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1 April 2014 Food Preference and Foraging Activity of Ants: Recommendations for Field Applications of Low-Toxicity Baits
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Abstract

Control of ants using baits of low toxicity cannot be effective without knowledge of bait distribution patterns and bait station densities, which are determined by ants' foraging activities. Furthermore, the success of toxic baits also depends upon attractiveness of bait carriers. Here, we assessed ground and vine foraging activity and food preferences for the three ant species (Linepithema humile (Mayr) (Hymenoptera: Formicidae), Anoplolepis custodiens (F. Smith) and Crematogaster peringueyi Emery) under field conditions. We found that L. humile's vineyard foraging activity was high and that movement of ant bait by C. peringueyi and A. custodiens in the vineyard was relatively low. Consequently, more bait stations need to be dispensed for more effective control of C. peringueyi and A. custodiens than for L. humile. Different bait densities are discussed for the various ant species. Food preference trials indicated that vineyard foraging ants preferred wet bait attractants over dry ones, making liquids the most ideal carriers for baiting these ants. Linepithema humile was attracted to 25% sugar water, while C. peringueyi was attracted to both 25% sugar water and honey. Anoplolepis custodiens was attracted to tuna but was also attracted to 25% sugar water. Thus, future bait formulations should be tailor made to suit these specific food requirements if baits are to be successful in ant pest management.

Introduction

In vineyards, the mutualism between ants and the vine mealybug, Planococcus ficus (Signoret) (Hemiptera: Pseudococcidae), results in population explosions of both insects, thereby causing pest injury and economic losses (Kriegler and Whitehead 1962; Way 1963; Myburgh et al. 1973). The Argentine ant, Linepithema humile (Mayr) (Hymenoptera: Formicidae), the cocktail ant, Crematogaster peringueyi Emery, and the common pugnacious ant, Anoplolepis custodiens (F. Smith), are the major pest ants associated with the vine mealybug in South African vineyards (Addison and Samways 2000). Linepithema humile is a cosmopolitan, invasive pest in agricultural and urban areas (Suarez et al. 2001) that nests predominantly in the soil, while C. peringueyi and A. custodiens are of southern African origin, the former nesting in the canopy and the latter in the soil (Addison and Samways 2000). Current recommendations for control include the use of chemical stem barriers, which target only ground nesting species by preventing access into the canopy (Addison 2002). This control method is designed to break the mutualism between the ants and mealybugs so that natural enemies, primarily encyrtid wasps, can effectively control P. ficus without ant interference (Samways 1990).

There is no documented control method for vine-nesting species in South Africa, but lowtoxicity baits could be a viable option, as the recruitment to food sources and subsequent food-sharing behavior of ants can be used to distribute toxicant through the colony no matter where the colony is located (Hooper-Bui and Rust 2000; Rust et al. 2004). Effective control of South African ants using baits of low toxicity is limited by inadequate knowledge on ant foraging activity and optimum bait station density. Optimal density of bait stations per unit area may vary depending on the ant species and the level of ant infestation. If ants have long foraging distances, then bait density could be lower than if ants have short foraging trails. Daane et al. (2006) dispensed liquid baits at 85–620 baits/ha against L. humile in Californian vineyards. At high densities, these baits resulted in fewer L. humile, fewer mealybugs, and less damage to grape clusters. Ant foraging ranges and behavior are affected by a number of factors, such as temperature, circadian rhythm, competition, food availability, food particle size, and photoperiod (Oster and Wilson 1978; Hölldobler and Wilson 1990). Markin (1968), for example, found that L. humile workers foraged up to 45 m away from the nest. Similarly, Ripa et al. (1999) found up to 21% of marked L. humile 54 m from the feeding station. Vega and Rust (2001, 2003) found marked ants up to 61 m from feeding stations. However, ant foraging activity in urban settings may differ from a vineyard because of varying abundance of food resources. Level of infestation by honeydew-producing mealybugs would presumably also impact foraging activity. Although L. humile can forage for long distances, these ants generally nest in close proximity to food sources and relocate nests when nearby food sources become exhausted (Suarez et al. 2001; Tsutsui et al. 2003; Heller and Gordon 2006). In South African citrus orchards, A. custodiens has been observed to forage 111 m away from their nest during peak honeydew production periods and up to 50 m in April, when the mealybugs are abundant (Steyn 1954). No research has been carried out to ascertain C. peringueyi foraging activity.

