Evaluating the relative importance of northern African mineral dust sources using remote sensing
- 1Department of Geography, King's College London, University of London, London, UK
- 2Department of Earth and Planetary Sciences, Birkbeck College, University of London, London, UK
Correspondence: Natalie L. Bakker (email@example.com)
Northern African mineral dust provides the Amazon Basin with essential nutrients during the boreal winter months, when the trajectory of the Saharan dust plume is towards South America. This process, however, is still poorly understood. There is little knowledge of where the dust is coming from, and, thus, little information regarding the concentration of nutrients in the dust. This information is vital to assess the impact it will have on the Amazon. In order to further our understanding of the problem, this study analyses northern African dust sources of the boreal winter dust seasons between the years 2015 and 2017. It utilises high spatio-temporal resolution remote sensing data from SEVIRI, MODIS, VIIRS, and Sentinel-2 to identify dust sources, classify them according to a geomorphic dust source scheme, and quantify the relative importance of source regions by calculating the total dust mass they produce. Results indicate that palaeolakes emit the most dust, with the Bodélé Depression as the single largest dust source region. However, alluvial deposits also produce a substantial amount of dust. During the boreal winter dust seasons of 2015–2017, ∼36 % of the total dust mass emitted from northern Africa was associated with alluvial deposits, yet this geomorphic category has been relatively understudied to date. Furthermore, sand deposits were found to produce relatively little dust, in contrast to the results of other recent studies.
Mineral dust is an important component of the Earth system, affecting radiative forcing, cloud properties, and playing a key role in terrestrial, oceanic, atmospheric, and biogeochemical exchanges (Harrison et al., 2001; Jickells et al., 2005; Mahowald et al., 2010). The Sahara and the Sahel are the world's largest dust source regions, emitting several hundred teragrams of mineral dust yearly (Ridley et al., 2012). Most of this dust is carried over large distances and transported west and southwest across the Atlantic Ocean (Chiapello et al., 1997). During the boreal summer dust is blown by the trade winds from northern Africa towards the Caribbean, whereas during winter it takes a more southerly route towards the Amazon Basin. It has been suggested that this dust has a significant fertilising effect on the nutrient-deficient Amazonian rainforest soils (Swap et al., 1992; Yu et al., 2015). In order to better understand past, current, and future impacts of northern African mineral dust on the Amazon Basin, the biogeochemical properties of the dust need to be determined. Recently it has been shown that these properties differ significantly based on the geology and geomorphology of the terrestrial source (Gross et al., 2015, 2016); therefore, it is critical to precisely identify dust sources and their geomorphic nature.
Previous dust source identification studies have used geochemistry and mineralogy of dust samples, satellite remote sensing techniques, or back trajectory analysis (Schepanski et al., 2012; Scheuvens et al., 2013; Muhs et al., 2014). In the latter case, the performance of trajectory models is highly dependent on the initial conditions, and it is restricted by the quality of the input data (Gebhart et al., 2005). Tracing sources using the geochemistry and mineralogy of dust samples proves difficult for Saharan dust, as samples are sporadic in time and space, and transport affects measurements in poorly understood ways (Formenti et al., 2011). Satellite remote sensing in comparison, provides high spatio-temporal data across the region and has been found to be an effective method of identifying dust source areas (Prospero et al., 2002; Washington et al., 2003; Schepanski et al., 2012). Notwithstanding, many remote sensing techniques identify erroneous sources as they average both emission and transport (Prospero et al., 2002; Washington et al., 2003); thus, methods need to be adopted that only identify the site of dust emission (Schepanski et al., 2012; Ashpole and Washington, 2013).
