Introduction
Leafy spurge (Euphorbia esula L.)
is a herbaceous, deep-rooted, dicotyledonous,
perennial weed which infests at least 458
counties in 26 states and 6 Canadian provinces
(Dunn 1979). Leafy spurge is distributed on
several habitats ranging from xeric to subhumid
and from subtropical to subarctic. It is most
common in moderately moist habitats existing in
the continental climate of North America (Selleck
et al. 1962).Leafy spurge is a
long-lived plant native to Europe and Asia. It
was introduced to North America in 1827 and first
reported in North Dakota in 1909 (Messersmith and
Lym 1983). It spreads rapidly by seeds and
rhizomes and forms colonies primarily in untilled
agricultural land.
Leafy spurge has become a
troublesome weed in the Northern Great Plains
region of North America where it grows largely
devoid of insect and disease pests (Messersmith
et al. 1985). This weed, which is extremely
persistent and competitive, has contributed
significantly to economic losses to livestock
producers.
Leafy spurge continues to be a
serious problem in North Dakota, infesting over
1,000,000 acres (ac) of land, predominately
rangeland (North Dakota Department. of
Agriculture 1996). Chemicals are the primary
method for control and eradication attempts.
However, biological control methods with insects
show great potential (Lacey et al. 1984, Lym and
Carlson 1994, Spencer 1994). Sheep grazing has
been a control method since the 1930s but has
been utilized sparingly (Bartz et al. 1985;
Helgeson and Longwell 1942; Helgeson and Thompson
1939). Goat grazing studies investigating the
potential to control leafy spurge are limited but
have shown potential as a control technique (Lym
et al.1997; Sedivec et al. 1994; Hanson 1994).
Study objectives were to
determine 1) the effect of goat grazing on leafy
spurge stem density and associated herbaceous
production, and 2) differences between
multi-species grazing and single species grazing
of leafy spurge-infested rangeland in regard to
herbaceous species utilization patterns. The
study hypothesis was graminoid degree of use on
the CG treatment should be significantly greater
than the other two treatments.
Some knowledge of range, weather,
animals, and season of the year is essential when
determining the most desirable mix of grazing
animals in any given situation. Great potential
exists for use of multi-species grazing of
livestock to maintain forage production and
species diversity. Land managers should recognize
the value of multi-species grazing and be
encouraged to apply this concept on public and
private lands.
Study Area
The study area comprised 211.3 ha
located in Sections 12 and 13, T149N, R63W in
southeast Eddy County, North Dakota. Research was
conducted on mixed-grass prairie of Camp Grafton
South (CGS), a facility of the North Dakota
National Guard. Camp Grafton South is comprised
of 10,000 ac found approximately 20.0 miles east
of New Rockford, North Dakota. The area is
predominately rangeland that has been exposed to
many decades of cattle grazing.
The 30-year annual average
precipitation at the McHenry weather station in
Eddy County is 18.6 in. annually (NOAA, NCDC
1996). In 1993, more than 80 % of total
precipitation occurred from May to August. During
this time period nearly 12.2 in. of precipitation
was above the expected average for this period.
This high rainfall precipitation pattern
continued in 1994 with 18.9 in. above average
rainfall received.
The study area vegetation was
primarily mixed-grass prairie (Whitman and Wali
1975, Barker and Whitman 1989). Küchler (1964)
classified the potential natural vegetation of
this northern transition grass prairie as a
moderately dense, short to medium tall
wheatgrass-bluestem-needlegrass (Agropyron-Andropogon-Stipa)
association. Dominant grasses found on CGS
included western wheatgrass (Agropyron smithii
Rydb.), blue grama (Bouteloua gracilis
H.B.K.), Kentucky bluegrass (Poa pratensis
L.), smooth brome (Bromus inermis
Leyss.), needle-and-thread (Stipa comata
Trin. & Rupr.), green needlegrass (Stipa
viridula Trin.), quackgrass (Agropyron
repens L.), little bluestem (Schizachryium
scoparium Michx.), and various upland sedges
(Carex spp.) (Barker and Whitman 1989). Forb
species included leafy spurge (Euphorbia esula
L.), fringed sage (Artemisia frigida
Willd.), white sage (Artemisia ludoviciana
Nutt. ), silver-leaf scurf pea (Psoralea
argophylla Pursh.), white aster (Aster
ericoides L.), dotted gayfeather (Liatris
punctata Hook.), prairie coneflower (Ratibida
columnifera Nutt.), and stiff sunflower (Helianthus
rigidus Pers.). The dominant shrub species
were western snowberry (Symphoricarpos
occidentalis Moench) and prairie rose (Rosa
arkansana Porter)(Barker and Whitman 1989).
