2 Object-Based Classification of Worldview Imagery for Mapping Invasive
2.6 Conclusions
Four different classification methods were tested on a Worldview-2 image to classify six land cover types with an objective of accurately mapping the invasive wetland plant
Phragmites. Four and eight band datasets were classified using the per-pixel maximum likelihood classifier and object-based methods. Three major conclusions have been determined as a result. First, object-based methods resulted in higher classification accuracy than their respective per-pixel maximum likelihood classifications. Using four band imagery, the overall classification accuracy for the object-based method was 19.7% higher than per-pixel MLC. Similarly, eight band imagery and object-based classification resulted in an increase of 10.6% in overall classification accuracy over eight band per- pixel MLC. Therefore, object-based methods were superior than per-pixel MLC for classification. Second, for both per-pixel MLC and object-based methods, eight band imagery resulted in higher classification accuracy than four band imagery. Eight band per-pixel MLC was 10.4% overall more accurate than four band, while eight band object- based was 1.3% overall more accurate. Although the eight band object-based method did not result in a large increase in accuracy over the four band object-based method, the accuracy of the vegetation classes was improved by using the eight band imagery and the associated method. Therefore, the additional spectral information provided by the
Worldview-2 satellite was useful in separating the classes on Walpole Island and
mapping the invasive plant. Third, the best method for mapping Phragmites was the eight band object-based method. This method increased overall accuracy of the six class classification by 21% over the four band per-pixel MLC, 10.6% over the eight band per- pixel, and 1.3% over the four band object-based method. The Kappa statistic for the
Phragmites and Non-Phragmites classification for the eight band object-based method was also 0.422 higher than the four band per-pixel MLC, 0.211 higher than the eight band per-pixel, and 0.025 higher than the four band object-based method. Therefore, the eight band object-based method was the best for both classifying the six land covers and for distinguishing between Phragmites and Non-Phragmites.
This study showed that a single date, eight band high resolution image classified with object-based methods was effective for mapping an invasive wetland plant species in a southwestern Ontario Great Lakes coastal wetland. Although detailed steps for Method 2 presented here were significant for extracting the six classes, its extension for classifying other images collected by the Worldview-2 satellite for this purpose may not be
appropriate. A similar classification scheme may be appropriate for images collected late in the growing season when vegetation conditions are similar. The Worldview-2 satellite may be an option for mapping Phragmites for management as a single date image can provide high accuracy for the invasive wetland plant.
2.7 References
Adam, E., Mutanga, O., & Rugege, D. (2010). Multispectral and hyperspectral remote sensing for identification and mapping of wetland vegetation: a review.Wetlands Ecology and Management, 18(3), 281-296. DOI: 10.1007/s11273-009-9169-z. Arzandeh, S., & Wang, J. (2002). Texture evaluation of RADARSAT imagery for
wetland mapping. Canadian Journal of Remote Sensing, 28(5), 653-666.
Arzandeh, S., & Wang, J. (2003). Monitoring the change of Phragmites distribution using satellite data. Canadian journal of remote sensing, 29(1), 24-35.
Environment Canada. (2003). The Ontario great lakes coastal wetland atlas: A summary of information (1983-1997) (Catalogue Number CW66-221/1997E).
Peterborough, ON: Ontario Ministry of Education. eoPortal Directory. 2012. Worldview-2. Available from
<https://directory.eoportal.org/web/eoportal/satellite-missions/v-w-x-y- z/worldview-2> [accessed (November 28, 2012)]
Ghioca-Robrecht, D. M., Johnston, C. A., & Tulbure, M. G. (2008). Assessing the use of multiseason Quickbird imagery for mapping invasive species in a Lake Erie coastal marsh. Wetlands, 28(4), 1028-1039.
Gilmore, M. S., Wilson, E. H., Barrett, N., Civco, D. L., Prisloe, S., Hurd, J. D., & Chadwick, C. (2008). Integrating multi-temporal spectral and structural information to map wetland vegetation in a lower Connecticut River tidal marsh.Remote Sensing of Environment, 112(11), 4048-4060.
doi:10.1016/j.rse.2008.05.020.
