ABSTRACT Pathogenicity of infective juveniles (IJs) of selected Steinernema spp. on field populations of the red imported fire ant (RIFA), Solenopsis invicta Buren, was ascertained using mound drench and broadcast spray treatments. No statistical differences were found between treatment programs. Monitoring individually marked mounds in treated areas generally provided a higher percent reduction value in mound activity than resulted from monitoring mound per unit area (0.25-acre plot).
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The red imported fire ant (RIFA), Solenopsis invicta, Buren,
has a distribution spanning the southeastern United States and continues
to spread westward through Texas. RIFA is a serious pest impacting the
lives of people both in rural environments. Problems range from a nuisance
pest to life threatening through their sting to people, domestic and wild
animals (Lofgren 1986). Management has focused on the use of insecticides
(Drees and Vinson 1989) and non-chemical solutions are few. The recent
development of low-cost, large-scale production of Entomogenous nematodes
of the genera Steinernema=Neoaplectana and Heterorhabditis (Bedding
1984) has enabled large-scale field testing with modest success against
a number of turf- and soil-infesting insect pests (Kaya 1985, Poinar 1986).
Several researchers have examined the susceptibility of various fire ant
species to strains of S. carpocapsae in laboratory bioassays (Poole
1976, Laumond et al. 1979, Quattlebaum 1980). We decided to further examine
the efficacy of Steinernematidae on field populations of RIFA using a program
if individual mound drench and broadcast spray treatments, and the combination
of these methods.
Materials and Methods
The James Northrup turf farm in Brazoria County, Texas, was selected
as the site for this test. Historically, this farm had received only spot
treatments for RIFA. Circular 0.5 acre (within 0.8 acre square plots) plots
were established for each of 8 treatments, replicated 3 times in a randomized
block design. All active RIFA mounds were marked prior to treatment and
monitored. Mounds were determined to be active if numerous ants emerged
from mounds when disturbed (Frankie, 1983). Treatments were as follows:
1. 1 gal. water per mound
(19 April, 9 May)
2. 2.0 x 105 infective
juveniles (IJ's) per mound (19 April, 9 May)
3. 1.6 x 106 dissected
IJ's per mound (19 April, 9 May)
4. 8.0 x 105 IJ's
per mound (19 April, 9 May)
5. 1.6 x 106 IJ's
per mound (19 April, 9 May)
6. 5 tablespoons hydramethylnon
(Amdro®) per mounds (19 April)
7. 2.0 x 105 IJ's
per mound followed by 200 IJ's per inch2 broadcast (19 April),
with repeated mound drenches (9 May)
8. 1.6 x 106 IJ's
per mound followed by 200 IJ's per inch2 broadcast (19 April),
with repeated mound drenches (9 May)
The mean number of active RIFA mounds per plot was determined for each
treatment and subjected to analysis of variance using the Least Significant
Difference Test (P 0.05)(Microsoft, 1981) for each monitoring date. Percent
reduction was calculated using Henderson's Formula (Henderson and Tilton
1955).
Results and Discussion
No significant differences between the number of active mound per plot
were documented during this demonstration (Table1). High variability and
low number of replications may have been contributing factors. Heavy rains
during the course of the monitoring period resulted in excessive mound
movement in some of the plots. Regardless, percent reduction was calculated
using Henderson's formula (Henderson and Tilton 1955). There was a trend
for all treatments to eventually reduce active RIFA mound numbers relative
to untreated plots. On the 25 April and 3 June evaluation dates, percent
reductions calculated from data generated by monitoring individually treated
and marked mounds were consistently higher than those calculated using
number of active mounds per unit area (0.25-acre plot). Establishment of
satellite mounds or excessive mound movement following nematode drenches
has been observed in earlier tests (Miller, Drees, Vinson, and Georgis,
in press).
