Improvements to a laser-induced fluorescence instrument for measuring SO2 – impact on accuracy and precision
This work describes key improvements made to the in situ laser-induced fluorescence instrument for measuring sulfur dioxide (SO2) that was originally described by Rollins et al. (2016). Here, we report measurements of the SO2 fluorescence emission spectrum. These measurements allow for the determination of the most appropriate bandpass filters to optimize the fluorescence signal, while reducing the instrumental background. Because many aromatic species fluoresce in the same spectral region as SO2, fluorescence spectra were also measured for naphthalene and anisole to determine if ambient SO2 measurements could be biased in the presence of such species. Improvement in the laser system resulted in better tunability, and a significant reduction in the 216.9 nm laser linewidth. This increases the online/offline signal ratio which, in turn, improves the precision and specificity of the measurement. The effects of these improvements on the instrumental sensitivity were determined by analyzing the signal and background of the instrument, using varying optical bandpass filter ranges and cell pressures and calculating the resulting limit of detection. As a result, we report an improvement to the instrumental sensitivity by as much as 50 %.
Sulfur dioxide (SO2) is responsible for a number of health and environmental impacts. Through reaction with the hydroxyl radical (OH), SO2 produces sulfuric acid, which affects the pH of aqueous particles and leads to acid deposition. Sulfuric acid also condenses onto organic and black carbon particles, producing sulfate, which increases the aerosol hygroscopicity and influences the accumulation of aerosol liquid water (Fiedler et al., 2011; Carlton et al., 2020). Sulfuric acid is believed to be the most important source gas globally for homogeneous nucleation and growth of new aerosol particles, which may occur primarily in the tropical upper troposphere (Brock et al., 1995; Dunne et al., 2016; Williamson et al., 2019). SO2 and sulfate particles can be transported long distances, driving the production of haze pollution in areas downwind of SO2 emissions (Andreae et al., 1988). Both the direct radiative forcing from aerosol and the indirect forcing from aerosol–cloud interactions are important for climate. While both tend to produce an offset to greenhouse-gas-induced warming by reducing incoming shortwave radiation, the effect of aerosol–cloud interactions is complicated and produces large uncertainties in climate models (Finlayson-Pitts and Pitts, 2000; IPCC, 2021). Changing emissions distributions, coupled with an incomplete understanding of the chemistry and microphysics associated with sulfur and aerosol formation in the atmosphere, necessitates further studies which require precise and accurate measurements of SO2 throughout the troposphere and lower stratosphere.
Regulation of anthropogenic emissions has resulted in decreased atmospheric SO2 concentrations in the United States and Europe since the 1970s. However, during the early 21st century, emissions began increasing dramatically in Asia as a result of increased fossil fuel burning (Smith et al., 2011; Hoesly et al., 2018). The main source of SO2 to the troposphere is through direct emission, followed by oxidation of dimethyl sulfide (DMS). The remaining pathways of SO2 formation, H2S, CS2, and carbonyl sulfide (OCS) oxidation, contribute negligible fluxes (Feinberg et al., 2019). As of 2014, global emission rates of SO2 were reported to be approximately 113 Tg S yr−1 – more than double the flux during the 1950s (Hoesly, et al., 2018). Anthropogenic sources of sulfur, mainly from fossil fuel combustion and smelting, are the largest global sources of SO2 to the atmosphere and, as of the year 2000, comprised around 67 % of total global SO2 emissions (Feinberg et al., 2019; Lee et al., 2011; Smith et al., 2011). Biogenic sources make up a small but significant fraction of SO2 emissions, with the majority derived from marine phytoplankton, in the form of dimethyl sulfide, which exhibits a global source rate that is approximately 26 % of total global SO2 input (Lee et al., 2011; Feinberg et al., 2019).
