ArticlePDF Available

Interspecific Repellent Effect of Hydroalcoholic Solution of Nest Refuse from Two Leaf-cutter Ant Species

Authors:

Abstract and Figures

Leaf-cutting ants manage their waste continuously to avoid risks of colony contamination. The presence of residues or their odor near foraging areas is enough for ants to stop attacking plant tissues. However, to date, no study has demonstrated an interspecific effect of nest waste on the deterrence of leaf-cutting ants. Here, we tested whether a hydroalcoholic extract of nest refuse (NR) of the leaf-cutting ants Acromyrmex balzani Emery, 1890 and Atta opaciceps Borgmeier (Hymenoptera: Formicidae, Attini) causes an interspecific deterrent effect. Field colonies of Ac. balzani (n = 30) and A. opaciceps (n = 36) were used. For each colony, we offered baits made with plastic straws covered by citrus pulp and sprayed with a hydroalcoholic solution of 20% (vol/vol) alcohol/water (Control) or an extract of 20% (vol/vol) of NR from Ac. balzani and/or A. opaciceps. Over 20-30 minutes we recorded the amount of baits removed and data were compared through survival analysis and Linear Mixed Effect (LME) model. Ants avoided collecting baits sprayed with NR resulting in less than 20% of these baits being carried to the nest versus 80% of control baits. The deterrence was both intra and interspecific, considering that the response was similar for baits from both species. Such results reinforce the premise that the presence of nest refuse alters the foraging behavior of ants and paves the way for new studies that can verify its effectiveness in reducing foliar consumption on a larger spatial scale.
Content may be subject to copyright.
Open access journal: http://periodicos.uefs.br/index.php/sociobiology
ISSN: 0361-6525
DOI: 10.13102/sociobiology.v70i3.8701
Sociobiology 70(3): e8701 (September, 2023)
Introduction
Leaf-cutting ants (LCA) (Hymenoptera: Formicidae,
Attini) (genera Atta and Acromyrmex) cause signicant
economic damage and are, therefore, considered an important
agricultural pest in their areas of occurrence (Holldöbler &
Wilson, 1990; Urbas et al., 2007). Several methods for the
management of LCA have been used, such as insecticide
application, fungicides, and the use of entomopathogenic fungi.
However, some of these methods have high costs and adverse
effects on the environment and human health (Montoya-Lerma
et al., 2012; Della Lucia et al., 2013, Zanetti et al., 2014).
An alternative and less environmentally toxic method is
the use of substances with a deterrent effect. These substances
Abstract
          



    
Acromyrmex balzani    Aa opaciceps  
Ac. balzan
A. opaciceps

Ac.
balzaniA. opaciceps


  versus  
   



Sociobiology
An international journal on social insects

Arcle History
Edited by





Keywords
Aa opacicepsAcromyrmex balzani


Corresponding author






act on the insect’s behavior and prevent or inhibit foraging
and are generally associated with secondary metabolites
produced by plants (Dethier et al., 1960; Lara, 1991).
LCA efciently manage their waste (here referred
to as nest refuse, NR) produced in the colony, since such
behavior guarantees the health of individuals and the integrity
of their symbiotic fungus (Bot et al., 2001). Previous studies
showed that ants avoid cutting tissues from plants that are in
contact with dry NR mounds (Zeh et al., 1999; Farji-Brener &
Sasal, 2003; Ballari & Farji-Brener, 2006) and, more recently,
Sousa-Souto et al (2022) observed that the liquid NR extract
also proved to be deterrent against ant attack to the plants.
Thus, odors associated with NR may be the main mechanism
of deterrent action.




          

ID
Leandro Sousa-Souto, Bianca G. Ambrogi, Rafaella S. Santos – Nest refuse extract delays bait collection
LCA cultivates the same species of symbiont fungus,
Leucoagaricus gongylophorus (Pagnocca et al., 2011), and
maintains similar habits of hygiene, and communication
between nestmates. Likewise, the NR produced by different
species of these two genera probably has similar chemical
characteristics. Given these similarities, it is likely that the
deterrent effect of the NR extract is interspecic.
In the present study, we veried the interspecic
deterrent effect of NR in liquid formulation (hydroalcoholic
extract) on leaf-cutting ants of the species Acromyrmex balzani
Emery, 1890 and Atta opaciceps Borgmeier. For this, the study
started from the following hypotheses i) since NR is toxic and
avoided by leaf-cutting ants, even attractive baits prepared
with this substrate can also be avoided; ii) if substrate-treated
baits have an intraspecic deterrent effect, there is a high
probability that they also have an interspecic effect.
