The Extent of Desert Dunes in Northern Nigeria as Shown by Image Enhancement Author(s): Janet E. Nichol Reviewed work(s): Source: The Geographical Journal, Vol. 157, No. 1 (Mar., 1991), pp. 13-24 Published by: Blackwell Publishing on behalf of The Royal Geographical Society (with the Institute of British Geographers) Stable URL: http://www.jstor.org/stable/635140 . Accessed: 11/11/2011 03:48 Your use of the JSTOR archive indicates your acceptance of the Terms & Conditions of Use, available at . http://www.jstor.org/page/info/about/policies/terms.jsp JSTOR is a not-for-profit service that helps scholars, researchers, and students discover, use, and build upon a wide range of content in a trusted digital archive. We use information technology and tools to increase productivity and facilitate new forms of scholarship. For more information about JSTOR, please contact [email protected]. Blackwell Publishing and The Royal Geographical Society (with the Institute of British Geographers) are collaborating with JSTOR to digitize, preserve and extend access to The Geographical Journal. http://www.jstor.org The GeographicalJournal,Vol. 157, No. 1, March1991, pp. 13-24 Theextentof desertdunesin northern Nigeriaas shownby imageenhancement JANET E. NICHOL Department of Geography, National University of Singapore This paper was accepted for publication in October 1990 On satellite imagery dune lineations can be identified in areas where surface relief and air photos give little or no indication of the former existence of dunes. Enhancement techniques applied to LANDSAT imagery of part of the Sudan zone of northern Nigeria were able to extend the known area of fixed linear dunes as far south as the northern Guinea zone, and the 1000-millimetre isohyet. Existing and new soil and land use data were interpreted in the context of observed dune lineations on the imagery. Findings provide a different perspective on the results of earlier soil surveys in these areas (which were structured upon the assumption of soil catenary relationships between sampling sites, as in traditional land systems survey), since fundamental differences in soil properties between dune and interdune bear little relationship to topographic position within a land system. KEYWORDS: Nigeria,desertdunes,imageenhancement,lineations,vegetationindex,colourspace transform. THE ABSOLUTE previous ESTABLISHING extent of desert conditions has direct relevance to assessments of the magnitude of climatic change in desert marginal areas, as well as for soil surveys for agricultural and land use planning. Numerous workers have observed on air photos the presence of systems of fixed longitudinal sand dunes bordering the world's deserts interpreting them as indicators of past more extensive desert conditions, when rainfall totals were much lower than at present (Grove, 1958; Grove and Warren, 1968; Lancaster, 1987; Maiguet, 1983). There have, however, been few attempts to utilize satellite imaging technology to confirm and supplement previous observations. After Grove, subsequent investigations of the ancient erg of Hausaland (Falconer, 1911) have been mainly of two types: (a) a study of the spatial aspects of dune morphology used as an indicator of Quaternary environmental change (Grove and Warren, 1968; White, 1971; McTainsh, 1984); (b) soil surveys of the dunefields for agricultural purposes (Sombroek and Zonneveld, 1971; NEDECO, 1974; Bennett et al., 1981). Areas with persisting dune forms in terms of relief and/or land use differences between dune and interdune have been recognized by both groups. In addition to the 'ancient erg' whose south-western limit is shown on Figure 1, these areas include a zone of bare, uncultivated lateritic ironstone strips farther north, extending approximately 100 kilometres westwards from a north-south line of quartzite hills near Kazaure (Grove and Pullan, 1963). These strips are 0016-7398/91/0001--0013/$00.20/0 oriented in the present wind direction, ENE-WSW, similar to the ancient erg, and are believed to owe their formation to wind funnelling between the gaps in the hills, depositing sand in the lee of the gaps and leaving bare those areas in the lee of the hills. The origin of these bare strips and their relation to the 'ancient erg' remains to be fully explained. Local relief is approximately 30 metres and the strips postdate the existing drainage system (ibid.). Soils to the south and west of Falconer's ancient erg, south of a line running roughly through Kano have been regarded as largely