 come with many challenges, the potential for new scientific insights based on these measurements justifies meeting them. Airborne atmospheric O2 measurements provide unique constraints on carbon cycle and physical climate processes (e.g., Bent, 2014; Nevison et al., 2015; Resplandy et al., 2016; Stephens et al., 2018; Asher et al., 2019; Morgan et al., 2019). Precise, high-resolution, global-scale, seasonally resolved, profiling airborne measurements can be used to observe the impact of biogeochemical land and ocean exchanges at large scales and with high fidelity. Further scientific investigations using AO2 and Medusa measurements are planned and will be facilitated by the methodological presentation given here.
Web links and DOIs for collections of individual flight AO2 and Medusa data files for each campaign are provided in the reference list and Table S2 in the Supplement. For AO2, these include 1 Hz AO2 data interpolated from the native 0.4 Hz measurements with both the original measurements and those adjusted to match Medusa (https://doi.org/10.26023/PPR2-97CQ-N106, Stephens et al., 2021a; https://doi.org/10.5065/D6N29VC6, Stephens et al., 2021b; https://doi.org/10.5065/D6J38QVV, Stephens et al., 2021g; https://doi.org/10.5065/D65Q4TF0, Stephens et al., 2021h; https://doi.org/10.5065/D67H1GXJ, Stephens et al., 2021i; https://doi.org/10.5065/D679431D, Stephens et al., 2021j; https://doi.org/10.5065/D6WW7G0D, Stephens et al., 2021k; https://doi.org/10.5065/D6DJ5CZ5, Stephens et al., 2021l; https://doi.org/10.3334/ORNLDAAC/1880, Stephens et al., 2021m). For Medusa, these include measured values on each flask as well as files defining the averaging kernel to use when comparing to 1 Hz data (https://doi.org/10.26023/J0VT-J67P-330R, Keeling et al., 2021a; https://doi.org/10.26023/4NM6-3MPG-WC14, Keeling et al., 2021b, https://doi.org/10.26023/30T9-FZ21-4G04, Keeling et al., 2021c; https://doi.org/10.26023/P4PE-KKYS-FZ07, Keeling et al., 2021d; https://doi.org/10.26023/MYW6-DQQ6-PZ0R, Keeling et al., 2021e; https://doi.org/10.26023/GA02-K0FR-C10M, Keeling et al., 2021f; https://doi.org/10.26023/XQW5-YHPP-XG0M, Keeling et al., 2021g; https://doi.org/10.26023/FF65-2RZM-ZB00, Keeling et al., 2021h; https://doi.org/10.26023/R8JN-Z3TG-2E0N, Keeling et al., 2021i; https://doi.org/10.26023/X9KY-CK34-VR10, Keeling et al., 2021j; https://doi.org/10.26023/AWHD-19RV-GC14, Keeling et al., 2021k; https://doi.org/10.26023/CS11-P31Q-V713, Keeling et al., 2021l; https://doi.org/10.3334/ORNLDAAC/1881, Morgan et al., 2021; https://doi.org/10.5065/D6H130FW, Stephens et al., 2021c; https://doi.org/10.5065/D6MS3R6C, Stephens et al., 2021d; https://doi.org/10.26023/PV4Q-2XBJ-670C, Stephens et al., 2021e; https://doi.org/10.26023/2H6N-AZ1Y-N04, Stephens et al., 2021f). In addition to these individual flight files, several merge products are available, which combine AO2 and Medusa data with state parameters and measurements from other instruments. These include a 1 Hz merge for START-08 (https://doi.org/10.5065/D61834TJ, UCAR/NCAR – Earth Observing Laboratory, 2013), 10 s and Medusa merges for all HIPPO campaigns (https://doi.org/10.3334/CDIAC/HIPPO_010, Wofsy et al., 2017a; https://doi.org/10.3334/CDIAC/HIPPO_014, Wofsy et al., 2017b) 10 s and Medusa merges for ORCAS (https://doi.org/10.5065/D6SB445X, Stephens, 2017), and 10 s and Medusa merges for all ATom campaigns (https://doi.org/10.3334/ORNLDAAC/1581, Wofsy et al., 2018). All of the individual files have been updated online in conjunction with this publication. We are in the process of updating all of the online merge files and working towards creating an online repository for the COBRA campaigns. Users of these data should be sure to access the most recent versions at the provided web links and DOIs.
The supplement related to this article is available online at: https://doi.org/10.5194/amt-14-2543-2021-supplement.
BBS led the development of the AO2 instrument and Medusa sampler, field operations for all campaigns, lab experiments, and the drafting of the manuscript. EJM led the preparation, sampling, analysis, and data processing for Medusa flasks since ARISTO-2015, and supported field operations and testing for both systems during this time. JDB led the preparation, sampling, analysis, and data processing of Medusa flasks for START-08 and HIPPO, and supported field operations and testing for both systems during this time. RFK contributed to the development of Medusa for COBRA, oversaw the analysis of Medusa samples for all campaigns, and contributed to AO2 design and testing. ASW assembled AO2 and Medusa, conducted laboratory tests, and supported field operations from ACME-07 through ATom. SRS provided engineering design for both AO2 and Medusa, and supported field operations during ACME-07, START-08, and HIPPO. BCD contributed to the development of Medusa for COBRA, provided troubleshooting assistance for both AO2 and Medusa through ATom, and led the Harvard QCLS measurements. All authors contributed to the editing of the manuscript text.
