II.14
Effect of Multiple Concentrations and Rates of Carbaryl-Bran Bait
Mark A. Quinn, R. Nelson Foster, and K. C. Reuter
Introduction
Multiple
Concentrations and Rates of Bran Bait-A Case Study
Conclusions
References
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Introduction
Insecticidal baits are a viable alternative to conventional insecticidal
sprays for controlling grasshoppers (Quinn et al. 1989). Baits are
particularly effective when the grasshopper community is composed
largely of bran acceptors, or those species that readily consume
bran baits (see chapter II.12
on bait acceptance). Most of the recent studies involving bran baits
have used concentrations in the range of 2-5 percent toxicant at
rates near 1.5 lb/acre. The efficacy of higher concentrations and
rates has not been studied extensively. As part of the Grasshopper
Integrated Pest Management Project, a study was conducted in northwestern
South Dakota to determine the effects of multiple concentrations
and rates of carbaryl bran bait on grasshoppers on mixed-grass rangeland.
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Multiple
Concentrations and Rates of Bran Bait-A Case Study
Fifty-one 40-acre plots were treated with aerial applications of
carbaryl bran bait in the following concentrations and rates: 2
percent carbaryl at 0.5, 1, 2, 5, and 10 lb/acre; 5 percent carbaryl
at 0.5, 1, and 2 lb/acre; and 10 percent carbaryl at 0.5, 1, and
2 lb/acre. An additional nine plots were used as controls. The baits
were applied with a Cessna Ag Truck operating at an altitude of
40-60 ft at 115 miles per hour (mi/hour) and equipped with a standard
Transland 20244 spreader. Swath widths were 45 ft. Treatments were
applied over a 17-day period from June 27 to July 13, 1987. Approximately
56 percent of grasshoppers were in the nymphal stage at the time
of treatments (table
II.14-1).
Densities of grasshoppers were estimated in the center of each
plot by counting grasshoppers in 40 0.1-m2
rings (Onsager and Henry 1977) placed approximately 16 ft apart
in a 210-ft-diameter circle. Relative abundance of each grasshopper
species and instar was determined by collecting grasshoppers near
the circle of rings with a sweep net. Densities of individual species
were estimated by multiplying their relative abundance by total
grasshopper density. Grasshopper populations were monitored before
treatment and 2, 4, and 7 days after treatments. Populations were
monitored approximately daily from June 26 to July 20 in the control
plots.
Changes in densities of total grasshoppers, bran-accepting species,
and bran-rejecting species in the control plots were compared with
changes in plots treated with the insecticidal baits to determine
overall treatment effects. Major bran-accepting species included
Melanoplus sanguinipes, other Melanoplus species,
Ageneotettix deorum, Phoetaliotes nebrascensis, and Aulocara
elliotti. Bran-rejecting species included Aeropedellus clavatus,
Amphitornus coloradus, Trachyrhachys kiowa, and Opeia obscura.
Although O. obscura may be vulnerable to insecticidal
baits (see the bait acceptance chapter in this section), we included
it in the bran-rejector category because it was not affected by
the insecticidal bait in our particular study.
Mean pretreatment densities of total grasshoppers ranged from 13.1
to 22 grasshoppers/yd2 in the
treatment plots. M. sanguinipes, A. deorum, and A. clavatus
constituted 32, 15, and 14 percent of all grasshopper species,
respectively, during the pretreatment period (table
II.14-1). Bran acceptors constituted 72 percent of all
species.
All insecticidal bait treatments, except the 2 percent carbaryl
at 0.5 lb/acre, caused significant reductions in total grasshopper
density compared with controls (table
II.14-2). The greatest mean mortalities, ranging from
72 to 86 percent, occurred in plots treated with 2 percent carbaryl
bran bait at 5 and 10 lb/acre, 5 percent carbaryl bran bait at 1
lb/acre, and 10 percent carbaryl at 2 lb/acre. The more standard
treatments of 2 percent carbaryl at 1 and 2 lb/acre gave intermediate
results, causing average mortalities of 52 and 64 percent, respectively.
Applications of bran bait at 0.5 lb/acre were least effective, killing
less than 50 percent of all grasshoppers.
All treatments caused significant mortality of bran-accepting species
of grasshoppers compared with controls (table
II.14-2). The greatest mortality occurred in plots treated
with 2 percent carbaryl at 10 lb/acre (97 percent), 5 percent carbaryl
at 2 lb/acre (90 percent), 2 percent carbaryl at 5 lb/acre (90 percent),
and 5 percent carbaryl at 1 lb/acre (88 percent). The commonly used
treatments of 2 percent carbaryl at 1 or 2 lb/acre caused 72 and
89 percent mortalities, respectively, of bran-accepting grasshopper
species. Applications of 2 and 5 percent carbaryl at 0.5 lb/acre
caused 45-54 percent reductions in the bran acceptors. Densities
did not change in control plots.
In general, bran-rejecting species were not affected by the treatments
(table II.14-2).