Different ant species have different dietary requirements, and consequently this must be considered during ant bait formulation. Effective proportions of fat, carbohydrates, and proteins in the bait may differ between species and with the colonies' nutritional needs (Rust et al. 2000). Physical state of the bait, liquid versus solid, and particle size also affect the rate of collection of the bait (Hooper-bui and Rust 2000). Most of the research on ant food preference has been done on L. humile (Baker et al. 1985). To date, no food preference studies have been done in South African vineyards to determine ideal food requirements for L. humile, A. custodiens, or C. peringueyi.

When dissolved in 25% sugar water, preliminary investigations showed that low toxicity baits were non-repellent to foragers (Nyamukondiwa and Addison 2011), palatable, and exhibited sufficient delayed toxicity to allow trophallaxis (Stringer et al. 1964). The present research was aimed at determining (i) the foraging activity (that is the distance each ant travels from its nest to the source of food) of vineyard ants (L. humile, C. peringueyi, and A. custodiens) using liquid baits labeled with a marker and (ii) whether specific bait matrices (different food attractants) had different attractiveness to the three ant species under field conditions. Results of this trial will help us to better determine bait station density, bait distribution patterns, and the best attractant to use when formulating toxicants for the control of these three ant species. This information is critical for the practical use of ant baits in agro-ecosystems.

Materials and Methods

Study sites

Preference trials were carried out during austral spring (October 2007), as this is the optimum time for application of baits because ant populations are low (Nelson and Daane 2007). Foraging activity evaluations were carried out during summer (December 2007, January and February 2008) in the Stellenbosch Winelands region. Ideally this should also have been conducted in spring, but selection of a suitable marker for the ants delayed this experiment. Linepithema humile trials were carried out at Joostenberg farm (33.80S, 18.81E), C. peringueyi at La Motte farm (33.88S, 19.08E), and A. custodiens trials were carried out at Plaisir de Merle farm (33.87S, 18.94E). Drip irrigation was used in all vineyards. The Plaisir de Merle site was a trellised white Chenin blanc vineyard, the La Motte vineyard comprised trellised white Chenin blanc grapes, and the Joostenberg farm had trellised red Pinotage wine grapes. In all vineyards, standard sprays of alphacypermethrin and chlorpyrifos were routinely used to control ants during the growing season.

Experiment 1: Determination of ant foraging Activity

Trial layout and sampling methods. Five bait stations were placed 10 m apart (Daane et al. 2006) on one side of the perimeter of a vineyard block approximately 100 m x 100 m, and ants were allowed to feed on 25% sugar solution that had been labeled with 0.25% calco red (N-1700®, Passaic Color and Chemical Company, Paterson, New Jersey). These foraging activity trials were carried out on three dates (December 2007, January and February 2008). The calco red labeled sugar water was soaked in cotton wool and held in place on Petri dishes. The concentration of calco red dye used followed recommendations from literature (see discussions in Vega and Rust 2001). Ants were allowed to forage on the calco red labeled sugar water for one week before ant sampling was done. The labeled sugar was replenished once during the week because the bait easily dried out due to crystallization of the sugar component.