Material and Methods
Study site and LCA species used
The study was carried out on the campus of the
Federal University of Sergipe in São Cristóvão (10º55’33.55
“S 37º6’8.327” W) and the chosen species were the most
common and have the highest density in the area.
The species Acromyrmex balzani has a wide distribution
in disturbed environments, in addition to a high density of
colonies in these environments, reaching 900 colonies/ha
(Sousa-Souto et al., 2013). This species has the characteristic
of discarding NR outside the nest, in piles on the soil surface,
adjacent to the nest entrance. Likewise, the Atta opaciceps
species was chosen because it is easily found in the study
area, forming mounds up to 2.5 m in diameter with numerous
entrances (Delabie et al., 1997).
Nest refuse (NR) collection
The nest refuse produced by A. balzani was collected
directly in the eld, at the study site, and in the mounds
discarded by the colonies. The NR from A. balzani colonies
is characterized as a light-colored residue in front of the nest
entrance. The material was collected with a spoon, deposited
in paper bags, taken to the Laboratory, and placed in an oven
at 60 °C for 48 hours in order to eliminate possible pathogens
or contaminants.
The NR produced by A. opaciceps was collected from
10 colonies maintained at the Laboratório de Entomologia
Florestal - UFS. This substrate is discarded in plastic chambers
arranged for that purpose and has a dark brown color. The
material was collected and deposited in paper bags and later
taken to the oven at 48 °C for 48 hours for drying.
Hydroalcoholic extracts preparation
Hydroalcoholic extracts (HE) were prepared following
the methodology of Barbosa et al. (2006) with adaptations of
Sousa-Souto et al. (2022). The HE were prepared with 80mL
of 100% ethyl alcohol, 80mL of distilled water, and 40 mL
of crushed NR of A. balzani or A. opaciceps. The extracts
were strained and mixed twice a day, placed at rest at room
temperature for 48h when they were then vacuum ltered
through a Büchner funnel and lter paper (90 mm diameter),
and stored in a refrigerator at 8 °C before eld tests.
Preparation of attractive baits
The attractive baits were composed of colored straws
impregnated with citrus pulp, allowed to dry and sprayed with
a 1:1 control solution (ethyl alcohol and distilled water) or
with hydroalcoholic extract of the substrate produced by both
species, differentiated by color between treatments: white –
control (Cont); pink - Acromyrmex extract (ExtAc); blue -
Atta extract (ExtAt).
The citrus pulp was used in this study because it is
reported as a substance with high attractive power for ants
and for that reason widely used in ant killer baits, so that ants
disseminate the toxic substance inside the colony (Boaretto &
Forti, 1997; Carlos et al., 2009).
Field tests
For the tests, 30 A. balzani and 36 A. opaciceps eld
colonies at the study site were systematically selected. The
colonies were marked with wooden sticks and their location
was georeferenced with GPS. We identied the foraging areas
of each colony and, following a methodology modied from
Moreira & Forti (1999), with 10 attractive articial baits per
treatment offered, totaling 30 baits per colony.
In our study area, A. balzani forages without the
formation of permanent foraging trails. As a result, ants return
to the nest in a scattered manner. For this reason, baits were
offered in two different ways: for A. balzani colonies, the
baits were arranged like a half moon, at 25 cm of distance
from the nest entrance (Figure 1A). For A. opaciceps, the
baits were arranged in a line, parallel to the foraging trail,
at 10 cm of distance from the trail and 1 m from the nest
entrance (Figure 1B).
After the rst contact of a worker with any of the
baits, we started the period of 30 minutes of observation
for colonies of A. balzani and 20 minutes for colonies of A.
opaciceps and the number of baits collected by leaf-cutting
ants was recorded. The difference in the observation time
between species was due to the size of the colonies and the
form of recruitment (smaller nests and slower recruitment in
A. balzani). During the observation period, we consider as
collected any bait that has been removed from the pile, even
if the bait has subsequently been abandoned.
The number of baits remaining between treatments was
compared using a Generalized Linear Mixed Model (GLMM)
with a Poisson distribution and a logarithmic link function.
This modeling approach offers more exibility for variables
that do not follow a normal distribution (Bolker et al., 2009). We
used the “lme4” package in R to adjust the GLMM to our data.
