O2 : CO2 exchange ratio for net turbulent flux observed in an urban area of Tokyo, Japan, and its application to an evaluation of anthropogenic CO2 emissions
- 1National Institute of Advanced Industrial Science and Technology (AIST), Tsukuba 305-8569, Japan
- 2Department of Earth and Ocean Sciences, National Defense Academy of Japan, Yokosuka 239-8686, Japan
- 3National Institute for Environmental Studies, Tsukuba 305-8506, Japan
- 4Meteorological Research Institute, Tsukuba 305-0052, Japan
Correspondence: Shigeyuki Ishidoya (email@example.com)
In order to examine O2 consumption and CO2 emission in a megacity, continuous observations of atmospheric O2 and CO2 concentrations, along with CO2 flux, have been carried out simultaneously since March 2016 at the Yoyogi (YYG) site located in the middle of Tokyo, Japan. An average O2 : CO2 exchange ratio for net turbulent O2 and CO2 fluxes (ORF) between the urban area and the overlaying atmosphere was obtained based on an aerodynamic method using the observed O2 and CO2 concentrations. The yearly mean ORF was found to be 1.62, falling within the range of the average OR values of liquid and gas fuels, and the annual average daily mean O2 flux at YYG was estimated to be −16.3 µmol m−2 s−1 based on the ORF and CO2 flux. By using the observed ORF and CO2 flux, along with the inventory-based CO2 emission from human respiration, we estimated the average diurnal cycles of CO2 fluxes from gas and liquid fuel consumption separately for each season. Both the estimated and inventory-based CO2 fluxes from gas fuel consumption showed average diurnal cycles with two peaks, one in the morning and another one in the evening; however, the evening peak of the inventory-based gas consumption was much larger than that estimated from the CO2 flux. This can explain the discrepancy between the observed and inventory-based total CO2 fluxes at YYG. Therefore, simultaneous observations of ORF and CO2 flux are useful in validating CO2 emission inventories from statistical data.
Precise observation of the atmospheric O2 concentration (O2∕N2 ratio) has been carried out since the early 1990s to elucidate the global CO2 cycle (Keeling and Shertz, 1992). The approach is based on the –O2 : CO2 exchange ratios (oxidative ratio; OR = – mol mol−1) for the terrestrial biospheric activities and fossil fuel combustion. The OR value of 1.1 has been used widely for the terrestrial biospheric O2 and CO2 fluxes (Severinghaus, 1995). On the other hand, the ORs of 1.95 for gaseous fuels, 1.44 for oil and other liquid fuels, and 1.17 for coal or solid fuels are usually used (Keeling, 1988). Therefore, OR is a useful indicator of cause(s) of the observed variations in the atmospheric O2 and CO2 concentrations. The atmospheric CO2 concentration has been observed not only at remote sites such as Mauna Loa (19.5∘ N, 155.6∘ W), Hawaii, USA, to capture a baseline variation in the background air (e.g., Keeling et al., 2011), but also recently in urban areas to estimate CO2 emissions locally from fossil fuel combustion (e.g., Mitchell et al., 2018; Sargent et al., 2018). For the latter purpose, simultaneous observations of the atmospheric O2 and CO2 concentrations should provide important insight into validating the inventory-based CO2 emissions from gaseous, liquid and solid fuels. Steinbach et al. (2011) estimated a global dataset of spatial and temporal variations of OR for the fossil fuel combustion using the EDGAR (Emission Database for Global Atmospheric Research) inventory and fossil fuel consumption data from the UN energy statistics. The statistically estimated OR should be validated by observed OR; however, observations of the atmospheric O2 concentration in urban areas are still limited (e.g., van der Laan et al., 2014; Goto et al., 2013a). Moreover, simultaneous observations of the OR and CO2 flux between an urban area and the overlying atmosphere have never been reported before. Observations of the CO2 flux have been carried out at various urban stations, such as London, UK (Ward et al., 2013), Mexico City, Mexico (Velasco et al., 2009), Beijing, China (Song and Wang, 2012), and Tokyo, Japan (Hirano et al., 2015), allowing us to observe urban CO2 emission directly in the flux footprint. Therefore, if the OR for the net turbulent O2 and CO2 fluxes (hereafter referred to as “ORF”) can be observed, then such information can be used as a useful constraint for evaluating the contributions of the gaseous, liquid, and solid fuels and the terrestrial biospheric activities to the observed CO2 flux. From the measurements, it also becomes possible to observe the urban O2 flux by multiplying the CO2 flux by ORF.