Although global emission rates of SO2 have continued to decrease since the early 21st century, atmospheric sulfur concentrations are expected to be affected by continued climate change and could represent feedback mechanisms within the climate system. Due to reductions in sulfur deposition, Hinckley et al. (2020) found that farmers in the United States need to apply sulfur-containing fertilizer to croplands to enhance nitrogen uptake to plants at a rate of 20–300 kg S yr−1. In addition, Kesselmeier et al. (1993) reported that terrestrial sources of sulfur exhibit behavior similar to monoterpenes in that they are light and temperature dependent. This suggests that increasing sulfur emissions are likely to occur as global temperatures continue to rise. Lastly, the effect of climate warming on the variability in moisture conditions, and increased land use change, is expected to increase both the frequency and duration of biomass burning events, which are expected to further increase sulfur emissions (Westerling et al., 2006; Heyerdahl et al., 2002). In conjunction, while fossil fuel burning sources of SO2 are continuing to decrease, it is likely that these climate-related and additive sources may keep SO2 emissions from returning to preindustrial levels.
Even small SO2 mixing ratios can produce important effects. Remote regions, including much of the equatorial marine boundary layer, exhibit mixing ratios of SO2 of the order of 100 ppt (parts per trillion). Still, in these regions, the biogenic SO2 may be the primary source of cloud condensation nuclei. In addition, convective transport from these regions into the tropical tropopause layer can allow these small sources to reach the lower stratosphere. Sulfate aerosol lifetimes in the stratosphere are approximately 100 times that of aerosol within the lower troposphere, allowing them to persist for 1–2 years (Holton et al., 1995). As a result, sources of sulfate aerosol and aerosol precursor species reaching the UT/LS (upper troposphere; lower stratosphere) are disproportionately important for climate compared to short-lived aerosols in the lower troposphere. However, to date, few studies have reported measurements of SO2 in the UT/LS (Inn et al., 1981; Georgii and Meixner, 1980; Rollins et al., 2017, 2018). Understanding in detail the impact that SO2 has on the stratosphere is only becoming increasingly important as discussions of albedo modification by injection of SO2 into the stratosphere are becoming more common (National Research Council, 2015).
Despite the potential implications that changing SO2 concentrations present in the UT/LS and the remote lower troposphere, few in situ measurements are routinely made in either of these areas. Most direct measurements have been made through the use of pulsed fluorescence instruments which are available commercially; however, this technique tends to exhibit interferences from other fluorescent species and limited precision. Most measurements of SO2 with parts per trillion by volume (pptv SO2) precision have been made using chemical ionization mass spectrometry (CIMS). Many CIMS SO2 ionization chemistry schemes can be sensitive to variations in ambient water vapor, complicating tropospheric measurements (Huey et al., 2004; Eger et al., 2019). Operation of CIMS instruments on unpressurized aircraft capable of reaching the tropical lower stratosphere (>17 km) is also challenging from an engineering perspective.
As an alternative, the development of a compact, in situ laser-induced fluorescence (LIF)-based SO2 instrument was recently reported by Rollins et al. (2016), with a 1σ precision of 2 ppt over a 10 s integration period. That technique was developed and originally used to quantify SO2 in the UT/LS region on two NASA WB-57F missions, namely VIRGAS (Volcano-plume Investigation Readiness and Gas-phase and Aerosol Sulfur ) in 2015 and POSIDON (Pacific Oxidants, Sulfur, Ice, Dehydration, and cONvection) in 2016. In the UT/LS ,where potentially interfering fluorescent species (e.g., aromatic compounds) are in negligible concentrations, the instrument was used in a mode where the excitation laser was maintained on an SO2 resonance, and the optical background was determined using periodic SO2-free zero-air additions. However, it is expected that LIF measurements of SO2 in the more complex chemical environment of the troposphere, and especially in areas where fossil fuel combustion is occurring and through biomass burning plumes, might result in interferences from species, including aromatics, that are also formed during these processes. Prior to the deployment of the instrument on a NASA Global Hawk mission in 2017 (HOPE-EPOCH), the LIF instrument was improved to allow for rapid dithering of the excitation laser on and off an SO2 resonance and to allow for continuous discrimination of SO2 from other fluorescent species. It was also operated this way during the NASA ATom-4 (Atmospheric Tomography Mission) in 2018 and the NASA/NOAA Fire Influence on Regional to Global Environments Experiment – Air Quality (FIREX-AQ) experiment in 2019. Following ATom-4, it has been investigated how further improvements to the detection of SO2 might be accomplished by quantifying the spectral region of SO2 fluorescence for separation from scattering and identification of fluorescence emissions from potentially interfering aromatic species. Here, we report on these recent improvements and use of the instrument.