Sociobiology 70(3): e8701 (September, 2023)
The model consisted of the response variable ‘number
of baits remaining’, the xed effect, represented by the
variable ‘treatment’, with three levels (ExtAc, ExtAt, and
Control), and the random effect ‘nests’, allowing to evaluate
the variation in the number of baits remaining among the
different observed colonies, even if the treatment effect is
the same for all colonies. In another approach, the “survival”
time of the baits (i.e., the time until they were removed)
between the different treatments was tested using survival
analysis (Kaplan-Meier), followed by pairwise comparisons
using log-rank tests, to verify if there was a preference for
the collection by a certain treatment level, at a signicance
level of 5% (Crawley, 2007). The Kaplan-Meier method is
widely used to estimate the survival function when dealing
with censored data, that is, where the event of interest (bait
withdrawal) is not observed for all baits in the group or
in all treatments, during the observation period (Barber &
Jennison, 1999). Data were analyzed using R software (R
Development Core Team, 2023).
Results
Deterrence was observed for extracts from colonies
of LCA and this effect differed signicantly from control
extracts. Both foragers of A. balzani and A. opaciceps avoided
the baits treated with NR extracts, regardless of their origin
(intraspecic or interspecic). Ants avoided treated baits even
with the attractive effect of citrus pulp. In general, 85% of
the baits with NR were rejected, while approximately 80%
of the control baits were carried to the nests during the
observation period.
For A. balzani colonies, the average number of remaining
baits (unloaded) was 2.93 ± 0.61 (mean ± standard error) for
the control (Cont), 9.27 ± 0.36 for the intraspecic extract
(ExtAc ) and 9.6 ± 0.28 for the interspecic extract (ExtAt).
Thus, there was a signicant difference between the number
of remaining baits of Cont x ExtAc (p = 0.001) and Cont. x
ExtAt (p < 0.001), but there was no signicant difference
between ExtAc versus ExtAt treatments (p = 0.906) (Figure 2A).
Fig 1. Experimental design indicating the arrangement of the baits near the nests of leaf-cutting ants: For Acromyrmex
balzani the baits were arranged radially (A). For Atta opaciceps nests the baits were placed parallel to the foraging trail (B).
Fig 2. Results of the bioassay with eld colonies of Acromyrmex balzani. A - Boxplot showing the remaining baits among the three
treatments. Horizontal lines indicate median values, the top and bottom box indicate the upper and the lower quartiles, respectively, and
dots are outliers. In B, bait survival probability over the observation time of 30 minutes (1800 seconds).
Leandro Sousa-Souto, Bianca G. Ambrogi, Rafaella S. Santos – Nest refuse extract delays bait collection
Regarding the “bait survival”, there was a signicant
difference in the probability of bait survival of the ExtAc
versus Control (p = 0.018) and ExtAt versus Control (p <
0.001) but there was no difference between ExtAc versus
ExtAt (p = 0.508) (Figure 2B).
Similar results were observed for colonies of A.
opaciceps. The average number of remaining (unloaded)
baits was 1.47 ± 0.36 (mean ± SE) for control, 6.44 ± 0.57
observed in ExtAc, and 8.19 ± 0.43 for the (ExtAt). There
was a signicant difference between the NR extracts and
the control (p < 0.001), and betwwen ExtAc versus ExtAt
(p = 0.015) (Figure 3A). As observed in A. balzani, there
was a signicant difference in the “bait survival” among the
extracts (p < 0.001), but no difference between the ExtAc
versus ExtAt treatments (p = 0.52) (Figure 3B).
Discussion
The nest refuse from LCA is being better studied and
most results have shown multiple uses, either as an additional
source of nutrients and organic material to the soil (Cerda et
al., 2012; Santos et al., 2018; 2019), or through its deterrent
effect against herbivory of the ants themselves (Sousa-Souto
et al., 2022) and, more recently, against aphids (Mecenas
et al., 2023). Our results show that extracts in liquid form,
prepared with the disposal substrate (NR) have both intra and
interspecic deterrent effects on the foraging behavior of ants,
corroborating similar results using dry waste (Zeh et al., 1999;
Farji-Brener & Sasal, 2003; Ballari & Farji-Brener, 2006).
In the present study, hydroalcoholic extracts from A.
balzani and A. opaciceps colonies were efcient in reducing
bait collection by ants when compared to the control extract.
Almost all control baits were collected by the different
sampled colonies and there was little collection of treated baits
(less than 40% in the most active colonies). In addition, some
behavioral changes were noted, although not measured, as for
example, the processing time (touch of antennae and jaws on
the bait) and the start of loading the baits were signicantly
shorter for control baits when compared to the baits of the
ExtAt and ExtAc treatments. Besides the longer processing
time of baits with NR by workers, few baits were actually
loaded, even after the observation time had ended.