Seven days after placing baits into vineyards, thirty pitfall traps were arranged in five transects of 1, 2, 4, 8, 16, and 32 m from the bait stations running along the vine rows. All pitfalls ran along vine rows where the baits were placed. Each bait station had one transect associated with it, replicated five times (over five rows 10 m apart) to give a total of 30 traps. Pitfall traps consisted of plastic containers (35 mm diameter × 60 mm height). These were drilled into the soil, and the soil surface was leveled so that the trap rim was flush with the soil surface. Approximately 4 mL of three parts concentrated glycerol and seven parts 70% ethyl alcohol were placed in each of the pitfall traps to preserve the captured ants (following Majer 1978). This liquid is relatively non-volatile. Pitfall traps were left in the vineyard for 48 hours, after which the traps and their catch were collected for laboratory analysis.

When pitfall traps were being collected, tuna baits were used to sample arboreal ant species, as these would not have been sampled in pitfall traps and are also potential pest species. Crematogaster peringueyi forage and nest in the vine canopy, while the other species mentioned nest primarily on the ground. Roughly 5 cm3 of shredded tuna chunks were placed in small plastic containers (70 mm diameter × 7 mm height) at the crutch of vines above each of the pitfall traps along each of the five transects. Ants were left to forage on the tuna for 30 minutes, after which all ants feeding on the tuna bait were collected by sweeping them in different containers containing 70% ethyl alcohol as a preservative.

Ant samples collected from both pitfall and tuna traps were taken to the laboratory for analysis. Calco red positive ants were detected by crushing the ant's abdomen on white paper towels and observing its coloration through a microscope. A pink coloration of the abdomen indicated the presence of calco red.

Experiment 2: Food preference assessments

Eight food attractants (bait matrices) were assessed for their attractiveness to L. humile, C. peringueyi, and A. custodiens during spring (October) 2007. These included: (1) 25% sugar solution; (2) agar (in 25% sugar solution) (Warren Chemical Specialities,  www.warrenchem.co.za); (3) tuna (Pick'n pay,  www.picknpay.co.za); (4) honey (Fleures® Honey Products, Pretoria, South Africa); (5) dog food (Boss® chicken beef and beef platter, Promeal Private Limited, South Africa); (6) dry fish meal; (7) dry sorghum grit; (8) 25% peanut butter (in distilled water) (Nola Yum Yum®, Nola, Randfontein, South Africa). Tests were conducted in vineyards using choice test arenas. Choice test arenas were made of round plastic containers (270 mm diameter by 65 mm height) with eight plastic tubes (125 mm long by 8 mm diameter) that extended through eight openings at 45° in the inside of the choice test arena, as described in Tollerup et al. (2004). The tubes directed all ants to the center of the choice test arena before they could forage on a bait of their choice. Ants were free to move in and out of the choice test arenas during the test period. Five choice test arenas were used (five replicates), and eight bait matrices, approximately 10 mL, were placed in small Petri dishes, which were randomly assigned to positions in the choice test arenas on the perimeter of the test arena. Active ant nests were selected in the vineyards, and each arena was placed close by, with approximately 10 m distance between arenas. Ants were allowed to forage on the baits, and the experiment was replicated at five nests for each of the three ant species. Each experiment started at ~08:00 hours in the morning, after which ant counts occurred hourly for four hours following food deployment. Specifically, this was done by counting the number of ants sitting at each bait matrice at every hour. For L. humile, Rust et al. (2000) reported increased foraging activity in the afternoon compared to mornings, but this may be dependent on microhabitat temperatures, which may differ from in different habitats and has not been tested for L. humile, C. peringueyi, and A. custodienns in a South African context.

Data collection and analysis

The proportion of ants testing positive for calco red for each of the respective distances of the two trapping methods and for each of the three ant species was calculated. For each distance, and for each of the two trapping methods, data were pooled across the five transects. Since the results (proportion of calco red positive ants) were measured under different conditions (months), using standard ANOVA in this case was inappropriate because it fails to model the correlation between the repeated measures. The proportion of ants that carried the dye labeled sugar water at each of the various distances from the bait source for the two trapping methods was therefore calculated for each ant species using repeated measures ANOVA in Statistica 7 (StatSoft,  www.statsoft.com). Tukey-Kramer's post hoc tests were used to identify statistically heterogeneous means. During the food preference tests, the number of ants foraging at each bait station was recorded at hourly intervals up to four hours. Before analysis, data were checked for normality and equality of variances using the Shapiro-Wilk test and Hartley-Bartlett tests, respectively, and in all cases these assumptions were met. Results were then subjected to ANOVA in Statistica 7, and Tukey-Kramer's post hoc test was again used to separate means.

