This work reports the first measurements of ethene (C2H4) distributions in the upper troposphere. These are obtained by retrieving vertical profiles from 5 to 20 km from infrared solar occultation spectra recorded in 2005 and 2006 by the Atmospheric Chemistry Experiment-Fourier Transform Spectrometer (ACE-FTS). Background volume mixing ratios (vmrs) ranging from a few to about 50 pptv (10−12) are measured at the different altitudes, while for certain occultations, vmrs as high as 200 pptv are observed. Zonal distributions and vertically resolved latitudinal distributions are derived for the two year period analyzed, highlighting spatial –including a North-South gradient– as well as seasonal variations. We show the latter to be more pronounced at the highest latitudes, presumably as a result of less active photochemistry during winter. The observation of C2H4 enhancements in remote Arctic regions at high latitudes is consistent with the occurrence of fast transport processes of gaseous pollution from the continents leading to Arctic haze.
 Recently, we have presented satellite observations of ethene for the first time [Coheur et al., 2007], using infrared measurements provided by the ACE-FTS. Although the retrieval of ethene using optical instruments is challenging due to the weak spectral signature, this result triggered analyses on an extended scale. This work presents for the first time distributions of ethene in the upper troposphere, retrieved from ACE-FTS occultations in 2005 and 2006.
 The ACE-FTS measures the solar radiation between 750 and 4400 cm−1 at a spectral resolution of 0.02 cm−1 [Bernath et al., 2005]. Launched in August 2003 onboard SCISAT into a 74° inclined orbit at 650 km altitude, ACE-FTS operates primarily in solar occultation mode. It records up to 15 sunrises and 15 sunsets per day, with an orbital coverage optimized for high latitudes. Level 1 data are transmittance spectra obtained by dividing the atmospheric spectra at given tangent altitudes between 5 and 150 km by a composite exoatmospheric spectrum from the same occultation.
 For this work, we rely on the same retrieval method as described by Coheur et al. . The spectral window 949.86–950.88 cm−1, which includes the C2H4ν7 vibrational band, was chosen in order to handle a larger set of data. Unapodized spectra are analyzed, with an appropriate instrument line shape function [Boone et al., 2005]. The line parameters are from HITRAN 2004 including all recent updates [Rothman et al., 2005]. In the retrieval process, the temperature and pressure profiles are fixed to their values from the ACE-FTS operational processing (version 2.2). The trace gas profiles are similarly taken from version 2.2., but are readjusted, along with those for ethene, for all interferers in the microwindow. The retrievals are performed considering all spectra between 5 and 20 km tangent height.
 Ethene vertical profiles have been successfully retrieved for about half of the ACE-FTS occultations in the two years period considered. This means that for at least the other half the signal was too weak to be detected and the retrieval failed. Overall, this translates to a total of 4292 measurements around 14 km and 2176 around 6 km, where observations are frequently affected by clouds.
 The C2H4 contribution to the spectra is illustrated in Figure 1 for a measurement at Northern tropical latitude, representative of a relatively elevated vmr (92 pptv) around 9 km. We find that a value of 20 pptv is close to the detection threshold at all altitudes in the troposphere, similar to that of other remote-sensing techniques and significantly higher than that of in-situ air sampling measurements, which can detect vmrs as low as 3 pptv [Blake et al., 2003]. The lowest values retrieved in this work for C2H4 are not very reliable (error of 100% or larger) while for higher concentrations, the detection is unambiguous (see Figure 1) and the estimated errors on the retrieved profile do not exceed 40%.
 In order to display the ethene distributions and considering the restricted geographical coverage provided by the ACE-FTS, we have accumulated the retrieved vmrs for the two years (Figure 2). The zonal distribution around 6 km is shown in Figure 2 (top), with vmrs interpolated on a 5° latitude by 10° longitude grid. The majority of vmrs are well below 100 pptv, except for some localized grid boxes, which show enhancements above 140 pptv. The air masses with elevated C2H4 concentrations are likely due to the outflow of continental pollution plumes by rapid lofting processes, whereas lower concentrations result from the horizontal and vertical mixing of sources on timescales not exceeding the ethene lifetime. Overall, we note that the lower values retrieved from the ACE-FTS spectra are within the range of those generally reported from aircraft measurements in the free troposphere [Pozzer et al., 2007, and references therein; Blake et al., 2003]. The observation of enhanced ethene in the upper troposphere is also consistent with earlier observations of urban pollution [Blake et al., 2003] or biomass burning plumes [Pickering et al., 1996]. Figure 2 (bottom) shows the average latitudinal trend of the ethene profiles for three altitudes (around 6, 8 and 14 km), considering the entire 2005-2006 dataset, thus minimizing but not fully removing the effects of seasonal variations, as discussed below. For Figure 2 (bottom), the measurements were averaged in 20° latitude bins, with the one standard deviation of the ensemble of values divided by the square-root of the number of observations being provided as an estimate of the variability. Around 6 km, we observe a latitudinal gradient, with an average vmr in the Arctic about 50% higher than in the Antarctic. The concentrations progressively decrease with increasing altitude, following the tropopause height, and larger concentrations are found in the tropical upper troposphere.