In this paper, we first present the simultaneous observational results of the O2 and CO2 concentrations and the CO2 flux in the urban area of Tokyo, Japan. From a relationship between the vertical gradients of the observed O2 and CO2 concentrations, we derive ORF based on an aerodynamic method (Yamamoto et al., 1999). The present paper follows Ishidoya et al. (2015), who reported ORF for the O2 and CO2 fluxes between a forest canopy and the overlaying atmosphere. We also compare the observed ORF with the OR value of the overlaying atmosphere above the urban canopy (hereafter referred to as “ORatm”) to highlight the characteristics of the O2 and CO2 exchange processes in the urban canopy air at the YYG site. Finally, we estimate the average diurnal cycles of CO2 fluxes from gas and liquid fuel consumption separately by using the ORF, CO2 flux, and inventory-based CO2 emission from human respiration in order to validate the inventory-based CO2 emissions from gas consumption and traffic.
2.1 Site description
In order to observe the atmospheric O2 and CO2 concentrations and CO2 flux between the urban area and the overlaying atmosphere, the instruments were installed on a roof-top tower of Tokai University (52 m above ground, 25 m above roof) at Yoyogi (YYG; 35.66∘ N, 139.68∘ E), Tokyo, Japan. The YYG site is a mid-rise residential area and located in the northern part of Shibuya ward, Tokyo. Figure 1 shows the location of the YYG site and the flux footprints averaged for summer and winter runs, calculated by the model of Neftel et al. (2008). The main land cover around the site is characterized by low- to mid-rise residential buildings with a mean height of 9 m. The population density in this area is 16 600 persons per square kilometer. At the YYG site, the prevailing wind is from SW in the summer and NW in the winter. The flux footprint includes a vegetated area of 9 % in the summer and 2 % in the winter, reflecting seasonal changes in the wind direction.
2.2 Continuous measurements of the atmospheric O2 and CO2 concentrations and CO2 flux
Observations of the atmospheric O2 and CO2 concentrations have been carried out at the YYG site using a continuous measurement system employing a paramagnetic O2 analyzer (POM-6E, Japan Air Liquid) and a non-dispersive infrared CO2 analyzer (NDIR; Li-820, LI-COR) since March 2016. The O2 concentration is reported as the O2∕N2 ratio in per meg:
where the subscripts “sample” and “standard” indicate the sample air and the standard gas, respectively. Because O2 is about 20.94 % of air by volume (Tohjima et al., 2005a), the addition of 1 µmol of O2 to 1 mol of dry air increases δ(O2∕N2) by 4.8 per meg (). If CO2 were to be converted one-for-one into O2, this would cause an increase of 4.8 per meg of δ(O2∕N2), equivalent to an increase of 1 µmol mol−1 in O2 for each 1 µmol mol−1 decrease in CO2. Therefore, the ratio of 4.8 per meg µmol mol−1 was used to convert the observed δ(O2∕N2) to O2 concentration relative to an arbitrary reference point. In this study, δ(O2∕N2) values of each air sample were measured with the paramagnetic analyzer using working standard air that was measured against our primary standard air (cylinder no. CRC00045; AIST scale) using a mass spectrometer (Thermo Scientific Delta-V) (Ishidoya and Murayama, 2014).
Sample air was taken at the tower heights of 52 and 37 m using a diaphragm pump at a flow rate higher than 10 L min−1 to prevent thermally diffusive fractionation of air molecules at the air intake (Blaine et al., 2006). Then, a large portion of the air is exhausted from the buffer, with the remaining air allowed to flow into the analyzers from the center of the buffer. It is then sent to an electric cooling unit with a water trap cooled to −80 ∘C at a flow rate of 100 mL min−1, with the pressure stabilized to 0.1 Pa and measured for 10 min at each height (one-cycle measurements). The method to sample a small subset of air from a high flow rate is similar to those used in Goto at el. (2013b), and we have confirmed that the atmospheric δ(O2∕N2) values observed by the measurement system agree well with those obtained from independent continuous measurements of δ(O2∕N2) using the mass spectrometer (see Fig. 4 in Ishidoya et al., 2017). After nine cycles of measurements (five and four cycles for 37 and 52 m, respectively), high-span standard gas, prepared by adding appropriate amounts of pure O2 or N2 to industrially prepared CO2 standard air, was introduced into the analyzers with the same flow rate and pressure as the sample air and measured for 5 min, and then low-span standard gas was measured by the same procedure. The dilution effects on the O2 mole fraction measured by the paramagnetic analyzer were corrected experimentally, not only for the changes in CO2 of the sample air or standard gas measured by the NDIR, but also for the changes in Ar of the standard gas measured by the mass spectrometer as δ(Ar∕N2). The analytical reproducibility of the δ(O2∕N2) and CO2 concentration achieved by the system was about 5 per meg and 0.06 µmol mol−1, respectively, for 2 min average values. Details of the continuous measurement system used are given in Ishidoya et al. (2017).
