Mapping cropped areas using digital multispectral video systems: a case study in the area of lake Toolibin, Western Australia. G Drysdale1, G Metternicht2 and G Beeston1 1 Spatial Resources information Group:
Agriculture Western Australia 3 Baron Hay Court South Perth WA 6151 Phone +618 9368 3467, Fax 08 93683939 Email
[email protected] Email
[email protected] 2 School of Spatial Sciences:
Curtin University of Technology GPO Box U 1987 Perth WA 6845 Phone +618 9266 7566, Fax 618 9266 2703 Email
[email protected] Abstract The project investigates the applicability and accuracy of landscape analysis of crops and remnant vegetation using highresolution multispectral video systems. The Digital Multispectral Video (DMSV) is an airborne system capable of 2m pixel resolution of images in the Blue, Green, Red and NIR wavelength bands. The DMSV was flown over Lake Toolibin in September 1998 coinciding with field data collection of land cover. DMSV images were visually compared with Landsat TM and Aerial photography to determine their appropriateness for delineation of remnant vegetation. Using different spectral classification methods within Intergragh Image Analyst software the project determines whether DMSV is an appropriate remote sensing technique for the detection of canola, pasture, remnant vegetation and wheat.
Background Information Over the past 10 years numerous studies have been carried out incorporating the use of airborne remote sensing systems. Digital Multispectral Video is fast becoming the forefront of airborne systems and has proved to be an accurate and effective tool providing immediate, highresolution results at a realistic cost. Airborne videography emerged in the 1960s and early 1970s, with works by Robinove and Skibitzke (1967) and Mozer and Seige (1971), but it was not before the 1980s that main research and operational applications in mapping and resource management began (Mausel et al., 1992; King, 1995). Airborne videography has been tested and applied for detection and mapping of crop types and conditions, including weed infestation and diseases, and the effect of soil salinity (Richardson et al.,1985; Wiegand et al., 1994; Cloutis et al., 1996; Wiegand et al., 1996). Other applications in agricultural areas include identification of sitevariability in cropped areas (Yang and Anderson, 1996; Moran et al., 1996). These works have demonstrated the potential of airborne videography as a noninvasive and rapid method of generating georeferenced maps that help, for instance, the control of
GPSequipped mobile fertilising units, or the identification of within field variability. Forestry applications of videographic data comprised prediction of habitat complexity (Coops and Catling, 1996); mapping forest species (Everitt et al., 1986; King and Vlcek, 1990, Thomasson et al., 1994), detection of signs of stress and structural damage in natural and revegetated areas (Levesque and King, 1996 and 1999).
Aims and Objectives This study aims to visually compare Digital Multispectral Video images with Landsat TM and aerial photography to determine their appropriateness for delineation of remnant vegetation. Determine whether Digital Multispectral Video data can delineate between landuses using classification methods within INTERGRAPH Image Analyst software. Determine whether Digital Multispectral Video data is an appropriate remote sensing technique for the detection of canola, pasture, remnant vegetation and wheat.
Study Area The research project was carried out within an area known as the Toolibin Lake Catchment. The Toolibin Lake Catchment covers 44,760ha and consumes a majority of the shire of Wickepin, which forms part of the South West of Western Australia. The catchment lies 4 km south east of the township of Wickepin and 240 km south east of Perth. The climate consists of warm to hot summers and a cool wet winter. Rainfall varies from 375 mm to 425 mm from east to west of the catchment. The catchment lies within the ‘Zone of Ancient Drainage’ described as “broad flat valleys of low gradient with salt lake chains at their lowest point, gently sloping valley sides, some rock outcrops and large areas of yellow sandplain”. Small stands of native vegetation occupy 14.6 per cent of the catchment (Baxter, 1996). The dominant landuse is dryland agriculture based on crops (wheat barley, oats and lupins, while canola is being planted more frequently) and pastures mainly for sheep. Toolibin Lake Catchment has been used extensively for research purposes including the Toolibin Catchment Revegetation Manual (Baxter, 1996) thus providing a library of applicable land degradation and revegetation issues. The Digital Multispectral Video (DMSV) data was acquired over a 2kmband running 17km in a Northeast direction from Lake Toolibin. The area was chosen for it’s diverse agricultural and natural land uses, geophysical and hydrological features.
Figure 1. Study Area Location.