The authors declare that they have no conflict of interest.
We would like to thank the many colleagues who have provided support over the years in the form of advice, brainstorming, data, and camaraderie in the field. In particular we would like to thank the pilots, mechanics, technicians, and other support staff of the NCAR Research Aviation Facility and Earth Observing Laboratory, the NASA Airborne Science Program and Earth Science Project Office, and the University of North Dakota and University of Wyoming flight research facilities. We are grateful for test flight support, laboratory preparation of standards and flasks, and flask measurements at Scripps from Sara Afshar, Bill Paplawsky, Adam Cox, Shane Clark, Heather Graven, Chris Atwood, and Elizabeth McEvoy. We also thank John Miller and Heather Graven for supporting Medusa field operations during COBRA. We would like to thank the Harvard QCLS and NOAA PANTHER teams for their sharing of START-08, HIPPO, ORCAS, and ATom N2O measurements, including Steve Wofsy, Eric Kort, Rodrigo Jimenez, Jasna Pittman, Sunyoung Park, Roisin Commane, Bin Xiang, Greg Santoni, John Budney, Yenny Gonzalo Ramos, Fred Moore, Jim Elkins, and Eric Hintsa. We also thank Andrew Manning, Benni Birner, and Yuming Jin for valuable discussions. This material is based upon work supported by the National Center for Atmospheric Research, which is a major facility sponsored by the National Science Foundation under Cooperative Agreement No. 1852977.
This research has been supported by the National Science Foundation, Directorate for Geosciences (grant nos. EAR-0321918, ATM-0628519, ATM-0628388, PLR-1501993, PLR-1502301, AGS-1547626, AGS-1547797, AGS-1623745, and AGS-1623748) and NASA (grant nos. NAG5-11430 and NCC5-590).
This paper was edited by Piet Stammes and reviewed by two anonymous referees.
Akima, H.: A method of bivariate interpolation and smooth surface fitting for irregularly distributed data points, ACM T. Math. Software., 4, 148–159, https://doi.org/10.1145/355780.355786, 1978. a
Armbruster, M. H. and Austin, J. B.: The Adsorption of Gases on Smooth Surfaces of Steell, J. Am. Chem. Soc., 66, 159–171, https://doi.org/10.1021/ja01230a001, 1944. a
Asher, E., Hornbrook, R. S., Stephens, B. B., Kinnison, D., Morgan, E. J., Keeling, R. F., Atlas, E. L., Schauffler, S. M., Tilmes, S., Kort, E. A., Hoecker-Martínez, M. S., Long, M. C., Lamarque, J.-F., Saiz-Lopez, A., McKain, K., Sweeney, C., Hills, A. J., and Apel, E. C.: Novel approaches to improve estimates of short-lived halocarbon emissions during summer from the Southern Ocean using airborne observations, Atmos. Chem. Phys., 19, 14071–14090, https://doi.org/10.5194/acp-19-14071-2019, 2019. a, b
Battle, M., Bender, M., Hendricks, M. B., Ho, D. T., Mika, R., McKinley, G., Fan, S.-M., Blaine, T., and Keeling, R. F.: Measurements and models of the atmospheric ratio, Geophys. Res. Lett., 30, 1786, https://doi.org/10.1029/2003GL017411, 2003. a
Battle, M., Mikaloff Fletcher, S. E., Bender, M. L., Keeling, R. F., Manning, A. C., Gruber, N., Tans, P. P., Hendricks, M. B., Ho, D. T., Simonds, C., Mika, R., and Paplawsky, B.: Atmospheric potential oxygen: New observations and their implications for some atmospheric and oceanic models, Global Biogeochem. Cy., 20, GB1010, https://doi.org/10.1029/2005GB002534, 2006. a
Battle, M. O., Munger, J. W., Conley, M., Sofen, E., Perry, R., Hart, R., Davis, Z., Scheckman, J., Woogerd, J., Graeter, K., Seekins, S., David, S., and Carpenter, J.: Atmospheric measurements of the terrestrial O2 : CO2 exchange ratio of a midlatitude forest, Atmos. Chem. Phys., 19, 8687–8701, https://doi.org/10.5194/acp-19-8687-2019, 2019. a, b
Belyaev, S. and Levin, L.: Techniques for collection of representative aerosol samples, J. Aerosol Sci., 5, 325–338, https://doi.org/10.1016/0021-8502(74)90130-X, 1974. a
Bender, M. L., Tans, P. P., Ellis, J. T., and Orchardo, J.: A high precision isotope ratio mass spectrometry method for measuring the ratio of air, Geochim. Cosmochim. Ac., 58, 4751–4758, https://doi.org/10.1016/0016-7037(94)90205-4, 1994. a