the product of harmattan dust deposition (Bennett, 1980; McTainsh, op.cit.) This is based on the soil textural bands identified by the Land Resources Development Centre from extensive soil surveys in the Kano Plains (Bennett et al. 1981: 29). The bands, based on particle size analysis, divide the Kano Plains into 13 regions whose boundaries are aligned east-west and in which particle sizes decrease from north to south. McTainsh has confirmed these observations on the probable aeolian origin of the soils to the south-west of Kano with further studies of present-day dust deposition, and recognizes a coarser size fraction in the soils than in the present day dust, which he attributes to higher wind speeds during Quarternary arid phases (McTainsh, 1984). However, some uncertainty regarding the origin of the soils to the south-west of Kano is illustrated by the following observation by Bennett et al (ibid): Therehas neverbeen any doubt as to the aeolianoriginof the mainlysandy materialto the north of Kano,or of the BirninKuduarea in the east. Indeedtheir persistingdune ? 1991 The Royal Geographical Society 14 DESERTDUNESIN NORTHERNNIGERIA Fig. 1. The mappedextentof linearfeatures formsaresufficientevidenceof wind action.Whatwas less certainwas the aeoliannatureof the siltyor veryfinesandy componentof themorepedologicallydevelopedsoilsfarther south. Rathermoreevidencethan an increasedsilt or very finesandcontentwas neededto convincethe scepticalwhen no otherchangein profileformwas evident. Satellite image interpretation The lineations comprising the 'ancient erg' were first noticed upon visual inspection of a LANDSAT MSS false colour print, as alternating light and dark toned strips aligned in the prevailing wind direction. In areas to the east of Kano where the sand dune features exhibit considerable topographic expression, their image appearance is pronounced, both on black and white air photos and on satellite imagery. However, around the edges of the dunefield where the features are less evident, they are more easily seen on satellite imagery due to its superior spectral characteristics. Moreover, the assessment of spatial characteristics such as continuity and precise orientation of individual dunes, as well as the ultimate extent of the dunefield require the synoptic qualities of such medium-scale satellite imagery. Landsat MSS imagery of November 1978 was available in digital format for the area shown on Figure 1 and image processing was carried out of a 512 x 512 pixel extract (Fig. 1), in an attempt to enhance the contrast between the alternating light and dark-toned lineations representing the dunefield. (These will subsequently be referred to as Type A, for the light toned areas occupying the highest topographic position, and Type B for darker toned areas at a slightly lower elevation). Image enhancement comprised the monitor display of individual MSS wavebands as well as image transforms commonly used for differentiating vegetation from its background and between various types of parent material. Within the area of the image extract, the dune lineations are not visible on the ground, on air photos, (Plate I) or on individual wavebands of MSS imagery. Also, a standard false colour composite, even when contrast stretched, is unable to provide a clear differentiation of dune and interdune areas (Plate II). The coincident spectral plots (Fig. 2a) show a considerable overlap in pixel brightness values, although mean values for Type A are consistently higher than those for Type B. Interestingly, Type B areas possess brightness values whose means and DESERTDUNESIN NORTHERNNIGERIA .15 would in most cases have a high ratio value. Exceptionsto this generalrule might occur in arid regions where dry soils exhibit high reflectancein both visible and near infra red wavelengthregions, andvegetationmightbe expectedto havea higherred (visible)reflectance(Tucker,1979) owingto moisture stressat mosttimesof year.Thusvaluesfor the above ratiowould be lower. The large contrast observed on the vegetation index imagebetweenType A areas(low ratio value) and TypeB areas,(Fig.2b) is thus surprisingin view of both the time of year (lateNovemberwhen Sudan zone vegetation would be suffering considerable moisturestress)and the low vegetationcanopycover (0-20 per cent,mainlyof farmlandtrees).Townsend and Justice (1986) found vegetationindices in the Sudan zone of West Africa to have substantially decreasedby mid-November.Thus significantimage Significanceof imagetransforms differencesowing