Data Sets Remotely Sensed Data
The SpecTerra Systems Digital MultiSpectral Video system (DMSV) is a four CCD camera imaging system designed primarily for the acquisition of high resolution digital multispectral imagery of terrain, vegetation, water bodies and coastal environments (Honey, 1995). The four CCD cameras record 578 lines of 740 pixels per line and the system is capable of recording up to 70% stereo overlap. The resolution (pixel size) and total frame size are dependent on the focal length and flying height of the airborne system at the time of data acquisition. By incorporating optional logging of GPS navigation and time data the images can be positioned accurately providing the ability to cross reference field survey information. The system was mounted on a small aircraft and the imagery acquired at 10000ft above ground level (11000ft above sea level) giving a 2m pixel resolution. Interchangeable narrow bandpass interference filters were used to generate images for Blueband 1(center wavelength 450nm), Greenband 2 (center wavelength 550nm), Redband 3 (center wavelength 650nm) and NIR band 4 (center wavelength 750nm). The DMSV data was acquired on the 16 of September 1998 clear skies prevailed over the Lake Toolibin Catchment. Images were captured for two runs 17km in length, the initial at a compass bearing of 45o and the final 225o. The images were georeferenced to an orthorectified aerial photography of the area during the mosaicing process. Aerial Photography the aerial photo mosaic consists of 1:25,000 color photos captured on the 13 of October 1996. These were scanned at 400dpi and rectified to a digital cadastre database using mostly 3rd order polynomial transformations (a few 2nd order) and mosaiced with a 3 meter pixel resolution (Robinson, 1997). Landsat TM bands 5,4 and 2; acquired on the 3rd of February 1996 with a 25meter pixel resolution was displayed in red, green and blue respectively.
Field Data
The field data was collected on the 16th and 17th of September coinciding with the DMSV flight. Color Aerial Photography at 1:25,000, which was captured on the 13 of October 1996 (the same photos used to generate the Aerial Photo Mosaic) along with an analogue copy of the cadastre was used for geographic location purposes and land use data recording.
Method and techniques Ground data collection
During the field inventory the visible (some areas were difficult to access due to boggy conditions and a 2WD vehicle) land uses characteristics (e.g. crop type, remnant vegetation and lakes) across the entire study area were recorded and color photographs were taken using an Olympus automatic camera. The position and direction of the photos were recorded and used for reference during analysis. The land uses intensively investigated included canola, lupins, wheat, pasture and pasture on stubble, that is, paddocks harvested in season prior to 1998. At the time of the DMSV data acquisition, most of the crops were in early flowering. The attributes recorded for these land uses were location, height, maturity, and dry weight equivalent (DWE). The location of the elected land use was referenced to the aerial photography from 1996. Following this, the height and maturity of the land use was documented by removing a plant and measuring it against a 1meter ruler, where a color photo was taken. An agronomist then assessed the maturity status with reference to the photographic information. To determine the dry weight equivalent (DWE), 1/10th m2 quadrant was placed over three or four sample locations within a paddock in order to gather an average DWE for that land use. All green matter within the quadrant was cut at ground level with a scalpel, while trying to avoid gathering excess dirt and animal manure as this would need to be removed prior to drying. The samples were placed in a bag and the vegetation density noted for each sample (by eye in comparison to the paddock average that is high, medium or low). The samples were brought back to the work shed and washed thoroughly by rinsing in clean water, spinning dry and manually picking out erroneous matter. The clean samples were then placed in ovens and dried over 1 or 2 days. The dry vegetation samples were weighed and each weight recorded in grams per 1/10th m2, and converted to an average tonne/hectare, as shown in Table 1. (Bryant, 1998). Table 1. Land use samples and their associated Dry Weight Equivalent. LANDUSE
Vegetation
DWE g per
& Maturity
Density
Lupins:
Low
1/10th m2 22.06
2.2
4.4
Medium High Low
40.82 69.85 9.68
4.1 7.0 0.97
2.8
Medium High Low
30.77 49.24 63.34
3.1 4.9 6.3
7.2
Medium
63.68
6.4
Early flowering Canola: Early flowering Wheat:
Tonne/Ha Average T/Ha
63.68
6.4
High Pasture on land Low cropped prior Medium to 1998 High Very High
90.95 7.9
9.1 0.8
24.66 36.41 46.25
2.5 3.6 4.6
Pasture
24.96 43.82 56.84
2.5 4.4 5.7
Early flowering
Medium
Low Medium High
2.9
4.2
