Biological Control Using Ants: Current Status, Opportunities, and Limitations
by
,
Junir Antônio Lutinski
1,*
,
Cladis Juliana Lutinski
2,
Alécio Ortiz
1,
Fernanda Staub Zembruski
1,
Marcia Orth Ripke
1 and
Flávio Roberto Mello Garcia
3
1
Health Sciences Pos Graduate Program, Universidade Comunitária da Região de Chapecó (Unochapecó), Chapeco 89809-900, SC, Brazil
2
Biology Laboratory, Universidade Federal da Fronteira Sul (UFFS), Chapeco 89815-899, SC, Brazil
3
Departamento de Ecologia, Zoologia e Genética, Instituto de Biologia, Universidade Federal de Pelotas, Pelotas 96010-900, RS, Brazil
*
Author to whom correspondence should be addressed.
Agronomy 2024, 14(7), 1558; https://doi.org/10.3390/agronomy14071558
Submission received: 30 May 2024
/
Revised: 2 July 2024
/
Accepted: 9 July 2024
/
Published: 18 July 2024
(This article belongs to the Section Pest and Disease Management)
Abstract
:Interest in biological pest control using ants in agroforestry and agricultural systems has increased in recent decades due to the diversity and abundance of these insects in different ecosystems. Biological pest control has emerged as an alternative to reduce the impact of production on agroecosystems, and ants play a crucial role in this context. Therefore, this study aimed, based on an extensive and rigorous literature review, to describe the potential of ants as biological control agents, as well as the pests that have been targeted by this control. The search was carried out between July and November 2023, using databases such as Lilacs, Scielo, and Google Scholar. The selected descriptors were “Predatory ants”, “Natural enemy ants”, and “Chemical defense ants”, used in Portuguese, English, and Spanish. These terms were used in isolation and with the Boolean operator “AND”. A total of 47 articles published between 1976 and 2023 were reviewed. The results showed that 34 genera and 70 species of ants have potential for use in biological control. Among the most notable genera are Camponotus, Crematogaster, Oecophylla, Pheidole, Solenopsis, and Wasmannia. Their role as biological control agents can be complementary, contributing to the maintenance and balance of agroecosystems through pest predation, which can reach 100% efficiency. The predatory potential of ants has been verified, with an emphasis on biological control against invertebrate pests of cultivated plants. Among the pests potentially controlled by ants are mites, coleopterans, fruit flies, bedbugs, lepidopterans, thrips, mollusks, and other ants. The scientific literature already contains robust evidence proving the potential of ants as biological control agents, especially for invertebrate pests.
1. Introduction
The search for sustainable production in agroecosystems and the food and nutritional security of the population has been a constant, with pesticides at the center of this context over the last few decades [1]. The movement of people and international trade, combined with climate change, has resulted in the dispersal and population growth of many organisms with the potential to become agricultural pests [2]. On the one hand, the emergence of resistance to products already in use has led to a search for new molecules and new pesticides capable of meeting production demands [3] and an increase in the volume of pesticides used. On the other hand, there is increasing pressure from consumer markets for safer products and from society in general, which advocates for less environmental impact from production chains [4]. In this context, biological pest control is emerging as an alternative to reduce the effect of production on agroecosystems.
Historically, biological pest control has been consolidated as an alternative where natural enemies regulate the density of organisms with the potential to become pests while also helping to reduce damage and production costs [5]. Biological control minimizes the use of pesticides and helps maintain biodiversity [6]. Ants are among the organisms potentially contributing to biological pest control [7]. These insects occupy the most varied trophic niches in their ecosystems, emphasizing the predation of other invertebrate organisms and some species’ chemical interactions of defense and repellency [8].
Ants (Hymenoptera: Formicidae) represent a diversity of 22 subfamilies, 503 genera, and 15,876 valid species [9]. They are a dominant group of terrestrial fauna that play a variety of roles in the ecosystems they inhabit, such as the degradation of organic matter, nutrient recycling, soil aeration, seed removal, and predation [1,10]. Among the characteristics that make ants of interest in agroecosystems and biological control are their abundance, diversity, dominance, ease of sampling, sensitivity to environmental disturbances, and the numerous ecological interactions they have with other organisms such as fungi, animals, and plants [9,11].
The predatory nature of some ant taxa stands out in regulating the structure and function of the ecosystems in which they are found [12], suppressing the populations of their prey, and reducing the abundance and distribution of species with the potential to become pests [13,14]. The predatory potential of ants in controlling agricultural pests has been the subject of studies worldwide in different crops, biomes, soils, and climatic conditions, both in isolation and integrated with other control mechanisms [1].
Another mechanism developed by ants that has been studied in the context of ecology and agroecosystems is chemical defense [15]. This is a prominent feature of the adaptive behavior of some ant species that produce and release complex chemical compounds, often endowed with bioactive properties such as toxins and defensive pheromones [16,17]. The potential of ants to control agricultural pests, especially herbivores, derives from studies carried out in Africa, America, and Asia. However, this knowledge is fragmented and needs to be systematized.
Considering the need for constant progress in the search for sustainable agricultural pest management practices, the ecological role of ants as predators, and the chemical defense used by some of these insects, interest in the potential of these organisms in biological pest control is emerging [18,19]. By feeding on insects that are harmful to crops, ants help regulate pest populations naturally, reducing the need for chemical interventions [20] and, consequently, contributing to lower production costs, food safety, and human health. Therefore, this study was based on the following problem: what does the scientific literature say about the potential of ants for biological pest control in agroecosystems? Its objectives were: (a) to map scientific production on the predatory role of ants and the chemical defense of these insects against pests in agroecosystems and (b) to list the species of ants and pests that have been the target of studies on biological control.
2. Materials and Methods
2.1. Study Characterization
An integrative literature review was conducted to examine the scientific literature on ants’ potential as biological control agents. The integrative literature review is a research method that enables synthesizing and analyzing existing theoretical and empirical literature on a given phenomenon [13,21]. This method provides new questions, reflections, and criticisms, potentially identifying gaps and advancing knowledge in the field.
2.2. Search, Selection, and Inclusion of Articles
The following steps were followed in the integrative review: (1) Identifying the research question; (2) Searching the scientific literature, establishing inclusion and exclusion criteria, and selecting the studies; (3) Categorizing the results found; (4) Evaluating the selected articles; (5) Analyzing, interpreting and discussing the results; (6) Synthesizing the information and producing knowledge [21].
The following study question was formulated to guide the integrative review: What does the scientific literature say about the potential of ants in the biological control of pests in agroecosystems? A search for articles was carried out from July to November 2023, with no restriction on the time of publication, in the following databases: Lilacs, Scielo, and Google Scholar. The descriptors selected were “Predatory ants”, “Natural enemy ants”, and “Chemical defense ants”, used in Portuguese, English, and Spanish. These terms were used in isolation and with the Boolean operator “AND”.
Only articles were selected, excluding theses, dissertations, monographs, and abstracts. The inclusion criteria were articles that, after reading the title and abstract, were related to the study problem. After this stage, the selected articles were read in their entirety and once again assessed for their relevance to the topic. The consulted time series were not restricted, but only open-access studies were included. All selected articles were downloaded to a Portable Document Format (.pdf) electronic directory. A total of 531 articles were identified initially. The preliminary analysis involved reading the titles, abstracts, and keywords. Based on this pre-analysis, 40 articles that answered the study question were selected for the review (Appendix A).