2.1 SO2 spectroscopy
Fluorescence occurs during the radiative relaxation of a molecule after its absorption of a photon. Thus, the LIF signal is proportional to the molecular absorption cross section at the laser wavelength and the quantum yield for fluorescence. A study by Manatt and Lane (1993) compiled numerous measurements of SO2 absorption cross sections over varying wavelengths to find six absorption bands between 100 and 400 nm. Because strong absorption by oxygen (O2) occurs below 200 nm, the three spectral regions between 200 and 400 nm are most appropriate for atmospheric measurements of SO2. Excitation into the B2) state, with a wavelength region of 170–235 nm, is typically chosen for SO2 fluorescence detection due to the higher absorption cross section and fluorescence quantum yield compared to longer wavelengths. Pumping into the B or A bands (λ>240 nm), while useful for absorption measurements, results in negligible fluorescence. Another consideration is the predissociation threshold near 218.7 nm (Bludský et al., 2000). As a result, pumping at wavelengths less than ∼215 nm results in negligible fluorescence. Considering the absorption cross section and fluorescence quantum yields, excitation at 220.6 nm is theorized to produce the maximum detectable signal using LIF (Rollins et al., 2016).
Due to the limited availability of practical laser technology for airborne instrumentation, Rollins et al. (2016) targeted a band head at 216.9 nm through the use of the fifth harmonic produced from a tunable 1084.5 nm fiber-amplified diode laser. The detected fluorescence was selected using a long-pass filter (Thorlabs FGUV5) in combination with a bandpass filter (Asahi XUV0400), allowing transmission of the red-shifted fluorescence in the wavelength region of 240–400 nm. A more detailed description of the LIF SO2 instrument can be found in Rollins et al. (2016). Generally, while precision sufficient for measurements in the UT/LS was achieved (2 ppt over 10 s integration period), the detection limit was primarily controlled by the background from scattered photons, and it was anticipated that, in polluted regions where other fluorescent species exist, the detection limit might be further degraded due to these additional sources of background.
2.2 Laser subsystem improvements
The SO2 instrument uses a custom-built fiber laser system. Pulses from a fiber-coupled tunable diode laser near 1084.5 nm are used to seed a fiber amplifier system. Originally, the seed laser operated in a gain-switching mode, where short pulses of current injected into the seed laser generated the ∼1 ns optical output pulses. In the present design, the seed laser is instead operated in a constant current mode, and its output is modulated using a fiber-coupled electro-optic modulator (EOM). The EOM can produce pulses of less than 1 ns full width at half maximum and with an extinction ratio of 40 dB. While the original design was somewhat simpler to operate than the present design, gain-switching of the seed laser significantly broadened the laser spectrum and eliminated the possibility of tuning the laser wavelength by modulating the seed laser injection current. Instead, the wavelength of the system was tuned by adjusting the temperature of the seed laser, which had a settling time of the order of seconds. The new design is also operated at a laser repetition rate of 200 kHz instead of the 25 kHz of the original design. This reduces the peak power leading to less spectral broadening within the fibers and also increases the dynamic range of the single-photon-counting LIF signal to 200 kHz rather than 25 kHz. While less UV laser power is achieved with the higher repetition rate and lower pulse energy, the overall sensitivity to SO2 improves because the SO2 spectrum can now be fully resolved, which increases the convolution of the SO2 spectrum with the laser spectrum.
Output from the fiber amplifier is passed through three nonlinear crystals (KTP, LBO, and BBO), in the same configuration as described by Rollins et al. (2016), to produce the fifth harmonic of the fiber output at 216.9 nm with, typically, 1 mW of power. Overall, injecting the seed laser at constant current and operating the amplifier with lower peak powers results in a significantly narrower laser linewidth. Due to the narrower laser linewidth, the Doppler-broadened SO2 spectrum can now be fully resolved (Fig. 1). This significantly increases the effective SO2 absorption cross section. The laser wavelength can also be tuned rapidly to measure on and off an SO2 resonance many times for each second, which eliminates spectral interferences from other fluorescent species (Fig. 2).