It should be noted that we used the gravimetrically prepared air-based CO2 standard gas system with uncertainties of ±0.13 µmol mol−1 on the TU-10 scale (Nakazawa et al., 1991) to determine CO2 concentration in this study. The highest concentration of the gravimetrically prepared standard gas was about 450 µmol mol−1, while CO2 concentrations of more than 600 µmol mol−1 were observed in this study. Therefore, we compared the NDIR-based CO2 concentrations observed in this study with those observed by using cavity ring-down spectroscopy (CRDS; G2401, Picarro) on the NIES-09 scale (Machida et al., 2011) at the YYG site (our unpublished data). Although the highest CO2 concentration of the gravimetrically prepared standard of the NIES-09 scale is similar to that of the TU-10 scale, a slope of 0.974 ppm ppm−1 is derived from a least-squares regression line fitted to the relationship between the CO2 concentrations observed by NDIR on the TU-10 scale and those by CRDS on the NIES-09 scale with a correlation coefficient (r) of 0.978. On the other hand, we obtained a slope of 1.002 per meg per meg−1 (r=0.999) from the regression line fitted to the relationship between the O2 concentrations of gravimetrically prepared standard gases (Aoki et al., 2019) measured by the mass spectrometer on the AIST scale and the gravimetric values of the standard gases covering a much wider range than the atmospheric variations in the O2 concentration. Therefore, the uncertainty in OR due to the span uncertainties of O2 and CO2 concentrations is expected to be within 3 %.
In order to observe the CO2 flux at the YYG site, the turbulence and the turbulent fluctuation of CO2 were observed at 52 m with a high time resolution of 10 Hz by using a sonic anemometer (WindMasterPro, Gill) and an open-path infrared gas analyzer (LI-7500, LI-COR) starting November 2012. The sensors were located at more than 5 times the mean building height (9 m), and then it was above the urban roughness sublayer. Turbulent flux of CO2 was calculated by the eddy correlation method using EddyPro® (Licor) for every 30 min period. Correlations were applied in the calculation for water-vapor density fluctuation (Webb et al., 1980) and mean vertical wind by using the double rotation algorithm (Wilczak et al., 2001). The calculated flux was filtered for data quality based on the steady test and the integral turbulence characteristics in Aubinet et al. (2012). We used the flag 0–2 data in EddyPro® software based on Mauder and Foken (2006).
3.1 Variations in the atmospheric O2 and CO2 concentrations
We show the 10 min average values of the atmospheric O2 and CO2 concentrations observed at the height of 52 m at YYG in Fig. 2. As seen in the figure, O2 and CO2 concentrations vary in opposite phase with each other on timescales ranging from several hours to a seasonal cycle. In general, opposite phase variations of atmospheric O2 and CO2 are driven by fossil fuel combustion and terrestrial biospheric activities. In contrast, the atmospheric O2 variation in µmol mol−1 due to the air–sea exchange of O2 is much larger than that of CO2 on timescales shorter than 1 year (e.g., Goto et al., 2017; Hoshina et al., 2018); this is because the equilibration time for O2 between the atmosphere and the surface ocean is much shorter than that for CO2 due to the influence of the carbonate dissociation effect on the air–sea exchange of CO2 (Keeling et al., 1993). Therefore, we attribute the opposite phase variations in O2 and CO2 observed in this study mainly to fossil fuel combustion and terrestrial biospheric activities. Figure 2 also shows that ΔO2, obtained by subtracting O2 at 41 m from that at 52 m on the tower, varies in opposite phase with the corresponding ΔCO2. High ΔO2 values are more frequently observed in the winter than in the summer, and short-term (several hours to days) decreases in the O2 concentration are intense in the winter.
To examine a relationship between the appearances of high ΔO2 and O2 concentration decrease, detail variations in the O2 and CO2 concentrations, ΔO2 and ΔCO2 for the periods 16–23 December and 1–9 July 2016, are shown in Fig. 3. As seen in the figure, increases in ΔO2 coincide with decreases in O2 concentration in December, especially in the nighttime. Such a coincidence is also seen in July; however, the increases in ΔO2 are much smaller than those in December. Therefore, it is highly likely that O2 is consumed within the urban canopy at YYG, more so in the winter due to an increased usage of gas and/or liquid fuels for heating and to a temperature inversion near the surface. The daily mean CO2 flux from the urban area to the overlaying atmosphere shown in Fig. 2 shows a seasonal cycle with a wintertime maximum, consistent with the enhancement of O2 consumption in the urban canopy.