The articles that met the eligibility criteria were read, and relevant information was extracted and tabulated in an Microsoft Excel database (.xlsx) v. 2010 (14.0.7268.5000). The information extracted included year of publication, scientific journal, authors, title, country where the study was carried out, objective, species or genus evaluated, focus (predators or chemical defense), summary, and conclusion. Tabulating this information allowed for systematic organization and analysis of the selected articles, facilitating the synthesis of findings and identification of key insights related to the potential of ants in biological pest control within agroecosystems.
3. Results
We included 47 articles published between 1976 and 2024. Studies have historically emphasized ants’ predatory role and, more recently, chemical defense (Figure 1).
The crops evaluated in the studies include cotton, peanuts, sugar beets, coffee, sugarcane, beans, corn, and soybeans. In the context of fruit growing, the studies covered banana, cashew, citrus, coconut, mango, pequi, and peach orchards. The role of ants in balancing the agroecosystem, interactions with other predators and parasitoids, and comparisons between conventional and organic crops were also covered (Table 1).
Ants from seven subfamilies with potential for biological control were listed. Myrmicinae was the most included with 12 genera and 28 species, followed by Formicinae with 8 genera and 17 species, Dolichoderinae with 7 genera and 6 species, Ponerinae with 4 genera and 8 species, Ectatomminae with 2 genus and 7 species, Pseudomyrmecinae with 1 genus and 4 species, and Dorylinae with 1 genus. The diversity reported in the articles was distributed across five continents (Africa, America, Asia, Europe, and Oceania) (Table 2).
The predatory potential of ants was verified, emphasizing biological control against herbivorous invertebrates of cultivated plants carried out by ants Anoplolepis sp., Dolichoderus sp., Oecophylla sp., and Wasmannia sp. Specifically, as biological control agents of the coffee berry borer Hypothenemus hampei (Ferrari, 1867) (Coleoptera: Scolytidae), the species Pseudomyrmex ejectus, Pseudomyrmex simplex, Solenopsis geminata, Tetramorium bicarinatum, Tetramorium simillimum, and Wasmannia auropunctata were identified. In the control of Diatraea saccharalis (Fabricius, 1794) (Lepidoptera, Pyralidae) in sugarcane (Saccharum officinarum L.), the ants Camponotus atriceps, Crematogaster sp., Dorymyrmex sp., Ectatomma ruidum, Pheidole sp., and Solenopsis invicta were noted. For the control of tephritid fruit flies (Diptera: Tephritidae), the ants Dorymyrmex sp., Ectatomma brunneum, Formica fusca, Leptotorax sp., Odontomachus brunneus, Oecophylla longinoda, Pheidole gertrudae, Pheidole megacephala, Pheidole oxyops, Solenopsis sp., Solenopsis invicta, and Solenopsis geminata were observed (Table 2).
4. Discussion
The potential of ants as biological control agents in agroecosystems, especially as predators, has been explored since the 1970s [22,66]. Studies have focused on different crops [23,37,38,47,52,53], types of cultivation [26,57,62,63], and the role of these insects in the ecological balance and sustainability [39,50,51] of these environments. However, since the year 2000, there has been an intensification of studies related to ant fauna. Among the studies that contributed to this increase in scientific production was the work by Hölldobler and Wilson [8], which gathered information on the biology, ecology, biodiversity, and biogeography of these insects, encouraging researchers around the world to consider them as subjects of their research. In the field of taxonomy, an important advancement was the work of Barry Bolton, which resulted in an online database that gathers and updates information from all over the world on the classification of ants [9].
Regarding distribution, the studies included in this review were conducted on five continents, with contributions from America, Europe, Africa, Asia, and Oceania. The studies conducted in the Americas addressed the role of ants in agroecosystems more comprehensively, including biological control through predation [38,41], chemical defense [31], as well as interaction with other organisms beneficial to production [31,36]. The reviewed studies from other continents emphasized biological control by ants. Similarly, the studies conducted in America covered a greater diversity of crops such as cotton, peanuts, beets, coffee, sugar cane, cabbage, beans, corn, soybeans [23,24,27,31,34], fruits such as Citrus sp. and peaches [7,43], and chemical defense against herbivores [31]. Studies conducted in Europe have emphasized the potential of the species Linepithema humile in Portugal [28], Myrmicaria opaciventris in France, and Crematogaster scutellaris in Italy [32,63], all focused on biological control. The African studies focused on the ant Oecophylla longinoda against cashew pests [49] and Pheidole megacephala in coffee crops [52]. In Asia, the potential of Monomorium floricola, Crematogaster sp., Technomyrmex albipes, and Oecophylla smaragdina in palm plantations was evaluated [23]. Studies from Oceania (both conducted in Australia) evaluated the weaver ant (Oecophylla smaragdina) for the control of the red thrips Selenothrips rubrocinctus and Amblypelta lutescens [64].
The biodiversity of ants listed in this review can be attributed to a greater concentration of studies on the American continent, where most of the subfamilies and most of the genera and species listed are native. Myrmicinae comprises a subfamily with 147 genera and 7133 valid species [9], ranging from highly specialized species to generalists, from predators to fungus cultivators [67,68]. Ant species such as Crematogaster, Pheidole, Solenopsis, and Wasmannia nest and forage in soil, leaf litter, and vegetation. They are tolerant of modified environments, including agroecosystems. Their omnivorous diet, which includes a variety of small invertebrates [69], underscores their significance in biological control and ecosystem balance.
Formicinae includes 52 genera and 3265 valid species, among which the Camponotus genus stands out, with 1087 species distributed on all continents except Antarctica [9]. Ants from this genus are notable for their variety of niches in ecosystems, their tolerance to different environments, and the generalist nature of some species [68,69]. The Formica genus comprises 179 valid species in Asia, Europe, North and Central America, and northwest Africa [9], sharing characteristics and habits with the Camponotus genus [70]. Oecophylla consists of three valid species distributed in Africa, Asia, and Oceania. Known as weaver ants, dominant in the forest canopy, their colonies can exceed 500,000 individuals and construct hundreds of nests in various trees, fiercely defending them against other colonies. They are predators of insects in both vegetation and ground habitats [8]. Conversely, Nylanderia fulva and Paratrechina longicornis are South American ants that are invasive, generalists, and opportunists in soil and vegetation [69,71], justifying their potential as biological control agents.
Dolichoderinae comprises 28 genera and 714 valid species distributed across all continents except Antarctica [9]. The genus Azteca stands out, with 84 species occurring in the Americas. These ants nest and forage in vegetation, with some species forming obligatory associations with plants of the Cecropia genus [72]. The chemical defense exhibited by Dolichoderinae ants against invertebrate pests, including other ants, has been the subject of numerous studies [69]. Ponerinae (50 genera and 1275 valid species), along with Ectatomminae (12 genera and 305 valid species), Dorylinae (27 valid genera and 756 valid species), and Pseudomyrmecinae (3 genera and 235 valid species) [9], encompass a cosmopolitan ant fauna, excluding Antarctica. These ants are predators from the soil and leaf litter to the forest canopy, specializing in various niches and preying on invertebrates and small vertebrates [66,69,73,74]. Some species tolerate environmental changes and are frequently encountered in agroecosystems, highlighting their potential as biological control agents and ecosystem regulators.