Bent, J.: Airborne oxygen measurements over the Southern Ocean as an integrated constraint of seasonal biogeochemical processes, PhD thesis, University of California, San Diego, USA, 2014. a, b, c, d, e, f, g, h, i, j, k, l, m, n, o, p, q
Birner, B., Chipperfield, M. P., Morgan, E. J., Stephens, B. B., Linz, M., Feng, W., Wilson, C., Bent, J. D., Wofsy, S. C., Severinghaus, J., and Keeling, R. F.: Gravitational separation of and age of air in the lowermost stratosphere in airborne observations and a chemical transport model, Atmos. Chem. Phys., 20, 12391–12408, https://doi.org/10.5194/acp-20-12391-2020, 2020. a, b, c, d
Blaine, T. W., Keeling, R. F., and Paplawsky, W. J.: An improved inlet for precisely measuring the atmospheric Ar N2 ratio, Atmos. Chem. Phys., 6, 1181–1184, https://doi.org/10.5194/acp-6-1181-2006, 2006. a
Buckley, D. H.: Influence of chemisorbed films on adhesion and friction of clean iron, Tech. Rep. NASA-TN-D-4775, NASA Lewis Research Center, Cleveland, OH, United States, Washington, D.C., 1968. a, b
Cleveland, W. S. and Devlin, S. J.: Locally weighted regression: An approach to regression analysis by local fitting, J. Am. Stat. Assoc., 83, 596–610, https://doi.org/10.1080/01621459.1988.10478639, 1988. a
Desai, A. R., Moore, D. J. P., Ahue, W. K. M., Wilkes, P. T. V., De Wekker, S. F. J., Brooks, B. G., Campos, T. L., Stephens, B. B., Monson, R. K., Burns, S. P., Quaife, T., Aulenbach, S. M., and Schimel, D. S.: Seasonal pattern of regional carbon balance in the central Rocky Mountains from surface and airborne measurements, J. Geophys. Res., 116, G04009, https://doi.org/10.1029/2011JG001655, 2011. a
Gaubert, B., Stephens, B. B., Basu, S., Chevallier, F., Deng, F., Kort, E. A., Patra, P. K., Peters, W., Rödenbeck, C., Saeki, T., Schimel, D., Van der Laan-Luijkx, I., Wofsy, S., and Yin, Y.: Global atmospheric CO2 inverse models converging on neutral tropical land exchange, but disagreeing on fossil fuel and atmospheric growth rate, Biogeosciences, 16, 117–134, https://doi.org/10.5194/bg-16-117-2019, 2019. a
Gerbig, C., Lin, J. C., Wofsy, S. C., Daube, B. C., Andrews, A. E., Stephens, B. B., Bakwin, P. S., and Grainger, C. A.: Toward constraining regional-scale fluxes of CO2 with atmospheric observations over a continent: 2. Analysis of COBRA data using a receptor-oriented framework, J. Geophys. Res., 108, 4757, https://doi.org/10.1029/2003JD003770, 2003. a
Graven, H. D., Keeling, R. F., Piper, S. C., Patra, P. K., Stephens, B. B., Wofsy, S. C., Welp, L. R., Sweeney, C., Tans, P. P., Kelley, J. J., Daube, B. C., Kort, E. A., Santoni, G. W., and Bent, J. D.: Enhanced Seasonal Exchange of CO2 by Northern Ecosystems Since 1960, Science, 341, 1085–1089, https://doi.org/10.1126/science.1239207, 2013. a
Guenther, P. R., Bollenbacher, A. F., Keeling, C. D., Stewart, E. F., and Wahlen, M.: Calibration Methodology for the Scripps 13C 12C and 18O 16O Stable Isotope Program 1969–2000. A Report Prepared for the Global Environmental Monitoring Program of the World Meteorological Organization, Tech. rep., Scripps Institution of Oceanography, La Jolla, CA 92093-0244, 2001. a
Guo, H., Campuzano-Jost, P., Nault, B. A., Day, D. A., Schroder, J. C., Dibb, J. E., Dollner, M., Weinzierl, B., and Jimenez, J. L.: The Importance of Size Ranges in Aerosol Instrument Intercomparisons: A Case Study for the ATom Mission, Atmos. Meas. Tech. Discuss. [preprint], https://doi.org/10.5194/amt-2020-224, in review, 2020. a
Ishidoya, S., Sugawara, S., Morimoto, S., Aoki, S., and Nakazawa, T.: Gravitational separation of major atmospheric components of nitrogen and oxygen in the stratosphere, Geophys. Res. Lett., 35, L03811, https://doi.org/10.1029/2007gl030456, 2008. a
Ishidoya, S., Aoki, S., Goto, D., Nakazawa, T., Taguchi, S., and Patra, P. K.: Time and space variations of the ratio in the troposphere over Japan and estimation of the global CO2 budget for the period 2000–2010, Tellus B, 64, 18964, https://doi.org/10.3402/tellusb.v64i0.18964, 2012. a