Field data was collected concurrently with the time of flight, enabling the ground data to be subsequently used to generate realistic analysis during digital image classification. Visual interpretation of remnant vegetation
Because of its large resolution (2m), the DMSV image was used as a reference to create a common boundary for the remnant vegetation area calculation. All three images (DMSV, Aerial Photography and Landsat TM) were then referenced to the common boundary and the area of remnant vegetation determined for each image by screen digitizing. A simple methodology was implemented to ensure the same technique was employed for the three images. • Using place smart line within MicroStation remnant vegetation areas were lassoed. • All Lake Toolibin and Lake Walbyring were included as remnant vegetation as there is an abundance of tree and scrub species that lie within these lakes which are of very high conservation value. Other waterways and dams were excluded from the area, • If any two areas of remnant vegetation were more than 20 meters apart two different lassoes were made, • Any single tree or small group of trees with a diameter equal or larger than 20metres was included as remnant vegetation, • All roadside corridors were included as remnant vegetation, During the screen digitizing visible minor shadows were included, while visible large areas of shadow were excluded. The approach was applied on the data sets as follows: DMSV (1998, 2m resolution): the NIR band was viewed in black and white and reference was made to the Red, Green and Blue bands viewed as a color composite image. The black and white NIR band provided the best enhancement for detection of remnant vegetation. Aerial Photo Mosaic (1996, 3m resolution): the Toolibin.tif image was viewed in color, which provided an adequate background for delineation between remnant vegetation and other landuses. Landsat TM (1996, 25m resolution): a color composite of bands 5,4 and 2 displayed as red, green, and blue respectively. The color contrast was enhanced using a Linear Clip (Intergraph, 1999) of each band independently. This provided the best distinction between remnant vegetation and other land uses. The areas of remnant vegetation computed for each image are
shown in Table 2. Table 2. Area of Remnant Vegetation. Image Type
Total Area (ha)
DMSV Aerial Photo
2704.46 2704.46
Remnant Vegetation (ha) 1015.20 1010.00
Landsat TM
2704.46
1078.04
Digital Classification of the DMSV
With detailed field data collected at the time of flight it was possible to perform supervised digital image classification. Four methods were tested: Minimum Distance, Maximum Likelihood, Parallelepiped and a Density Slice of the Normalized Difference Vegetation Index (NDVI). Supervised Training
To generate the Minimum Distance, Maximum Likelihood and Parallelepiped classified images 10 training sites were selected within the four known landuses (classes) namely, Canola, Pasture, Remnant Vegetation and Wheat. A composite image of the Blue, Green and Red bands was enhanced using a linear clip, and the 40 training sites were selected by the Region Growing method (Intergraph, 1999). The Region Growing method allows the user to define a seed point on the image and the neighbouring pixels that will be included in the training site if certain userdefined criteria are met. Three different methods of training site selection were performed and training set statistics were calculated on the Blue, Green, Red and NIR band. After viewing the statistics for each training set, the method which resulted in the lowest average total standard deviation of the pixel values for each class in each band was chosen, as compact clusters with small standard deviations generally reduce the chances of erroneous labelling during the classification procedure. The chosen training set used Center Point; (where only the selected pixel on the image become the seed value) with a Pixel Difference, (which allows the user to allocate a numerical value by which a pixel value can vary from the seed value to determine the pixels inclusion) of +/ 5. Image Classification
When performing image classification, Image Analyst allows the user to work with a chosen training set, select an appropriate classification algorithm and DMSV Bands for computation. Using the predefined training set (CP5.00.trn) Minimum Distance, Maximum Likelihood and Parallelepiped classification algorithms on all 4 Bands (Blue, Green, Red and NIR) were computed. The Minimum Distance classifier computes the Euclidean distance (distance measurement of one pixel to other pixels, based on the Pythagorean theorem) from an unknown pixel to the mean vector of each class, and assigns the pixel to the class to which it is closest. For computational efficiency, Image Analyst considers only the pixels within a specified number of standard deviations of a class mean vector for classification. The default threshold is 3 standard deviations from the class mean (Intergraph, 1999).
