MILITARY TRAINING IMPACT ASSESSMENT AND MONITORING UTILIZING
REMOTELY SENSED IMAGES AND GROUND TRUTH OBSERVATIONS
J. Carlson, E. Hagemann, P. Maggio, P. Pope and J. Walkey
Environmental Remote Sensing Center, University of Wisconsin, Madison
Madison, Wisconsin, U.S.A.
ABSTRACT
This study, as part of a larger project, investigated the utility of remote sensing and geographic
information systems (GIS) for the detection, monitoring and classification of changes in land cover resulting
from military training maneuvers on Fort Bliss, Texas. The integration of multi-temporal satellite imagery,
aerial photos, existing databases and field studies utilizing Global Positioning Systems (GPS) provided
information on the ability of the various technologies and methodologies to detect impacts, to monitor change
in land cover over time due to impacts and to quantify levels of impact.
1. INTRODUCTION
1.1. Background
Remote sensing-based studies of arid lands
have proven particularly useful in gaining an
understanding of fragile desert environments
(Peterson ef al., 1987). Imagery from remote
sensors, such as Landsat Thematic Mapper (TM),
Systeme Probatoire d'Observation de la Terre
(SPOT), and high altitude aerial photography have
provided an impetus to augment resource
management efforts in arid lands (Lillesand and
Kiefer, 1994). Desertification and degradation of
arid and semi-arid lands has been estimated to
affect 19% of global land area to some degree. In
North America fully 37% of arid or semi-arid
lands have experienced severe to extremely severe
degradation (Dregne, 1977). There is a need to
understand and model the causes and consequences
of desertification in order to ameliorate the effects
of potentially destructive land uses.
The Army has established the Integrated
Training Area Management (ITAM) mission to
investigate land-use and land-cover relationships in
the installations which they administer. A fully
implemented ITAM program would provide
decision makers with the information necessary to
plan training activities while optimizing the
protection of military-base ecological resources.
The Army Environmental Center (AEC)
Was a sponsor of a project at the University of
Wisconsin-Madison's | Environmental Remote
Sensing Center which analyzed the development of
remote sensing and GIS methods to be used in the
ITAM mission (Environmental Monitoring
Practicum, 1995). Conducted on the Army base of
Fort Bliss and the Jornada Long Term Ecological
Research Site, located in southwestern Texas and
southern New Mexico, that collaborative project
investigated the approximately 1000 km? of the
base used regularly for vehicle maneuvers.
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1.2. Project Objective and Impact Definition
This project's main goal was to determine
the utility of remote sensing techniques for
evaluating impacts to the maneuver areas at Ft.
Bliss. Detection, monitoring, and quantification of
impacts were key objectives of the analysis.
Fundamental to the analysis was a
definition of impacts. Off-road vehicle activities
have been shown to cause loss of vegetation cover
resulting in accelerated soil erosion (Tuttle and
Griggs, 1987). Impacts due to vehicle activity at
Ft. Bliss include sparse or absent interdunal
vegetation in the mesquite covered dune training
areas, damage to the coppice dunes, replacement of
relic grasslands by non-native grasses and
shrubland, as well as increases in dune drift, soil
erosion and dust (Goran ef al., 1983; Shaw and
Diersing, 1990; Tuttle and Griggs, 1987).
Loss of interdunal vegetation, the most
frequently observed impact (Goran ef al., 1983;
Marston, 1986), was adopted as the definition of
training impacts. While there are various ground-
based techniques for making detailed assessments
of these and other training impacts (Marston,
1986; Goran et al, 1983), it is the loss of
interdunal vegetation which would be most
detectable with remote sensing techniques.
2. STUDY AREA
Training activity at Ft. Bliss occurs on
1,339 km“ (330,891 acres) of the Tularosa Valley.
This area is divided into fifteen Maneuver Area
(MA) units. This portion of the Tularosa Basin is
dominated by rounded and elongated coppice dunes
fixed by mesquite (Prosopsis glandulosa) with
small, isolated grassland (Bouteloua eriopoda)
flats (Marston, 1986).
The Ft. Bliss environmental staff
suggested four out of the fifteen MAs as the focus
for study. These included MAs 4C, 4D, 5D, and
SE. These areas were selected because they