Ishidoya, S., Murayama, S., Takamura, C., Kondo, H., Saigusa, N., Goto, D., Morimoto, S., Aoki, N., Aoki, S., and Nakazawa, T.: O2:CO2 exchange ratios observed in a cool temperate deciduous forest ecosystem of central Japan, Tellus B, 65, 21120, https://doi.org/10.3402/tellusb.v65i0.21120, 2013a. a
Ishidoya, S., Sugawara, S., Morimoto, S., Aoki, S., Nakazawa, T., Honda, H., and Murayama, S.: Gravitational separation in the stratosphere – a new indicator of atmospheric circulation, Atmos. Chem. Phys., 13, 8787–8796, https://doi.org/10.5194/acp-13-8787-2013, 2013b. a
Ishidoya, S., Tsuboi, K., Matsueda, H., Murayama, S., Taguchi, S., Sawa, Y., Niwa, Y., Saito, K., Tsuji, K., Nishi, H., Baba, Y., Takatsuji, S., Dehara, K., and Fujiwara, H.: New atmospheric ratio measurements over the Western North Pacific using a cargo aircraft C-130H, SOLA, 10, 23–28, https://doi.org/10.2151/sola.2014-006, 2014. a, b
Jin, Y., Keeling, R. F., Morgan, E. J., Ray, E., Parazoo, N. C., and Stephens, B. B.: A mass-weighted isentropic coordinate for mapping chemical tracers and computing atmospheric inventories, Atmos. Chem. Phys., 21, 217–238, https://doi.org/10.5194/acp-21-217-2021, 2021. a
Keeling, R. and Manning, A.: Studies of recent changes in atmospheric O2 content, in: Treatise on Geochemistry (Second Edition), edited by: Holland, H. D. and Turekian, K. K., Elsevier, Oxford, https://doi.org/10.1016/B978-0-08-095975-7.00420-4, 385–404, 2014. a, b, c
Keeling, R., Stephens, B., Bent, J., Watt, A., Shertz, S., and Paplawsky, W.: HIPPO-1 Multiple Enclosure Device for Unfractionated Sampling of Air (MEDUSA) Flask Data. Version 2.0, https://doi.org/10.26023/J0VT-J67P-330R, 2021a. a
Keeling, R., Stephens, B., Bent, J., Watt, A., Shertz, S., and Paplawsky, W.: HIPPO-1 Multiple Enclosure Device for Unfractionated Sampling of Air (MEDUSA) Kernel Data. Version 2.0, https://doi.org/10.26023/4NM6-3MPG-WC14, 2021b. a
Keeling, R., Stephens, B., Bent, J., Watt, A., Shertz, S., and Paplawsky, W.: HIPPO-2 Multiple Enclosure Device for Unfractionated Sampling of Air (MEDUSA) Flask Data. Version 2.0, https://doi.org/10.26023/30T9-FZ21-4G04, 2021c. a
Keeling, R., Stephens, B., Bent, J., Watt, A., Shertz, S., and Paplawsky, W.: HIPPO-2 Multiple Enclosure Device for Unfractionated Sampling of Air (MEDUSA) Kernel Data. Version 2.0, https://doi.org/10.26023/P4PE-KKYS-FZ07, 2021d. a
Keeling, R., Stephens, B., Bent, J., Watt, A., Shertz, S., and Paplawsky, W.: HIPPO-3 Multiple Enclosure Device for Unfractionated Sampling of Air (MEDUSA) Flask Data. Version 2.0, https://doi.org/10.26023/MYW6-DQQ6-PZ0R, 2021e. a
Keeling, R., Stephens, B., Bent, J., Watt, A., Shertz, S., and Paplawsky, W.: HIPPO-3 Multiple Enclosure Device for Unfractionated Sampling of Air (MEDUSA) Kernel Data. Version 2.0, https://doi.org/10.26023/GA02-K0FR-C10M, 2021f. a
Keeling, R., Stephens, B., Bent, J., Watt, A., Shertz, S., and Paplawsky, W.: HIPPO-4 Multiple Enclosure Device for Unfractionated Sampling of Air (MEDUSA) Flask Data. Version 2.0, https://doi.org/10.26023/XQW5-YHPP-XG0M, 2021g. a
Keeling, R., Stephens, B., Bent, J., Watt, A., Shertz, S., and Paplawsky, W.: HIPPO-4 Multiple Enclosure Device for Unfractionated Sampling of Air (MEDUSA) Kernel Data. Version 2.0, https://doi.org/10.26023/FF65-2RZM-ZB00, 2021h. a
Keeling, R., Stephens, B., Bent, J., Watt, A., Shertz, S., and Paplawsky, W.: HIPPO-5 Multiple Enclosure Device for Unfractionated Sampling of Air (MEDUSA) Flask Data. Version 2.0, https://doi.org/10.26023/R8JN-Z3TG-2E0N, 2021i. a
Keeling, R., Stephens, B., Bent, J., Watt, A., Shertz, S., and Paplawsky, W.: HIPPO-5 Multiple Enclosure Device for Unfractionated Sampling of Air (MEDUSA) Kernel Data. Version 2.0, https://doi.org/10.26023/X9KY-CK34-VR10, 2021j. a
Keeling, R., Stephens, B., Bent, J., Watt, A., Shertz, S., and Paplawsky, W.: START-08 Multiple Enclosure Device for Unfractionated Sampling of Air (MEDUSA) Flask Data. Version 1.0, https://doi.org/10.26023/AWHD-19RV-GC14, 2021k. a
Keeling, R., Stephens, B., Bent, J., Watt, A., Shertz, S., and Paplawsky, W.: START-08 Multiple Enclosure Device for Unfractionated Sampling of Air (MEDUSA) Kernel Data. Version 1.0, https://doi.org/10.26023/CS11-P31Q-V713, 2021l. a