In this study, we focus on the short-term variations of O2 and CO2 for periods of several hours to days, to elucidate the O2 and CO2 exchange processes between the urban area and the atmosphere by examining two types of OR: one is ORatm calculated from a relationship between the O2 and CO2 concentration values observed at 52 or 37 m and the other one is ORF, for the O2 and CO2 fluxes between the urban area and the overlaying atmosphere, calculated from a relationship between ΔO2 and ΔCO2. The relationships of the O2 and CO2 fluxes with ORF are based on the aerodynamic method of Yamamoto et al. (1999):
Here, FO (FC) (µmol m−2 s−1) represents the O2 (CO2) flux from the urban area to the overlaying atmosphere, K is the vertical diffusion coefficient, and ΔO2Δz−1 (ΔCO2Δz−1) is the vertical concentration gradient of O2 (CO2). The vertical diffusion is a sum of mass-independent eddy and mass-dependent molecular diffusion; however, the effect of molecular diffusion on the observed variations of O2 and CO2 concentrations is generally negligible in the troposphere. It is significant in the stratosphere (e.g., Ishidoya et al., 2013a). Therefore, we used the same diffusion coefficient K for O2 and CO2 in Eqs. (2) and (3), which enabled us to estimate FO by using the observed ΔO2, ΔCO2 and FC as in Eq. (4). In general, ORatm reflects wider footprints of O2 and CO2 than ORF due to horizontal atmospheric transport (Schmid, 1994). We note that the definitions of ORF and ORatm are similar to those of ERF and ERatm, respectively, reported by Ishidoya et al. (2013b, 2015).
In order to calculate ORatm for short-term variations, (1) we applied a best-fit curve consisting of the fundamental and its first harmonics (periods of 12 and 6 months) and a linear trend to the maximum (minimum) values of O2 (CO2) observed at 52 m during the successive 1-week periods and regarded the best-fit curve as its baseline variation; (2) then, the baseline variation of O2 (CO2) concentration was subtracted from the respective O2 (CO2) concentrations observed at 52 m. Figure 4 shows the baseline variations and the variations in the O2 and CO2 concentrations observed at Minamitorishima (MNM; 24.28∘ N, 153.98∘ E), Japan (updated from Ishidoya et al., 2017). MNM is a small and isolated coral island located 1850 km southeast of Tokyo, Japan, and the observation site was operated by the Japan Meteorological Agency (JMA) under the Global Atmosphere Watch program of the World Meteorological Organization (WMO/GAW). The baseline variations of O2 and CO2 at YYG show clear seasonal cycles with peak-to-peak amplitudes of 28 and 16 µmol mol−1, respectively, with a corresponding seasonal maximum and minimum appearing in mid August. The amplitude of the seasonal O2 (CO2) cycle and the appearance of a seasonal maximum (minimum) were found to be larger and earlier, respectively, than those observed at MNM, while the annual average values of the baseline concentration variations of O2 and CO2 at YYG did not differ significantly from those at MNM. These characteristics of the seasonal cycles and the annual average values of the baseline variations at YYG and their comparison with those at MNM are generally consistent with those observed at similar latitude over the western Pacific region (Tohjima et al., 2005b). Therefore, in spite of the fact that the YYG site is located in a megacity, the baseline variations of O2 and CO2 concentrations are similar to those in the background air.
3.2 O2 : CO2 exchange ratio between the urban area and the overlaying atmosphere
Figure 5a shows the relationship between all the ΔO2 and ΔCO2 values to obtain the average ORF throughout the observation period in this study. When errors in both species are non-negligible, a standard least-squares linear regression will give a biased and erroneous slope. Therefore, we apply an unweighted Deming regression analysis to the data (e.g., Linnet, 1993), assuming the ratio between the squared analytical standard deviations to be (ppm ppm−1) to take into account the measurement uncertainties of CO2 and O2 concentrations. We consider the slope obtained by Deming regression to be ORF, but we use a standard deviation obtained from a standard least-squares regression to indicate the uncertainty of the slope. The jackknife method (Linnet, 1990) could be used to derive a standard error for Deming regression; however, by using a short dataset extracted from the observed data used in the present study, we confirmed that the standard deviations obtained from an ordinary regression are larger than the errors from the jackknife method. Therefore, using a standard deviation from ordinary regression is reasonable to ensure larger uncertainty for the ORF. The average ORF value was calculated to be 1.620±0.004 (±1σ). This value falls within the range of the average OR values of 1.44 for liquid fuels and 1.95 for gas fuels, which suggests that the O2 and CO2 fluxes at the YYG site were driven mainly by a consumption of liquid and gas fuels rather than terrestrial biospheric activities of which OR is about 1.1 (Severinghaus, 1995). The relationship between the O2 and CO2 concentration anomalies, calculated by subtracting the respective baseline variations shown in Fig. 4 from the observed O2 and CO2 concentrations, is also shown in Fig. 5b. By applying the Deming regression analysis to the data, we obtained an average ORatm value of 1.541±0.002 (±1σ) throughout the observation period. The ORatm value also falls within the range of the average OR values for liquid fuels and gas fuels. However, the ORatm in this figure is not appropriate in representing the OR for the O2 and CO2 fluxes around the YYG site since it was determined by using the entire 18 months of collected observations that the site is influenced by various trajectories of air masses with a much wider regional signature than the flux footprints. Therefore, we compare below the ORF and ORatm values by changing the aggregation periods to calculate the ORs and examine the validity of using ORF rather than ORatm to evaluate the relationship between the local O2 and CO2 fluxes.