The Maximum Likelihood method classifies the input pixels into one of the training classes by using the Bayes decision function for normal patterns with an equal class probability of occurrence or a set of apriori probabilities that the user assigns, they may be determined from external sources of information about the scene. The algorithm quantitatively evaluates the variance and correlation of the class spectral response patterns when classifying an unknown pixel. The discriminant function of a given pixel, being a member of a particular class, is computed. The pixel is then assigned to the class that has the largest discriminant function. The default confidence threshold for Null class is 95% (Intergraph, 1999). The Parallelepiped method classifies unknown pixels based on the category of spectral ranges in which they lie. Once a pixel is identified as being in a class, it is blocked out of any other overlapping classes. Therefor the behavior of the algorithm is influenced by the order of classes specified. The order that the classes are evaluated can be specified using the Reorder option, a variable in Image Analyst. If a pixel lies outside all class ranges, it is interpreted as unknown or Null class. The default Null class threshold value is 3 standard deviations from the class mean (Intergraph, 1999). The three image classification algorithms were implemented using the default settings mentioned above and the landuse classes displayed in suitable distinguishing colors. The Normalized Difference Vegetation Index (NDVI)
The NDVI, often referred to as the greenness index, is derived from a ratio of the NIR and RED bands via the algorithm. NDVI = (NIRRED)/(NIR+RED) Performing a complex arithmetic equation using the NIR and RED bands created a NDVI image (ndvi.cpx). Complex Arithmetic is a spectral operand within Image Analyst that allows the user to create complex arithmetic equations with userdefined parameters. The appropriate bands and an extensive list of operators (e.g. +, x, cos, sqrt etc) are available for selection in order to create a desired expression. The expression can be saved for use later. A new training set (ie. ndvi.trn) was created with a copy of the location of training sites and they allocated parameters from CP5.00.trn (that is, the training set using a seed value, center point, and Pixel Difference of +/5.00). The statistics were calculated using the ndvi.cpx created image for the four classes (canola, pasture, remnant vegetation and wheat) When viewing the statistics it becomes evident that it would be difficult to separate pasture and wheat using the NDVI results, as they posses a similar mean greenness value while canola and remnant vegetation present very different pixel values, as illustrated in Table 3. Table 3. The NDVI training set class statistics using ndvi.cpx computed image. CLASS Canola Pasture Remveg
MINUMUM 139 169 7
MAXIMUM 200 255 97
MEAN 173.31 252.80 45.08
Wheat
225
255
254.78
Because of the distinctive NDVI values for canola and remnant vegetation, a density slicing of the NDVI was performed to identify the spatial location of these two land uses. To replace the existing pixel values with a new single value the Image Analyst Tool Replace Values was used.
The Replace Values tool allows the user to replace a single pixel value, multiple values, or a range of values with a new allocated value in a selected image. The full image range of pixel values (0255) were replaced according to the chosen class intervals, see Table 4, which allowed for accurate classification to be performed. Subsequently a Density Slice, which allows the user to isolate pixel values and assign them a color, was performed on the creating a new image (densli_ndvi.cpx). This meant that the canola and remnant vegetation areas of the image were clearly highlighted Table 4. New Replacement Values allocated to Class pixels. Existing Value 06 797 98138 139200
Class Remveg Canola
Replacement Value 0 50 0 150
201255
0
NDVI Classification
The NDVI Density Slice image (densli_ndvi.cpx) was required to be a classified image to ensure that accuracy assessment could be determined. Using the CP5.00 training set and methodology, three training sites within remnant vegetation and canola were selected. The minimum distance classification algorithm was applied on the densli_ndvi.cpx, which produced the resultant classified image (ndviclass.cpx). Ground truth assessment
To perform ground truth assessment within Image Analyst all the images to be compared must be classified images. Therefore it was required that the ground truth data be converted into a classified image which could subsequently be used to assess the accuracy of the supervised classification results. The ground truth classification image was created using the information gathered at time of field data collection. The image was reclassed using Replace Values tool and then a Density Slice was performed on the image with the colors chosen to simulate the classification outputs. The class colors are represented in Table 5. Table 5. Replacement pixel values, Density slice Color and training set name for the ground truth landuse classes CLASS Canola Pasture
Pixel Value 200 150
Color Yellow Red
Remveg Wheat Lupins Other Outside Unclassed
100 250 50 25 75
Blue Green Orange Purple Grey Black
Unclassed
Black
Comparing Classified images for Accuracy Assessment
The Compare classmaps command within Image Analyst computes a confusion matrix that compares two classified images (one being the ground truth image) that have been produced with different classification parameters or methods. The confusion matrix is a report that contains a matrix of the number of pixels assigned to each class in a particular classification. All classified images (Minimum Distance, Maximum Likelihood, Parallelepiped and NDVI) were independently compared with the ground data classification and the confusion matrix computed.