Keeling, R. F.: Development of an interferometric oxygen analyzer for precise measurement of the atmospheric O2 mole fraction, PhD thesis, Harvard University, USA, 1988. a, b, c
Keeling, R. F. and Shertz, S. R.: Seasonal and interannual variations in atmospheric oxygen and implications for the global carbon cycle, Nature, 358, 723–727, https://doi.org/10.1038/358723a0, 1992. a, b
Keeling, R. F., Manning, A. C., McEvoy, E. M., and Shertz, S. R.: Methods for measuring changes in atmospheric O2 concentration and their application in Southern Hemisphere air, J. Geophys. Res., 103, 3381–3397, https://doi.org/10.1029/97JD02537, 1998. a, b, c, d, e, f, g, h, i, j, k, l
Keeling, R. F., Blaine, T., Paplawsky, B., Katz, L., Atwood, C., and Brockwell, T.: Measurement of changes in atmospheric Ar/N2 ratio using a rapid-switching, single-capillary mass spectrometer system, Tellus B, 56, 322–338, https://doi.org/10.3402/tellusb.v56i4.16453, 2004. a, b, c, d, e, f, g, h
Keeling, R. F., Manning, A. C., Paplawsky, W. J., and Cox, A. C.: On the long-term stability of reference gases for atmospheric O2/N2 and CO2 measurements, Tellus B, 59, 3–14, https://doi.org/10.1111/j.1600-0889.2006.00228.x, 2007. a, b, c, d, e
Kort, E. A., Eluszkiewicz, J., Stephens, B. B., Miller, J. B., Gerbig, C., Nehrkorn, T., Daube, B. C., Kaplan, J. O., Houweling, S., and Wofsy, S. C.: Emissions of CH4 and N2O over the United States and Canada based on a receptor-oriented modeling framework and COBRA-NA atmospheric observations, Geophys. Res. Lett., 35, https://doi.org/10.1029/2008GL034031, 2008. a, b, c
Kozlova, E. A., Manning, A. C., Kisilyakhov, Y., Seifert, T., and Heimann, M.: Seasonal, synoptic, and diurnal-scale variability of biogeochemical trace gases and O2 from a 300-m tall tower in central Siberia, Global Biogeochem. Cy., 22, https://doi.org/10.1029/2008GB003209, 2008. a
Langenfelds, R. L.: Studies of the global carbon cycle using atmospheric oxygen and associated tracers, PhD thesis, University of Tasmania, Hobart, Australia, 2002. a, b, c, d
Manning, A. C., Keeling, R. F., and Severinghaus, J. P.: Precise atmospheric oxygen measurements with a paramagnetic oxygen analyzer, Global Biogeochem. Cy., 13, 1107–1115, https://doi.org/10.1029/1999GB900054, 1999. a
Morgan, E. J., Stephens, B. B., Long, M. C., Keeling, R. F., Bent, J. D., McKain, K., Sweeney, C., Hoecker-Martínez, M. S., and Kort, E. A.: Summertime Atmospheric Boundary Layer Gradients of O2 and CO2 over the Southern Ocean, J. Geophys. Res., 124, 13439–13456, https://doi.org/10.1029/2019JD031479, 2019. a, b, c
Morgan, E., Stephens, B., Bent, J., Watt, A., Afshar, S., Paplawsky, W., and Keeling, R.: ATom: L2 Measurements from Medusa Whole Air Sampler (Medusa), Version 2, ORNL DAAC, Oak Ridge, Tennessee, USA, https://doi.org/10.3334/ORNLDAAC/1881, 2021.
Nevison, C. D., Manizza, M., Keeling, R. F., Kahru, M., Bopp, L., Dunne, J., Tiputra, J., Ilyina, T., and Mitchell, B. G.: Evaluating the ocean biogeochemical components of Earth system models using atmospheric potential oxygen and ocean color data, Biogeosciences, 12, 193–208, https://doi.org/10.5194/bg-12-193-2015, 2015. a, b
Nevison, C. D., Manizza, M., Keeling, R. F., Stephens, B. B., Bent, J. D., Dunne, J., Ilyina, T., Long, M., Resplandy, L., Tjiputra, J., and Yukimoto, S.: Evaluating CMIP5 ocean biogeochemistry and Southern Ocean carbon uptake using atmospheric potential oxygen: Present-day performance and future projection, Geophys. Res. Lett., 43, 2077–2085, https://doi.org/10.1002/2015GL067584, 2016. a
Okabe, H.: Intense Resonance Line Sources for Photochemical Work in the Vacuum Ultraviolet Region, J. Opt. Soc. Am., 54, 478–481, https://doi.org/10.1364/JOSA.54.000478, 1964. a
Pan, L. L., Bowman, K. P., Atlas, E. L., Wofsy, S. C., Zhang, F., Bresch, J. F., Ridley, B. A., Pittman, J. V., Homeyer, C. R., Romashkin, P., and Cooper, W. A.: The stratosphere-troposphere analyses of regional transport 2008 experiment, B. Am. Meteor. Soc., 91, 327–342, https://doi.org/10.1175/2009BAMS2865.1, 2010. a