Figure 6 shows examples of the ORF calculated by applying Deming regression fitted to ΔO2 and ΔCO2 values during the successive 12 h periods observed in January 2017 and July 2016. The corresponding ORatm and wind direction observed for the periods are also shown in the figure. As seen in the figure, variabilities in the ORF and ORatm are larger in July than in December. The average ORF, calculated using the OR values within a range of 0.5 to 2.5, were 1.65±0.20 and 1.52±0.32 in the winter (December to February) and summer (July to September), respectively. The corresponding average ORatm values were 1.61±0.15 in the winter and 1.45±0.27 in the summer. To examine the dependency of the OR on the wind direction, we also calculated ORF and ORatm for the periods when the prevailing wind directions were observed to be from 320 to 360∘ (NW) and from 180 to 220∘ (SW) in the winter and summer, respectively. The number of measurements taken during the time of these prevailing winds constituted 30 % (winter) and 8 % (summer) of the total number of measurements. The calculated ORF, ORatm and prevailing winds are shown by blue dots in Fig. 6. The average ORF (ORatm) values, calculated using the OR values within a range of 0.5 to 2.5, were 1.65±0.25 (1.58±0.19) in the winter and 1.58±0.40 (1.42±0.33) in the summer, respectively. Therefore, the average ORF and ORatm calculated using all the values obtained from the 12 h aggregation periods did not differ significantly from those that were calculated using only the data that were associated with the above-mentioned prevailing wind directions. The average ORF seems to be slightly higher than ORatm; however, their uncertainties are too large to discuss the significance of the slight difference. Taking these facts into consideration, we use all the O2 and CO2 concentration data without filtering by the wind direction to increase the number of data points for calculating ORF and ORatm; this is consistent with the purpose of this study to derive representative OR values at the YYG site in order to validate the CO2 emission inventory (Hirano et al., 2015). For analyses of specific events, we have reported analytical results of ORatm and simultaneously measured PM2.5 aerosol composition for a week long pollution event at the YYG site (Kaneyasu et al., 2020).
To examine the seasonal difference between the ORF and ORatm values, we show the ORF values calculated by applying regression lines to 1 d and 1-week successive ΔO2 and ΔCO2 values in Fig. 7. The corresponding ORatm values, obtained by applying Deming regression fitted to successive O2 and CO2 concentration anomalies in Fig. 5b, are also shown. Since there is no statistically significant difference between the two (based on the uncertainties shown in the figure (±1σ)), we focus our discussion on the OR values obtained from the 1-week successive data. Clear seasonal cycles with wintertime maxima are found in both the ORF and ORatm values at YYG. Larger ORatm values in the winter than in the summer in urban areas have been reported by some past studies (e.g., van der Laan et al., 2014; Ishidoya and Murayama, 2014; Goto et al., 2013a) and generally interpreted as a result of the wintertime increase and decrease in fossil fuel combustion and terrestrial biospheric activities, respectively. Biospheric activities included in the summertime and wintertime flux footprints at YYG were 9 % and 2 %, respectively (Hirano et al., 2015), and there was no significant solid fuel consumption, such as a coal-fired power-generation plant of which OR is expected to be 1.17 (Keeling, 1988), detected in the footprints. At YYG, the effect of emissions from coal combustion is evaluated simultaneously by the use of aerosol composition monitored every 4 h (Kaneyasu et al., 2020). From these measurements, emission contribution from coal combustion can be detected under a limited meteorological condition, such as a stagnant condition under a weak south-southwesterly wind. This condition occurred only several times a year, mostly from spring to fall. Therefore, the wintertime ORF was determined mainly by gas and liquid fuel consumption around the YYG site, given that few vegetation and weak terrestrial biospheric activities took place in the wintertime. If we assume the wintertime ORF is determined only by gas and liquid fuel consumption, with OR values of 1.95 and 1.44, respectively, then 45 % of the CO2 flux during the December to February (DJF) period was driven by gas fuel consumption, with the rest attributed to liquid fuel consumption. It should be noted that the contributions of gas and liquid fuels are expected to be underestimated and overestimated since we have ignored the contribution from human respiration with OR values in the range of 1.0 to 1.4. The respiration quotients (the reciprocal of OR) for carbohydrates, lipid and protein are known to be about 1.0, 0.7 and 0.8, respectively. We also conducted detail analyses to separate out the contributions from the consumption of gas and liquid fuels and human respiration by using the observed CO2 flux and ORF and comparing the results with the CO2 emission inventory in Sect. 3.3.