Most of the literature consulted has underscored the potential of ants as biological control agents in agroecosystems. Way et al. [23] recorded the predation of Opisina arenosella eggs by Oecophylla smaragdina. Perfecto [24] verified the predation of the corn caterpillar Spodoptera frugiperda and the corn leafhopper Dalbulus maidis by Pheidole radoszkowskii and Solenopsis geminata, as well as the reduction in damage caused by the cartridge caterpillar to corn plants. The presence of predatory ants under the plants can interfere with the presence of other arthropods [55], benefiting the crop. Knutson and Campos [38] described Solenopsis invicta ants as beneficial to production in Texas despite the pest role attributed to the species in the United States of America. Fernandes et al. [41] described the role of this ant in reducing pest populations at the start of bean cultivation, while Baldwin et al. [14] highlighted its potential in controlling Helicoverpa zea. Additionally, this ant can impact the community of epigeic arthropods, both harmful and beneficial to production in aggregate ecosystems, making its benefit dependent on the management adopted in production [45].
Population control of Diatraea saccharalis by predatory ants was verified by Rossi and Fowler [34]. Sujii et al. [35] confirmed the pasture leafhopper (Deois flavopicta) predation by Pachycondyla obscuricornis. Queiroz, Almeida, and Pereira [20] gathered evidence of the impact of predation by Formica polyctena on various insects, as well as by the ants Ectatomma ruidum and Ectatomma tuberculatum on coffee pests and Solenopsis invicta on insects attacking cotton and soybean crops. Santos et al. [37] also reported the foot-washing ant Solenopsis invicta as a predator of immature specimens of Anthonomus grandis in cotton crops. Milligan et al. [52] documented a 12% reduction in the population of Sesamia calamistis attributed to the ant Pheidole megacephala, while Larsen and Philpott [42], Morris et al. [58], and Martins et al. [65] presented evidence that ants reduce the infestation of the coffee berry borer Hypothenemus hampei.
The predation of the psyllid Cacopsylla pyricola by ants was reported by Paulson and Akre [25]. Rodrigues et al. [42] documented the role of Pseudomyrmex termitarius in predating Toxoptera citricida in mandarin orchards. Abeijon et al. [7] described the predation of Anastrepha fraterculus larvae by Pachycondyla, Pheidole, Pogonomyrmex, and Solenopsis ants, as well as their role in biological control of tephritid flies [20,60]. However, these and other reviewed studies have suggested that ants sometimes play a supportive role as predators in both orchards and agroecosystems in general [27,31]. Thus, the effectiveness of these insects in biological pest control depends on their interaction with other predators and the management practices adopted in each case.
In this regard, Way and Khoo [26] emphasized that ants serve as an alternative to chemical insecticides when such practices are not feasible or when production systems prohibit the use of synthetic compounds. Schifani et al. [63] also underscored the role of ants as supplements in integrated pest management strategies, while Lange et al. [39] noted that the no-till system can sustain a more diverse and abundant ant fauna, thereby enhancing the environmental quality of the crop.
Additionally, Way, Paiva, and Cammell [28] described the activity of the ant Linepithema humile in extensive areas due to their existence as supercolonies. Mendonça and Romanowski [30] reported the predation of Eugeniamyia dispar by ants Pseudamyrmex sp. and Pheidole sp., while Kenne et al. [32] highlighted the role of Myrmicaria opaciventris as a biological control agent against termites. The predation of thrips Selenothrips rubrocinctus by weaver ants (Oecophylla) was reported by Peng and Christian [33]. Peng, Christian, and Reilly [46] reported that the aggressive behavior of Oecophylla smaragdina repels pests from the shoots of African mahogany. Some ant species are important predators of the pasture tick (Rhipicephalus (B.) microplus). Veríssimo [47] discussed the role of Nylanderia fulva in the biological control of Atta spp. Regarding chemical defense, Vandermeer et al. [31] indicated that the ant Azteca sp. has potential as a pest control agent due to its positive effect on insect pests, highlighting its potential as a biological control agent.
Despite the outstanding potential of ants in the biological control of pests, the antagonistic role of predatory and/or generalist species of these insects on other natural enemies involved in biological control must be considered. The association between Camponotus ants and aphids (Hemiptera: Aphididae) is well documented in the scientific literature [68]. The protection from predators and parasites provided by the ants to the aphids is rewarded by the production of honeydew, thus establishing a symbiotic relationship. The negative impact of invasive ants such as Linepithema humile [62] and Solenopsis invicta [20,44] on other natural enemies and, consequently, on the ecological balance is also well known.
In this context, Milosavljević et al. [75] analyzed the effects of ants on the population regulation of Diaphorina citri Kuwayama (Hemiptera: Liviidae) by the parasitoid Tamarixia radiata (Waterston) (Hymenoptera: Eulophidae) in southern California over four years. The presence of the ant Linepithema humile increased D. citri densities threefold, indicating the need to control this ant to maximize the biological control of the psyllid. Hoddle et al. [76] found that Linepithema humile protects D. citri from natural enemies and highlighted the need to control this ant species to increase the effectiveness of natural enemies against D. citri.
On the other hand, in the context of predation, there is no consensus on the impact of ants on the ecological balance of agroecosystems. Janssen et al. [77] gathered evidence that, contrary to expectations, there is no increase in pest populations due to intraguild predation, even when the predator is the inferior natural enemy. These authors suggested that the introduction of generalist natural enemies, often intraguild predators, may not affect the biological control performed by native natural enemies.
5. Conclusions
It was possible to list 32 genera and 47 species of ants with potential for use in biological control. The most prominent genera are Camponotus, Crematogastes, Oecophylla, Pheidole, Solenopsis, and Wasmannia. Their role as biological control agents can be complementary, contributing to the maintenance and balance of agroecosystems through pest predation, with efficiency rates reaching up to 100%.
However, there are limitations to the use of ants as biological control agents. One such limitation is the need for taxonomic knowledge, as species within the same genus can sometimes become pests; for example, pests of citrus, corn, and coffee grown around the world, but with ant species’ distribution restricted to a particular region or continent. Additionally, the distribution of predator species does not always align with the dispersal area of the pests, which can be considered another significant limiting factor.
Some ants such as Camponotus are known for their relationships with sucking insects like aphids, where they provide protection for these pest species. Generalist invasive species like Linepithema humile and Solenopsis invicta can negatively impact biological control as they affect the populations of other natural enemies, thus becoming antagonists in pest control. In this context, certain ant species become the pests that need to be controlled.
Despite decades of recognizing the potential of ants as biological control agents, there are still gaps in knowledge, particularly regarding the impact of conventional pest control techniques on these insects. Consequently, their potential for pest control may have been affected. Nevertheless, the scientific literature already contains robust evidence of the potential of ants as biological control agents, especially against invertebrate pests.
Author Contributions
Conceptualization, J.A.L. and F.R.M.G.; methodology, J.A.L., F.R.M.G. and M.O.R.; software, J.A.L. and M.O.R.; formal analysis, J.A.L., C.J.L., A.O., F.S.Z., M.O.R. and F.R.M.G.; investigation, J.A.L., C.J.L., A.O., F.S.Z., M.O.R. and F.R.M.G.; resources, J.A.L.; writing—original draft preparation, J.A.L., C.J.L., A.O., F.S.Z., M.O.R. and F.R.M.G.; writing—review and editing, J.A.L. and F.R.M.G.; supervision, J.A.L.; project administration, J.A.L.; funding acquisition, J.A.L. All authors have read and agreed to the published version of the manuscript.