to vegetationwould be unlikely, Vegetationindex The most commonly used veg- anddifferencesin soil backgroundreflectancemaybe etationindex, the NDVI, is essentiallya ratio of the assumedto be affectingthe ratio (Elvidgeand Lyon, nearinfra-redand visiblepartsof the spectrumsuch 1985). that, standarddeviationsdo not differsubstantiallyfrom those of the whole scene, the smallerrange being merely the result of the characteristicsof sample populations. (Approximately 200 pixels were sampledfor each of types A and B from a scene of 262 000 pixels). Severaltransformedimages gave better contrast betweendune and interdune;notablythe Saturation componentof the Colour Space Transform,and a densitysliceof the NormalizedDifferenceVegetation Index (NDVI) (Plates III and IV). The coincident spectralplots of these two images(Fig.2b) show an almostcompleteseparationbetweenbrightnesslevels in the Saturationcomponentand a clear separation betweenstandarddeviationsfor the Vegetationindex (NDVI). NDVI = NIR-VIS/NIR+ VIS Colour space transform This transform is recogandexploitsthe generallyhigherinfraredreflectance nized as a means of enhancingsubtle differencesin of healthy vegetationrelative to soils with higher soil and rock coloursby quantifyingand transformvisible reflectance.Thus, highly vegetated areas ing colour into its componentsHue, Saturationand PLATEI An air photo of part of the studyarea DESERTDUNESIN NORTHERNNIGERIA 16 PLATEII Falsecolourcomposite (b) 250 200 a) n E (a) 80 <G ^- , 70D Max - ' 150 MSS7 MSS6 MSS5 MSS4 -_ 601 '0 .Q 40Q, tI -SD + - C .O =r Max - ~~ -_, . -i- -Mean 100 -SD -Mean -SD I -SD c) 50 Min Min 3020 I' --- Whole Scene (By subsampling) Type A Type B HUE SAT INT NDVI (Tlraining area data) J Fig.'2. Coincidentspectralplots Type A ----- Type B DESERTDUNESIN NORTHERNNIGERIA Intensity (Drury, 1987). The magnitude of each of these components can then be adjusted within the whole of the digital range before reconverting to RGB coordinates. The effect is one of decorrelating the wavebands and improving deficiencies in colour contrast as a result of any of the components, Hue (the dominant wavelength), Saturation (purity of colour) or Intensity (brightness) (Gillespie et al., 1986). Low Saturation values, typical of arid environments (Terhalle and Bodechtel, 1986), may inhibit interpretability, even if Intensity and Hue values are distinct, since the colours may not be pure. This situation could be caused by relatively broad wavebands of imagery, such as those of LANDSAT MSS, or by the broad spectrum reflectance characteristics of most rocks and soils (Kaufmann, 1988). To illustrate, in terms of the study, the differences in colour saturation between Type A and B areas would not be adequately enhanced by a contrast stretch in RGB space. This was therefore achieved by first converting to HSI coordinates, and stretching along the Saturation axis. Reconversion to RGB coordinates would not have resulted in further contrast improvements and therefore was not carried out. The colour space transform gave the best separation between Type A and Type B areas (Plate III). In particular the Saturation component exhibited little 17 overlap in digital values, (Fig. 2b) and Intensity also gave a good contrast. Although the colour space transform is scene specific, its application to other image extracts provided a consistently good separation between Type A and B areas. This transformation was applied to the whole scene and the extent of linear features was mapped (Fig. 1). They reveal what appears to be a relict dunefield extending approximately 150 kilometres downwind of the ancient erg (as previously delineated by Grove), continuing across the Basement Complex plains around Kano. The results of both vegetation index and colour space transforms also suggested spectral differences in soil colour between Type A and Type B areas. Field investigations were subsequently carried out to establish the nature of the contrast in terms of soil and land use characteristics. Spatial filters Brightness values for a 7.8-kilometre transect across four dunes on the Saturation component (Fig. 3) also show a clear difference in mean values between Type A and Type B, but with high within-class variation especially in Type B areas. For this reason, the application of spatial filters to a density sliced image in an attempt to reduce the within-class variation was unable to enhance the separation since the method depends on a greater PLATEIII Colourspacetransformedimage 18 DESERTDUNESIN NORTHERNNIGERIA