Monitoring, Mapping, Risk, and Management    

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Mapping

Mapping is an integral part of management for any land manager. Mapping allows for a means to record a species temporally and spacially. While its one of many land management tools, its important to know that while a particular plant species can be mapped to particular area, they may not be consistently found for that transect. Continous monitoring aids mapping efforts and give valuable information to the land manager.

Links

iMap Invasives

Nebraska Weed Control Association Weedmapper

Weed Manager's Guide to Remote Sensing

NatureServe

USDA Forest service threats from invasive species

Invasive Ant species in Newzeland

Assessing Invasive Animals in Australia, 2008

Invasive Animals

Environment.Gov

Invasive Animals: Prevention and Detection

Biosecurity New Zealand (MAFBNZ)

 

NEBRASKA WEED CONTROL ASSOCIATION MAPPING PROJECT

The Nebraska Weed Control Association's state-wide mapping project is nearing its final stages in 2007. This unique system will allow for land managers and county agencies to map, monitor, and control invasive plants withing the State of Nebraska and keep everything standardized for all partners in Nebraska concerned with invasive plants .

Key Points about this system:

  • Noxious and Invasive weed management using ArcIMS
  • Allows for expansion of technology while integrating various web technologies to disseminate information
  • View of real time data from each county in Nebraska as well as partner agencies
  • Downloadable data in cvs form to integration into existing databases in the USA.
  • Creation of maps and control methodology

You can visit the NWCA system by visiting http://www.neweedmapper.org.

NORTH PLATTE RIVER REMOTE SENSING PROJECT

Research conducted by Sunil Narumalani and Deepak Mishra (CALMIT) and Panhandle Research and Extension Center - Robert Wilson, Ann Koehle, and Patrick Reece

Objective:

Project Overview
The objective of our research was to quantify and map four dominant invasive plant species spread along the floodplain of the North Platte River, Nebraska using airborne hyperspectral remote sensing data and geographic information technology. Emphasis was given to four of the most common invasive species including Saltcedar (Tamarix sp.), Russian Olive (Elaeagnus angustifolia), Canada Thistle (Cirsium arvense), and Musk Thistle (Carduus nutans)along the flood plain of North Platte river corridor within 1 mile buffer. This research was aimed to protect the natural resources of Nebraska from the impacts of non-indigenous species, and help practitioners manage and mitigate the effects of established and potential non-indigenous species.

In Situ Data

In September 26-27, 2005 an in situ investigation using a Trimble Pro-XRS (Trimble Navigation, Inc., Sunnyvale, CA) differentially corrected Global Positioning Systems (DGPS) and video/digital photography was performed.  Several areas with dense invasive species coverage were accessed, and few patches occupied by homogeneous or relatively pure saltcedar and Russian olive species were delineated for classifier training (Figure 2). Musk Thistle and Canadian Thistle we found intermixed with each other and sometime with Reed Canary Grass along the wetland borders. Several GPS points of Cottonwood, Ash, Willow, and Water Cress plants were also collected during the field survey. However, the results revealed that most of these patches were smaller than 900 m2 and the LANDSAT data would not yield an accurate analysis because its spatial resolution is 30 meters (Figure 2).  Consequently, alternative airborne data were sought to enable the mapping of the invasive species distribution along the river corridor. After the processing and classification of the airborne imagery, another field survey was performed on 1-3 March 2006 using DGPS equipment and video equipment to obtain accurate locational data for accuracy assessment of the classified maps223 GPS points were recorded for validation of the classified image resulting from spectral angle mapping.

Airborne Hyperspectral Data

An aerial remote sensing platform for hyperspectral data collection was used for this investigation.  The instrument array included an AISA Eagle hyperspectral imager from Visible to Near Infrared (VNIR), a system which can provide high spatial and spectral resolution.  AISA Eagle data used for the present study were acquired on 13 April 2005. AISA imagery for the entire study area was captured in 22 flight lines (strips) (Figure 3). Ground data indicated low wind (~ 3 m s-1), high visibility (30 km), and clear skies.  The sensor altitude was (2.073 km), and the image was acquired at nadir at a spatial resolution of 1.5 m and spectral resolution of 62 bands.  The spectral bands ranged from 392.39 to 981.68 nm with a 12 bit radiometric output. The image data were georectified and converted to at-platform radiance by applying the calibration coefficients provided by AISA Eagle processing software ‘Caligeo’ for subsequent processing.

Data processing techniques

The data processing technique utilized Spectral Angle Mapping (SAM) on the minimum noise fraction (MNF) transform of the 62 band AISA Eagle image.  MNF determines the inherent dimensionality, identify and segregate noise in the image, and reduce the computational requirements for subsequent processing (Boardman and Kruse, 1994).  It is essentially two cascaded principal components transformations.  The first transformation, based on an estimated noise covariance matrix, decorrelates and rescales the noise in the data.  This results in transformed data where the noise has unit variance and no band-to-band correlations.  The second transform is a standard principal component transformation of the noise-whitened data.  For further spectral processing, the inherent dimensionality of the data is determined by examining the final eigenvalues and the associated images.  Based on the MNF output graph of eigenvalues and visually inspecting the output components, the first ten MNF bands were selected for SAM. SAM is a physically-based spectral classification that uses n-dimensional (n = number of bands) angles to match pixels to reference spectra (Kurse et al. 1993).  The algorithm determines the similarity between the two spectra by calculating the angle and treating them as vectors in n-dimensional space.  Smaller angles represent closer matches to the reference spectrum.  Conversely, pixels that fall further away than the specified maximum angle threshold are not classified.  The maximum acceptable angle between a endmember spectrum vector and a pixel vector (in number-of-bands dimensional space) was kept as 0.1 radians.   Endmember spectra used by SAM were derived by overlapping the ground data on the MNF image. The selected fourteen endmembers were Saltcedar, Russian Olive, Canadian Thistle, Musk Thistle, Reed Canary Grass, Cottonwood, Willow, Ash, Water Cress, Wetland, Water, Sand, Cropland, and Roads.

Remote Sensing image

Sample of what Remote sensing is showing us.

Stage Two

Analysis is being conducted farther down the Platte River from Kingsley Dam to the city of North Platte. Stay tuned for an update on this stage of the project.

NOTE: Flight Line images below are in high resolution format and may take a little time to load on your screen.

Flight 1
Flight 2
Flight 3
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Flight 5
Flight 1
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Flight 22
Flight Line Index of Stage One
Prediction Map
Stage One project area
Flight 21
Flight 22
Flight Line Index
Prediction
Stage One Project Area

Distribution Maps
Spotted Pail Distribution Map-Spotted Pail
thumb Distribution Map-Horse Creek
South Mitchell Distribution Map-South Mitchell

Media: Powerpoint Slide One | PowerPoint Slide Series (note: you must have powerpoint to view these files)

* To request images or more information, please contact us or the research authors.

 
   
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