However, the greatest reduction in bran rejectors (60 percent) occurred
in plots treated with 2 percent carbaryl at 10 lb/acre. Because
changes in densities in these plots were highly variable, it could
not be determined if this reduction was caused by mortality or natural
variation in grasshopper populations.
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Conclusions
The following conclusions can be drawn from the study. First, the
quantity of carbaryl bran bait applied to rangeland affects grasshopper
mortality. Baits applied at 0.5 lb/acre are relatively ineffective.
The highest rates (5 and 10 lb/acre) were very effective in controlling
grasshoppers. These results do not suggest, however, that more bait
is always better (see chapter II.15
on multiple applications of bran bait). For example, 78 percent
mortality was achieved in plots treated with 5 percent carbaryl
at 1 lb/acre. Also, the small increase in mortality caused by higher
rates may not be economically justifiable.
Second, the concentration of carbaryl seemed less important than
the rate of application. For example, 2 and 10 percent carbaryl
applied at a rate of 2 lb/acre caused similar grasshopper mortalities.
Finally, high mortality of grasshoppers was achieved because the
grasshopper community was composed mainly of the bran-accepting
Melanoplus species. Insecticidal baits are less effective
when there is a higher proportion of bran-rejecting species (Quinn
et al. 1989, Jech et al. 1993).
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References
Cited
Jech, L. E.; Foster, R. N.; Colletto, D.; Walgenbach,
D. D.; Roland, T. J.; Rodriguez, G. D.; Bohls, R.; Houston, R. D.;
Meeks, W. K.; Queener, R. L.; Jackson, C. L.; Dines, J. L.; Puclik,
M. J.; Scott, A. K. 1993. Field evaluation of diflubenzuron and
carbaryl bran baits against grasshopper (Orthoptera: Acrididae)
populations in South Dakota. Journal of Economic Entomology 86:
557-565.
Onsager, J. A.; Henry, J. E. 1977. A method for
estimating the density of rangeland grasshoppers (Orthoptera: Acrididae)
in experimental plots. Acrida 6: 231-237.
Quinn, M. A.; Kepner, R. L.; Walgenbach, D. D.;
Bohls, R. A.; Pooler, P. D.; Foster, R. N.; Reuter, K. C.; Swain,
J. L. 1989. Immediate and 2nd-year effects of insecticidal spray
and bait treatments on populations of rangeland grasshoppers. Canadian
Entomologist 121: 589-602.
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Section II Contents
Table II.14-1-Relative abundance
of grasshopper species and instars and number of plots occupied
on the pretreatment sampling dates, June 26-July 7, 1987, Harding
County, SD
|
Species
|
No. of plots occupied
|
Percentage of grasshoppers1
|
Percentage of individuals
in each instar
|
Adult
|
|
I
|
II
|
III
|
IV
|
V
|
|
Melanoplus sanguinipes
(F.)
|
55
|
32.31
|
0.0
|
0.9
|
13.6
|
17.0
|
32.1
|
36.4
|
|
Ageneotettix deorum
(Scudder)
|
55
|
14.35
|
0.0
|
0.8
|
4.6
|
15.2
|
57.6
|
21.8
|
|
Aeropedellus clavatus
(Thomas)
|
51
|
13.95
|
0.0
|
0.0
|
0.0
|
0.0
|
0.0
|
100.0
|
|
Melanoplus dawsonii
(Scudder)
|
40
|
5.31
|
0.4
|
4.7
|
23.8
|
27.7
|
20.6
|
22.8
|
|
Melanoplus confusus
Scudder
|
47
|
4.57
|
0.0
|
0.0
|
0.0
|
0.0
|
0.0
|
100.0
|
|
Amphitornus coloradus
(Thomas)
|
50
|
4.55
|
0.0
|
0.0
|
2.7
|
9.5
|
43.1
|
44.6
|
|
Melanoplus infantilis
Scudder
|
44
|
3.76
|
0.2
|
2.8
|
15.9
|
15.3
|
31.7
|
34.0
|
|
Trachyrhachys kiowa
Thomas
|
48
|
2.50
|
0.0
|
0.6
|
10.5
|
16.8
|
35.0
|
37.1
|
|
Melanoplus
spp.