spectralhomogeneityof at least one class, than is foundhere. Fielddata Collectionof new, and the use of existing,fielddata dependedon the identificationandmanualtransferof the dune lineationsonto 1/25 000 scale air photos. Previouslyunidentifieddifferencesin toneandtexture on the air photos became evident once the major imagery,and precise trendswere known from the fieldlocationscould then be found. Fielddata comprisedinformationon soil, vegetation and land use fromthreesources: a) A studyof land use and woody vegetationto the westof Kanowas previouslycarriedout by theauthor as partof the KanoRuralEnergyProject(Cline-Cole et al., 1989). Projectsitesmarkedon airphotoscould be accuratelylocated on either dune or interdune. Figure4 shows the dunelineationssuperimposedon x metrevegetation landusemap.Twelve250 250 the which fell exactly on either a dune or quadrats location were selectedfrom this previous interdune for which informationon woody vegetation study, a available (Table II).The data comprised was each within shrubs and trees of list comprehensive includingspecies,basalareaand height.At quadrat, timeof thispreviousstudylargespatialvariations the were observed,however, no attemptwas made to explain these becausethe presentlydescribedlineations were not then apparent. b) New soil data were collectedfrom 15 sites to the west of Kanowithin the area coveredby the 512 x 512 pixel extract. Transectsperpendicularto the dune lineationswere markedon the air photos and soil samples were obtained from locations correspondingdistinctlyto eitherTypeA or TypeB areas. Soils were sampled at a consistent depth of in all cases 40 to 50 cm, corresponding approximately the limit approximately is This to the mid-Bhorizon. to which soils can be sampled in the dry season without mechanicalmeans, and also corresponds approximatelyto rootingdepth. c) Existingsoil data from the EnvironmentalData Bankof NorthernNigeria(locatedin the Department by of Geography,BayeroUniversity,Kano),collected the Land Resources Development Centre of used the of Overseas Surveys were also Directorate land et al., op cit). This survey adopted a (Bennett corresites sampling thus and approach systems to toposequences.Data from 5 toposesponded 27 siteswereused(e.g.E.D.B.on comprising quences west of 4). Data were used only for areasto the on the Fig. evident were lineations distinct where Kano (areashadedon Figure1). imagery indeximage IV Vegetation PLATE DESERTDUNESIN NORTHERNNIGERIA 19 Fig.3. Brightnessvaluesfor a transectacrossfour dunes Results Soils Soil differences were immediately evident in the field. Type A soils are dark grey-brown, (2.5Y 4/4 and 10YR 4/3 to 5/4), Fine Sandy Loam and Fine Sandy Clay Loam, gleyed with mottles. Type B soils are yellowish red (7.5YR 4/4 and 5YR 5/6), Sands, Loamy Sands and Sandy Loams. Of the soil samples from 42 different sites, only 3 do not fall within these colour class limits for Type A and Type B areas respectively. Furthermore, changes from one type to the other occurred rather suddenly across the dune lineations although relief varied only slightly, in the order of 10 metres over distances of approximately one to two kilometres. Type A occupied the highest topographic position where any relief was evident. In the highest areas Type A soils were blocky, dark grey and hard. Farmers interviewed were aware of differences in both soil colour and agricultural properties, though preferences varied between farmers. Those working the grey soils (locally termed 'laka') recognized them for their water and nutrient retention properties and their ability to grow rice, though the soils were heavier to work. The lighter, reddish soils ('jigawa') were preferred for being easier to work, though they did not retain organic fertilizer and therefore farmers tended not to apply it. Apart from rice, crops grown on each soil type were similar. Particle size analysis using the Bouyoucos hydrometer method was carried out for the 15 newly collected soil samples (Table I), but only broad textural classes were available for the E.D.B. data. FABLE I Soil texturalclasses(%) Mean Coarse Sand Fine Sand Very Fine Sand Silt Clay Type A 9.7 47.7 14.3 21.8 6.8 Type B 57.3 24.0 5.3 4.3 9.2 Figure 5 indicates distinct textural distributions for A and B type soils. While none of the samples contained more than 40 per cent silt and clay combined, (the generally agreed size limit for aeolian dust suspension over long distances, [Bennett et al., 1981: 31; Pye, 1987: 125]), all of the Type B samples contained less than 20 per cent. The high sand content of the Type B samples compares with sandy soils of the dune crests in the dunefields farther east at 12?12'N, 10?6'E (Hudu, 1986), and with the sand sheet (Couverture Sableuse) of the ancient erg of southern Niger at approximately 13?N (White, 1971). Particle sizes for Type A soils also appear to be similar in their high 20 DESERTDUNESIN NORTHERNNIGERIA ' A B ~: A "B ,t ^ '- ---"'"'^ j x5 vBr ; ^- _W< n '2 ^a~... B _ .. _ _ B --- - ^ To\ o B i.' i..