Figure 7 also shows that the ORF values were systematically larger than ORatm throughout the year, except for October 2016 and July 2017. The average ORF and ORatm during DJF were 1.67±0.03 and 1.63±0.02, respectively, both of which agree with the OR value of 1.65 calculated using the statistical data of fossil fuel consumption in Tokyo reported by the Agency of Natural Resources and Energy (http://www.enecho.meti.go.jp/en/, last access: 18 December 2018), assuming OR values of 1.95, 1.44 and 1.17 for gas, liquid and solid fuel consumption, respectively (hereafter referred to as “ORff”). By using the same procedure as above, the average ORff was calculated to be 1.52±0.1 for the Kanto area of about 17 000 km2 that includes Tokyo. Therefore, it is suggested that not only ORF, but also ORatm at YYG, mainly reflected an influence of the fossil fuel consumption in Tokyo rather than that in the wider Kanto area in the wintertime. Both the ORF and ORatm values in the summer were lower than ORff in Tokyo (1.65), but ORatm was also found to be lower than ORff for the Kanto area (1.52). These lower ORF and ORatm values, compared to those of the ORff, suggest that the ratio of fossil fuel combustion to terrestrial biospheric activities and human respiration is lower in the summer than that in the winter. The slightly lower ORatm than ORF at YYG throughout the year is probably due to the higher contribution of the air mass from the Kanto area to ORatm than ORF, since the Kanto area as a whole has lower ORff than for Tokyo; in addition, the southern Kanto area (including Tokyo) has a larger vegetation coverage of about 50 % than that in the area around the YYG site. From the comparison results of the ORF with ORatm in Figs. 5–7, it is suggested that the ORatm reflects wider footprints of O2 and CO2 than ORF for the aggregation periods at least longer than 12 h to calculate the ORatm. Therefore, to use ORF rather than ORatm is more appropriate to validate inventory-based CO2 emissions from gas, liquid and solid fuels in the flux footprint.
3.3 Consumption of gas and liquid fuels estimated from the observed CO2 flux and O2 : CO2 exchange ratio for net turbulent flux
In this section, we derive average diurnal cycles of ORF, CO2 and O2 fluxes and estimate the CO2 fluxes from gas and liquid fuel consumption separately. Figure 8 shows the average diurnal cycles of ΔO2 and ΔCO2 for each season. To derive the average diurnal cycles, the observed ΔO2 and ΔCO2 values of each day in a season were overlain on top of the values of other days, added up and divided by the number of days in the season. The error bars shown in Fig. 8 indicate ±1 standard error (). The ΔO2 and ΔCO2 values vary systematically in opposite phase and take positive and negative values, respectively, indicating transport of O2 uptake and CO2 emission signals from the urban area to the overlaying atmosphere throughout the year. Daily maxima of ΔO2 shown in Fig. 8 are higher in the winter than in the summer and occur in the nighttime. These characteristics would be attributable to an enhancement of the anthropogenic O2 consumption in the winter, while the nighttime decrease in O2 concentration would be due to the O2 consumption near the surface and temperature inversion near the surface. It must be noted that the ΔCO2 values in the daytime are nearly zero, while the ΔO2 values are not. The intercepts of the regression lines fitted to the relationship between ΔO2 and ΔCO2 in Fig. 8 are 0.27, 0.41, 0.45 and 0.44 µmol mol−1 in DJF, MAM, JJA and SON, respectively. Unfortunately, we did not fix the cause(s) of such biases yet, although it (they) may be related, to some extent, to natural exchange processes between the urban area and the overlaying atmosphere. Therefore, because of these issues, the use of ORF, calculated by applying a Deming regression fitted to 2 h period values of ΔO2 and ΔCO2 of the climatological diurnal cycle (the number of data included in each 2 h periods were 400–800, depending on the season), to determine the relationship between the O2 and CO2 fluxes, is preferable. The ORF values plotted in Fig. 8 show diurnal cycles with daytime minima in DJF, MAM and SON, while no clear cycle is found in JJA. From 10:00 to 16:00 local time, the ORF values are in the range of 1.44–1.59 for all seasons. On the other hand, the ORF values from 18:00 to 09:00 local time are more variable, in the range of 1.39–1.74, and are clearly larger in the winter than in the summer.
The observed CO2 flux and the estimated O2 flux for each season are shown in Fig. 8. The CO2 flux shows clear diurnal cycles with two peaks for all seasons, one in the morning and the other in the evening. The shape of the diurnal CO2 flux cycle, with larger flux in the winter than in the summer, was also found in our previous study at YYG for the period 2012–2013 (Hirano et al., 2015). On the other hand, the O2 flux shows similar diurnal cycles but in opposite phase with the CO2 flux. The daily mean CO2 fluxes were 15.6±0.2, 11.2±0.1, 9.3±0.1 and 11.5±0.1 µmol m−2 s−1 in DJF, MAM, JJA and SON, respectively, while the respective daily mean O2 fluxes were , , and µmol m−2 s−1. The annual average daily mean O2 flux was −16.3 µmol m−2 s−1. Steinbach et al. (2011) reported a global dataset of CO2 emissions and O2 uptake associated with fossil fuel combustion using the EDGAR inventory with country-level information on OR, based on the fossil fuel consumption data from the UN energy statistics database. The O2 uptake around Tokyo for the year 2006 has been shown to be about e16–e17 kgO2 km−2 yr−1 (Fig. 2 in Steinbach et al., 2011), which corresponds to −9 to −24 µmol m−2 s−1 of O2 flux and is consistent with those observed in this study. In this regard, the atmospheric O2 concentration decreased secularly due mainly to fossil fuel combustion at a rate of change of about −4 µmol yr−1 (e.g., Keeling and Manning, 2014), corresponding to −0.04 µmol m−2 s−1 of O2 flux, assuming 5.1×1014 m2 for the surface area of the earth, 5.124×1021 g for the total mass of dry air (Trenberth, 1981) and 28.97 g mol−1 for the mean molecular weight of dry air. Therefore, the consumption rate of atmospheric O2 in an urban area of Tokyo is several hundred times larger than the global mean surface consumption rate.