Table 1.

Summary of the effects of distance and month on Linepithema humile foraging distance in small field trials. Bold treatments are statistically significant.

t01_01.gif

Figure 1.

Proportion of Linepithema humile positive of a calco red labeled bait source (where 1.0 = 100%) at different distances from the bait source in a vineyard at Joostenberg farm. There was a significant drop in foraging activity after 2 and 8 m from the vine canopy and on the ground respectively. Ground and vine data were analyzed separately, and means with the same letter are not significantly different (Bars represent ±95% CI). High quality figures are available online.

f01_01.jpg

Figure 2.

Proportion of Anoplolepis custodiens positive of a calco red labeled bait source (where 1.0 = 100%) at different distances from the bait source in a vineyard at Plaisir de Merle farm. Ground and vine data were analyzed separately, and means with the same letter are not significantly different (Bars represent ±95% CI). High quality figures are available online.

f02_01.jpg

Results

Experiment 1: Determination of ant foraging Activity

Linepithema humile. There were no significant monthly differences in L. humile foraging activity during the three different trial dates both on the ground and on the vine (Table 1). However, foraging activity was highly significant both on the ground and in the vine (Table 1), with distance generally decreasing from the bait source for both ground and vine sampled ants, which was to be expected (Figure 1). There was a significant drop in foraging activity after 2 m in the vine canopy and after 8 m on the ground (Figure 1).

Anoplolepis custodiens. The proportion of ants occurring on the ground was generally higher than those occurring in the vine canopy (Figure 2). Nevertheless, a considerable number of ants were caught on the vines, where they were observed tending mealybugs. There were no significant monthly differences in foraging activity during the three trial days (during December, January, and February) both on the ground and on the vine (Table 2). However, foraging distance during the three different months was significant both on the ground and on the vine (Table 2), with distance from the bait source being significant on the ground while on the vine there was no difference in number of marked ants until after 8 m (Figure 2). A significant drop in A. custodiens foraging activity occurred on the ground after 2 m (Figure 2).

Table 2.

Summary of the effects of distance and month on Anoplolepis custodiens foraging distance in small field trials. Bold treatments are statistically significant.

t02_01.gif

Crematogaster peringueyi. Detection of the calco red labeled sugar water again generally decreased with distance from the bait source (Figure 3). The distance foraged by C. peringueyi was highly significant for both ground-sampled and vine-sampled ants (Table 3). Crematogaster peringueyi were more predominant on the vines as opposed to the ground. There were no monthly differences in C. peringueyi foraging activity during the three trial days (during December, January, and February) both on the ground and on the vine (Table 3). Transport of the calco red labeled sugar water dropped significantly after 4 m in the vines and after only 1 m on the ground (Figure 3).

Figure 3.

Proportion of Crematogaster peringueyi positive of a calco red labeled bait source (where 1.0 = 100%) at different distances from the bait source in a vineyard at La Motte farm. Ground and vine data were analyzed separately, and means with the same letter are not significantly different (Bars represent ±95% CI). High quality figures are available online.

f03_01.jpg

Table 3.

Summary of the effects of distance and month on Crematogaster peringueyi foraging distance in small field trials. Bold treatments are statistically significant.

t03_01.gif

Table 4.