While the major dust source areas within the Sahara and the Sahel have been identified using remote sensing (Prospero et al., 2002; Schepanski et al., 2009; Ginoux et al., 2012; Ashpole and Washington, 2013), only a few studies classify the geomorphology of these sources (Crouvi et al., 2012; Ashpole and Washington, 2013), and knowledge of the relative importance of the major dust regions is lacking. Studies analysing the fertilisation effect of dust on the Amazon focus primarily on the impact of palaeolake Bodélé (Bristow et al., 2010; Yu et al., 2015) as this has been shown to be the most important source region (Koren et al., 2006; Ben-Ami et al., 2010). The latest estimates of phosphorous input into the Amazon are based solely on the phosphorous concentration in Bodélé dust (Yu et al., 2015), but this is unlikely to reflect the diversity of the surfaces producing dust.
The aim of this study is to identify wintertime dust sources, as only this dust is transported to the Amazon. The sources are classified according to the geomorphic dust source scheme developed by Bullard et al. (2011), after which the importance of the various dust sources is quantified, and the amount of dust each region produces is calculated. This is achieved via a combination of remote sensing products with different temporal and spatial resolutions, to optimise the identification of dust storms, dusts source regions, and the geomorphology of individual dusts sources. The Spinning Enhanced Visible and Infrared Imager (SEVIRI) dust red, green, blue (RGB) colour composite has a high temporal resolution and is used here to detect dust storms, whereas the Visible Infrared Imaging Radiometer Suite (VIIRS) dust RGB with higher spatial resolution is utilised to accurately determine the dust source locations. The Moderate Resolution Imaging Spectroradiometer (MODIS) aerosol optical depth product is employed to quantify how much dust the sources produce, and the high spatial resolution (10 m) Sentinel-2 true colour composite is used to identify the geomorphology of each source. The study examines the dust storms of the 2015–2017 winter dust seasons. Both the number of individual dust sources of each geomorphological class, as well as the total dust mass emitted per class and dust source region are estimated.
The study analyses northern African dust sources during the boreal wintertime, defined as the area between the latitudes 5 and 40∘ N and the longitudes 20∘ W and 40∘ E. The dust seasons analysed run between 1 December 2015 and 29 February 2016 and 1 December 2016 and 28 February 2017, following the wintertime dust months of Schepanski et al. (2009). Figure 1 provides a complete overview of the data and methodology.
2.1 Detecting dust storms
MSG-SEVIRI was utilised to detect dust storms every 15 min at a spatial resolution of 3 km at nadir. The dust RGB method of Lensky and Rosenfeld (2008) was employed, whereby infrared channels are utilised to produce an image in which dust is portrayed in a pink colour. To achieve this, the red band is allocated the brightness temperature difference (BTD) between channels at 12 and 10.8 µm, green the BTD between channels at 10.8 and 8.7 µm, and blue the brightness temperature (BT) of the 10.8 µm channel. Processed SEVIRI dust RGB images were acquired from the database of the FENNEC project (FENNEC, 2019). By visually interpreting images, all dust events of the 2015–2017 boreal winter dust seasons were identified. Although the high temporal resolution of SEVIRI makes it suitable for observing the evolution of dust storms (Schepanski et al., 2009, 2012; Ashpole and Washington, 2012), its low spatial resolution means it is less suited for determining the precise location and nature of the sources.
2.2 Identifying dust point sources
VIIRS was used to identify dust point sources as it is currently the sensor with the highest spatial resolution that has a daily temporal resolution; it has 5 imaging-resolution bands (I-bands) at a 375 m resolution, and 16 moderate-resolution bands (M-bands) at a 750 m resolution. The same dust RGB method was employed using the infrared M-bands, centred at 8.55, 10.76, and 12.01 µm. Dust point sources were identified manually using visual interpretation. The individual dust plumes were tracked upwind back to their first point of occurrence (see Fig. 2), except for those forming under clouds (dust storms with sources under clouds were visible on approximately 2 d per month; thus, this was not a significant problem). As this process is labour intensive, this step was only performed on the 10 largest dust storms (in areal coverage) of each dust season; i.e. a total of 20 dust storms were analysed in this step.