One point to be reported is that many baits with NR
registered as “counted” were abandoned by the workers after
two or three minutes that were removed from the point of
origin. This behavior was not observed in ants that collected
the control baits. In addition, the behavior of attempting to
remove the citrus pulp inside of the plastic straw was also
observed. In fact, many abandoned straws were cut or bitten
by ants. This behavior is further evidence that baits with NR
showed characteristics that were recognized by the ants as
harmful to them, corroborating the hypothesis that odor is the
mechanism behind deterrence (Sousa-Souto et al., 2022). In
fact, a preliminary analysis through liquid chromatography
(HPLC-DAD) of the NR extracts suggests that the substances
present may be secondary metabolites from plants foraged by
the colonies, such as gallic and p-coumaric acids, two simple
phenolic acids (Mecenas et al., 2023).Thus, although the strong
Fig 3. Results of the bioassay with eld colonies of Atta opaciceps. A - Boxplot showing the remaining baits among three treatments.
Horizontal lines indicate median values, the top and bottom box indicate the upper and the lower quartiles, respectively, and dots are outliers.
In B, bait survival probability over the observation time of 30 minutes (1800 seconds).
Sociobiology 70(3): e8701 (September, 2023) 5
attractiveness of the citrus pulp in the baits treated with NR,
the deterrent effect was effective, causing rejection or later
abandonment of the treated baits.
Ants select the material to be harvested from the
physical or chemical characteristics of the host plant, such as
the absence of trichomes in the leaves, nutritional value of the
material, levels of secondary metabolites, energy expenditure
to incorporate this material into the symbiotic fungus garden
(Garcia et al., 2005; Verza et al., 2007). Vegetable materials
considered unsuitable for the cultivation of the fungus or
which may be toxic are generally rejected at the time of
cutting by foragers, or before incorporation into the fungus,
by garden workers (Verza et al., 2007). Thus, it is possible
that the rejection of baits with NR at the time of foraging
shows that the workers were able to associate the odor of
the baits with those phenolic acids mentioned above or other
potential risks for the colony.
Although LCA shares the same species of symbiont
fungus and has similarities in communication between
nestmates, the colonies differ through their highly specic
chemical prole (Viana-Bailez et al., 2011). The experimental
design of the present study, however, does not allow us to
conclude that the low collection of baits treated with the
interspecic extract was due to the recognition of the baits as
material from a rival colony (territorial behavior) or simply
due to the inherent odor of the disposal substrate.
Considering the composition of nest refuse between
the two species, we can highlight some striking differences
between these two substrates (Della Lucia et al., 2013).
First, there are differences in the origin of the plant material
of both NRs, for A. balzani (ExtAc) the NR composition is
of herbaceous plants (with a predominance of grasses). The
material is totally discarded outside the colony, making it drier
and more fragmented. The disposal material of A. opaciceps
is done mainly through underground chambers, although
some colonies deposit their NR in external piles adjacent to
the nest (Sousa-Souto et al., 2022). The incorporation of nest
waste in the inner chambers makes the substrate texture more
compact, with high moisture content and a more pronounced
odor. It is reported that residues deposited internally are more
susceptible to the proliferation of pathogens, compared to
waste discarded outside the nests (Farji-Brener et al., 2016).
Even with all these differences, however, the observed
interspecic effect of the extracts indicates that the deterrence
can be triggered simply by the characteristic odor of the
refuse substrate.
Despite advances in knowledge of the potential
deterrent effect of nest refuse on ant foraging, it is still
unclear whether such effects are long-term and whether its
use would be viable on a large scale. Thus, new studies must
be conducted to ll in the gaps that still exist, conrming (or
not) the use of NR extracts as a new perspective in integrated
pest management.
Acknowledgments
We would like to thank Hosana H. Mecenas, for the
support of data collection, to Dr. Genésio Tâmara Ribeiro,
from the Laboratório de Entomologia Florestal (LEFLO) da
Universidade Federal de Sergipe (UFS) and Dr. Yana Teixeira
dos Reis, from the Laboratório de Entomologia (UFS) for
their help in acquiring the substrate. To Dr. Paulo Cesar de
Lima Nogueira, from the laboratório de Química Orgânica
(UFS) for his assistance in conducting the chromatographic
analyses. To Dr. Sinara M. Moreira for suggestions for
improving the methodology. To the Conselho Nacional de
Desenvolvimento Cientíco e Tecnológico (CNPq), CAPES
(PROAP), and CAPES/FAPITEC (88881.157451/2017–01)
for funding.
References
Ballari, S.A. & Farji-Brener, A.G. (2006). Refuse dumps of
leaf-cutting ants as a deterrent for ant herbivory: does refuse
age matter? Entomologia Experimentalis et Applicata, 121:
215-219. https://doi.org/10.1111/j.1570-8703.2006.00475.x
Barber, S. & Jennison C. (1999). Symmetric tests and condence
intervals for survival probabilities and quantiles of censored
survival data. Biometrics, 55: 430-436.
https://doi.org/10.1111/j.0006-341X.1999.00430.x
Barbosa, F.R., Silva, C.S.B. & Carvalho, G.K.L. (2006).