The CO2 emission inventory was developed based on Hirano et al. (2015) with some modifications. We added human respiration based on the hourly population data (Regional Economy Society Analyzing System, https://resas.go.jp/, last access: 11 March 2020). Respiration amount per person was referred from Moriwaki and Kanda (2004). We also added CO2 emission due to gas consumption by restaurants to the Hirano et al. (2015) inventory, which only accounted for household emission. Monthly gas consumption in restaurants was acquired from the statistical data published by the local government (http://www.toukei.metro.tokyo.jp/tnenkan/2015/tn15q3i006.htm, last access: 11 March 2020). Diurnal variation in the gas consumption by the restaurants was obtained from Takahashi et al. (2006) and Takata et al. (2007). We also modified the household gas consumption using the study by Etsuki (2010). As for the traffic, we used traffic load data (http://www.jartic.or.jp/, last access: 11 March 2020) which recorded the number of vehicles on the road every hour every day, whereas Hirano et al. (2015) used traffic data for a single day in 2010.
The ORF is determined as a ratio of net turbulent fluxes of O2 and CO2 from mixed consumption of gas, liquid and solid fuels and terrestrial biospheric activities and human respiration. In this study, the total net turbulent CO2 flux from the urban area to the overlaying atmosphere is calculated using the eddy correlation method. The CO2 emission inventories from gas consumption, traffic and human respiration have also been updated from the original data published by Hirano et al. (2015). We can then proceed to separate out the CO2 flux from gas and liquid fuel consumption by using Eq. (4), followed by Eqs. (5)–(6):
where FG, FL and FR (µmol m−2 s−1) represent the CO2 fluxes from gas and liquid fuel consumption and human respiration from the urban area to the overlaying atmosphere, and ORG, ORL and ORR are the OR values for gas and liquid fuel consumption and human respiration, respectively. We use 1.95, 1.44 and 1.2 for ORG, ORL and ORR, respectively. For this analysis, it is assumed that the contributions from solid fuel consumption and terrestrial biospheric activities are negligible, given the fact that in the flux footprint area, significant solid fuel consumption is absent and the vegetated area is relatively small. We also assume an ORR value of 1.2 as an intermediate value of the reciprocal of respiration quotients for carbohydrates, lipid and protein. We use the FC observed by the eddy correlation method and the FR obtained from the CO2 emission inventory to estimate FG and FL.
Figure 9 shows average diurnal cycles of the observed total CO2 flux and the CO2 flux from gas and liquid fuel consumption estimated from Eqs. (4) to (6) for each season. The average diurnal cycles of the inventory-based total, gas, traffic and human respiration CO2 fluxes are also shown in the figure. As seen in Fig. 9, similar diurnal cycles with two peaks are found in both the observed and inventory-based total CO2 fluxes for all seasons. Two peaks of the diurnal cycles are also found in the diurnal cycles of the estimated and inventory-based CO2 fluxes from gas consumption; however, the evening peaks of the inventory-based flux in MAM, JJA and SON are clearly larger than the estimated values. It is also seen from the figure that the diurnal cycles of inventory-based traffic CO2 flux do not change significantly throughout the year, while those of the estimated CO2 flux from liquid fuel consumption show large variabilities, especially in the morning. Such variability may be caused by the smaller ΔO2 and ΔCO2 values observed during the daytime, compared to those in the nighttime, as well as a rapid change in the atmospheric stability after the daybreak. The actual diurnal cycles of liquid fuel consumption do not seem to change significantly throughout the year, considering the results of the inventory-based traffic CO2 flux. We therefore consider the standard deviations of the seasonal diurnal cycles of the estimated CO2 flux from liquid fuel consumption from the annual average diurnal cycle to be the uncertainties for the annual average cycle.