Funding
Coordination for the Improvement of Higher Education Personnel (CAPES); Community University of Chapecó Region (Unochapecó); CNPq for a productivity grant to FRMG.
Institutional Review Board Statement
Not applicable.
Data Availability Statement
The datasets analyzed in the present study are available from the corresponding authors on reasonable request.
Conflicts of Interest
The authors declare no conflicts of interest.
Appendix A
Figure A1.
Search Strategies for Articles Included in the Research on the Potential of Ants as Natural Enemies, 2023.
Figure A1.
Search Strategies for Articles Included in the Research on the Potential of Ants as Natural Enemies, 2023.
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Figure 1.
Historical series and frequency of studies on potential ants for biological control in agroecosystems, 1976–2023.
Figure 1.
Historical series and frequency of studies on potential ants for biological control in agroecosystems, 1976–2023.
Table 1.
Objectives of studies on the potential of ants for biological control in agroecosystems, 1976–2024.
Table 1.
Objectives of studies on the potential of ants for biological control in agroecosystems, 1976–2024.
| Author and Year | Research Aims |
|---|---|
| Coutinho, 1976 [22] | To analyze the possible interaction of predators capable of killing the snails. |
| Way et al., 1989 [23] | To analyze the role of ants as predators of Opisina arenosella Walker, 1864 eggs. |
| Perfecto, 1991 [24] | To determine whether ants can be used as a sustainable pest management strategy in irrigated cornfields. |
| Paulson and Akre, 1992 [25] | To evaluate the effectiveness of ants as biological control agents for sucking insects (Psyllidae). |
| Way and Khoo, 1992 [26] | To evaluate the role of ants in pest management. |
| Ruberson et al., 1994 [27] | Discuss the importance of ants in managing the caterpillar Spodoptera exigua (Hubner, 1808) in cotton crops. |
| Way, Paiva and Cammell, 1999 [28] | To investigate the role of natural biological control by the Argentine ant Linepithema humile.Mayr, 1868, in controlling the moth Thaumetopoea pityocampa (Denis & Schiffermüller, 1775). |
| Shatterand Vander Meer, 2000 [29] | To characterize the interaction between fire ants (Solenopsis invicta Buren 1972) on developing soybean plants. |
| Mendonça and Romanowski, 2002 [30] | To describe the attack of parasitoids and predatory ants, considered natural enemies of Eugeniamyia dispar Maia, Mendonça-Jr., and Romanowski, 1996, during a two-year population study. |
| Vandermeer et al., 2002 [31] | To evaluate the role of Azteca sp. ants as potential biological control agents on an organic coffee farm. |
| Kenne et al., 2003 [32] | To study the hunting behavior of Myrmicaria opaciventris Emery, 1893 (Hymenoptera: Formicidae) as a biological control agent against termites. |
| Peng and Christian, 2004 [33] | To evaluate the potential of weaver ants in controlling red thrips. |
| Rossi and Fowler, 2004 [34] | To investigate the fauna of predatory ants present in the sugarcane fields of two sugarcane mills. |
| Sujii et al., 2004 [35] | To assess whether the ant Pachycondyla obscuricornis Emery (Hymenoptera: Formicidae) could act in the biological control of nymph populations of the pasture leafhopper, Deois flavopicta Stal (Hemiptera: Cercopidae). |
| Queiroz, Almeida, and Pereira, 2006 [20] | To discuss the ecological importance of ants and their conservation in agroecosystems. |
| Resende et al., 2006 [36] | To describe the fauna of predatory insects, parasitoids, and ants associated with aphids on cabbage (Brassica oleracea L. var. acephala D.C.) grown in an organic system. |
| Santos et al., 2006 [37] | To list the main research on using biological control for the main arthropod pests of cotton in Brazil. |
| Knutson and Campos, 2008 [38] | To measure the impact of the red imported fire ant, Solenopsis invicta Buren 1972, on the abundance of the corn earworm, Helicoverpa zea (Boddie, 1850), eggs and larvae that feed on corn ears. |
| Lange et al., 2008 [39] | To evaluate the differences in the foraging activity of predatory ants between two areas, one conventional and the other with no-till systems. |
| Van Mele, 2008 [40] | To show the potential of Oecophylla sp. ants as predators in tree crops. |
| Fernandes et al., 2010 [41] | To evaluate the potential of predators and parasitoids for the natural biological control of pest insects and the ecological relationships between these natural enemies and pest and non-pest phytophages in bean plants. |
| Larsen; Philpott, 2010 [42] | To investigate the predatory ability of twignesting ants on the main pest of coffee, the coffee berry borer (Hypothenemus hampei) under different management systems in southwest Chiapas, Mexico. |
| Rodrigues et al., 2010 [43] | To study the population dynamics of the aphid Toxoptera citricida Kirkaldy, 1907, including predators and the interaction with ants. |
| Choate and Drummond, 2011 [44] | To evaluate the positive and negative points related to the effectiveness of biological control by ants and strategies for applicability. |
| Wickings and Ruberson, 2011 [45] | To examine the impact of removing Solenopsis invicta Buren 1972 from the soil community in a typical cotton agro-ecosystem. |
| Peng, Christian, and Reillyt, 2012 [46] | To investigate the control potential of the bed bug Amblypelta lutescens (Distant, 1911) by the weaver ant Oecophylla smaragdina Fabricius, 1775. |
| Veríssimo, 2012 [47] | To review the biological control of the tick Rhipicephalus (Boophilus) microplus (Canestrini, 1888). |
| Chevalier et al., 2013 [48] | To analyze the variation in the potential of ants as anti-herbivore agents in coffee plants. |
| Anato et al., 2015 [49] | To investigate the efficacy of Benin’s African weaver ant Oecophylla longinoda (Latreille, 1802) biocontrol agent against cashew pests. |
| De la Mora; García-Ballinas; Philpott, 2015 [50] | To study the relationships between local characteristics associated with agricultural management, landscape surroundings of farms, abundance and richness of ants, and predation services provided by ants in a tropical coffee landscape. |
| Offenberg, 2015 [51] | To evaluate the potential of ants as tools in sustainable agriculture. |
| Milligan et al., 2016 [52] | To investigate the removal of coffee pests by ants. |
| Wang et al., 2016 [53] | Review the biology, ecology, and impact of Nylanderia fulva, and discusses the potential for sustainable and effective management through biological control. |
| Wickings and Ruberson, 2016 [54] | To examine the contribution of fire ants to predation on cotton soil and foliage. |
| Gossler, Lange and Fernandes, 2017 [55] | To determine if the presence of ants interferes with the abundance of herbivorous and predatory arthropods on maize plants, Zea mays L. (Poaceae). |
| Cologna et al., 2018 [56] | To conduct an in-depth peptidomic analysis of the venom of Neoponera villosa Emery, 1901, and compare seasonal habitat and nesting variations using high-resolution mass spectrometry. |
| Diamé et al., 2018 [57] | To review the knowledge of the roles played by ants in orchards as functional elements, and on the potential of Oecophylla weaver ants as biological control agents. |
| Morris et al., 2018 [58] | To review the role of ants as biological control agents of the coffee berry borer (CBB), Hypothenemus hampei (Ferrari, 1867). |
| Abeijon et al., 2019 [7] | To evaluate the predation rate of Anastrepha fraterculus (Wiedemann, 1830) larvae by ants, considering the level of soil compaction and soil moisture content in a peach orchard (Prunus persica, Rosaceae). |
| Polania, 2019 [59] | To evaluate the invasive behavior of four ants native to South America. |
| Garcia et al., 2020 [60] | To present a review of the biological control of tephritid fruit flies in the Americas and Hawaii. |
| Magalhães and Ferro, 2020 [61] | To determine whether indirect defense occurs in the Caryocar brasiliense-ant system. |
| Anjos et al., 2021 [62] | To review how ants affect pest abundance, considering whether the pest produces honeydew and whether it spends part of its life-cycle in the soil. |
| Baldwin et al., 2023 [14] | To document the occurrence of Solenopsis invicta Buren 1972 and its potential to prey on Lepidoptera eggs in peanut and cotton crops. |
| Schifani et al., 2023 [63] | To investigate the interactions between the Mediterranean ant Crematogaster scutellaris and the parasitoids Trissolcus japonicus and Trissolcus mitsukurii, assessing the possibility that the ants damage the parasitized eggs. |
| Exélis et al., 2023 [64] | To demonstrate the services of the Asian weaver ant in pest management. |
| Martins et al., 2024 [65] | To evaluate predatory ant richness in Conilon coffee in monoculture and intercropped with teak or Australian cedar. |
Source: the authors (2024).