Resplandy, L., Keeling, R. F., Stephens, B. B., Bent, J. D., Jacobson, A., Roedenbeck, C., and Khatiwala, S.: Constraints on oceanic meridional heat transport from combined measurements of oxygen and carbon, Clim. Dyn., 47, 3335–3357, https://doi.org/10.1007/s00382-016-3029-3, 2016. a, b, c
Santoni, G. W., Daube, B. C., Kort, E. A., Jiménez, R., Park, S., Pittman, J. V., Gottlieb, E., Xiang, B., Zahniser, M. S., Nelson, D. D., McManus, J. B., Peischl, J., Ryerson, T. B., Holloway, J. S., Andrews, A. E., Sweeney, C., Hall, B., Hintsa, E. J., Moore, F. L., Elkins, J. W., Hurst, D. F., Stephens, B. B., Bent, J., and Wofsy, S. C.: Evaluation of the airborne quantum cascade laser spectrometer (QCLS) measurements of the carbon and greenhouse gas suite – CO2, CH4, N2O, and CO – during the CalNex and HIPPO campaigns, Atmos. Meas. Tech., 7, 1509–1526, https://doi.org/10.5194/amt-7-1509-2014, 2014. a, b
Steinbach, J.: Enhancing the usability of atmospheric oxygen measurements through emission source characterization and airborne measurement, PhD thesis, Friedrich-Schiller-Universität, Jena, Germany, 2010. a, b, c, d, e, f
Steinbach, J., Gerbig, C., Rödenbeck, C., Karstens, U., Minejima, C., and Mukai, H.: The CO2 release and Oxygen uptake from Fossil Fuel Emission Estimate (COFFEE) dataset: effects from varying oxidative ratios, Atmos. Chem. Phys., 11, 6855–6870, https://doi.org/10.5194/acp-11-6855-2011, 2011. a
Stephens, B.: ORCAS Merge Products. Version 1.0, https://doi.org/10.5065/D6SB445X, 2017. a
Stephens, B., Keeling, R., and Paplawsky, W.: Shipboard measurements of atmospheric oxygen using a vacuum-ultraviolet absorption technique, Tellus B, 55, 857–878, https://doi.org/10.3402/tellusb.v55i4.16386, 2003. a, b, c, d, e, f, g, h, i, j
Stephens, B., Bent, J., Watt, A., Keeling, R., Morgan, E., and Afshar, S.: ARISTO-2015 Airborne Oxygen Instrument. Version 1.0, https://doi.org/10.26023/PPR2-97CQ-N106, 2021a. a
Stephens, B., Bent, J., Watt, A., Keeling, R., Morgan, E., and Afshar, S.: ORCAS Airborne Oxygen Instrument. Version 2.0, https://doi.org/10.5065/D6N29VC6, 2021b. a
Stephens, B., Bent, J., Watt, A., Keeling, R., Morgan, E., Afshar, S., and Paplawsky, W.: ORCAS Medusa Flask Sampler Flask Data. Version 2.0, https://doi.org/10.5065/D6H130FW, 2021c. a
Stephens, B., Bent, J., Watt, A., Keeling, R., Morgan, E., Afshar, S., and Paplawsky, W.: ORCAS Medusa Flask Sampler Kernel Data. Version 2.0, https://doi.org/10.5065/D6MS3R6C, 2021d. a
Stephens, B., Keeling, R., Bent, J., Watt, A., Morgan, E., Afshar, S., and Paplawsky, W.: ARISTO-2015 Multiple Enclosure Device for Unfractionated Sampling of Air (MEDUSA) Flask Data. Version 1.0, https://doi.org/10.26023/PV4Q-2XBJ-670C, 2021e. a
Stephens, B., Keeling, R., Bent, J., Watt, A., Morgan, E., Afshar, S., and Paplawsky, W.: ARISTO-2015 Multiple Enclosure Device for Unfractionated Sampling of Air (MEDUSA) Kernel Data. Version 1.0, https://doi.org/10.26023/2H6N-AZ1Y-N04, 2021f. a
Stephens, B., Keeling, R., Bent, J., Watt, A., Shertz, S., and Paplawsky, W.: HIPPO-1 Airborne Oxygen Instrument. Version 2.0, https://doi.org/10.5065/D6J38QVV, 2021g. a
Stephens, B., Keeling, R., Bent, J., Watt, A., Shertz, S., and Paplawsky, W.: HIPPO-2 Airborne Oxygen Instrument. Version 2.0, https://doi.org/10.5065/D65Q4TF0, 2021h. a
Stephens, B., Keeling, R., Bent, J., Watt, A., Shertz, S., and Paplawsky, W.: HIPPO-3 Airborne Oxygen Instrument. Version 2.0, https://doi.org/10.5065/D67H1GXJ, 2021i. a
Stephens, B., Keeling, R., Bent, J., Watt, A., Shertz, S., and Paplawsky, W.: HIPPO-4 Airborne Oxygen Instrument. Version 2.0, https://doi.org/10.5065/D679431D, 2021j. a
Stephens, B., Keeling, R., Bent, J., Watt, A., Shertz, S., and Paplawsky, W.: HIPPO-5 Airborne Oxygen Instrument. Version 2.0, https://doi.org/10.5065/D6WW7G0D, 2021k. a
Stephens, B., Keeling, R., Bent, J., Watt, A., Shertz, S., and Paplawsky, W.: START-08 Airborne Oxygen Instrument. Version 2.0, https://doi.org/10.5065/D6DJ5CZ5, 2021l. a
Stephens, B., Morgan, E., Watt, A., Bent, J., Afshar, S., Keeling, R., and Paplawsky, W.: ATom: L2 In Situ Measurements from the NCAR Airborne Oxygen Instrument (AO2), V2, ORNL DAAC, Oak Ridge, Tennessee, USA, https://doi.org/10.3334/ORNLDAAC/1880, 2021m. a