2.3 Fluorescence background
Signal on the detector may result from SO2 fluorescence or from a host of other sources. These include Rayleigh, Raman, or aerosol scattering or fluorescence from the LIF chamber or windows and red-shifted fluorescence from other gases and aerosols in the sample. Because the SO2 absorption spectrum has a fine structure, the signal from SO2 can selectively be reduced by more than 1 order of magnitude by tuning the laser less than 10 pm off an SO2 resonance (Fig. 1). All other sources of photons, however, are expected to have no appreciable structure at this spectral resolution. Therefore, the signal from SO2 can accurately be distinguished from other photon sources by constantly tuning the laser on and off an SO2 resonance.
The instrumental precision, however, is determined by the Poisson counting statistics of the sum of the SO2 fluorescence and background signals which, at low SO2 mixing ratios, is dominated by the non-SO2 count rate. Therefore, the detection limit is determined by these background sources of photons.
Knowledge of the SO2 emission spectrum is key for choosing detection bandpass filters to maximize the SO2 signal, while minimizing the detection of photons from non-SO2 sources. While the Rayleigh and Raman scatter by N2 and O2 occur at constant and known wavelengths, red-shifted fluorescence from other gases and aerosols may vary by compound. Many aromatic species have been reported to have non-negligible absorption cross sections and fluorescence quantum yields when pumped near 216.9 nm. Because aromatics and SO2 are co-emitted during combustion of many fuels, it is important to understand the affect they may produce on ambient LIF SO2 measurements.
While many aromatics are released during combustion, two compounds reported as having large emission ratios and significant absorption cross sections at 216.9 nm are naphthalene and anisole (Grosch et al., 2015; Koss et al., 2018; Mangini et al., 1967; Warneke et al., 2011). Emission ratios of these compounds are dependent on the type of combustion, fossil fuel, or biomass and the elements involved in the combustion. Naphthalene is released through both fossil fuel combustion and biomass burning, with the latter producing an emission ratio greater than 1 ppb ppm CO (ppb – parts per billion; ppm – parts per million; carbon monoxide; Warneke et al., 2011). Anisole is primarily released through biomass burning, with an emission ratio reported in combination with cresol as 1.5 ppb ppm CO (Koss et al., 2018). The absorption cross sections reported for these compounds near 216.9 nm are cm2 molecule−1 for naphthalene (Grosch et al., 2015) and cm2 molecule−1 for anisole (Mangini et al., 1967). With the emission ratio of SO2 being similar to these aromatics, in addition to similar absorption cross sections, it is anticipated that aromatics could significantly interfere with ambient SO2 measurements. To optimize the detection of the fluorescence spectral region for SO2, we measured the spectral distributions of the fluorescence emission from SO2, naphthalene, and anisole.
The optical bench used for the LIF SO2 detection is shown in Fig. 3. The 216.9 nm laser, approximately 1 mW, enters the cell perpendicular to the entrance of the sampled air. Sampled air (2500 standard cubic centimeters per minute – sccm) enters the system through a custom butterfly valve machined from PEEK (polyether ether ketone) that reduces the pressure to 170 mbar, which shows minimal change through the sample cell. The majority of the gas exits the sample cell opposite to the inlet, while 250 sccm is exhausted through each of the cell side arms to eliminate dead space in the flow system. Detection of the fluorescence is then measured orthogonally to both the sample flow and laser axes. A UV-fused silica aspheric lens (Edmund Optics; numerical aperture of 0.5) is used to collect approximately 10 % of the solid angle relative to the center of the cell. After passing through the measurement cell, the beam passes through a LIF reference cell with a similar arrangement to the measurement cell. A constant flow with a mixing ratio near 500 ppb SO2 is maintained in the reference cell. Feedback from the reference cell is used to ensure that the laser is tuned to the SO2 resonance peak and to quantify any changes in the instrument sensitivity due to changes in the laser spectrum. The exhausts of the measurement and reference cells are tied together, such that small perturbations in the system pressure will also be equally observed in the two cells. A National Instruments CompactRIO (cRIO) computer system is used for controlling all timing requirements. This includes the timing of the seed laser pulses, amplification, and photon counting and gating.