Figure 10 shows the same diurnal cycles of the observed, estimated, and inventory-based CO2 fluxes as in Fig. 9 but for the annual average cycle. The observed total CO2 flux is found to be significantly smaller than the inventory-based flux in the evening. Similar discrepancy was also seen in our previous study (Hirano et al., 2015). The main cause of this discrepancy in the evening is likely the much larger inventory-based CO2 flux from gas consumption than the estimated flux. The estimated CO2 flux from liquid fuel consumption is somewhat larger than the inventory-based traffic CO2 flux in the evening, thus contributing to the above-mentioned discrepancy to some extent. Although the uncertainty in the estimated CO2 flux is large in the morning, the observed peak of the estimated CO2 flux from gas fuel consumption early in the morning and the gradual increase in the estimated CO2 flux from liquid fuel consumption over the same time period can be distinguishable. Such temporal variations of the estimated CO2 flux are reasonable since gas fuel consumption for domestic heating and cooking should increase early in the morning and liquid fuel consumption from the traffic should increase during the morning commute. Consequently, it is confirmed that the simultaneous observations of the ORF and CO2 flux are useful in validating the CO2 emission inventories developed based on statistical data. However, as shown in Figs. 8–10, a large number of ΔO2 and ΔCO2 measurement data are needed to derive reliable ORF based on an aerodynamic method. If we measure O2 concentration with high time resolution to determine net turbulent O2 flux by an eddy correlation method, then it will be possible to derive high-time-resolution ORF as a ratio of the observed O2-to-CO2 fluxes. Such an innovative technique will enhance the value of the ORF observations significantly for an evaluation of the urban CO2 emissions.
Continuous simultaneous observations of atmospheric O2 and CO2 and CO2 flux have been carried out at the YYG site, Tokyo, Japan, since March 2016. Sample air was taken from air intakes set at heights of 52 and 37 m of the YYG tower, allowing us to apply an aerodynamic method by using the vertical gradients of the O2 and CO2 concentration measurements. We compared ORF obtained from the aerodynamic method with ORatm, representing OR of the overlaying atmosphere above the urban canopy. We found clear seasonal variations with wintertime maxima for both ORF and ORatm as well as slightly higher ORF than ORatm throughout the year. The annual mean ORF and ORatm were observed to be 1.62 and 1.54, respectively, falling within the range of the respective average OR values of 1.44 and 1.95 of liquid and gas fuels. The slightly lower ORatm than ORF throughout the year was probably due to an influence of the air mass from the wider Kanto area to ORatm at YYG since the OR value of 1.1 for the terrestrial biospheric activities is lower than those for liquid and gas fuel consumption; in addition, the influence of the vegetation included in the flux footprints at YYG was much smaller than that in the surrounding Kanto area. Therefore, we prefer to use ORF rather than ORatm to validate the inventory-based CO2 emissions from gas, liquid and solid fuels in the YYG flux footprint region.
Seasonal variations were seen in the average diurnal ORF cycles, showing daytime minima in DJF, MAM and SON, while no clear diurnal cycle was distinguishable in JJA. The daily mean O2 flux at YYG, calculated from the ORF and CO2 flux, was about −25 and −14 µmol m−2 s−1 in the winter and the summer, respectively, which means the consumption rate of atmospheric O2 in an urban area of Tokyo is several hundred times larger than the global mean surface consumption rate. We estimated the average diurnal cycles of CO2 flux from the consumption of gas and liquid fuels for each season, based on the average diurnal cycles of ORF and CO2 flux and the CO2 emission inventory of human respiration around the YYG site. Discrepancy between the estimated and inventory-based CO2 fluxes from gas fuel consumption was found to be the main cause of the significantly smaller evening peak of the observed total CO2 flux than that of the inventory-based total flux. Along with the peak in the estimated CO2 flux from the gas fuel consumption, the gradual increase in the estimated CO2 flux from the liquid fuel consumption found in the morning is consistent with the fact that the gas fuel consumption for domestic heating and cooking, and liquid fuel consumption from traffic during commuting, occur in the morning. Therefore, we can use simultaneous observations of ORF and CO2 flux as a powerful tool to validate CO2 emission inventories obtained from statistical data.
The data at the YYG site presented in this study can be accessed by contacting the corresponding author.
SI designed the study and drafted the manuscript. Measurements of O2 concentrations, CO2 concentrations, and CO2 flux were conducted by SI, SI and YT, and HS, respectively. HS prepared CO2 emission inventory data. NA prepared standard gas for the O2 measurements. SI and KT conducted O2 observations at MNM. HS, NK and HK examined the results and provided feedback on the manuscript. All the authors approved the final manuscript.
The authors declare that they have no conflict of interest.
We thank Takashi Nakajima at Tokai University, Shohei Murayama at the National Institute of Advanced Industrial Science and Technology (AIST), and JANS Co. Ltd. for supporting the observation.
This study was partly supported by the JSPS KAKENHI (grant nos. 24241008, 15H02814 and 18K01129), the Environment Research and Technology Development Fund (grant no. 1-1909), and the Global Environment Research Coordination System from the Ministry of the Environment, Japan.
This paper was edited by Thomas Karl and reviewed by three anonymous referees.
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