Table 2.
Diversity of ants and pests assessed by studies on the potential of ants for biological control in agroecosystems, 1976 to 2023. Au = augmentative biological control; Co = conservation biological control; Cl = classic biological control.
Table 2.
Diversity of ants and pests assessed by studies on the potential of ants for biological control in agroecosystems, 1976 to 2023. Au = augmentative biological control; Co = conservation biological control; Cl = classic biological control.
| Ant | Type of Biological Control | Prey | Area/Crop | Condition | Country | Impact/Efficiency | References |
|---|---|---|---|---|---|---|---|
| Dolichoderinae | |||||||
| Azteca sp. Forel | Cl | Pieris rapae (L.) | Coffee | Field | Mexico | Larval predation | [31] |
| Co | Herbivorous arthropods | Various crops | Field | Brazil | Reduction of the pest population | [20] | |
| Au | Eunica bechina ((Hewitson), Edesa rufomarginata (De Geer) and Prodiplosis floricola (Felt) | Caryocar brasiliense Camb. (Caryocaraceae) | Field | Brazil | Chemical defense | [61] | |
| Dolichoderus sp. Lund | Co | Herbivorous pests of orchards | Fruit growing | Field | Brazil | 25% reduction in infestation | [20] |
| Dolichoderus thoracicus (Smith) | Co | Herbivorous pests of orchards | Fruit growing | Field | Brazil | 25% reduction in infestation | [20] |
| Co | Hypothenemus hampei (Ferrari) | Coffee | Field | USA | Reduction of the pest population | [58] | |
| Dorymyrmex Mayr, 1866 | Co | Diatraea saccharalis (Fabricius) | Sugarcane | Field | Brazil | Predation on eggs and larvae | [34] |
| Cl | Termites | Conventional and no-till agriculture systems | Field | Brazil | Greater efficiency in no-till systems | [39] | |
| Cl | Herbivorous arthropods | Milho Zea mays L. | Field | Brazil | 41.5% reduction in the pest population | [55] | |
| Dorymyrmex brunneus Forel | Co | Herbivores pests | Coffee | Field | Brazil | Potential predator | [65] |
| Iridomyrmex rufoniger (Lowne) | Co | Citrus pests | Citrus | Field | Australia | Not informed | [62] |
| Linepithema humile (Mayr, 1868) | Co | Citrus pests | Citrus | Field | EUA | Not informed | [62] |
| Cl | Thaumetopoea pityocampa (Denis & Schiffermüller) | Pinus pinaster Aiton | Field | Portugal | 100% efficiency | [28] | |
| Tapinoma sessile (Say) | Cl | Cacopsylla pyricola (Foerster) | Pear | Field | USA | Reduction of the pest population | [25] |
| Technomyrmex albipes (Smith) | Cl | Opisina arenosella Walker | Coconut | Field | Sri Lanka | Egg predation | [23] |
| Dorylinae | |||||||
| Neivamyrmex sp. Borgmeier | Cl | Anthonomus grandis Boheman | Cotton | Field | Brazil | Predation on immature stages | [37] |
| Ectatomminae | |||||||
| Ectatomma brunneum Smith | Co | Lipaphis pseudobrassicae Davis | Brassica oleracea L. | Field | Brazil | Not informed | [36] |
| Cl | Rhipicephalu (Boophilus) microplus | Pasture | Field | Brazil | Potential predator | [47] | |
| Cl | Anastrepha sp. | Fruit growing | Field | Brazil | Potential predator | [60] | |
| Co | Herbivores pests | Coffee | Field | Brazil | Potential predator | [65] | |
| Ectatomma edentatum Roger | Co | Herbivores pests | Coffee | Field | Brazil | Potential predator | [65] |
| Ectatomma planidens Borgmeier | Cl | Termites | Conventional and no-till agriculture systems | Field | Brazil | Efficient in no-till systems | [39] |
| Ectatomma ruidum (Roger) | Co | Herbivorous coffee pests | Coffee | Field | Brazil | Efficiency of 17.8% | [20] |
| Ectatomma tuberculatum (Olivier) | Co | Herbivorous coffee pests | Coffee | Field | Brazil | Efficiency of 11.3% | [20] |
| Co | Herbivores pests | Coffee | Field | Brazil | Potential predator | [65] | |
| Gnamptogenys striatula Mayr | Co | Anastrepha obliqua Macquart and Hypothenemus hampei (Ferrari) | Coffee | Field | Mexico | Up to 62% efficiency | [50] |
| Gnamptogenys sulcata (Smith) | Co | Herbivores pests | Coffee | Field | Brazil | Potential predator | [65] |
| Formicinae | |||||||
| Anoplolepis sp. Santschi | Co | Herbivorous arthropods | Various crops | Field | Brazil | Reduction of pest populations | [20] |
| Brachymyrmex sp. Mayr | Cl | Membracids | Coffee (Coffea canephora Pierre) and beans Guandu [Cajanus cajans (L.)] | Field | Brazil | Artificial egg predator | [48] |
| Co | Hypothenemus hampei (Ferrari) | Coffee | Field | USA | Reduction of pest populations | [58] | |
| Camponotus sp. Mayr | Cl | Nasutitermes sp. | Conventional and no-till agriculture systems | Field | Brazil | Efficient in no-till systems | [39] |
| Cl | Membracids | Coffee (Coffea canephora Pierre) and beans Guandu [Cajanus cajans (L.)] | Field | Brazil | Artificial egg predator | [48] | |
| Au | Eunica bechina ((Hewitson), Edesa rufomarginata (De Geer) and Prodiplosis floricola (Felt) | Caryocar brasiliense Camb. (Caryocaraceae) | Field | Brazil | Chemical defense against herbivores | [61] | |
| Camponotus atriceps (Smith) | Co | Diatraea saccharalis (Fabricius) | Sugarcane | Field | Brazil | Predation on eggs and larvae of the pest | [34] |
| Camponotus crassus Mayr | Cl | Membracids | Coffee (Coffea canephora Pierre) and beans Guandu [Cajanus cajans (L.)] | Field | Brazil | Artificial egg predator | [48] |
| Cl | Diabrotica speciosa (Germar) | Zea mays L. | Field | Brazil | 41.5% reduction in the pest population | [55] | |
| Camponotus melanoticus Emery | Cl | Membracids | Coffee (Coffea canephora Pierre) | Field | Brazil | Artificial egg predator | [48] |
| Camponotus modoc Wheeler | Cl | Cacopsylla pyricola (Foerster) | Pear | Field | USA | Reduction of pest populations | [25] |
| Camponotus renggeri Emery | Cl | Rhipicephalu (Boophilus) microplus | Pasture | Field | Brazil | Tick predator | [47] |
| Camponotus rufipes (Fabricius) | Cl | Membracids | Coffee(Coffea canephora Pierre) | Field | Brazil | Artificial egg predator | [48] |
| Formica fusca Linnaeus | Cl | Rhagoletis pomonella (Walsh) | Fruit growing | Field | Canada | Potential predator | [60] |