--^,< B /'^ ~ JitO..t,..,.,. <~ | I::.'-' Uncultivoted Cultivoted Settlement Fig. 4. Landuse in part of the studyarea,sixkilometresw~estof Kano - - -CLAY--~ 100 j I - VF SANO--F. SANO - ' ' ' ', - SILT i 80- -. - ^ COARSE SAND I TYPEA/ yt- t -(r- C3 60s0fl . - - ! ---^^ ^^ . , ' X PARTICLESIZE ( Microns) Fig. 5. Meanparticlesize distributions v DESERTDUNESIN NORTHERNNIGERIA Fine Sand and Very Fine Sand contents, to those described by McTainsh as 'Zaria aeolian mantles' for this same area to the south-west of Kano. The high Coarse Sand content of Type B soils, however, renders them coarser than those of McTainsh but similar to McTainsh's 'Dunesand' samples for areas to the north-east of Kano e.g. at Wurma. It is maintained, however, that results are not directly comparable since McTainsh did not distinguish between dune and interdune sites, and specific sampling locations are not given. In the case of the soil surveys by Bennett et al., (1981) sampling locations were mapped and the data could thus be related to either Type A or B. Specific particle size data were not available but the broad textural groupings for Type A and B sites were found to be comparable to those in the present study. Twelve out of 13 sites on Type B areas contained at least 50 per cent of particle sizes over 100rm (Fine Sand and coarser), the modal group being Fine Sandy Loam, while in Type A the modal group was Fine Sandy Clay Loam. Type A soils were found to be more acidic than Type B soils, with pH values of 5.6 and 6.7 respectively. Land use Around Kano, differences in soil suitability for agriculture do not greatly affect land use, owing to land pressure. Nevertheless, field observations and land-use mapping from air photos indicated a higher proportion of uncultivated shrubland on the Type A areas (Table II and Fig. 4). Villages appear to cluster on the lighter soils of Type B although larger settlements such as a university campus and an army barracks are sited on Type A. TABILE 11 Land use and woody vegetation % cultivated %?settled No. of villages No. of trees/ha. Basalarea(sq.m/ha.) Type A Type B 76.0 2.0 3.0 26.2 0.5 92.0 1.0 19.0 23.5 2.0 Woody vegetation consists of stunted thorny shrubs in uncultivated areas and cultivated trees on farmland. Wood production is four times higher in Type B areas, owing to larger tree sizes (Table II). The secondary drainage network appears to be controlled by the dune lineations, in that tributary streams are aligned in the same ENE-WSW direction and frequently follow the edge of Type A areas or the boundary between Types A and B (Fig. 4). Discussion The recognition of linear dunes on multispectral satellite imagery in areas where they are not visible 21 either on the ground or on black and white air photos is thought to be the result largely of differences in reflectance properties between the grey soils of Type A and the red soils of Type B, and to a lesser extent to differences in land use and vegetation. These produce high and low reflectance values for Types A and B respectively in all wavebands and waveband combinations, except for the vegetation index image in which Type B has higher values. The very high visible reflectance of Type A areas must partially account for their lower vegetation index (NIR/VISIBLE)values. Another contributory factor is the higher woody biomass in Type B areas thus increasing the near infra-red reflectance (see Basal Area in Table II), although this factor is probably less significant since at the image date, over 80 per cent of the scene comprised bare soil. The colour space transform gave the best separation between Type A and B lineations by enhancing the inherent colour differences, and particularly the variation in Saturation across the image (Fig. 2b). The transform is likely to have increased the differences observed in the field between the grey soils of Type A and the red soils of Type B by increasing the purity (Saturation) of the colours. The dune features are, in places, of uneven width and spacing. When the