Discussion and Results Delineation of Remnant Vegetation
The three data sources have been ranked according to their appropriateness for visual identification of remnant vegetation in Table 6. The 25m resolution of the Landsat TM image produces coarse accuracy when dealing with the data visually in comparison to the 2m resolution DMSV, and 3m resolution Aerial Photo mosaic. The three maps, with line work in different colors were overlaid after area calculations were computed. This simple spatial analysis clearly displayed the areas of under and over identification within the Landsat TM scene. The 25m resolution enlarged the lasso boundary for most vegetation regions, while some of the smaller single trees did not exhibit the characteristic tone of remnant vegetation and therefor were not included. The results of the area computed for Remnant Vegetation (Table 2), highlight the similarity between the Aerial photography and DMSV identification capabilities with only a 5.20ha of difference (greater for DMSV), which can be equated as 0.19% of the total study area. The year of data collection, 1996 for the Aerial Photography and 1998 for the DMSV data must be considered when comparing these results as the vegetation within the DMSV image has a further two years growth. Vegetation patches with a diameter smaller than 20m, which were not included on the aerial photography of 1996, may well have been lassoed in the DMSV image for 1998 due to the age of the vegetation and greater resolution of the data. Table 6.Image comparison for remnant vegetation delineation. Data / Technique DMSV
Very Good
Good Fair
The 2mpixel resolution made it possible to NIR band in selectively identify small B/W single trees and shrub. supported by a Revegetation strategies color implemented throughout composite of the study area were easily Red, Green depicted and excluded and Blue. from the calculation. Narrow roads, buildings, thin tree bands, fence lines and dams were recognized. Aerial Single trees were lassoed Photography although delineation
Color photographs 1:25,000 scanned at 400dpi. Displayed as color.
between trees, shrubs and small buildings increased in difficulty. The color image aided in detection of shadow. The larger scale image 1:25,000, 3m pixels decreased the clarity. Generally an acceptable method for mapping remnant vegetation. Landsat TM Band 5, 4 and 2 displayed as Red, Green, and Blue respectively. Color contrast enhancement using a linear clip of each band independently.
The 25m pixels merged landuses together making it difficult to accurately classify vegetation boundaries. Dense overstory put constraints on the inner roads to provide distinct change in reflectance while small trees merged into other landuses. Without considerable knowledge of the area and prior vegetation detection (DMSV and Aerial Photography) legitimate extraction of vegetation would have been extremely difficult. However detection of densely vegetated areas within the lakes would have been possible due to the distinguishing change in reflectance.
Digital Classification Images
A visual comparison of the four classification algorithms with the Ground truth classification was performed. From these a general idea of the suitability of each classification could be drawn. Table 7 highlights some conclusions based on of the visual interpretation. Table 7. Visual interpretation of the Classification algorithms. Minimum Distance CANOLA
Maximum Likelihood CANOLA
CANOLA
Density slice Ndvi CANOLA
Canola area slightly underclassed. A little overclassification of Overclassification of pasture. pasture. PASTURE PASTURE
Canola area classed O.K. Over classification of pasture.
Canola area classed O.K. Major inclusion of pasture and some wheat areas as canola.
PASTURE
Pasture area: a lot of underclass. A lot of overclassification of wheat. REMVEG
Pasture area: a lot of underclass. Major overclassification of wheat. REMVEG REMVEG
Canola area classed very well.
Pasture area: a lot of underclass. Over classification of wheat. REMVEG
Remveg areas: Remveg areas: generally good, a lot generally good, a lot of under of under
Parallelepiped
Remveg areas Remveg areas classed classed O.K. A lot of well. A fair amount of underclassification. over classification in
classification. WHEAT
classification. WHEAT
pasture areas.