Receitas para obtenção de inseticidas naturais de origem
vegetal. In Barbosa, F.R., Silva, C.S.B. & Carvalho, G.K.L.
Uso de inseticidas alternativos no controle de pragas agrícolas.
Documentos, 191. Embrapa Semi-Árido, p. 10-27.
Boaretto, M.A.C. & Forti, L.C. (1997). Perspectivas no controle
de formigas cortadeiras. Série Técnica IPEF, FCA/UNESP,
11: 31-46.
Bolker, B.M., Brooks, M.E., Clark, C.J., Geange, S.W.,
Poulsen, J.R., Stevens, M.H.H. & White, R. (2009).
Generalized linear mixed models: A practical guide for
ecology and evolution. Trends in Ecology and Evolution, 24:
127-135. https://doi.org/10.1016/j.tree.2008.10.008
Bot, A.N.M., Currie C.R., Hart, A.G. & Boomsma, J.J.
(2001). Waste management in leaf-cutting ants. Ethology,
Ecology and Evolution, 13: 225-237.
https://doi.org/10.1080/08927014.2001.9522772
Carlos, A.A., Forti, L.C., Camargo, R.S., Moreira, S.M.,
Verza, S.S. & Diniz, E.A. (2009). Attractiveness of different
citrus pulps to the leaf-cutting ant Atta sexdens rubropilosa
(Hymenoptera: Formicidae). Sociobiology, 54: 799-805.
Cerda, N.V., Tadey, M., Farji-Brener, A.G. & Navarro, M.C.
(2012). Effects of leaf- cutting ant refuse on native plant
performance under two levels of grazing intensity in the
Leandro Sousa-Souto, Bianca G. Ambrogi, Rafaella S. Santos – Nest refuse extract delays bait collection
Monte Desert of Argentina. Applied Vegetation Science, 15:
479-487. https://doi.org/10.1111/j.1654-109X.2012.01188.x
Crawley, M.J. (2007). The R book. England: Ed John Wiley
& Sons Ltd. 951p. https://doi.org/10.1002/9780470515075
Delabie, J.H.C., Nascimento, I.C., Fonseca, E., Sgrillo,
R.B., Soares, P. A.O., Casimiro, A.B. & Furst, M. (1997).
Biogeograa das formigas cortadeiras (Hymenoptera;
Formicidae; Myrmicinae; Attini) de importância econômica
no leste da Bahia e nas regiões periféricas dos estados
vizinhos. Agrotrópica, 9: 49-58.
Della Lucia, T.M.C., Gandra, L.C. & Guedes, R.N.C. (2013).
Managing leaf-cutting ants: peculiarities, trends and challenges.
Pest Management Science, 70: 14-23.
https://doi.org/10.1002/ps.3660
Dethier, L., Browne, B. & Carroll, N.S. (1960). The
designation of chemicals in terms of the responses they elicit
from insects. Journal of Economic Entomology, 53: 134-136.
https://doi.org/10.1093/jee/53.1.134
Farji-Brener, A.G., Elizalde, L., Fernández-Marín, H. &
Amador-Vargas, S. (2016). Social life and sanitary risks:
evolutionary and current ecological conditions determine
waste management in leaf-cutting ants. Proceedings of the
Royal Society B: Biological Sciences, 283: 1-7.
https://doi.org/10.1098/rspb.2016.0625
Farji-Brener, A.G. & Sasal, Y. (2003). Is dump material an
effective small-scale deterrent to herbivory by leaf-cutting
ants? Ecoscience, 10: 151-154.
https://doi.org/10.1080/11956860.2003.11682761
Garcia, M.G., Forti, L.C., Verza, S.S., Noronha, N.C. Jr. &
Nagamoto, N.S. (2005). Interference of epicuticular wax from
leaves of grasses in selection and preparation of substrate for
cultivation of symbiont fungus by Atta capiguara Gonçalves,
1944 (Hym. Formicidae). Sociobiology, 45: 937-947.
Holldöbler, B. & Wilson, E.O. (1990). The ants. Cambridge:
Harvard University Press.
https://doi.org/10.1007/978-3-662-10306-7
Lara, F.M. (1991). Tipos de resistência. In: Lara, F.M. Princípios
de resistência de plantas a insetos. Ícone, 2ª ed., p. 35-74.
Mecenas, H.H.B., Ambrogi, B.G. & Sousa-Souto, L. (2023).