light toned Type A lineations are extended upwind from the study area they frequently meet high points on maps representing large rocks or inselbergs (Fig. 6). This is not always the case, however, and in some instances the lineations appear to traverse high ground. It seems possible that, like the Kazaure laterite ridges, the features are controlled topographically, owing their formation or their preservation, or both, to elevated terrrain. White observes that the erg landscape in southern Niger is best preserved on the higher land surfaces, being part of a once continuous sand sheet, now degraded and unrecognizable in the lower sites (White, op. cit.). Grove and Pullan surmise that in the Kazaure region, sand moved westwards through gaps in the hill masses, while strips in the lee of the hills remained bare for long distances downwind. Thus areas to the lee of the gaps became covered with sand and remain today as cultivated areas with sandy soils, though the majority of the dune sand has since been removed. (Grove and Pullan, op. cit.). The grey soils of Type A are similar in colour, consistency, their high degree of mottling and their acid reaction, to hydromorphic soils in the same region (Klinkenberg and Higgins, 1968), and probably correspond to former interdune hollows, the relief having been inverted. Smaller seasonal streams which once followed the interdune depressions (as in the ancient erg farther east) still do follow the former interdunes, whereas the main watercourses have eroded laterally across the dune landscape. This 22 DESERTDUNESIN NORTHERNNIGERIA drainagepattern can be seen on Figure 4, and is readilyapparentby close examinationof air photos throughoutthe additionalareas of relict dunefields delineatedon Figure1. These observations accommodate Grove and Pullans'theory for the uncultivatedironstoneridges west of Kazaure,that the sanddepositedin the sandy corridorshas beenremovedduringa subsequentarid phase (Grove and Pullan, op. cit.). However, their theorythat the Kazauredunespost-datethe drainage system(ibid.) does not appearto applyto the Kano dunes.In this respect,as in the fact that the Type A (formerinterdune)soils are mainly cultivated,the Kanoarearesemblesthe dunefieldsfarthereastwhere thedarkgreysoils of the interdunesarevaluedforrice cultivation,and settlementsare located on the red, better-drainedsoils. A sequenceof eventsrelatingthe Kanodunesto the farthereast and to the Kazaureironstone dunefields can be hypothesized,takinginto consideration ridges atleastfourlateQuaternaryaridphases,(Servantand 1980). During one of these arid Servant-Vildary, extendedfromthe SaharaDesert dunes linear phases, atleastas far south-westas the areamapped(Fig.1), althoughthe dune-forming processes near the marginsof the dunefieldwere more influencedby local relief than in other areas. This was the result both of the derivationof dune sand from the areas upwind,thus setting up a funnellingeffect between highpoints, and also the fact that rockyoutcropsare moretypicalof BasementComplexgeology (Fig. 1). This would explainthe unevenwidth and spacingof the Kazaurelineationsin particular.Those observed aroundKanoare moreregularlyspaced,for example than to the south-eastof Kano city where they are approximately2-3 kilometresapart,suggestingless topographiccontrol and more resemblanceto the sand sheet of south-westNiger describedby White (op. cit.). The influenceof topographyin the Kano region may be as much in preservation as in formation. Duringa subsequentwetterperiodthe dune sands may have been stabilizedfor long enough to have aquiredtheirredstaining,mainlyas a resultof in situ of silicatemineralsin a savannaclimate weathering and (Cooke Warren,1973). Iron-richwaterfromthe would contributeto iron segregationmottling dunes inthe interdunes,this giving rise to groundwater lateritesunder a regime of seasonally fluctuating watertables.The Kazaurelateriteridgesrepresenta advancedstagein thetransitionof the indurated more layerto ironpanby surfaceexposureand a plinthite Fig. 6. The relationshipbetweentopographyand linearfeatures DESERTDUNESIN NORTHERNNIGERIA declining water table, especially in this area with higher relief and more arid climatic conditions than in Kano. The process of relief inversion is also more advanced in the Kazaure area with uncultivated laterite ridges being elevated to a height of 30 metres above the cultivated sandy strips (Grove and Pullan, 1963). This later stage of transition to ironpan has only limited distribution in the Kano study