Grazing treatments
The study area consisted of three
tracts of land, each equally infested with 30 to
40% leafy spurge. Study area No. 1 was a 92.2 ac
plot grazed by cattle only (CO). Study area No.2
was 102.3 ac and grazed by cattle and goats (CG)
together. Study area No.3 was grazed by goats
only (GO) and included 21.5 ac.
The CO was stocked with 21
cow/calf (angus/hereford cross) pairs in 1993,
1994 and 1995. Grazing dates were 15 June to 1
November (140 days) and a stocking rate of 0.98
ac/Animal Unit Month (AUM). The GO was grazed by
30 angora goat nannies from 27 May through 1
September (96 days) and a stocking rate of 0.98
ac/AUM. The CG was grazed by 21 cow/calf pairs
from 15 June through 1 November (140 days) at a
stocking rate of 0.98 ac/AUM and by 156 angora
goat nannies from 27 May through 1 September (96
days)at a stocking rate of 0.62 ac/AUM. Overall
stocking rate on the CG treatment was 0.74
ac/AUM. The CG grazing treatment was stocked 56 %
higher than either single species grazing
treatment, with the added stocking rate the
addition of goats. Cattle stocking rates remained
the same between CO and CG treatments. Goats were
added to the CG treatment without adjusting
cattle numbers due to the attempt to mimic what
livestock producers would do in a real situation.
Methodology and Design
The paired-plot clipping
technique was used to determine forage production
and disappearance for leafy spurge, graminoids,
shrubs, and other forbs (Milner and Hughes 1968).
Plant species nomenclature follows The Great
Plains Flora (Great Plains Flora Association
1986).
Peak herbage mass was calculated
yearly for all treatments from two, 0.82 ft2
(0.91 ft x 0.91 ft) quadrats within each of 32
exclosures (8.2 ft x 16.4 ft) in 1993 through
1995. Two quadrats were clipped inside and two
outside each exclosure. The goats only, cattle
only, and cattle and goat treatments had 14, 6,
and 12 exclosures, respectively. Exclosures were
randomly located on sandy and overflow range
sites for each treatment. Paired grazed and
ungrazed plots were clipped in early August when
herbage mass was near maximum (Whitman et al.
1952) and again immediately following the grazing
season to determine degree of disappearance.
Herbage was hand clipped to ground level in each
quadrat. Samples were oven dried at 140o
F for 48 hours. Vegetation samples were hand
separated into leafy spurge, graminoids, shrubs,
forbs, and litter during removal process.
Utilization or herbage
disappearance was estimated by the difference
between peak herbage mass inside and outside
exclosures at the end of the grazing season.
Disappearance of forage from paired grazed plots
was used to estimate utilization.
Leafy spurge communities were
mapped for each treatment using aerial photos.
Twelve 75 m permanent transects were randomly
dispersed to collect leafy spurge stem counts, 4
on the CO, 4 on the GO, and 4 on the CG. There
were 15 permanent quadrats distributed evenly
throughout the transect. Leafy spurge stem counts
were conducted before angora goat grazing on 25
and 26 May, 1993, to achieve initial stand
counts.
Leafy spurge stems counts were
conducted in late May 1994 through 1996 to
compare yearly differences on the same transects
initiated in 1993 using the same methodology.
Stems were counted using 1.0 ft2 (1.0
ft x 1.0 ft) frame on 10 line transects in the
spring of the year before grazing. Fifteen
systematically placed 1.0 ft2 quadrats
per transect were used to determine forb and
shrub composition per stand. Species were
identified and densities recorded. Relative
frequency and relative density were computed and
summed to produce importance values. Density data
represented individual plants.
Statistical Analyses
Statistical analysis for leafy
spurge stem densities and degree of use for
graminoids, leafy spurge, and western snowberry
were attained using the multi-response
permutation procedure (Biondini et al. 1988) at
the 95 % confidence level. Multi-response
permutation procedure allowed evaluation of
nonnormality and absolute differences which were
resistant to outliers. A modified t-test (Zar
1984) was used to evaluate percentage change in
grass, leafy spurge, and western snowberry
production at a confidence level of 95 %.
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