 Ethene time series are shown in Figure 3, again around 6 km, for the 45–90° latitude bands in both hemispheres. The shapes of the seasonal cycles, shown by the curves in Figure 3, are modelled with a sine function with the mean value and amplitude as principal fitted parameters. The derived mean vmrs over the two years are 49 ± 2 and 38 ± 3, for the 45–90°N, and 45–90°S latitude bands, respectively, thus confirming the North/South gradient already apparent in Figure 2 at the same altitude. It should be stressed that these average vmrs remain likely biased towards high values due to the difficulty in measuring low concentrations with the ACE-FTS. As apparent from Figure 3, the amplitude of the seasonal cycle in the southern hemisphere is weak (5 ± 2 pptv for the 45–90°S band) and questionable in light of the high variability of the individual measurements. It is larger in the northern hemisphere (21 ± 2 pptv for the 45–90°N band) and especially at higher latitudes, although clearly existing at mid-latitudes also (a value of 14 ± 3 pptv is calculated for the 30–60°N band excluding the Arctic). For the two bands shown in Figure 3, low mixing ratio values prevail during the summer months and elevated mixing ratios in winter, with minima and maxima found around the summer and winter solstices, respectively. No seasonal variations are observed in the tropics. To our knowledge, these spatial and temporal variations in the upper troposphere have never been reported before and show general qualitative consistency with ground measurements [Hakola et al., 2006, and references therein; Sahu and Lal, 2006].
 From the spatial and seasonal variations displayed in Figures 2 and 3 we conclude that larger C2H4 mixing ratios are found in northern high latitudes during winter, with maxima close to those of the highly polluted local plumes found at tropical and mid-latitudes. The average winter maximum vmr for the 60–90°N band (not shown) is indeed well above 50 pptv, with several values reaching 200 pptv. The observation of such enhancements for the short-lived C2H4 molecule in the remote Arctic region likely originates from the uplift of continental pollution, from North America, Asia and Europe, followed by poleward transport [Stohl, 2006]. Subsequent descent of these air masses down to the lower troposphere is considered to be one of the main transport pathways which results in a high-level of pollutants within the Arctic haze that regularly occurs in winter and early spring [Law and Stohl, 2007, and references therein]. From this point of view, it is interesting to note that most ACE profiles with elevated C2H4 concentrations at these high northern latitudes are correlated with enhancements of other pollutants, including carbon monoxide (CO), ethane (C2H6) and ethyne (C2H2) and occasionally HCN (Figure 4), suggesting in this case a biomass burning origin [Rinsland et al., 2007a]. However, we find a moderate correlation between C2H4 and these tracers on a global scale at 6 km in the troposphere, as illustrated in Figure 4 (right) by the correlation with C2H2.
 Distributions of C2H4 in the upper troposphere (5 to 20 km altitude range) have been obtained from the ACE-FTS infrared satellite measurements in 2005 and 2006. Despite poor geographical coverage, especially in the tropics, zonal and latitudinal distributions have been gathered and analyzed. We have found that the C2H4 mixing ratios in the troposphere are characterized by a north to south gradient, with seasonally average values larger by 10 pptv at northern as compared to southern mid and high latitudes (49 ± 1 and 38 ± 3 pptv). The amplitude of the seasonal cycle was found to be largest in the northern hemisphere, with derived seasonal peak values up to 70 pptv and individual concentrations up to 200 pptv at polar latitudes around the winter solstice. These enhancements in the remote Arctic upper troposphere likely originate from transported continental pollution plumes, as also revealed by a good correlation with CO, C2H2 and C2H6 in individual profiles. More generally, we anticipate that these measured distributions of ethene will help in the modelling of chemical processes occurring in the upper troposphere, in particular over remote Arctic regions. The simultaneous high precision of ACE-FTS measurements of species with a range of atmospheric lifetimes offer the potential to use such chemical transport model predictions to quantify the location of the source region, the type of emission (relative contributions of biomass burning, biogenic, oceanic, and industrial sources), the age of the air in the observed parcel and their contributions to ozone production and air quality.
 The research in Belgium was funded by the Fonds de la Recherche Scientifique (FRS-FNRS, M.I.S. n°F.4511.08), the Belgian State Federal Office for Scientific, Technical and Cultural Affairs and the European Space Agency (ESA-Prodex arrangement C90-327). Financial support by the “Actions de Recherche Concertées” (Communauté Française de Belgique) is also acknowledged. C. Clerbaux and S. Turquety are grateful to CNES (Centre National d’Etudes Spatiales) for financial support. The ACE mission is supported primarily by the Canadian Space Agency (CSA) and some support was also provided by the UK Natural Environment Research Council (NERC). NASA Langley Research Center was supported by NASA′s Atmospheric Chemistry and Modeling Program (ACMAP). P.F. Coheur and L. Clarisse are Research Associate and Scientific Collaborator with the F.N.R.S (Belgium).