2.3 Classifying geomorphology of dust sources
The geomorphology of the dust point sources of the 20 largest dust storms was analysed using Sentinel-2 imagery. This sensor collects visible, near-infrared, and short-wave infrared imagery at a spatial resolution of 10–60 m, and a temporal resolution of 5 d. Using the 10 m resolution true colour composites, it is possible to distinguish many geomorphic features within the imagery. Cloud free, Level-1C Sentinel-2 data were obtained for each of the dust point source locations identified from the VIIRS data. Each point source was interpreted and allocated to one of the geomorphic classes described by Bullard et al. (2011). These classes are based on differences in surface characteristics governing their susceptibility of aeolian erosion, provided they meet the criteria to be readily identifiable from remote sensing data. The classes from the scheme identified in this study are “palaeolakes”, “alluvial deposits”, “stony surfaces”, and “sand deposits”. Furthermore, the class “anthropogenic” was added to the classification scheme, defined as dust sources linked to urban areas, villages, roads, and agricultural lands. Examples of the various geomorphic classes can be found in Appendix A. Drake et al. (2008) demonstrated that the geomorphic classification scheme could characterise dust sources in the western Sahara region successfully. To account for the spatial resolution differences between VIIRS and Sentinel-2, point sources were classified as the most prominent feature and/or the most common geomorphic class within 750 m of the point location determined with VIIRS.
The identified point sources tended to spatially cluster into 12 major dust source regions according to their geomorphological type (Fig. 3). In most regions, a single geomorphological source class dominated, and a predominant geomorphology per region could be determined. In two cases, namely in the southern Air and El Eglab dust source regions, there was no single predominant geomorphic class; thus, they were classified as mixed palaeolake and alluvial deposit (50∕50 %). Once the major dust source regions were established, all dust plumes of the 2015–2017 wintertime dust seasons were assigned to the nearest major source region based on its upwind edge and then assigned the predominant geomorphic class of the region they originated from. A further four prominent dust source regions were added (see regions with dashed outlines in Fig. 3), which emitted dust plumes during the two winter dust seasons, although they did not emit during the 20 largest dust storms. The predominant geomorphology of these regions was determined separately via visual interpretation of Sentinel-2 data using the same methods that were employed for the 20 largest dust storms.
The accuracy of using only the 20 largest dust storm days of the two seasons to determine the major dust regions and their predominant geomorphology was evaluated by randomly selecting 3 additional days (29 December 2015, 21 January 2017, and 8 February 2017), identifying all point sources of these days, analysing the geomorphic class of each detected point source, and subsequently determining what percentage of these dust point sources coincided with those defined by the map of predominant dust geomorphologies. The geomorphological classes of a further 163 dust point sources were identified from the 3 randomly chosen days. Of the 163 dust point sources, 161 (98.77 %) corresponded to the predominant geomorphology assigned to the region.
2.4 Determining dust plume area
After the main dust source regions were determined, the next step was to estimate how much dust was emitted per region. To do so, firstly, the dust plume area was calculated for all dust plumes of the 2015–2017 wintertime dust seasons using the automated dust detection technique developed by Ashpole and Washington (2012). In this method, the following thresholds are applied to the brightness temperatures (in Kelvin) of the 10.76, 12.01, and 8.55 µm channels of VIIRS imagery:
Background surface features that were incorrectly detected as dust were removed manually, after which dust plumes could be outlined and their size calculated. The methodology is objective, easily reproducible, fast, and was found to be consistent for moderate-to-heavy dust storms occurring during daytime hours (Ashpole and Washington, 2012). The method was applied to VIIRS, rather than SEVIRI or MODIS, due to its higher spatial resolution and its seamless continuation between swaths.