Stephens, B. B.: Field-based atmospheric oxygen measurements and the ocean carbon cycle, PhD thesis, University of California, San Diego, 1999. a, b, c
Stephens, B. B., Keeling, R. F., Heimann, M., Six, K. D., Murnane, R., and Caldeira, K.: Testing global ocean carbon cycle models using measurements of atmospheric O2 and CO2 concentration, Global Biogeochem. Cy., 12, 213–230, https://doi.org/10.1029/97gb03500, 1998. a, b
Stephens, B. B., Wofsy, S. C., Keeling, R. F., Tans, P. P., and Potosnak, M. J.: The CO2 budget and rectification airborne study: Strategies for measuring rectifiers and regional fluxes, in: Inverse Methods in Global Biogeochemical Cycles, Geophysical Monograph Series, American Geophysical Union, 114, 311–324, https://doi.org/10.1029/GM114p0311, 2000. a
Stephens, B. B., Bakwin, P. S., Tans, P. P., Teclaw, R. M., and Baumann, D. D.: Application of a differential fuel-cell analyzer for measuring atmospheric oxygen variations, J. Atmos. Ocean. Tech., 24, 82–94, https://doi.org/10.1175/JTECH1959.1, 2007a. a, b, c
Stephens, B. B., Gurney, K. R., Tans, P. P., Sweeney, C., Peters, W., Bruhwiler, L., Ciais, P., Ramonet, M., Bousquet, P., Nakazawa, T., Aoki, S., Machida, T., Inoue, G., Vinnichenko, N., Lloyd, J., Jordan, A., Heimann, M., Shibistova, O., Langenfelds, R. L., Steele, L. P., Francey, R. J., and Denning, A. S.: Weak northern and strong tropical land carbon uptake from vertical profiles of atmospheric CO2, Science, 316, 1732–1735, https://doi.org/10.1126/science.1137004, 2007b. a
Stephens, B. B., Long, M. C., Keeling, R. F., Kort, E. A., Sweeney, C., Apel, E. C., Atlas, E. L., Beaton, S., Bent, J. D., Blake, N. J., Bresch, J. F., Casey, J., Daube, B. C., Diao, M. H., Diaz, E., Dierssen, H., Donets, V., Gao, B. C., Gierach, M., Green, R., Haag, J., Hayman, M., Hills, A. J., Hoecker-Martinez, M. S., Honomichl, S. B., Hornbrook, R. S., Jensen, J. B., Li, R. R., McCubbin, I., McKain, K., Morgan, E. J., Nolte, S., Powers, J. G., Rainwater, B., Randolph, K., Reeves, M., Schauffler, S. M., Smith, K., Smith, M., Stith, J., Stossmeister, G., Toohey, D. W., and Watt, A. S.: The Ratio and CO2 Airborne Southern Ocean Study, B. Am. Meteor. Soc., 99, 381–402, https://doi.org/10.1175/bams-d-16-0206.1, 2018. a, b, c
Sturm, P., Leuenberger, M., Moncrieff, J., and Ramonet, M.: Atmospheric O2, CO2 and δ13C measurements from aircraft sampling over Griffin Forest, Perthshire, UK, Rapid Commun. Mass Sp., 19, 2399–2406, https://doi.org/10.1002/rcm.2071, 2005. a
Sun, J., Oncley, S. P., Burns, S. P., Stephens, B. B., Lenschow, D. H., Campos, T., Monson, R. K., Schimel, D. S., Sacks, W. J., De Wekker, S. F. J., Lai, C.-T., Lamb, B., Ojima, D., Ellsworth, P. Z., Sternberg, L. S. L., Zhong, S., Clements, C., Moore, D. J. P., Anderson, D. E., Watt, A. S., Hu, J., Tschudi, M., Aulenbach, S., Allwine, E., and Coons, T.: A multiscale and multidisciplinary investigation of ecosystem–atmosphere CO2 exchange over the Rocky Mountains of Colorado, B. Am. Meteor. Soc., 91, 209–230, https://doi.org/10.1175/2009BAMS2733.1, 2010. a
Sweeney, C., Karion, A., Wolter, S., Newberger, T., Guenther, D., Higgs, J. A., Andrews, A. E., Lang, P. M., Neff, D., Dlugokencky, E., Miller, J. B., Montzka, S. A., Miller, B. R., Masarie, K. A., Biraud, S. C., Novelli, P. C., Crotwell, M., Crotwell, A. M., Thoning, K., and Tans, P. P.: Seasonal climatology of CO2 across North America from aircraft measurements in the NOAA/ESRL Global Greenhouse Gas Reference Network, J. Geophys. Res., 120, 5155–5190, https://doi.org/10.1002/2014jd022591, 2015. a
Tohjima, Y.: Method for measuring changes in the atmospheric ratio by a gas chromatograph equipped with a thermal conductivity detector, J. Geophys. Res., 105, 14575–14584, https://doi.org/10.1029/2000JD900057, 2000. a
UCAR/NCAR – Earth Observing Laboratory: NSF/NCAR Hercules C130 Aircraft, UCAR/NCAR – Earth Observing Laboratory, https://doi.org/10.5065/D6WM1BG0, 1994. a
UCAR/NCAR – Earth Observing Laboratory: NSF/NCAR GV HIAPER Aircraft, UCAR/NCAR – Earth Observing Laboratory, https://doi.org/10.5065/D6DR2SJP, 2005. a