Repellent effect of leaf-cutting ant waste against the aphid
Lipaphis erysimi (Kaltenbach). Archives of Agriculture Research
and Technology, 4: 1049.
https://doi.org/10.54026/AART/1049
Montoya-Lerma, J., Giraldo-Echeverri, C., Armbrecht, I., Farji-
Brener, A. & Celle, Z. (2012). Leaf-cutting ants revisited:
Towards rational management and control. International Journal
of Pest Management, 58: 225-247.
https://doi.org/10.1080/09670874.2012.663946
Moreira, A.A. & Forti, L.C. (1999). Distribuição de substratos
nas colônias de Atta laevigata (F. Smith, 1858) (Hymenoptera:
Formicidae). Scientia Agricola, 56: 465-469.
https://doi.org/10.1590/S0103-90161999000200029
Pagnocca, F.C., Rodrigues, A. & Bacci Jr, M. (2011).
Microrganismos associados às formigas-cortadeiras. In: Della
Lucia, T.M.C. (Ed) Formigas cortadeiras: da bioecologia ao
manejo. Editora UFV, 1ª ed., p. 262-283.
R Development Core Team. (2023). R: A language and
environment for statistical computing.
Santos, R.S., Guerra, M.B.B., Ambrogi, B.G. & Sousa-Souto,
L. (2018). Nest refuse of leaf-cutting ants as a growing substrate
for organic farming systems. Organic Agriculture, 8: 315-324.
https://doi.org/10.1007/s13165-017-0199-1
Santos, R.S., Haum, H.B.M. & Sousa-Souto, L. (2019).
Nest refuse of Atta opaciceps (Hymenoptera: Formicidae)
increases plant biomass and diversity during the regrowth of
herbaceous species. Applied Soil Ecology, 133: 160-165.
https://doi.org/10.1016/j.apsoil.2018.10.002
Sousa-Souto, L., Viana-Junior, A.B. & Nascimento, E.S.
(2013). Spatial distribution of Acromyrmex balzani (Emery)
(Hymenoptera: Formicidae: Attini) nests using two sampling
methods. Sociobiology, 60: 162-168.
https://doi.org/10.13102/sociobiology.v60i2.162-168
Sousa-Souto, L, Ambrogi, B.G. & Santos, R.S. (2022). Nest
refuse extract deters ant herbivory. Entomologia Experimentalis
et Applicata, 170: 437-441. https://doi.org/10.1111/eea.13154
Urbas, P., Araújo, M.V., Leal, I.R. & Wirth, R. (2007). Cutting
more from cut forests: edge effects on foraging and herbivory
of leaf-cutting ants in Brazil. Biotropica, 39: 489-495.
https://doi.org/10.1111/j.1744-7429.2007.00285.x
Verza, S.S., Forti, L.C., Lopes, J.F.S., Camargo, R.S. & Matos,
C.A.O. (2007). Inuence of physical and chemical factors during
foraging and culture of the symbiont fungus in Atta sexdens
rubropilosa (Hymenoptera: Formicidae). Insect Science, 14:
295-300. https://doi.org/10.1111/j.1744-7917.2007.00155.x
Viana-Bailez, A.M., Bailez, O. & Malaquias, K.S. (2011).
Comunicação química em formigas-cortadeiras. In Della Lucia,
T.M.C. (ed), Formigas cortadeiras: da bioecologia ao manejo.
Editora UFV, 1ª ed., p. 141-164.
Zanetti, R., Zanuncio, J.C., Santos, J.C., Silva, W.L.P., Ribeiro,
G.T. & Lemes, P.G. (2014). An overview of integrated
management of leaf-cutting ants (Hymenoptera: Formicidae)
in Brazilian forest plantations. Forests, 5: 439-454.
https://doi.org/10.3390/f5030439
Zeh, J., Zeh, A. & Zeh, D. (1999). Dump material as an effective
small-scale deterrent to herbivory by Atta cephalotes. Biotropica,
31: 368-371. https://doi.org/10.1111/j.1744-7429.1999.tb00149.x
ResearchGate has not been able to resolve any citations for this publication.
Article
Full-text available
About one-third of organic agriculture production in Brazil is carried out by smallholders, who seek to use low-cost organic fertilizers in their crops. In this study, we evaluated the nest refuse of leaf-cutting ants (NR) in the formulation of growing substrates for lettuce (Lactuca sativa) and arugula (Eruca sativa) seedlings. A completely randomized design with six treatments and four repetitions was applied. The treatments were basis growing substrate (CONT), commercial substrate (TropstratoHT®—TROP), and four formulations using NR of two species of leaf-cutting ants associated with 75 or 85% (volume fraction) of CONT. Substrates were submitted to chemical analysis for determination of macro- and micronutrients while plant vigor was evaluated considering plant height (PH), root length (RL), stem diameter (SD), dry mass (DM), and number of leaves (NL) at 15, 20, 25, and 30 days after sowing. The data were submitted to a chemometric evaluation by means of principal component analysis (PCA). Treatments with 25% of NR resulted in lettuce seedlings from 42 to 53% higher and with a twofold increase of dry mass compared to the commercial substrate (TROP) (P < 0.05). For arugula, similar results were found for PH and NL between TROP and the substrate with 25% of NR and these results differed significantly from the other treatments (P < 0.05). PCA revealed the formation of five groups of treatments, with TROP and two treatments based on NR presenting higher correlation with the nutrient content and plant vigor (P < 0.01). This study is the first to indicate the feasibility of nest refuse of leaf-cutting ants in the composition of substrates for organic agriculture in small-scale production.