2.5 Measuring average aerosol optical depth per plume
In order to determine the concentration of dust within the dust plumes, the average (arithmetic mean) aerosol optical depth (AOD) per dust plume was calculated for all dust storms of the 2015–2017 wintertime seasons. As the VIIRS AOD product was found to contain large data gaps, particularly over bright desert surfaces, the MODIS aerosol product (MOD04_L2, MYD04_L2) was employed. MODIS monitors AOD on a daily basis at a 10 km spatial resolution, and combines the MODIS Dark Target (Kaufman et al., 1997; Levy et al., 2013) and MODIS Deep Blue (Hsu et al., 2004) algorithms. MODIS Dark Target uses the spectral radiances between 0.47 and 2.1 µm to measure AOD over oceans and dark land surfaces. MODIS Deep Blue is designed to analyse aerosols over bright-reflecting surfaces, such as deserts, utilising measurements from the blue wavelengths (412 and 470 nm). The combined algorithms allow MODIS to record data across northern Africa consistently (Sayer et al., 2013).
The methodology presented here does have the following limitations: (1) The once daily temporal resolution of MODIS, as dust storms in northern Africa can form during any time of the day (Schepanski et al., 2012), which causes a few dust storms to be missed. Nevertheless, the vast majority of dust storms in northern Africa initiate in the morning between the hours of 06:00 and 12:00 LT (local time) (Schepanski et al., 2009), and the dust storms in this study were observed to span several hours, such that the MODIS mean overpass time of 13:30 LT covered nearly all dust emissions; albeit dust plumes emitting after 13:30 LT were missed (which occurred on 1–2 d per season). (2) The MODIS and VIIRS overpass times are close but not identical, varying up to 20 min. (3) Dust storm days between 19 and 27 February 2016 had to be omitted from this study due to a MODIS technical outage, during which the satellite did not log any data; hence, there were no MODIS AOD data available for this period.
2.6 Estimating emitted dust mass per dust source region
The dust mass for all dust plumes of the 2015–2017 wintertime seasons was estimated by combining the dust plume area data with the average MODIS AOD. The dust column concentration equation by Kaufman et al. (2005) was applied to all dust storms, whereby dust mass is determined using the relationship between plume size and average dust AOD at 550 µm:
where Mdu is dust mass, A is the dust plume area, and τdu is the average AOD at 550 µm. The coefficient of 2.7 is derived through the extinction efficiency of 0.37 measured by Haywood et al. (2003). However, a more recent review of mass extinction efficiency measurements by Ansmann et al. (2012) shows higher reported values ranging between 0.37 and 0.57. An updated Kaufman equation was derived using the extinction efficiency of 0.57, resulting in a coefficient of 1.75:
Using Eqs. (2) and (3), the dust mass range was estimated (i.e. Eq. (3) for the lower limit, Eq. (2) for the upper limit). Ben-Ami et al. (2010) demonstrated that the Kaufman equation could successfully be used to calculate dust mass over northern Africa, although it should be noted that the equation has a relatively high uncertainty of ±30 % for AOD values between 0.2 and 0.4 and has potentially even greater errors for AOD values above 0.4.
Once the dust mass per dust plume was estimated, dust plumes were grouped per dust source region and per geomorphology, and as such the total dust mass per region and dust mass per geomorphic class could be estimated.
From the 20 largest dust storms, a total of 3512 individual dust point sources were identified (see Fig. 3). The dust point sources per geomorphological class are shown in Table 1; the vast majority were associated with alluvial deposits (51.11 %) or palaeolakes (42.85 %). Sand deposits, including dune fields and sand sheets, accounted for only 3.93 %. A few sources were linked to anthropogenic influences, such as villages, dirt roads, or agricultural fields. Moreover, 22 point sources had no clear distinguishable features to place them in one of the geomorphic categories, and were thus labelled as “unknown”.