Summary of the effects of bait and hour on food preference for Linepithema humile, Crematogaster peringueyi, and Anoplolepis custodiens. Bold treatments are statistically significant.

t04_01.gif

Experiment 2: Food preference assessments

Linepithema humile . Field trials revealed that treatment (baits) and time after bait deployment (measured in hours) were highly significant for this ant species (Table 4). Generally, L. humile was more attracted to sugarbased baits as opposed to protein-based baits. A 25% sugar solution was the most attractive bait and significantly differed from the rest of the treatments (Figure 4). Linepithema humile significantly preferred liquid baits (25% sugar water, honey, and agar) over solid baits (Figure 4). The number of foraging L. humile sigsignificantly increased with time (Figure 5).

Crematogaster peringueyi. There were no significant differences in this ant's preference for 25% sugar solution as compared to 25% honey. These two baits were the most attractive to C. peringueyi and significantly differed from the rest of the treatments (Figure 4). Both bait treatments and time had significant effects on this ant species (Table 4). The number of foraging C. peringueyi significantly increased with time (Figure 5).

Figure 4.

Average number of Linepithema humile, Crematogaster peringueyi, and Anoplolepis custodiens on different food baits during October 2007. Ant species were analyzed separately, and means with the same letter are not significantly different (bars represent ±95% CI). High quality figures are available online.

f04_01.jpg

Figure 5.

Average number Linepithema humile, Crematogaster peringueyi, and Anoplolepis custodiens on food baits over time in spring. Ant species were analyzed separately, and means with the same letter are not significantly different (bars represent ±95% CI). High quality figures are available online.

f05_01.jpg

Anoplolepis custodiens. Bait treatments had a significant effect during the field trials (Table 4). Anoplolepis custodiens was significantly attracted to tuna more than the other treatments (Figure 4). The number of foraging A. custodiens significantly increased over time (Figure 5).

Discussion

Linepithema humile had the highest proportion of ants foraging at 32 m, with C. peringueyi having the lowest proportion (Figures 1-3). The former are successful and aggressive competitors that generally dominate rapidly over other ant species (Hölldobler and Wilson 1990). They are unicolonial, meaning that ants from one colony are not aggressive to non-nestmates (Passera and Keller 1994). Markin (1968) found that, after five days, the exchange of worker ants between neighboring nests exceeds 50%. In this manner, L. humile can easily form supercolonies that can saturate an entire habitat. Nelson and Daane (2007) also found that L. humile is extremely vagile in Californian vineyards, whereas in citrus orchards Markin (1967, 1968) and Ripa et al. (1999) found that L. humile foraging seldom exceeds 61 m from a nest. Our research was limited to 32 m, as placing baits further apart would probably not result in effective control (see Daane et al. 2006). Linepithema humile foraged equally effectively on the ground and in the vine canopy, as indicated by the proportion of workers caught in each of the traps (pitfalls vs. food baits in the canopy).

The proportion of the arboreal C. peringueyi sampled on the ground were very low and inconsistent, confirming their arboreal foraging habits. The majority of ants foraged no further than 4 m from the bait source, both on the ground and in the vine canopy, indicating a very limited foraging area. Anoplolepis custodiens indicated a foraging distance of up to 8 m, that distance being where the highest proportion of workers were trapped, with more foraging occurring on the ground than in the vine canopy. This trial was conducted in summer when honeydew excretion by mealybugs was at its peak, thus giving honeydewfeeding ants the opportunity to forage in the vines. The large foraging activity ranges for L. humile compared to C. peringueyi and A. custodiens have implications for bait distribution density. To be economically viable, Daane et al. (2006) recommended that baits be dispensed at 85 baits/ha or less. Our results reveal that at 81 baits/ha (one bait every 9 m), low toxicity baits will reach ±80% of the L. humile population, only ±30% of A. custodiens workers, and ±20% C. peringueyi workers. Lower foraging activities for A. custodiens and C. peringueyi imply higher bait densities for effective ant control. At high densities, baits of low toxicity will less likely be adopted by growers because of the costs of materials and maintenance involved. However, bait distribution density also depends upon the size of the ant infestation. Thus, all these factors must be considered, including monitoring for pest intensity before determining optimum bait density.