| Formica neoclara Emery | Cl | Cacopsylla pyricola (Foerster) | Pear | Field | USA | Reduction of pest populations | [25] |
| Formica polyctena Foerster | Co | Herbivorous pests of orchards | Fruit growing | Field | Brazil | 25% efficiency | [20] |
| Lasius grandis Forel | Co | Citrus pests | Citrus | Field | EUA | Not informed | [62] |
| Lasius pallitarsis (Provancher) | Cl | Cacopsylla pyricola (Foerster) | Pear | Field | USA | Reduction of pest populations | [25] |
| Nylanderia fulva (Mayr) | Co | Atta spp. and Solenopsis invicta Buren | Agroecossystems | Field | EUA | Not informed | [53] |
| Cl | Atta spp. | Agroecossystems | Field | Brazil | Not informed | [59] | |
| Oecophylla sp. | Co | Herbivorous arthropods | Cashew, citrus, mango, cocoa, and oil palm | Field | Asia | Reduction of the pest population | [51] |
| Co | Fruit flies (Tephritidae) | Citrus and mango | Field | Australia and Southeast Asia | Reduction of the pest population | [57] | |
| Oecophylla longinoda (Latreille) | Cl | Pseudotheraptus wayi Brown | Coconuts | Field | East Africa | Reduction of pest populations | [26] |
| Cl | Pseudotheraptus devastans (Distant) | Coconuts | Field | Ivory Coast | Reduction of pest populations | [26] | |
| Cl | Antestiopsis intricata (Ghesquière & Carayon) | Coffee | Field | Ghana | Reduction of pest populations | [26] | |
| Cl | Apate terebrans (Pallas), Acrocercopus syngramma Meyrick, Helopeltis sp., Anoplocnemis curvipes (Fabricius), Pseudotheraptus devastus (Distant). Frankliniella schultzei (Trybom), Scirtothrips mangiferae (Priesner), Scirtothrips aurantii Faure | Cashew | Field | Benin | 72–150% increase in production | [49] | |
| Oecophylla smaragdina (Fabricius) | Cl | Amblypelta cocophaga China | Coconuts | Field | Solomon Islands | Reduction of pest populations | [26] |
| Cl | Brontispa longissima (Gestro) | Coconuts | Field | Solomon Islands | Reduction of pest populations | [26] | |
| Cl | Cremastopsyche pendula Joannis | Oil palm | Field | Malaysia | Reduction of pest populations | [26] | |
| Cl | Helopeltis theobromae Miller | Cocoa | Field | Malaysia | Reduction of pest populations | [26] | |
| Cl | Amblypelta theobromae Brown | Cocoa | Field | Papua New Guinea | Reduction of pest populations | [26] | |
| Cl | Pantorhytes biplagiatus Bates | Cocoa | Field | Solomon Islands | Reduction of pest populations | [26] | |
| Cl | Rhynchocoris humeralis (Thunberg) | Citrus | Field | China | Reduction of pest populations | [26] | |
| Co | Selenothrips rubrocinctus (Giard) | Mango | Field | Australia | 27.2% efficiency | [33] | |
| Cl | Beetles (Chrysomelidae) and bugs (Coreidae) | Coconuts | Field | Africa and Asia | Predators in tree crops | [40] | |
| Cl | Bugs and rodents | Cocoa | Field | Africa and Asia | Predators in tree crops | [40] | |
| Cl | Aphids, caterpillars, inflorescence eaters, leafminers and stinkbugs | Citrus | Field | Africa and Asia | Predators in tree crops | [40] | |
| Cl | Bugs, leafrollers, and tip borers | Cashew | Field | Africa and Asia | Predators in tree crops | [40] | |
| Cl | Bugs, fruit flies, leafhoppers, seed weevils, thrips and tip borers | Mango | Field | Africa and Asia | Predators in tree crops | [40] | |
| Cl | Bark beetles and shoot borers | Timber trees | Field | Africa and Asia | Predators in tree crops | [40] | |
| Cl | Tea mosquito bug, fruit-spotting bug, mango tip-borer, leafroller | Cashew | Field | USA | Pests controlled, higher quality nuts produced | [44] | |
| Cl | Amblypelta lutescens (Distant) | African mahogany Khaya senegalensis (Desr.) A. Juss | Field | Australia | Up to 94.6% reduction in infestation | [46] | |
| Cl | Selenothrips rubrocinctus (Giard) and Amblypelta lutescens Distant | Coconut, agarwood, lychee, cocoa, citrus, mango, cashew nuts and orchards | Field | Africa and Asia | Up to 100% reduction in eggs, larvae, and adults | [64] | |
| Paratrechina longicornis (Latreille) | Cl | Biomphalaria glabrata (Say) | Public health | Field | Brazil | Predation of 100% of accessible snails | [22] |
| Paratrechina parvula, Crozier | Cl | Anastrepha suspensa (Loew) | Fruit growing | Field | USA | Potential predator | [60] |
| Plagiolepis pygmaea (Latreille) | Co | Citrus pests | Citrus | Field | Spain | Not informed | [62] |
| Myrmicinae | |||||||
| Cephalotes sp. Latreille | Au | Eunica bechina ((Hewitson), Edesa rufomarginata (De Geer) and Prodiplosis floricola (Felt) | Caryocar brasiliense Camb. (Caryocaraceae) | Field | Brazil | Chemical defense against herbivores | [61] |
| Crematogaster sp. Lund | Cl | Opisina arenosella Walker | Coconut | Field | Sri Lanka | Egg predation | [23] |
| Co | Diatraea saccharalis (Fabricius) | Sugarcane | Field | Brazil | Predation on eggs and larvae of the pest | [34] | |
| Cl | Anthonomus grandis Boheman | Cotton | Field | Brazil | Predation on immature stages of the pest | [37] | |
| Cl | Nasutitermes sp. | Conventional and no-till agriculture systems | Field | Brazil | Efficient in no-till systems | [39] | |
| Au | Empoasca kraemeri Ross & Moore, Caliothrips brasiliensis (Morgan) and Thrips tabaci Lindeman | Beans crop | Field | Brazil | Reduction of pests at the start of cultivation | [41] | |
| Cl | Membracids | Coffee (Coffea canephora Pierre) and beans Guandu [Cajanus cajans (L.)] | Field | Brazil | Artificial egg predator | [48] | |
| Cl | Diabrotica speciosa (Germar) | Zea mays L. | Field | Brazil | 41.5% reduction in the pest population | [55] | |
| Co | Hypothenemus hampei (Ferrari) | Coffee | Field | USA | Reduction of the pest population | [58] | |
| Cl | Anastrepha ludens (Loew) | Fruit growing | Field | USA | Potential predator | [60] | |
| Au | Eunica bechina ((Hewitson), Edesa rufomarginata (De Geer) and Prodiplosis floricola (Felt) | Caryocar brasiliense Camb. (Caryocaraceae) | Field | Brazil | Chemical defense against herbivores | [61] | |
| Crematogaster crinosa Mayr | Co | Hypothenemus hampei (Ferrari) | Coffee | Field | USA | Reduction of the pest population | [58] |