UCAR/NCAR – Earth Observing Laboratory: Merged Selected GV Low Rate Flight-Level and Instrument Data and Interpolated GFS Analysis Variables. Version 1.0, https://doi.org/10.5065/D61834TJ (last access: 13 July 2020), 2013. a
van der Laan, S., van der Laan-Luijkx, I. T., Roedenbeck, C., Varlagin, A., Shironya, I., Neubert, R. E. M., Ramonet, M., and Meijer, H. A. J.: Atmospheric CO2, δ(), APO and oxidative ratios from aircraft flask samples over Fyodorovskoye, Western Russia, Atmos. Environ., 97, 174–181, https://doi.org/10.1016/j.atmosenv.2014.08.022, 2014. a
Vay, S. A., Anderson, B. E., Thornhill, K. L., and Hudgins, C. H.: An assessment of aircraft-generated contamination on in situ trace gas measurements: Determinations from empirical data acquired aloft, J. Atmos. Ocean. Tech., 20, 1478–1487, https://doi.org/10.1175/1520-0426(2003)020<1478:aaoaco>2.0.co;2, 2003. a, b
Wofsy, S. C., Fisher, J., Pickett-Heaps, C., Wang, H., Wecht, K., Wang, Q., Stephens, B., Shertz, S., Watt, A., Romashkin, P., Campos, T., Haggerty, J., Cooper, W., Rogers, D., Beaton, S., Hendershot, R., Elkins, J., Fahey, D., Gao, R., Schwarz, J., Moore, F., Montzka, S., Perring, A., Hurst, D., Miller, B., Sweeney, C., Oltmans, S., Hintsa, E., Nance, D., Dutton, G., Watts, L., Spackman, J., Rosenlof, K., Ray, E., Hall, B., Zondlo, M., Diao, M., Keeling, R., Bent, J., Atlas, E., Lueb, R. and Mahoney, M. J.: HIPPO Merged 10-Second Meteorology, Atmospheric Chemistry, and Aerosol Data. Version 1.0, https://doi.org/10.3334/CDIAC/HIPPO_010, 2017a. a
Wofsy, S., Fisher, J., Pickett-Heaps, C., Wang, H., Wecht, K., Wang, Q., Stephens, B., Shertz, S., Watt, A., Romashkin, P., Campos, T., Haggerty, J., Cooper, W., Rogers, D., Beaton, S., Hendershot, R., Elkins, J., Fahey, D., Gao, R., Moore, F., Montzka, S., Schwarz, J., Perring, A., Hurst, D., Miller, B., Sweeney, C., Oltmans, S., Nance, D., Hintsa, E., Dutton, G., Watts, L., Spackman, J., Rosenlof, K., Ray, E., Hall, B., Zondlo, M., Diao, M., Keeling, R., Bent, J., Atlas, E., Lueb, R. and Mahoney, M. J.: HIPPO MEDUSA Flask Sample Trace Gas And Isotope Data. Version 1.0, https://doi.org/10.3334/CDIAC/HIPPO_014, 2017b. a
Wofsy, S. C., Afshar, S., Allen, H. M., Apel, E. C., Asher, E. C., Barletta, B., Bent, J., Bian, H., Biggs, B. C., Blake, D. R., Blake, N., Bourgeois, I., Brock, C. A., Brune, W. H., Budney, J. W., Bui, T. P., Butler, A., Campuzano-Jost, P., Chang, C. S., Chin, M., Commane, R., Correa, G., Crounse, J. D., Cullis, P. D., Daube, B. C., Day, D. A., Dean-Day, J. M., Dibb, J. E., DiGangi, J. P., Diskin, G. S., Dollner, M., Elkins, J. W., Erdesz, F., Fiore, A. M., Flynn, C. M., Froyd, K. D., Gesler, D. W., Hall, S. R., Hanisco, T. F., Hannun, R. A., Hills, A. J., Hintsa, E. J., Hoffman, A., Hornbrook, R. S., Huey, L. G., Hughes, S., Jimenez, J. L., Johnson, B. J., Katich, J. M., Keeling, R. F., Kim, M. J., Kupc, A., Lait, L. R., Lamarque, J.-F., Liu, J., McKain, K., Mclaughlin, R. J., Meinardi, S., Miller, D. O., Montzka, S. A., Moore, F. L., Morgan, E. J., Murphy, D. M., Murray, L. T., Nault, B. A., Neuman, J. A., Newman, P. A., Nicely, J. M., Pan, X., Paplawsky, W., Peischl, J., Prather, M. J., Price, D. J., Ray, E. A., Reeves, J. M., Richardson, M., Rollins, A. W., Rosenlof, K. H., Ryerson, T. B., Scheuer, E., Schill, G. P., Schroder, J. C., Schwarz, J. P., St.Clair, J. M., Steenrod, S. D., Stephens, B. B., Strode, S. A., Sweeney, C., Tanner, D., Teng, A. P., Thames, A. B., Thompson, C. R., Ullmann, K., Veres, P. R., Vieznor, N., Wagner, N. L., Watt, A., Weber, R., Weinzierl, B., Wennberg, P. O., Williamson, C. J., Wilson, J. C., Wolfe, G. M., Woods, C. T., and Zeng, L. H.: ATom: Merged Atmospheric Chemistry, Trace Gases, and Aerosols, ORNL DAAC, Oak Ridge, Tennessee, USA, https://doi.org/10.3334/ORNLDAAC/1581, 2018. a
Wofsy et al.: HIAPER Pole-to-Pole Observations (HIPPO): fine-grained, global-scale measurements of climatically important atmospheric gases and aerosols, Philos. T. Roy. Soc. A, 369, 2073–2086, https://doi.org/10.1098/rsta.2010.0313, 2011. a