FIRE ANT PREDATION ON WATERFOWL
 
Bastiaan M. Drees, Professor and Extension Entomologist,
S. Bradleigh Vinson, Professor, Department of Entomology, and
Harold Whitehead, Warden of National Audubon Society
 

The National Audubon Society and the Texas General Land Office have concerns over the invasion of the red imported fire ant, Solenopsis invicta Buren., into the waterbird colonies along the Texas coast natural and man made "spoil" islands.

The red imported fire ant has been documented to feed on hatching eggs (Johnson 1961, 1962, Mount 1981, Mount et al. 1981). However, the impact of this ant behavior on egg clutch survival and nest density in fire ant-infested areas has remained undocumented. In the absence of this information, suppression programs using available control technology are not ecologically and economically justified. Programs using current technology provide only temporary suppression and require repeated applications. Discontinuation of treatments results in re-invasion of the ants to levels that may exceed those prior to initial treatment.

A pilot program was conducted to document the impact of the red imported fire ant suppression program, based on the use of the environmentally acceptable management tactics over time on 1) fire ant activity, 2) waterfowl survival during and after hatching.
 

Materials and Methods

Heavily infested islands at Rollover Pass in east Galveston Bay were selected for this pilot program. These islands are colonized by more than a dozen ground and shrub nesting water birds form March through August, including the great egret, great blue heron, olivaceous cormorant, snowy egret, Louisiana (tricolor) heron, roseate spoonbill, laughing gull, gull-billed tern and Forester's tern.

Treatment regimes were based on a preliminary fire ant survey and the geography of the four Rollover Pass islands. Island 1 and the eastern half of Island 4 were treated on 27 February and 29 September 1989 using the product, Logic® (fenoxycarb), an insect growth regulator, to maintain low levels of fire ant activity Island 3 and the west half of Island 4 were left untreated and had high levels of fire ant activity.

Fire ant mound densities were estimated on 27 February 1989, but thereafter, relative foraging ant activity between treated and infested areas was monitored using olive oil-soaked index cards. Ten one-inch-square cards were positioned in a transect line across each island or island portion. The number of ants associated with each card was estimated after 0.5 to 24 hours of exposure.

During periodic visits, 6 or more randomly-selected, egg-containing waterfowl nests were marked in treated and untreated areas. Numbers of marked nests containing chicks were determined during subsequent visits. Percent mortality was calculated form these sets of marked nests and observations were made to determine cause of death.
 

Results and Discussion (Note: Results presented here are preliminary, representing only two years of data)

A preliminary survey documented an estimated 180 mounds per acre on Islands 1, 3 and 4. Island 2 was found to harbor primarily a native ant species, Monomorium minutum Buckley, the little black ant. The effects of the 27 February 1989 Logic® treatments were not evident during the 1989 breeding season (Table 1).

Survey of nesting waterfowl on 23-24 May 1989 provided no indication of the impact of ants on hatching survival, although some hatchling chick were observed being attacked by red imported fire ants. During June 1989, hurricane Allison flooded the Rollover Pass Islands with a 5 ft. flood and 27 inches of rain. These adverse weather conditions eliminated bird nesting activities and all developing waterfowl. Hurricane Chantal produced 6 inches of rain on the islands on 1 August. Thus, no waterfowl developed on these islands in 1989.

On 21 April 1990, waterfowl nesting was already in progress preventing a spring broadcast application of ant bait. The 29 September 1989 Logic application to the eastern half of Island 4 had resulted in a 91.6 percent reduction in foraging activity. Heavy rains and floods occurred in May. On 1 June 1990, high tides had been occurring causing flooding conditions, and many laughing gull and tri-color heron nest had been submerged.

Although flood-related mortality of hatchling waterfowl was documented in April and May 1990, ant-related mortality on the infested portion of Island 4 was not documented until after June 1. Mortality increased to 100 percent of marked nests through the remainder of the monitoring period (Table 2).
 

Preliminary Conclusions

Literature Cited

Johnson, A. S. 1961. Antagonistic relationships between ants and wildlife, with special reference to imported fire ants and bobwhite quail in the southeast. Proc. Ainu. Conf. Southeast Assoc. Game Fish Comm. 15: 88-107.

Johnson, A. S. 1962. Antagonistic relationships between ants and wildlife, with special reference to imported fire ants and bobwhite quail in the southeastern United States. 100 pp. M. S. thesis, Auburn University, Auburn.

Mount, R. H. 1981. The red imported fire ant, Solenopsis invicta, as a possible serious predator on southeastern vertebrae: Direct observation and subjective impressions. J. Ala. Acad. Sci. 52: 66-70

Mount, R. H., S. E. Truth and W. H. Mason. 1981. Predation of the red imported fire ant, Solenopsis invicta (Hymenoptera: Formicidae), on eggs of the lizard, Cnemidophorus sexlineatus (Squamata: Teiidae).
 


Table 1. Number or red imported fire ant workers associated with olive oil-soaked index card, Rollover Pass Islands, Texas.
 

Average no. foraging red imported fire ants per card-
 
Olive-oil card station Treated Island 4E Untreated Island 4W
23-24 May 1989 31.8 27.6
29 September 1989 14.0 18.1
21 April 1990 2.7* 27.9*
1 June 1990 0.2 180.0
10 July 1990 4.0 19.5
 

* The September 1989 Logic® application in a 91.6 percent reduction of fire ant foraging activity.

 
Back to Results and Discussion


Table 2. Percent mortality of hatching waterfowl on fire ant treated and infested (untreated) part of Roll over Pass Island 4, Galveston Bay, Texas, 1990.

Percent Mortality of hatchling waterfowl
(number of marked nest observations in parentheses)
 
 
Date Treated Untreated
April 21*-May 6 14.3 (7) 50.0 (6)
May 6 - June 1 0.0 (4) 50.0 (4)
June 1* - June 15 10.0 (10) --
June 15*-June 24 N/O 100.0 (?)
June 24*-July 3 N/O 100.0 (5)
July 3*-July 10 N/O 100.0 (3)
July 10-July 20 N/O 100.0 (3)
 
* Dates when sets of nest containing waterfowl eggs were marked for subsequent observation of hatching success.
N/O = Non observed
 
Back to Results and Discussion
 

Acknowledgments

The assistance of Charles Barr, Robert Cavazos, John A. Jackman, and Glenn Avriett was much appreciated.


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