References Cited
Bedding, R.A. 1984. Large scale production, storage and transport of
the insect-parasitic nematodes Neoaplectana spp. and Heterorhabditis
spp. Ann. Appl. Biol. 104:117-120.
Frankie, O. F. 1983. Efficacy tests of single-mound treatments for control of red imported fire ant, Solenopsis invicta Buren. Southwestern Entomol. 8:42-45.
Henderson, C.F. and E. W. Tilton, 1955. Tests with acaricides against the brow wheat mite, J. Econ. Entomol. 48:157-161.
Kaya, M. K. 1985. Entomogenous nematodes for insect control in IPM systems. pp. 282-302. In M. A. Hoy and D. C. Herzog, [eds.], Biological control in agricultural IPM systems. Academic Press New York.
Lofgren, C. S. 1986. The economic importance and control of imported fire ants in the United States. pp. 227-256. In S. B. Vinson, [ed.], Economic impact and control of social insects. Praeger Publisher, New York.
Poinar, G. O., Jr. 1986. Entomophagous nematodes. pp.95-122, In J. M. Franz, [ed.], Biological plant and health protection. Gustav Fisher Verlag, New York.
Poole, M. A. 1976. Survey and control efficacy of endoparasites of Solenopsis richteri Forel and S. invicta Buren in Mississippi. Ph.D. dissertation, Mississippi State University, Mississippi State.
Quattlebaum, E. C. 1980. Evaluation of fungal and nematode pathogens
to control the red imported fire ant, Solenopsis invicta Buren.
Ph.D. dissertation, Clemson University, Clemson.
Table 1. Number of active red imported fire ant mounds per 0.25
acre plot and percent reduction in mound activity (Henderson and Tilton
1955) following individual mound treatments of water (drenches), hydramethylnon
(Amdro®) bait or infectious juvenile (IJ) Steinernema spp. parasitic
nematodes or mound drenches (19 April 1988 and May) or nematode mound drenches
plus a broadcast application of nematodes (19 April) in a Brazos County,
Texas commercial turf farm.
| Treatment and dose | 19 Apr. | 25 Apr. | 9 May | 3 June |
| water drench | 8.3a | 6.3a (7.3a) | 3.7a (9.7a) | 6.3a (9.7a) |
| 2.0 x 105 IJ's drench | 14.3a | 7.0a (10.0a)
36% 21% |
5.7a (10.3a)
11% 38% |
3.3a (7.7a)
70% 54% |
| 1.6 x 106
desiccated IJ's drench |
9.7a | 2.7a (4.0a)
63% 53% |
5.0a (8.3a)
0% 27% |
3.7a (6.0a)
50% 47% |
| 8.0 x 105
IJ's drench |
12.7a | 3.3a (5.0a)
66% 55% |
4.7a (6.7a)
17% 55% |
3.3a (5.7a)0
66% 62% |
| 1.6 x 106
IJ's drench |
12.7a | 3.3a (5.7a)
69% 49% |
5.3a (11.0a)
6% 26% |
3.7a (9.0)
61% 39% |
| hydramethylnon
4 tbsp/mound |
15.7a | 6.3a (9.0a)
47% 35% |
3.7a (6.7a)
47% 64% |
2.3a (6.7a)
81% 64% |
| 2.0 x 105
IJ's drench + broadcast (200 IJ's per square inch) |
10.0a | 8.7a (10.0a)
0% 0% |
6.7a (10.3a)
0% 12% |
5.0a (7.7a)
33% 34% |
| 1.6 x 106
IJ's drench + broadcast (200 IJ's per square inch) |
12.0a | 3.0a (5.7a)
67% 46% |
4.0a (6.3a)
25% 55% |
4.7a (8.0a)
48% 43% |
| LSD (P 0.05) | 14.83 | 8.233 (9.939) | 6.968 (9.959) | 4.641 (8.374) |
2/ Means followed by the same letter are not statistically different using the Least Significant Difference analysis of variance (P 0.05).