For measurements of the fluorescence emission spectra of SO2 and aromatic compounds, the entrance of a round-to-linear fiber optic bundle (ThorLabs FG105UCA) was placed at the focal point of the lens where the fluorescence-detecting photomultiplier tube (PMT) is typically located. The emission from the linear end of the fiber bundle was focused by a collimating lens (74-UV; Ocean Insight) onto the entrance slit of a scanning monochromator (Acton Research Corporation; model VM-502). Measurements were made with the monochromator in the V configuration, with slit sizes of 4 mm wide, using a Hamamatsu photomultiplier tube (H12386-210) connected at the exit of the monochromator.
In order to measure the SO2 fluorescence spectrum, a flow of 46 sccm from a 5 ppm SO2 gas cylinder (Scott-Marrin, Inc.) was mixed with 2500 sccm zero air, producing a concentration of approximately 90 ppb that was sampled into the cell. Figure 4a shows the observed spectrum in the presence (red) and absence (orange) of SO2. The signal observed at 202–236 nm, in the absence of SO2, is primarily from Rayleigh scatter of the laser, and the observed width is a measure of the spectral resolution of the experimental setup. Figure 4b shows just the SO2 fluorescence calculated after the subtraction of the background.
To verify the calibration and spectral resolution of the monochromator, a low-pressure, double-bore mercury (Hg) capillary lamp (Jelight Company Inc.) was positioned in front of the fiber as a spectral reference. The atomic Hg emission spectrum, from 200 too 500 nm, was measured using the monochromator to calibrate the monochromator and show that the monochromator fiber setup produces a spectral resolution with a full width half max (FWHM) of approximately 20 nm. Figure 4 shows that the SO2 fluorescence emission spectrum appears to occur in two regions. The main peak is centered around 302 nm and produces a FWHM value of 63 nm in our setup. A second peak may exist between 350–360 nm; however, it is not possible to accurately determine the peak position nor the width in this setup. Using the monochromator with relatively wide slits was necessary to achieve enough signal to measure the fluorescence emission spectrum in our setup, and this somewhat exaggerates the width of the emission spectrum in Figs. 4–6.
Measurements were similarly made with the aromatic compounds. Zero air was passed through the headspace of a vial containing a sample of pure (>99 %) crystalline naphthalene (Sigma-Aldrich), which has a vapor pressure of 0.04 mbar at 298 K. This resulted in a naphthalene concentration of approximately 3.6 ppm when the flow through the vial was 100 sccm and the total flow through the instrument was 1300 sccm. Liquid anisole (Sigma-Aldrich), with a vapor pressure of 5 mbar at 298 K, was similarly used to produce a concentration of approximately 26 ppm when the flow through the vial was 10 sccm and the total flow was 2260 sccm (Ambrose et al., 1976). A comparison of the fluorescence spectra of the aromatic compounds to the SO2 fluorescence spectrum is shown in Fig. 5.
Anisole produces a similar fluorescence spectrum to the main SO2 emission peak, with a maximum at 304 nm. The FWHM of 46 nm occurs between 286 and 332 nm, which is the latter half of the largest SO2 fluorescence peak. Similarly, naphthalene produces a fluorescence spectrum peaking at around 340 nm, with a FWHM value of 46 nm, which slightly overlaps with the tail end of the largest SO2 fluorescence peak and nearly completely overlaps with the second SO2 region.
Figure 5 shows that aromatic compounds could produce significant signal in the SO2 instrument during measurements in polluted environments. While naphthalene has a similar absorption cross section and rate of collisional quenching to SO2, its low-pressure fluorescence quantum yield has been reported to be 2–3 times larger due to a lower expected rate of photodissociation as a result of a larger dissociation energy threshold (Hui and Rice, 1973; Martinez et al., 2004; Reed and Kass, 2000; Suto et al., 1992). However, the observed naphthalene signal in our experiment is approximately 30 times lower than SO2. Because of its reduced rate of photodissociation, the fluorescence lifetime of naphthalene (340 ns) is much greater than that of SO2 (30 ns; Hui and Rice, 1973; Martinez et al., 2004). Therefore, the short counting gate used in this work for SO2 detection (25 ns) discriminates the majority of the naphthalene signal from that of SO2.