area and is seen typically along stream banks as, for example, adjacent to the Watari River where there are ironstone outcrops which have very high reflectance and appear as light toned areas on imagery (uncultivated areas in Fig. 4). The fixed dunes farther east, which retain their dune topography, may have been formed during a subsequent, less extensive arid phase. Conclusion Observations using enhanced satellite imagery have extended the known area of relict dune features in northern Nigeria as far south and west as the north Guinea zone, and from the 750-millimetre (Grove, 1958), to the 1000-millimetre isohyet. This finding challenges statements (based largely on observations of particle sizes of soil samples) about the predominantly loessic nature of the soils to the south-west of Kano. Particle sizes measured for areas to the south-west of Kano, both in the present study as well as that by McTainsh, contain a considerable Very Fine Sand and are coarser than component (50-100lm) present-day dust (McTainsh and Walker, 1982). Soils sampled from Type B areas are much coarser than present-day dust, containing over 80 per cent of particles over 100btm. The present modal size of harmattan dust particles at Kano is 31.2btm (ibid.). While Very Fine Sand particles may be transported for short distances in suspension, the same may not be true of particles larger than 100am, even under high wind conditions. (In fact, McTainsh and Walker cite 12btm modal size for dust carried as far as 900 kilometres, (McTainsh and Walker, op. cit.). These observations can only be upheld either by invoking higher wind speeds or by re-evaluation of the theory of the loessic origin of the soils. McTainsh uses the former explanation (McTainsh, 1987). It is recognized in addition, that mixing may occur on the 23 margins of dunefields between loess and dune sands and that this could be used to explain the presence of some coarser textured material among loess deposits. This would in fact give a bi-modal distribution, but would be unlikely to account for proportions of over 80 per cent of medium and coarse sand in an allegedly loess mantle. The clear differences in soil colour and soil texture between Type A and B soils observed in the present study, from field sampling and from the samples contained in the Environmental Data Bank, suggest that distinct and individual processes have operated in adjacent sites corresponding to former dunes and interdunes. These findings from soil data and satellite image interpretation have relevance to estimations of the magnitude of climatic change in desert marginal areas. Assuming an upper annual rainfall limit of 150 millimetres for dune building to take place, though some workers suggest less (Talbot, 1980), an increase of the magnitude of 850 millimetres annual rainfall is suggested, as opposed to the previous implication of 600 millimetres (Grove, op. cit.). The findings may also advocate a more cautious approach to soil survey in desert marginal areas known to have been subject to climatic change in the recent past. However, they are supported by only limited field data and could usefully be supplemented by additional information as well as a more extensive examination of the data contained in the Environmental Data Bank for northern Nigeria. Although the 80-metre resolution of LANDSAT MSS imagery was found to be appropriate for the study,, the superior spectral sensitivity of LANDSAT TM imagery could usefully be investigated. Acknowledgements The author is grateful to Professor M. J. Mortimore for his interest in this and previous research projects in West Africa, and for his comments on the draft of this paper. A. T. Grove's advice and assistance in discussion have also been invaluable, as have Grant McTainsh's comments on the characteristics of harmattan dust in the Kano region. REFERENCES Bennett,J. G., 1980 Aeolian depositionand soil parent Cline-Cole,R.C., Falola,J. A., Main,H. A. C., Mortimore, M. J., Nichol,J. E.,andO'Reilly,F. D. 1989 Woodfuelin materialsin northernNigeria.Geoderma24: 241-55. Kano: production,consulmptionand trade in a West Bennett,J. G., Hutcheon,A. S. A., Ibanga,J., Kerr,W. B., Mansfield,J. E., Rackham,L. J., and Valette,J. 1981 African savanna environment. Tokyo: United Nations Land resourcesof central Nigeria: environmental aspects UniversityPress. of the Kano Plains, 1. Landforms and soils. Chatham: Cooke, R. U. and Warren,A. 1973 Geomorphologyin deserts.London:Batsford. 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