WHEAT
Wheat areas are Wheat areas are Wheat areas grossly underestimated. underclassed. Small underclassed or Overclassification of over classification of classed as wheat. pasture. pasture. The Lupin areas of the ground truth classification were classed as a mixture of wheat and pasture using the Minimum Distance, Maximum Likelihood and Parallelepiped algorithms. Density Slicing of the NDVI displayed the area as unclassified. From Table 7, it is assumed that the Minimum Distance and Maximum Likelihood classification are generally suitable, except for the fact that large regions of the study area remained unclassified. The Parallelepiped method had trouble classifying the wheat areas and again a considerable part of the study area was unclassified. A Density slice of the NDVI displayed major over classification of canola and large areas remained unclassified. Accuracy Assessment
In order to determine the accuracy and suitability of each classification algorithm a percentage value for the number of pixels assigned to each class from the results presented in the confusion matrix was manually computed. Table 8 displays these results while excluding inconsequential values. Table 8. Percentage of total Ground Truth Pixels assigned to each class. MINIMUM DISTANCE CLASSIFICATION GROUND Lupins Remveg
Pasture
Canola
Wheat
MIN_DIST
Canola Pasture
0.016 48.69
0.01 0.03
7.84 27.71
82.31 0.58
0.14 23.01
Wheat Remveg
35.31 0.12
0.05 58.03
0.37 0.09
0.07 0.12
38.07 0.04
Null
15.86
41.87
63.97
16.92
38.74
MAXIMUM LIKELIHOOD CLASSIFICATION GROUND Lupins Remveg
Pasture
Canola
Wheat
MAX_LIKE
Canola Pasture
0.00 44.01
0.01 0.01
3.96 25.33
73.78 0.33
0.02 13.89
Wheat Remveg
26.47 0.04
0.01 46.63
0.40 0.03
0.04 0.02
36.23 0.01
Null
29.47
53.34
70.27
25.83
49.85
Remveg
Pasture
Canola
Wheat
PARALLELEPIPED CLASSIFICATION PARALL
GROUND
Lupins
PARALL Canola Pasture
0.01 79.49
0.01 0.03
7.84 27.974
82.31 0.56
0.14 50.27
Wheat
4.52
0.05
0.11
0.05
10.81
Remveg Null
0.12 15.86
58.03 41.87
0.09 63.97
0.12 16.92
0.04 38.74
NDVI CLASSIFICATION PARALL
GROUND
Lupins
Remveg
Pasture
Canola
Wheat
Canola Remveg
5.77 3.59
1.86 74.56
44.55 8.19
78.72 3.81
21.54 7.51
Null
90.63
23.58
47.25
17.47
70.95
Minimum Distance, Maximum Likelihood and Parallelepiped
The resultant statistical percentage values above demonstrate that for most landuses classes the errors of commission (ground truth class, classified as other classes. e.g. GROUND Remveg X MIN_DIST Canola = 0.01%) is insignificant. The lupins were included within the ground truth classification to demonstrate its reflectance similarity to other classes. The results show lupins having spectral values similar to other to pasture and wheat, therefore being labelled as such, regardless of the algorithm used. The largest errors of commission were shown to occur where the existing wheat was classified as pasture. Also to a lesser, but consequential degree, where existing pasture was classified as canola. Density Slice of NDVI
The NDVI percentage results produced high accuracy for classifying existing remnant vegetation and canola, 75% and 79% respectively. Most of the remaining areas occupied by these two classes failed to be identified, that is 23% and 17% respectively were unclassified. The Null Result
The major concern in the four methods of classification is a very high percentage of Null (unclassified) values for all the existing landuse classes. Very high Null classes values demonstrate that the training sets do not properly characterize the heterogeneity. Generally, the most appropriate way to reduce the high Null values would be to collect more training sites within each landuse class. For example, training sites for remnant vegetation could be chosen within classes of dense overstory, aged vegetation, scattered vegetation, etc. Similarly crops (wheat and canola) could be segregated into areas differing in density, across different soil types or degree of weed content. The training set methodology chosen for all classification algorithms was CP5.00.trn, which demonstrated the lowest average total standard deviation for each class (eg. homogeneity). This restricted the classification algorithms to search for areas with such high constraints. Perhaps if training set with a higher level of standard deviation was employed; lower Null values would results in each classification. However this may result in higher misclassification errors for the exiting landuse classes.
Conclusion DMSV images have proved the most appropriate form of imagery for visual delineation of remnant vegetation. The 2mpixel accuracy made it possible to identify and map small patches of vegetation, and with a suitable enhancement it was even possible to distinguish between trees and shadow. The DVMS data has successfully delineated between landuses and been capable for detecting, Canola, Pasture Remnant Vegetation and Wheat. The project has highlighted that DMSV remotely sensed images, with a 2mpixel resolution, provide a useful tool for both visual and digital classification methods. It has also demonstrated that DMSV data possesses the capability to distinguish internal crop variability (e.g. density, yield, etc.)
Recommendations for further investigations Further research should be conducted to determine a proper way to reduce the number of “unclassified” pixels within the DMSV data. Some suggestions resulting from this study are: Create subclasses within a category such as, dense vegetation, scattered vegetation, aged vegetation, etc. These subclasses could be latter merged in one main category e.g. remnant vegetation. In this way, the heterogeneity of the land cover could be characterized, while keeping compact homogeneous clusters during the training phase. Perform an increase the amount of statistical analysis in order to determine the most suitable DMSV bands delineation between land cover classes. Collect more field data with increased accuracy for the location of samples. Use a GPS for ground truthing purposes.
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