No difference in the fluorescence emission (intensity or spectral distribution) was observed for the aromatic compounds with the laser tuned on or off the SO2 resonance. This is consistent with expectations based on the literature, as absorption cross sections for those compounds show no fine structure comparable to the features in the SO2 spectrum (Keller-Rudek et al., 2013). Therefore, these compounds would only increase the instrument background, resulting in reduced precision, and would result in unbiased ambient SO2 measurements in areas of high aromatic concentrations.
In order to achieve the highest sensitivity and lowest limit of detection, the impact of the fluorescence-detection bandpass filters was further investigated. With the instrument in its normal configuration for measuring SO2 (PMT photocathode located at focal point of fluorescence collection lens), different bandpass filters were used in front of the detection cell PMT to directly measure the SO2 fluorescence signal and quantify the background scatter over a few discrete regions of the spectrum. Figure 6 shows the fluorescence spectrum (red) and background (orange) observed using the monochromator scaled to the count rates observed with each of the tested filters. It was observed that the background increases with wavelength until around 300 nm. After this point, the background slowly decreases, reaching a minimum around 400 nm before increasing again near 420 nm. The boxes and closed circles are indicative of the filter measurements. The heights of the boxes indicate the fluorescence signal observed, and the width shows the range in which transmission was achievable with the filter. The closed circles indicate the background observed with the filter of the corresponding color.
To optimize the SO2 detection limit in zero air, the detection limit was calculated from the scaled SO2 fluorescence and background spectra, using a theoretical bandpass filter, assuming a low pass of 246 nm and a variable high pass limit, where 100 % transmission is observed in the pass band and 0 % transmission elsewhere. The detection limit was calculated with the filter high pass limit at 270 nm and in increasing increments of 10 nm to the full spectrum at 500 nm. Figure 7 shows the results of this calculation as a function of the high pass filter limit. As the upper end of the pass band is initially increased from 250 to 300 nm, the calculated detection limit rapidly decreases due to significant gains in signal relative to background here. A minimum in the SO2 detection limit occurs over the range of 350–450 nm, with a theoretical detection limit as low as 1.8 ppt over a 1 s integration period. For polluted environments where 1 ppb of naphthalene may be present, the detection limit would increase by 20 % within this detection range due to the increased background from naphthalene fluorescence.
The dielectric bandpass filter that we have used previously for SO2 measurements in the atmosphere (Asahi XUV0400) efficiently reduces signal from Rayleigh scatter, and we find that the additional inclusion of the absorptive glass filter (Thorlabs FGUV5) originally used with this instrument is no longer necessary. Removal of the FGUV5 filter allows for greater transmission within the SO2 fluorescence spectrum range and provides the largest signal-to-noise ratio of the sampled bandpass filters. However, the transmission is still limited to 80 %–95 % with the Asahi XUV0400 filter alone in comparison to the theoretical filter. This results in a detection limit of approximately 3.4 ppt over a 1 s integration period, as shown by the marker in Fig. 7. Testing showed that the detection limit decreases with increasing pressure up to at least 250 mbar (Fig. 8). Because predissociation limits the SO2 fluorescence lifetime to ∼5 ns, the fluorescence quantum yield is rather insensitive to pressure in this regime, and therefore, the signal increases linearly with pressure due to the increased number density of SO2. While these measurements were performed under dry conditions, ambient measurements are expected to produce similar results because the short fluorescence lifetime will also limit the importance of collisional quenching by water vapor (Rollins et al., 2016). As a result, the detection limit can be reduced by approximately 15 % by increasing the cell pressure to around 250 mbar. While this is beneficial for measurements in the lower troposphere, UT/LS measurements will require the cell pressure to remain less than 100 mbar in order for the instrument to maintain an adequate flow rate.