During the 2015–2017 winter dust seasons a total of between 82.3 and 127.0 Tg of dust was emitted (see Table 2). During the 2015–2016 dust season between 54.6 and 84.3 Tg of dust was emitted, of which the 10 largest dust storms contributed 33.3 %, whereas the 10 largest dust storms of the 2016–2017 dust season produced 45.8 % of the 27.7–42.7 Tg emitted that season. The 2015–2016 dust season was significantly more dusty, producing approximately twice the amount of dust compared with the 2016–2017 dust season, which is also reflected in the amount of individual dust point sources identified per season in Table 1. The distribution of the dust over the various regions was, however, relatively similar in both seasons.
Table 2 shows the distribution of the emitted dust per dust source region, along with the frequency of emission, i.e. the percentage of days during which the region was an active dust source, the mean AOD, and the predominant geomorphology. The Bodélé Depression is identified as the single largest source region, emitting 44.5 % of the dust mass, and producing the densest dust plumes with an average (arithmetic mean) AOD value of 0.91. The Bodélé, Bahr el Gazel, and Ennedi regions were the most frequently emitting dust source regions, with all of them emitting during more than half of the days of the wintertime dust season. Mauritania and southern Niger were the least active regions, emitting dust on only 2 of the 172 d analysed.
Dust source regions of predominantly palaeolake origin emitted approximately 64 % of the total dust mass during the 2015–2017 winter dust seasons, compared with 36 % for the dust regions governed by alluvial influence (note that southern Air and El Eglab are counted as 50 % palaeolake and 50 % alluvial deposit). However, the importance of palaeolakes and alluvial deposits fluctuated considerably. Figure 4 compares the influence of palaeolakes versus alluvial deposits for the 10 largest dust storms of the 2016–2017 winter dust season, which demonstrates this variability.
4.1 Palaeolake and alluvial deposit dust sources
Our results indicate the importance of both palaeolakes and alluvial deposits as African mineral dust sources. Alluvial deposits were found to deflate more often, whereas palaeolakes produced more dust by emitting denser dust plumes. Dry lakebeds, most notably the Bodélé Depression, are widely known to be preferential dust sources (Prospero et al., 2002; Tegen et al., 2002). Alluvial deposits, however, have been recognised to a much lesser extent in dust source studies, especially when compared with palaeolakes (Bullard et al., 2011). Producing 51.11 % of the individual dust plumes and representing ∼36 % of the total dust mass, alluvial deposits make a significant contribution to the dust burden. Despite this, the latest estimates of the fertilisation effect of dust on the Amazon by Yu et al. (2015) determine total phosphorus deposition into the Amazon (0.022 Tg per annum) based solely on the phosphorous concentration in Bodélé dust, while not taking alluvial deposit dust sources into account. Given the fact that it has recently been shown that there are significant differences in the bioavailable phosphorous content within dust from different source geomorphologies (Gross et al., 2015, 2016), and the evidence presented here that alluvial deposits are important sources, the accuracy of the estimate of Yu et al. (2015) can be questioned. In Namibia, Dansie et al. (2017) established that alluvial dust source sediments contained up to 43 times greater concentrations of bioavailable iron and enriched nitrogen (N) and phosphorus (P) macronutrients than palaeolake pan sediments. Further research into the actual differences in nutrient content of the different northern African dust sources and dust source geomorphologies is needed to improve the precision of fertilisation estimates. This is particularly the case for the under-examined alluvial source regions.