Article
Full-text available
The most common control method uses toxic baits consisted of dehydrated citrus pulp as carrier and attractant. However, the portion of the citrus fruit that is attractive to ants is still unknown, despite its importance in chemical control. This study compared the attractiveness of different fruit parts of citrus pulps to Atta sexdens rubropilosa workers. Three treatments: pellets of industrial citrus pulp, albedo (mesocarp), and whole citrus pulp were offered randomly to ants and the removal of these substrates by workers was observed. The three pulps were equally attractive to this species (F = 0.8033; p = 0.4633). Although the whole pulp included the epicarp, it was as attractive as the other treatments, possibly because, the material was heated during processing, eliminating any volatile substance that could repel ants.
Article
Full-text available
Ants are recognized as one of the major sources of soil disturbance world‐wide. However, this view is largely based on isolated studies and qualitative reviews. Here, for the first time, we quantitatively determined whether ant nests affect soil fertility and plant performance, and identified the possible sources of variation of these effects. Using Bayesian mixed‐models meta‐analysis, we tested the hypotheses that ant effects on soil fertility and plant performance depend on the substrate sampled, ant feeding type, latitude, habitat and the plant response variable measured. Ant nests showed higher nutrient and cation content than adjacent non‐nest soil samples, but similar pH . Nutrient content was higher in ant refuse materials than in nest soils. The fertilizer effect of ant nests was also higher in dry habitats than in grasslands or savannas. Cation content was higher in nests of plant‐feeding ants than in nests of omnivorous species, and lower in nests from agro‐ecosystems than in nests from any other habitat. Plants showed higher green/root biomass and fitness on ant nests soils than in adjacent, non‐nest sites; but plant density and diversity were unaffected by the presence of ant nests. Root growth was particularly higher in refuse materials than in ant nest soils, in leaf‐cutting ant nests and in deserts habitats. Our results confirm the major role of ant nests in influencing soil fertility and vegetation patterns and provide information about the factors that mediate these effects. First, ant nests improve soil fertility mainly through the accumulation of refuse materials. Thus, different refuse dump locations (external or in underground nest chambers) could benefit different vegetation life‐forms. Second, ant nests could increase plant diversity at larger spatial scales only if the identity of favoured plants changes along environmental gradients (i.e. enhancing β‐diversity). Third, ant species that feed on plants play a relevant role fertilizing soils, which may balance their known influence as primary consumers. Fourth, the effects of ant nests as fertility islands are larger in arid lands, possibly because fertility is intrinsically lower in these habitats. Overall, this study provide novel and quantitative evidence confirming that ant nests are key soil modifiers, emphasizing their role as ecological engineers.
Article
Full-text available
Adequate waste management is vital for the success of social life, because waste accumulation increases sanitary risks in dense societies. We explored why different leaf-cutting ants (LCA) species locate their waste in internal nest chambers or external piles, including ecological context and accounting for phylogenetic relations. We propose that waste location depends on whether the environmental conditions enhance or reduce the risk of infection. We obtained the geographical range, habitat and refuse location of LCA from published literature, and experimentally determined whether pathogens on ant waste survived to the high soil temperatures typical of xeric habitats. The habitat of the LCA determined waste location after phylogenetic correction: species with external waste piles mainly occur in xeric environments, whereas those with internalwaste chambers mainly inhabit more humid habitats. The ancestral reconstruction suggests that dumping waste externally is less derived than digging waste nest chambers. Empirical results showed that high soil surface temperatures reduce pathogen prevalence from LCA waste. We proposed that LCA living in environments unfavourable for pathogens (i.e. xeric habitats) avoid digging costs by dumping the refuse above ground. Conversely, in environments suitable for pathogens, LCA species prevent the spread of diseases by storing waste underground, presumably, a behaviour that contributed to the colonization of humid habitats. These results highlight the adaptation of organisms to the hygienic challenges of social living, and illustrate how sanitary behaviours can result from a combination of evolutionary history and current environmental conditions. © 2016 The Author(s) Published by the Royal Society. All rights reserved.