Herdendorf, C. E. (1992). Lake Erie coastal wetlands: an overview. Journal of Great Lakes Research, 18(4), 533-551.
Jaworski, E., & Raphael, C. N. (1978). Fish, wildlife and recreational values of Michigan’s coastal wetlands. U.S. Fish and Wildlife Services, Twin Cities, Minnesota.
Jensen, J. R. (2005). Introductory digital image processing: A remote sensing perspective
(3rd ed.) (pp 311 & 501). Upper Saddle River, NJ: Pearson Prentice Hall, Upper Saddle River, N.J.
Laba, M., Downs, R., Smith, S., Welsh, S., Neider, C., White, S., Richmond, M., Philpot, W. & Baveye, P. (2008). Mapping invasive wetland plants in the Hudson River National Estuarine Research Reserve using quickbird satellite imagery.Remote Sensing of Environment,112(1), 286-300. doi:10.1016/j.rse.2007.05.003. Laba, M., Blair, B., Downs, R., Monger, B., Philpot, W., Smith, S., Sullivan, P., and
Baveye, P.C. (2010). Use of textural measurements to map invasive wetland plants in the Hudson River National Estuarine Research Reserve with IKONOS satellite imagery. Remote Sensing of Environment, 114(4), 876-886.
doi:10.1016/j.rse2009.12.002.
Lavoie, C. (2008). The Common Reed (Phragmites australis): A Threat to Quebec’s
Wetlands? Available from
<http://www.canards.ca/province/qc/nouvelle/pdf/phra_08e.pdf > [accessed (January 6, 2012)].
Lehrbass, B., & Wang, J. (2010). Techniques for object-based classification of urban tree cover from high-resolution multispectral imagery. Canadian Journal of Remote Sensing, 36(S2), 287-297.
Liu, J. G. (2000). Smoothing filter-based intensity modulation: a spectral preserve image fusion technique for improving spatial details. International Journal of Remote Sensing, 21(18), 3461-3472. DOI: 10.1080/01431160110088772.
Mal, T. K., & Narine, L. (2004). The biology of Canadian weeds. 129. Phragmites australis (Cav.) Trin. ex Steud. Canadian journal of plant science, 84(1), 365- 396.
McCullough, G.B. (1985). Coastal wetlands: Wetland threats and losses in Lake St Clair
(pp. 201-208). H.H. Prince and F.M. D’Itri. (Ed.) Michigan: Lewis Publishers Inc. Ontario Ministry of Finance 2012. Ontario Population Projections Update. Available
from <http://www.fin.gov.on.ca/en/economy/demographics/projections/> [accessed (July 6, 2012)].
Ozesmi, S. L., & Bauer, M. E. (2002). Satellite remote sensing of wetlands. Wetlands Ecology and Management, 10(5), 381-402.
Parker Williams, A., & Hunt, E. R. (2002). Estimation of leafy spurge cover from hyperspectral imagery using mixture tuned matched filtering. Remote Sensing of Environment, 82(2), 446-456.
Saltonstall, K. (2002). Cryptic invasion by a non-native genotype of the common reed,
Phragmites australis, into North America. Proceedings of the National Academy of Sciences, 99(4), 2445-2449. doi: 10.1073/pnas.032477999.
Satellite Imaging Corporation (2012). IKONOS Stereo Satellite Imagery. Available from <http://www.satimagingcorp.com/svc/ikonos-stereo-satellite-images.html> [accessed (December 10, 2011)].
Snell, E.A. (1987). Wetland Distribution and Conservation in Sothern Ontario. Working Paper No. 48. Ottawa: Environment Canada, Inland Waters and Lands
Directorate.
Wilcox, K. L., Petrie, S. A., Maynard, L. A., & Meyer, S. W. (2003). Historical distribution and abundance of Phragmites australis at Long Point, Lake Erie, Ontario. Journal of Great Lakes Research, 29(4), 664-680.