Typical mixing ratios of ozone that can be encountered during stratospheric sampling are not anticipated to affect the SO2 LIF signal. However, due to the relatively high quantum yield for SO2 photolysis at 216.9 nm, forming primarily sulfur monoxide (SO), the possibility of significantly enhancing the LIF signal through the chemiluminescent reaction of SO with ozone was investigated using higher ozone mixing ratios (Hui and Rice, 1972; Okabe, 1971; Ryerson et al., 1994). Figure 9 shows the observed LIF signal in the presence of significant additions of ozone to the inlet. At ozone additions up to 2000 ppm, small increases in LIF signal were observed with increasing O3 (2 % LIF signal ppm O3). This further demonstrates that, at stratospheric O3 mixing ratios accessible by aircraft (<5 ppm), the signal changes by <10 %. At O3 above 2000 ppm, significant decreases in the LIF signal were observed. We attribute these decreases to photolysis of O3 at 216.9 nm, followed by destruction of SO2 by fast reaction ( cm3 molecule−1 s−1) with the atomic oxygen produced by O3 photolysis (Sander et al., 2011).
With the instrument configured with the typical bandpass filter (Asahi XUV0400), and at a pressure of 170 mbar, calibrations were performed to assess the impact of the improvements on the precision of the SO2 measurement. Calibrations of the instrument are performed in which a mixture of zero air and SO2 standard are introduced to the instrument, with a mixing ratio range of around 1.6–8 ppb SO2. This mixture is comprised of a flow of 1–5 sccm of 5 ppm SO2, with 3000 sccm zero air which has passed through a KMnO4 scrubber, removing any SO2 that may be present in the zero air.
An example of the new calibration is shown in Fig. 10. Typical sensitivity is 26 counts per second (CPS) per ppt for SO2 and 1000 CPS of background. Thus, the background is a photon count rate equivalent to 38 ppt of SO2. In our previous work (Rollins et al., 2016), we reported an in-flight background of 480 CPS and sensitivity of 4.1 CPS per ppt or a background equivalent to 117 ppt of SO2. Therefore, the signal relative to background has increased threefold, which we attribute primarily to the narrower laser linewidth in the new configuration. With the new signal level, the 1σ detection limit for 1 Hz measurements is 3.4 ppt. For 10 s of integration time, the detection limit would be 1.1 ppt, which is nearly half of what we previously stated for 10 s of integration.
During the NASA ATom-4 field campaign, measurements of SO2 were acquired by both the LIF instrument and the California Institute of Technology chemical ionization mass spectrometer (CIT CIMS) instrument. ATom-4 sampled primarily pristine air masses with a limited number of measurements of ship emissions, biomass burning plumes, and volcanic emissions. This allowed for the first in situ comparison between the current LIF technique and another SO2 measurement method. CIT CIMS uses fluoride ion transfer chemistry from CF3O− reagent ion (e.g., ), followed by mass spectral analysis using a compact time-of-flight mass spectrometer (CToF) with typical mass resolution of m m =1200. The precision of CIMS measurements degrades with increasing water vapor concentration because of the rising interference of the formic acid signal () which has a mass that differs from SO2 by only 0.054 Da. In the marine boundary layer, when water vapor was ppm, the CIMS SO2 precision (1σ standard deviation over a 1 s integration period) is larger than 130 ppt, a value greater than the typical SO2 concentration (<100 pptv) as reported by the LIF instrument. Therefore, CIMS measurements, when water vapor was ppm, are excluded from the comparison. Figure 11a shows an orthogonal regression of both measurements from ATom-4 at 10 s time resolution. Overall, an excellent correlation was observed between the two instruments (R2=0.99). Furthermore, measurements during FIREX-AQ acquired during smoke plume penetration again show excellent correlation between the CIT CIMS and SO2 LIF instruments (Fig. 11b). This indicates that aromatic compounds are not biasing the SO2 LIF measurements. The CIMS instrument reported 12 % and 10 % lower SO2 than LIF during the ATom-4 and FIREX-AQ missions, respectively. While these are within the combined uncertainties of the measurements, it indicates a systematic calibration error with one or both of the instruments that has not been resolved at this time.