The results further showed that all three species preferred the 25% sugar solution over the other baits offered, except for A. custodiens, which preferred tuna. There was a general trend towards preference for liquid or moist baits compared to drier baits, such as dog food and fish meal, for all three ant species. Markin (1970) estimated that 99% of L. humile's diet consists of honeydew and nectar. Sucrose is the main ingredient of honeydew (Tennant and Porter 1991) and forms a significant part of nectar (Baker and Baker 1985). Baker et al. (1985) carried out food preference trials on L. humile and concluded that this ant preferred 25% sugar solution or honey over other solid protein based foods like tuna. Silverman and Roulston (2001) compared the consumption of gel and liquid sucrose formulations by L. humile, and results indicated that this species preferred foraging on the gel formulations, which was not supported by our study, although agar and honey were more preferred over drier baits. Crematogaster peringueyi is a vineyard ant that forages on mealybug honeydew (Kriegler and Whitehead 1962; Addison and Samways 2000), which also explains its attraction to sugar and honey baits during the food preference tests. Anoplolepis custodiens is a highly predatory ant species that preys on many insects in South Africa (Steyn 1954; Löhr 1992). Its predatory nature would account for this ant being most attracted to tuna.

High attractiveness of 25% sugar solution to L. humile and C. peringueyi indicates that liquid sugar baits are the most appropriate attractants/carriers for baiting these two species in future pest control. This bait matrix has the advantage that it is cheap and readily available, but it is prone to drying out (due to sugar crystallization) and fungal attack. Furthermore, when formulating toxicants for baiting A. custodiens, wet protein attractants, like tuna, are the most ideal bait matrix for maximum effectiveness and should be taken into account. The number of ant foragers at bait stations significantly increased with time, as would be expected due to pheromone calling and establishment of foraging trails (Goss et al. 1990; Greenberg and Klotz 2000).

The results of the present study on foraging activity of different ant species are not definitive. More research needs to be done before we can fully understand bait distribution patterns and bait station density. Foraging behavior of ants depends upon a number of environmental factors, one of which is the availability of food sources. Foraging activity field trials were done in summer when honeydew excreted by P. ficus and grape juice from the ripening grape clusters were at their peaks. Therefore, this is the time when ant baits would be at their least effective. We presume that ants forage for shorter distances during this time of the year, since food resources will be highly abundant and in close proximity. Nelson and Daane (2007) hypothesized that ant foraging on 25% sugar water peaks in spring. Rust et al. (2000) showed that L. humile foraged 26–60% and 16–40% of available protein in summer and winter respectively, suggesting considerable seasonal differences in activity and bait preferences. Thus, further research should focus on repeating the study in spring and autumn to deduce whether increased labeled bait acceptance will translate to increased bait movement in the vineyard. Furthermore, little is known about C. peringueyi intra-and interspecific competition, and thus more research should focus on assessing its dominance or lack thereof, which is one of the factors that will determine this ant's foraging behavior. Food preference may also differ depending on season, and consequently more research still needs to be done on species' seasonal food requirements (protein, lipids, and carbohydrates).

Acknowledgements

We are grateful to Professor Martin Kidd and Professor Daane Nel for their assistance with data analysis. We are also grateful to Matthew Addison for the critical comments on this manuscript and assistance with the calco red experiments. This work is based on the research supported in part by the National Research Foundation of South Africa (grant specific unique reference number (UID) 71909) and was further funded by Winetech. The bait arena was developed by researchers at the University of California, Riverside.

References

1.

P Addison , MJ. Samways 2000. A Survey of Ants (Hymenoptera: Formicidae) That Forage in the Western Cape Province, South Africa. African Entomology 8: 251–260. Google Scholar

2.

P. Addison 2002. Chemical stem barriers for the control of ants (Hymenoptera: Formicidae) in vineyards. South African Journal of Enology and Viticulture 23: 1–8. Google Scholar

3.