4.2 Do sand dunes produce dust?
While palaeolakes and alluvial deposits accounted for over 90 % of the emitted dust, sand deposits only accounted for 3.93 %. This contradicts recent results by Crouvi et al. (2012), who found that active sand dunes were the most frequent dust sources within the Sahara. The discrepancy between the results presented here and those found by Crouvi et al. (2012) is most likely explained by the type of data used and the difference in their spatial resolution. Crouvi et al. (2012) mapped dust sources onto a coarse-resolution () grid, and compared them to a map of soils. When more than one soil type was present in a grid cell, Crouvi et al. (2012) assigned it to the geomorphic unit with the highest areal coverage. This carries a large bias towards widespread sand sheets and dune fields, whereas palaeorivers and small to medium-sized palaeolakes (which could be picked up with the high-resolution Sentinel-2 data utilised in this study), for instance, are underrepresented and easily overlooked. Another major difference between the studies is that Crouvi et al. (2012) classify the Bodélé region as sand dunes, whereas in this study it is classified as a palaeolake. While dunes exist in the Bodélé Depression, they are commonly composed of fragments of lake sediments and the dunes themselves are subordinate in cover to lake sediment exposures (Bristow et al., 2009). Furthermore, Crouvi et al. (2012) identified quartz-rich sand dune fields surrounding the Bodélé Depression as a major source of dust, although closer examination of the dust sources in this region, using high-resolution data from VIIRS and Sentinel-2, showed this was not the case. The higher-resolution data used in this study have improved the accuracy of dust source identification, and suggest that sand dunes produce little dust in northern Africa during wintertime.
4.3 Location of dust sources
The majority of the locations of dust sources identified in this study correspond to previous studies such as Prospero et al. (2002), Schepanski et al. (2007, 2009, 2012), Ginoux et al. (2012), and Knippertz and Todd (2012). However, one area that has not been widely recognised as a major source region is central/southern Sudan; only Schepanski et al. (2009) mentions this region. In southern Sudan, a few of the sources lie within the Sahel, but most are located in the Sahara. While various studies have analysed Sahelian dust emissions (Klose et al., 2010; Bergametti et al., 2017; Kim et al., 2017), less is known about the importance of the Sahel compared with the Sahara. From our data, we find that the Sahelian dust sources account for a mere 5 %, with the vast majority of the wintertime dust sources being located in the Sahara. Of the Sahelian dust sources, 87 % are alluvial. The lack of lacustrine dust sources in the Sahel may be due to higher rainfall leading to moisture accumulation in the lake basins, which in turn suppresses dust production. The inundation of ephemeral lakes has previously been observed to lower dust emissions in semi-arid regions (Mahowald et al., 2003).
This study provides a quantitative analysis of wintertime northern African mineral dust sources. It outlines a novel methodology in which high temporal resolution remote sensing data are combined with high spatial resolution data to analyse dust sources more accurately than previous dust source studies. The results show the strong importance of alluvial deposits for the first time, while simultaneously reaffirming the importance of palaeolake sources. Sand deposits, in comparison, are found to produce relatively little dust. The results concur with previous studies that the Bodélé Depression is the single largest dust source region, yet also highlight that there are lesser studied regions, such as central Sudan, which are producing a substantial amount of dust. Furthermore, it stresses the significance of the Sahara over the Sahel regarding dust production, with 95 % of dust sources emitting from the Sahara.
SEVIRI data are available from the FENNEC project (http://www.fennec.imperial.ac.uk/, last access: September 2018). VIIRS data are available from NOAA CLASS (https://www.avl.class.noaa.gov/, last access: September 2018). Sentinel-2 data can be accessed through the ESA Copernicus Open Access Hub (https://scihub.copernicus.eu/dhus/\#/home, last access: July 2018). MODIS data are available from NASA Earthdata LAADS DAAC (https://ladsweb.modaps.eosdis.nasa.gov/, last access: December 2018).
The conceptualisation and methodology of this research were established by NLB and NAD. Investigation and formal analysis were carried out by NLB, and supervised by NAD and CSB. The interpretation of results was determined from discussions involving all three authors. The original draft of the paper was written by NLB, and reviewed and edited by NAD and CSB.
The authors declare that they have no conflict of interest.
The authors would like to thank Ian Ashpole and an anonymous referee for reviewing the paper and providing valuable comments and suggestions. Moreover, we thank the editor Matthias Tesche.
This research has been supported by the Natural Environment Research Council (grant no. NE/L002485/1).
This paper was edited by Matthias Tesche and reviewed by Ian Ashpole and one anonymous referee.
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