| Crematogaster curvispinosa Mayr | Co | Hypothenemus hampei (Ferrari) | Coffee | Field | USA | Reduction of the pest population | [58] |
| Crematogaster scutellaris (Olivier) | Au | Halyomorpha halys (Stål, 1855) | - | Laboratory | Italy | Potential as an adjuvant in pest control | [63] |
| Leptotorax sp. Mayr | Cl | Anastrepha suspensa (Loew) | Fruit growing | Field | USA | Potential predator | [60] |
| Leptothorax muscorum (Nylander) | Cl | Cacopsylla pyricola (Foerster) | Pear | Field | USA | Reduction of the pest population | [25] |
| Monomorium floricola (Jerdon) | Cl | Opisina arenosella Walker | Coconut | Field | Sri Lanka | Egg predation | [23] |
| Myrmica incompleta Provancher | Cl | Cacopsylla pyricola (Foerster) | Pear | Field | USA | Reduction of the pest population | [25] |
| Myrmicaria opaciventris Emery | Cl | Termites | Forest | Field | Cameroon | 75% of predation | [32] |
| Pheidole sp. Westwood | Co | Eugeniamyia dispar Maia, Mendonça-Jr. & Romanowski | Eugenia uniflora L. | Laboratory | Brazil | 13–41% of predation | [30] |
| Co | Diatraea saccharalis (Fabricius) | Sugarcane | Field | Brazil | Predation on eggs and larvae of the pest | [34] | |
| Co | Lipaphis pseudobrassicae Davis | Brassica oleracea L. | Field | Brazil | Not informed | [36] | |
| Cl | Anthonomus grandis Boheman | Cotton | Field | Brazil | Predation on immature stages of the pest | [37] | |
| Cl | Nasutitermes sp. | Conventional and no-till agriculture systems | Field | Brazil | Efficient in no-till systems | [39] | |
| Cl | Diamondback moth larvae, black cutworm larvae | Cauliflower | Field | USA | Decreased leaf damage by black cutworm larvae | [44] | |
| Cl | Membracids | Coffee (Coffea canephora Pierre) | Field | Brazil | Predation on artificial herbivore eggs | [48] | |
| Cl | Diabrotica speciosa (Germar) | Zea mays L. | Field | Brazil | 41.5% reduction in the pest population | [55] | |
| Co | Hypothenemus hampei (Ferrari) | Coffee | Field | USA | Reduction in pest population | [58] | |
| Cl | Anastrepha fraterculus (Wiedemann) | Prunus persica (L.) | Field | Brazil | Removal of up to 18.4% of larvae | [7] | |
| Pheidole flavens Roger | Co | Herbivores pests | Coffee | Field | Brazil | Potential predator | [65] |
| Pheidole gertrudae Forel, 1886 | Cl | Anastrepha sp. | Fruit growing | Field | Brazil | Potential predator | [60] |
| Pheidole megacephala (Fabricius) | Cl | Sesamia calamistis Hampson | Coffee | Field | Kenya | 12% reduction in infestation | [52] |
| Co | Hypothenemus hampei (Ferrari) | Coffee | Field | USA | Reduction in pest population | [58] | |
| Cl | Zeugodacus cucurbitae (Coquillett) | Fruit growing | Field | USA | Potential predator | [60] | |
| Co | Herbivores pests | Coffee | Field | Brazil | Potential predator | [65] | |
| Pheidole obscurithorax Naves | Co | Herbivores pests | Coffee | Field | Brazil | Potential predator | [65] |
| Pheidole oxyops Forel | Cl | Anastrepha sp. | Fruit growing | Field | Brazil | Potential predator | [60] |
| Co | Herbivores pests | Coffee | Field | Brazil | Potential predator | [65] | |
| Pheidole pallidula (Nylander) | Co | Citrus pests | Citrus | Field | Spain | Not informed | [62] |
| Pheidole protensa Wilson | Co | Anastrepha obliqua Macquart and Hypothenemus hampei (Ferrari) | Coffee | Field | Mexico | Up to 62% efficiency | [50] |
| Pheidole pubiventris Mayr | Co | Anastrepha obliqua Macquart and Hypothenemus hampei (Ferrari) | Coffee | Field | Mexico | Up to 62% efficiency | [50] |
| Pheidole radoszkowskii Mayr | Cl | Spodoptera frugiperda (J.E. Smith) and Dalbulus maidis (DeLong & Wolcott) | Zea mays L. | Field | Nicaragua | Reduction in pest abundance | [24] |
| Co | Hypothenemus hampei (Ferrari) | Coffee | Field | USA | Reduction in pest population | [58] | |
| Co | Herbivores pests | Coffee | Field | Brazil | Potential predator | [65] | |
| Pheidole synanthropica Longino | Co | Anastrepha obliqua Macquart and Hypothenemus hampei (Ferrari) | Coffee | Field | Mexico | Up to 62% efficiency | [50] |
| Pheidole triconstricta Forel | Co | Herbivores pests | Coffee | Field | Brazil | Potential predator | [65] |
| Pogonomyrmex naegelii Emery | Cl | Anastrepha fraterculus (Wied.) | Prunus persica (L.) | Field | Brazil | Removal of 4.1% of larvae | [7] |
| Pristomyrmex punctatus (Smith) | Co | Citrus pests | Citrus | Field | Japan | Not informed | [62] |
| Solenopsis sp. Westwood | Co | Diatraea saccharalis (Fabricius) | Sugarcane | Field | Brazil | Predation on eggs and larvae of the pest | [34] |
| Cl | Anthonomus grandis Boheman | Cotton | Field | Brazil | Predation on immature stages of the pest | [37] | |
| Cl | Nasutitermes sp. | Conventional and no-till agriculture systems | Field | Brazil | Efficient in no-till systems | [39] | |
| Cl | Membracids | Coffee Coffea canephora Pierre | Field | Brazil | Predation of artificial herbivore eggs | [48] | |
| Cl | Diabrotica speciosa (Germar) | Zea mays L. | Field | Brazil | 41.5% reduction in the pest population | [55] | |
| Co | Hypothenemus hampei (Ferrari) | Coffee | Field | USA | Reduction in pest population | [58] | |
| Solenopsis globularia (Smith) | Co | Anastrepha obliqua Macquart and Hypothenemus hampei (Ferrari) | Coffee | Field | Mexico | Up to 62% efficiency | [50] |
| Solenopsis invicta Buren | Au | Spodoptera exigua (Hübner) | Cotton | Field | USA | Reduction in pest population | [27] |
| Co | Herbivores pests of cotton | Cotton | Field | Brazil | Reduction in pest population | [20] | |
| Co | Herbivores pests of soybean | Soybean | Field | Brazil | Reduction in pest population | [20] | |
| Au | Empoasca kraemeri Ross & Moore, Caliothrips brasiliensis (Morgan) and Thrips tabaci Lindeman | Beans crop | Field | Brazil | Reduction of pest populations at the start of cultivation | [41] | |
| Cl | Sugarcane borer | Sugarcane | Field | USA | Reduced pest numbers, crop damage | [44] | |
| Au | Epigeic arthropods | Cotton agroecosystems | Field | USA | Effects are not uniform within a given trophic group | [44] | |