HG Baker , I. Baker 1985. Studies of nectar constitution and pollinator-plant coevolution, In: LE Gilbert , PH Raven , Editors. Coevolution of animals and plants. pp. 100–140. University of Texas Press. Google Scholar

4.

TC Baker , SE Van Vorhis Key , LK. Gaston 1985. Bait preference tests for Argentine ants (Hymenoptera: Formicidae). Journal of Economic Entomology 78: 1083–1088. Google Scholar

5.

KM Daane , KR Sime , BN Hogg , ML Bianchi , ML Cooper , MK Rust , JH. Klotz 2006. Effects of liquid insecticide baits on Argentine ants in California's coastal vineyards. Crop Protection 25: 592–603. Google Scholar

6.

SR Goss , JL Beckers , SA Deneubourg , JM. Pastels 1990. How trail laying and trail following can solve foraging problems for ant colonies. In: Hughes RN, Editor. Behavioral mechanism of food selection. NATO ASI Series 93: 119–192. Google Scholar

7.

L Greenberg , JH. Klotz 2000. Argentine ant (Hymenoptera: Formicidae) trail pheromone enhances consumption of liquid sucrose solution. Journal of Economic Entomology 93: 119–192. Google Scholar

8.

NE Heller , DM. Gordon 2006. Seasonal spatial dynamics and causes of nest movements in colonies of the invasive Argentine ant (Linepithema humile). Insect Sociology 51: 378–386. Google Scholar

9.

B Hölldobler , EO. Wilson 1990. The Ants. Harvard University Press. Google Scholar

10.

LM Hooper-bui , MK. Rust 2000. Oral toxicity of Abamectin, boric acid, Fipronil and hydramethylnon to groups of workers and queens of the Argentine ant Linepithema humile (Mayr). Journal of Economic Entomology 93: 858–864. Google Scholar

11.

PJ Kriegler , VB. Whitehead 1962. Notes on The Biology and Control of Crematogaster peringueyi var. angustior (Arnold) on Grape Vines. Journal of the Entomological Society of Southern Africa 25: 287–290. Google Scholar

12.

B. Löhr 1992. The pugnacious ant Anoplolepis custodiens (Hymenoptera: Formicidae) and its beneficial effects on coconut production in Tanzania. Bulletin of Entomological Research 82: 213–218. Google Scholar

13.

JD. Majer 1978. An improved pitfall trap for sampling ants and other epigaeic invertebrates. Journal of the Australian Entomological Society 17: 261–262. Google Scholar

14.

GP. Markin 1967. Food distribution with colonies of the Argentine ant, Iridomyrmex humilis (Mayr). PhD Dissertation, University of California-Riverside. Google Scholar

15.

GP. Markin 1968. Nest relationships of the Argentine ant, Iridomyrmex humilis (Hymenoptera: Formicidae). Journal of Economic Entomology 41: 511–516 Google Scholar

16.

GP. Markin 1970. The seasonal life cycle of the Argentine ant, Iridomyrmex humilis (Hymenoptera: Formicidae), in southern California. Annals of the Entomological Society of America 63: 1238–1242. Google Scholar

17.

AC Myburgh , V Whitehead , CC. Daiber 1973. Pests of Deciduous Fruit, Grapes and Miscellaneous Other Horticultural Crops in South Africa. Entomology Memoirs. Department of Agriculture and Technical Services, Pretoria 27: 1–38. Google Scholar

18.

EK Nelson , KM. Daane 2007. Improving liquid bait programs for Argentine ant control: Bait Station Density. Environmental Entomology 36: 1475–1484. Google Scholar

19.

C Nyamukondiwa , P. Addison 2011. Preference of foraging ants (Hymenoptera: Formicidae) for bait toxicants in South African vineyards. Crop Protection 30: 1034–1038. Google Scholar

20.

GF Oster , ZO. Wilson 1978. Caste and ecology of social insects: Monographs in population biology number 12. Princeton University Press. Google Scholar

21.