|
38
|
2.32
|
25.0
|
74.6
|
0.0
|
0.0
|
0.4
|
0.0
|
|
Orphulella speciosa
(Scudder)
|
31
|
2.13
|
0.4
|
2.0
|
11.8
|
34.1
|
29.5
|
22.2
|
|
Phoetaliotes nebrascensis
(Thomas)
|
39
|
2.10
|
4.5
|
40.1
|
36.7
|
14.8
|
3.9
|
0.0
|
|
Aulocara elliotti
Thomas
|
38
|
1.92
|
0.0
|
0.0
|
0.5
|
0.8
|
20.0
|
78.7
|
|
Melanoplus packardii (Scudder)
|
46
|
1.47
|
0.6
|
4.9
|
16.0
|
38.8
|
32.8
|
8.7
|
|
Melanoplus femurrubrum
(DeGeer)
|
17
|
1.36
|
6.1
|
20.8
|
42.8
|
15.6
|
11.0
|
3.7
|
|
Melanoplus bivittatus
(Say)
|
34
|
1.30
|
0.0
|
1.5
|
5.7
|
12.8
|
15.1
|
64.8
|
|
Opeia obscura
(Thomas)
|
39
|
1.19
|
0.0
|
2.4
|
15.3
|
39.3
|
36.1
|
6.9
|
|
Others (26 species)
|
-
|
4.91
|
6.8
|
10.6
|
13.6
|
14.3
|
23.0
|
31.7
|
|
All species
|
55
|
100.00
|
1.1
|
4.3
|
10.0
|
13.7
|
27.3
|
43.6
|
|
1Based on a total of 12,063 grasshoppers
collected
|
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Table II.14-2-Pretreatment densities
and reductions in grasshopper densities 7 days after treatments
with different rates and concentrations of carbaryl bran bait, Harding
County, SD
|
Grasshopper variable
|
Treatment1
|
Pretreatment density2
(x
± SEM) standard error of the means
|
Percent reduction3
(x
± SEM)
|
|
Total grasshoppers
|
Control
|
13.7 ± 1.91a
|
8.1 ± 12.66a
|
|
2% - 0.5
|
12.5 ± 2.43a
|
31.3 ± 10.69abcd
|
|
2% - 1.0
|
13.8 ± 0.61a
|
51.7 ± 17.01be
|
|
2% - 2.0
|
17.4 ± 2.81a
|
63.9 ± 2.17efgh
|
|
2% - 5.0
|
17.4 ± 4.21a
|
75.3 ± 8.20gk
|
|
2% -10.0
|
20.1 ± 6.57a
|
85.9 ± 7.91k
|
|
5% - 0.5
|
16.4 ± 1.40a
|
37.4 ± 15.58bcdf
|
|
5% - 1.0
|
18.6 ± 5.53a
|
77.9 ± 7.54hk
|
|
5% - 2.0
|
18.0 ± 4.92a
|
56.0 ± 8.05ceg
|
|
10% - 0.5
|
12.0 ± 2.83a
|
49.9 ± 5.98bcdf
|
|
10% - 1.0
|
13.9 ± 2.39a
|
58.7 ± 3.81deg
|
|
10% - 2.0
|
17.3 ± 2.33a
|
72.3 ± 4.71ek
|
|
Bran acceptors
|
Control
|
9.4 ± 1.43a
|
5.7 ± 12.77a
|
|
2% - 0.5
|
8.7 ± 1.42a
|
45.2 ± 19.72b
|
|
2% - 1.0
|
8.4 ± 0.60a
|
60.2 ± 17.80bcd
|
|
2% - 2.0
|
11.3 ± 1.40a
|
77.5 ± 4.85cdef
|
|
2% - 5.0
|
13.6 ± 4.53a
|
89.6 ± 5.79fg
|
|
2% -10.0
|
17.0 ± 5.23a
|
97.4 ± 2.34g
|
|
5% - 0.5
|
12.6 ± 1.30a
|
53.5 ± 11.42bc
|
|
5% - 1.0
|
15.1 ± 4.45a
|
87.9 ± 6.98efg
|
|
5% - 2.0
|
10.2 ± 2.44a
|
89.8 ± 1.25efg
|
|
10% - 0.5
|
8.2 ± 2.22a
|
72.1 ± 8.67cde
|
|
10% - 1.0
|
10.1 ± 1.12a
|
69.5 ± 4.07bcd
|
|
10% - 2.0
|
13.8 ± 1.74a
|
80.8 ± 8.47def
|
|
Bran rejectors
|
Control
|
3.4 ± 0.63a
|
0.1 ± 16.62ab
|
|
2% - 0.5
|
3.1 ± 0.86a
|
-34.6 ± 24.01b
|
|
2% - 1.0
|
3.2 ± 0.54a
|
34.6 ± 29.41ac
|
|
2% - 2.0
|
5.7 ± 1.90a
|
-27.0 ± 44.99ab
|
|
2% - 5.0
|
2.5 ± 0.28a
|
37.8 ± 8.79ab
|
|
2% -10.0
|
4.6 ± 1.13a
|
59.6 ± 28.41c
|
|
5% - 0.5
|
3.7 ± 0.44a
|
8.5 ± 27.83ab
|
|
5% - 1.0
|
3.4 ± 1.12a
|
33.4 ± 13.77ab
|
|
5% - 2.0
|
7.7 ± 2.47a
|
9.1 ± 20.79ab
|
|
10% - 0.5
|
3.2 ± 0.45a
|
15.4 ± 20.98ab
|
|
10% - 1.0
|
3.3 ± 1.33a
|
12.2 ± 43.52ab
|
|
10% - 2.0
|
3.3 ± 1.00a
|
-112.0 ± 117.23b
|
|
1Percent of carbaryl
applied-application rate in lb/acre.
2No./yd2.
3A negative percent reduction indicates an increase
in grasshoppers.
Note: Means within columns followed by the same letter are
not significantly different at the 0.1 level (Fisher's protected
SD).
|
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