Article
Full-text available
The selection of plants is one of the stages of foraging behavior, executed by leaf-cutting ants for the cultivation of symbiont fungus. Anatomical, biochemical and physiological characteristics of vegetal species are some of the factors that influence selection of substrate; however, most studies described in the literature refer to leaf-cutting ants. Due to the scarcity of studies on the role of epicuticular waxes of grasses in relation to foraging behavior of monocotyledonous leaf- cutters, we completed three experiments with the ant species Atta capiguara in which we analyzed: the attractiveness or selectivity of leaves of Saccharum officinarum (sugarcane) and/or Hypharrenia rufa (capim jaraguá), with and without epicuticular wax in relation to the worker of this ant species, their processing and elimination in the form of pellets of epicuticular wax from the referred fragments removed by the workers for cultivation of symbiont fungus. We observed that vegetal fragments without wax were those most transported by workers to the inside of the nests; that they processed the fragments equally with as much as without wax, and eliminated, in the form of pellets, wax removed from the same into garbage chambers of the colonies, leading us to conclude that for monocotyledonous leaf-cutters, epicuticular wax from vegetal leaves has great importance in vegetal integrity by being used as substrate, representing a physical barrier to the growth of symbiont fungus. (Sociobiology, v.45, n.3, p.937-948, 2005)
Article
Most conventional methods for controlling agricultural pests cause environmental problems. Thus, sustainable pest management methods have been constantly sought and tested in recent years. The waste substrate produced by leaf-cutting ants (referred to as ‘nest refuse’) is reported to be repellent to their own foraging. This substrate is avoided by leaf-cutting ants because it presents chemical and physical warning signs to the ants in addition to possible pathogens. In the present study, we experimentally analyzed whether a liquid formulation prepared with the discarded substrate produced by leafcutting ants of the species Acromyrmex balzani and Atta opaciceps would be repellent to the aphid Lipaphis erysimi. A total of 103 bioassays were carried out in petri dishes of Ꝋ = 150 mm, with two leaf discs of Brassica oleracea L. (var. acephala) sprayed with the control solution (water/alcohol 50%) or with the extract of the nest refuse of one of the ant species. Bioassays were compared using binomial analysis. Ant waste extracts from both species were efficient in repelling aphids (P < 0.05). New studies can help fill in the gaps found, such as the identification of substances potentially causing the effect, the duration of the effect, and the dosage and adequate amounts of extract to be applied, as well as other crops to be protected, and other pests to be repelled.
Article
Leaf‐cutting ants (LCA) try to reduce the risk of contamination in their colonies by avoiding contact with their nest refuse (NR), as it can harbor substances harmful to them and their symbiotic fungi. Here, we tested whether an aqueous extract with 10% vol/vol of NR of the leaf‐cutting ant Atta opaciceps Borgmeier (Hymenoptera: Formicidae, Attini) causes a deterrent effect. We placed leaves of Hibiscus rosa‐sinensis L. (Malvaceae) sprayed with NR extract or distilled water (control) in the foraging areas of 12 colonies – eight colonies of A. opaciceps and four of Atta sexdens (L.) – for 60 min, on three consecutive days. The fresh weight of remaining leaf fragments between treatments was compared using linear‐mixed effect models. Leaf consumption was significantly lower in the presence of NR extract for 48 h, indicating that the NR odor impregnated in the leaves may have been the responsible factor for the deterrence. Further studies are needed to establish a deterrent extract with a broad spectrum and lasting effect on plants, and to better understand the mechanisms involved in deterrence.
Article
The time interval in which a community plant recovers after a disturbance is strongly associated with the availability of nutrients and soil organic matter, factors that are widely known as limiting for the establishment of pioneer species. The nest refuse (NR) produced by leaf cutting ants may act to favour herbaceous regeneration in newly disturbed areas, but little is known about its effects in this process. In the present study, we experimentally verified the effect of NR on plant regeneration in a newly deforested area, testing the hypothesis that plots with NR act as hot spots for plant establishment, promoting greater aboveground biomass and altering the vegetation structure in comparison to control sites. Thirty plots of 30 × 30 cm were installed, where half of the plots received a layer of 3 cm of soil from the same site (control) while the other plots received a layer of 3 cm of a mixture of control soil + NR, in a 3:1 ratio (25% organic refuse). After 150 days of natural regeneration, we evaluated the diversity of herbaceous species that colonised each plot and the aboveground dry biomass. The species composition differed between treatments and the aboveground biomass was 45% higher in the plots with NR than control soil. In this way, refuse dumps can act as regeneration sites, favouring pioneer species in newly deforested areas.