L Passera , L. Keller 1994. Mate availability and male dispersion in Argentine ant Linepithema humile (Mayr) (=Iridomyrmex humilis). Animal Behavior 48: 361–369. Google Scholar

22.

R Ripa , F Rodriguez , MK Rust , I. Carral 1999. Distribution of liquid food and bait in colonies of Argentine ant (Hymenoptera: Formicidae). In: Proceedings 3rd International Conference on Urban Pests, Prague, Czech Republic . pp. 225–229. Grafické závod. Google Scholar

23.

MK Rust , DA Reierson , E Paine , LJ. Blum 2000. Seasonal activity and bait preferences of the Argentine ant (Hymenoptera: Formicidae). Journal of Urban Entomology 17: 201–212. Google Scholar

24.

MK Rust , DA Reierson , JH. Klotz 2004. Delayed toxicity as a critical factor in the efficacy of aqueous baits for controlling Argentine ants (Hymenoptera: Formicidae). Journal of Economic Entomology 97: 1017–1024. Google Scholar

25.

MJ. Samways 1990. Ant assemblages, structure and ecological management in citrus and subtropical fruit orchards in southern Africa. In: R Vander Meer , K Jaffe , A Codeno , Editors. Applied Myrmecology: A world perspective. Westview Press. Google Scholar

26.

J Silverman , TH. Roulston 2001. Acceptance and intake of gel and liquid sucrose compositions by the Argentine ant (Hymenoptera: Formicidae). Journal of Economic Entomology 94: 511–515. Google Scholar

27.

JJ. Steyn 1954. The Pugnacious Ant; Anoplolepis custodiens (Smith) and its Relation to the control of Citrus Scales at Letaba. Memoirs of the Entomological Society of Southern Africa 3: Pretoria. Google Scholar

28.

CE Stringer , CS Lofgren , FJ. Burtlett 1964. Imported fire ants toxic bait studies: evaluation of toxicants. Journal of Economic Entomology 57: 941–945. Google Scholar

29.

AV Suarez , DA Hollway , TJ. Case 2001. Patterns of spread in biological invasions dominated by long distance jump dispersal: Insights from Argentine ants. Proceedings of the National Academy of Science USA 98: 1095–1100. Google Scholar

30.

LE Tennant , SD. Porter 1991. Comparison of diets of two fire ant species (Hymenoptera: Formicidae): solid liquid components. Journal of Entomological Science 26: 50–465. Google Scholar

31.

ND Tsutsui , AV Suarez , RK. Grosberg 2003. Genetic diversity, asymmetrical aggression and recognition in a widespread invasive species. Proceedings of the National Academy of Science USA 100: 078–1083. Google Scholar

32.

K Tollerup , M Rust , K Dorschner , P Phillips , J. Klotz 2004. Low-toxicity baits control ants in citrus orchards and grape vineyards. California Agriculture 58: 213–217. Google Scholar

33.

SY Vega , MK. Rust 2001. Developing marking techniques to study movement and foraging of Argentine ants (Hymenoptera: Formicidae). Sociobiology 37: 27–39. Google Scholar

34.

SY Vega , MK. Rust 2003. Determining the foraging range and origin of resurgence after treatment of Argentine ant (Hymenoptera: Formicidae) in urban areas. Journal of Economic Entomology 96: 844–849. Google Scholar

35.

MJ. Way 1963. Mutualism between ants and honeydew producing Homoptera. Annual Review of Entomology 8: 307–344. Google Scholar
This is an open access paper. We use the Creative Commons Attribution 3.0 license that permits unrestricted use, provided that the paper is properly attributed.
Casper Nyamukondiwa and Pia Addison "Food Preference and Foraging Activity of Ants: Recommendations for Field Applications of Low-Toxicity Baits," Journal of Insect Science 14(48), 1-13, (1 April 2014). https://doi.org/10.1673/031.014.48
Received: 24 April 2012; Accepted: 1 February 2014; Published: 1 April 2014
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