Rollins et al. (2016) reported a new, in situ method for measuring SO2 in the UT/LS using LIF. Here, we report improvements to the technique that allow for measurements in polluted areas containing other fluorescent species and an overall reduction in the detection limit. This was accomplished by limiting non-SO2 fluorescence background sources and by improvements in the linewidth and tunability of the laser system. Similar to SO2, aromatic species are largely emitted during combustion processes, many of which have large absorption cross sections near 216.9 nm and significant fluorescence quantum yields. To determine the effect of these compounds on measuring SO2, the fluorescence spectra of SO2, and two aromatic compounds, naphthalene and anisole, were measured. While strong overlap was exhibited in the fluorescence spectra of these aromatic species with SO2, the excitation spectrum of SO2 has a fine structure near 216.9 nm while the excitation spectra of the aromatics is relatively invariant near 216.9 nm. Therefore, these compounds will only increase the background, slightly reducing the precision of the instrument, but will not result in biased SO2 measurements. Similar consequences for the LIF SO2 measurements are expected from other aromatic species, since those species generally do not have a fine structure in their excitation spectra.
The SO2 fluorescence spectrum was also used to determine the bandpass filter application that would best limit the amount of scatter observed and provide the best limit of detection. Using a theoretical bandpass filter, with transmission beginning at 246 nm, the ending transmission range, in which the lowest detection limit is expected, is 350–450 nm. This is expected to result in a detection limit of 1.8 ppt. Using the Asahi XUV0400 bandpass filter, we are able to reach a detection limit of 3.4 ppt.
Improvements in the laser system are responsible for significant performance improvements over our previous work. Here, we reduced the laser linewidth, which increased the LIF signal by nearly a factor of 3. The laser wavelength is now controlled by current tuning of the laser, which can be performed rapidly, allowing for measurements of online and offline fluorescence signals many times in a second. This eliminates the possibility of spectral interferences from other species such as aromatics. Increasing the laser repetition rate from 25 to 200 kHz also greatly increased the dynamic range.
While it is shown that increasing the cell pressure to around 250 mbar would reduce the limit of detection by approximately 15 %, this higher cell pressure can only be used in the lower troposphere. Measurements in the UT/LS will require the cell pressure to be operated near 40–50 mbar. It was also demonstrated that increased ozone concentrations observed in the UT/LS would not significantly influence LIF SO2 measurements. The resulting production of O(1D) does not become large enough to decrease SO2 within the sampling cell until reaching ozone concentrations greater than 4000 ppm, more than 2 orders of magnitude greater than stratospheric ozone concentrations.
The culmination of these changes to the LIF SO2 instrument has resulted in an increased instrumental sensitivity and lower limit of detection. Calibrations suggest that the instrumental sensitivity has improved by approximately 3 times, relative to the background, from that reported in Rollins et al. (2016). Comparison with measurements performed by the CIT CIMS instrument during the NASA ATom-4 and FIREX-AQ campaigns demonstrated good agreement. These results suggest that the LIF SO2 instrument is highly suitable for measurements in both polluted and pristine environments.
The data collected for FIREX-AQ are available from the NASA/NOAA FIREX-AQ data archive at https://www-air.larc.nasa.gov/cgi-bin/ArcView/firexaq (last access: 23 April 2019, NASA/NOAA, 2019). The data collected for ATom-4 are available from the NASA ESPO data archive at https://espoarchive.nasa.gov/archive/browse/atom/id14 (last access: 23 April 2019, NASA, 2019).
The research was designed by PSR and AWR. Measurements were taken by PSR, AWR, LX, JDC, and POW. The paper was written by PSR, with contributions from all coauthors.
The authors declare that they have no conflict of interest.
We would like to thank the NASA DC-8 crew and management team for their support during ATom-4 and FIREX-AQ integration and flights. We thank Michelle Kim and Hannah Allen for operating CIT's CIMS instrument during ATom-4.
This research was funded by the ATom investigation, under NASA's Earth Venture program, and the FIREX-AQ investigation, under NASA's Atmospheric Compostion: Upper Atmospheric Composition Observations program CE8 (CIT grant nos. NNX15AG61A and 80NSSC18K0660, respectively).
This paper was edited by Dwayne Heard and reviewed by two anonymous referees.
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