| Au | Epigeic Arthropods | Cotton agroecosystems | Field | USA | Changes in the dynamics of relationships between predators and prey | [54] | |
| Cl | Anastrepha suspensa (Loew) | Zea mays L. | Field | USA | Potential predator | [60] | |
| Cl | Helicoverpa zea (Boddie) | Peanuts and cotton | Field | USA | Potential predator | [14] | |
| Solenopsis geminata (Fabricius) | Cl | Spodoptera frugiperda (J.E. Smith) and Dalbulus maidis (DeLong & Wolcott) | Zea mays L. | Field | Nicaragua | Reduction in pest abundance | [24] |
| Cl | Apple snail | Rice | Field | USA | Damaged and consumed egg masses | [44] | |
| Co | Hypothenemus hampei (Ferrari) | Coffee | Field | USA | Reduction in pest population | [58] | |
| Cl | Ceratitis capitata Wied | Fruit growing | Field | USA | Potential predator | [60] | |
| Solenopsis saevissima (Smith) | Co | Diatraea saccharalis (Fabricius) | Sugarcane | Field | Brazil | Predation on eggs and larvae of the pest | [34] |
| Cl | Anthonomus grandis Boheman | Cotton | Field | Brazil | Predation on immature stages of the pest | [37] | |
| Cl | Rhipicephalu (Boophilus) microplus | Pasture | Field | Brazil | Potential tick predator | [47] | |
| Cl | Anastrepha fraterculus (Wiedemann) | Prunus persica (L.) | Field | Brazil | Removal of 42.9% of larvae | [7] | |
| Co | Herbivores pests | Coffee | Field | Brazil | Potential predator | [65] | |
| Tetramorium bicarinatum (Nylander) | Co | Hypothenemus hampei (Ferrari) | Coffee | Field | USA | Reduction in pest population | [58] |
| Tetramorium simillimum (Smith) | Co | Hypothenemus hampei (Ferrari) | Coffee | Field | USA | Reduction in pest population | [58] |
| Wasmannia sp. Forel | Co | Hypothenemus hampei (Ferrari) | Coffee | Field | USA | Reduction in pest population | [58] |
| Wasmannia auropunctata (Roger) | Co | Anastrepha obliqua Macquart and Hypothenemus hampei (Ferrari) | Coffee | Field | Mexico | Up to 62% efficiency | [50] |
| Cl | Cocoa mirids | Cocoa | Field | USA | Noted control of pest | [44] | |
| Co | Hypothenemus hampei (Ferrari) | Coffee | Field | USA | Reduction in pest population | [58] | |
| Ponerinae | |||||||
| Anochetus neglectus Emery | Co | Herbivores’ pests | Coffee | Field | Brazil | Potential predator | [65] |
| Neoponera obscuricornis (Emery) | Co | Deois flavopicta (Stal) | Brachiaria ruziziensis cv. B. Ruziziensis | Field | Brazil | 93.8% reduction | [35] |
| Cl | Rhipicephalu (Boophilus) microplus | Pasture | Field | Brazil | Up to 50.5% reduction in infestation | [47] | |
| Neoponera villosa (Fabricius) | Co | Herbivorous arthropods | Agroecosystems | Laboratory | Brazil | Not informed | [56] |
| Odontomachus brunneus (Patton) | Cl | Anastrepha suspensa (Loew) | Fruit growing | Field | Brazil | Potential predator | [60] |
| Odontomachus chelifer (Latreille) | Co | Herbivores pests | Coffee | Field | Brazil | Potential predator | [65] |
| Odontomachus haematodus (Linnaeus) | Cl | Nasutitermes sp. | Conventional and No-till Agriculture Systems | Field | Brazil | Efficient in no-till systems | [39] |
| Pachycondyla Smith | Au | Eunica bechina ((Hewitson), Edesa rufomarginata (De Geer) and Prodiplosis floricola (Felt) | Caryocar brasiliense Camb. (Caryocaraceae) | Field | Brazil | Chemical defense against herbivores | [61] |
| Pachycondyla harpax (Fabricius) | Co | Herbivores pests | Coffee | Field | Brazil | Potential predator | [65] |
| Pachycondyla striata Smith | Cl | Rhipicephalu (Boophilus) microplus | Pasture | Field | Brazil | Up to 50.5% reduction in infestation | [47] |
| Cl | Anastrepha fraterculus (Wiedemann) | Prunus persica (L.) | Field | Brazil | Removal of 6.1% of larvae | [7] | |
| Co | Herbivores pests | Coffee | Field | Brazil | Potential predator | [65] | |
| Pseudomyrmecinae | |||||||
| Pseudomyrmex sp. Lund | Co | Eugeniamyia dispar Maia, Mendonça-Jr. & Romanowski | Eugenia uniflora L. | Laboratory | Brazil | 13% to 41% of predation | [30] |
| Cl | Membracids | Coffee (Coffea canephora Pierre) | Field | Brazil | Predation on artificial herbivore eggs | [48] | |
| Cl | Diabrotica speciosa (Germar) | Zea mays L. | Field | Brazil | 41.5% reduction in the pest population | [55] | |
| Au | Eunica bechina ((Hewitson), Edesa rufomarginata (De Geer) and Prodiplosis floricola (Felt) | Caryocar brasiliense Camb. (Caryocaraceae) | Field | Brazil | Chemical defense against herbivores | [61] | |
| Pseudomyrmex ejectus (Smith) | Co | Hypothenemus hampei (Ferrari) | Coffee | Laboratory | Mexico | Up to 40% efficiency | [42] |
| Co | Hypothenemus hampei (Ferrari) | Coffee | Field | USA | Reduction in pest population | [58] | |
| Pseudomyrmex schuppi (Forel) | Co | Herbivores pests | Coffee | Field | Brazil | Potential predator | [65] |
| Pseudomyrmex simplex (Smith) | Co | Hypothenemus hampei (Ferrari) | Coffee | Laboratory | Mexico | Up to 40% efficiency | [42] |
| Co | Hypothenemus hampei (Ferrari) | Coffee | Field | USA | Reduction in pest population | [58] | |
| Pseudomyrmex termitarius (Smith) | Co | Herbivores pests | Coffee | Field | Brazil | Potential predator | [65] |
Source: the authors (2024).
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MDPI and ACS Style
Lutinski, J.A.; Lutinski, C.J.; Ortiz, A.; Zembruski, F.S.; Ripke, M.O.; Garcia, F.R.M. Biological Control Using Ants: Current Status, Opportunities, and Limitations. Agronomy 2024, 14, 1558. https://doi.org/10.3390/agronomy14071558
AMA Style
Lutinski JA, Lutinski CJ, Ortiz A, Zembruski FS, Ripke MO, Garcia FRM. Biological Control Using Ants: Current Status, Opportunities, and Limitations. Agronomy. 2024; 14(7):1558. https://doi.org/10.3390/agronomy14071558
Chicago/Turabian StyleLutinski, Junir Antônio, Cladis Juliana Lutinski, Alécio Ortiz, Fernanda Staub Zembruski, Marcia Orth Ripke, and Flávio Roberto Mello Garcia. 2024. "Biological Control Using Ants: Current Status, Opportunities, and Limitations" Agronomy 14, no. 7: 1558. https://doi.org/10.3390/agronomy14071558
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