Random effects were modeled with plant identity nested within site to account for the block design of the experiment and to control for variation between our sites. To model count data and to correct for over dispersion, we used a Poisson-lognormal model with a log link function by including a per-observation random effect as described above .We modeled CBB removal by ants using a GLMM. We included treatment , coffee plant distance to nest tree, ant activity on coffee plants after string placement, the interaction between treatment and distance, and the interaction between treatment and ant activity on plants as fixed effects . Random effects were modeled with plant identity nested within site to account for the block design of the experiment and to control for variation between our sites. To model count data in our response variable we used a Poisson distribution with a log link function.We constrained model selection to include biologically pertinent terms for inference and to aid in model interpretation. A full model of these terms was tested, along with subsequent models of different covariate combinations and a null intercept-only model of random effects . The best fit model was determined via backwards model selection compared to the full model, blackberries in containers where the model that resulted in the lowest AIC score with ∆AIC > +2 was selected. Overall significance in models was assessed using Wald type II Chisquared tests. Statistical differences among treatments were compared by Wald Z tests .
In all cases, fixed effect parameters and the variance of random effects was estimated by maximum likelihood with Laplace approximation using the ‘glmer’ function in the ‘lme4’ package in R . To aid in data interpretation, we removed one coffee plant replicate from our analysis where measured ant activity was more than double that of any other plant measured and may have resulted from an unusually high buildup of scale insects which are tended by A. sericeasur on coffee. Additionally, one nest tree replicate was not included in the tree activity analysis because the data were not collected at that site. Finally, coffee plant height and distance to nest tree were centered and scaled to aid model interpretation. All analyses were performed in R .Our experiment demonstrates that the addition of string to connect shade trees and coffee plants in coffee agroecosystems facilitates movement for A. sericeasur and potentially increases ant recruitment rates. Studies in natural systems have reported increases in ant activity with arboreal connections across the arboreal stratum , possibly driven by the easy access these pathways provide to resources . Other ants, such as Pogonomyrmex spp. prefer linear arboreal substrates and switch to cleared routes as a mechanism to reduce the energetic costs of ant foraging , and in some cases to decrease the risk of encountering predators . The observed increase in ant activity on connected coffee plants after the placement of strings suggests that structural connectivity can increase ant recruitment rates to foraging areas in coffee and may enhance the efficiency of movement for A. sericeasur.
This may lead to increased foraging efficiency for ants and enhanced resource capture rates on coffee. However, this could also reflect other benefits associated with using linear arboreal substrates, such as avoiding predators, a behavior that is known to occur in A. sericeasur . Using more efficient foraging pathways and thereby avoiding the leaf litter as a primary foraging substrate may potentially protect A. sericeasur workers from the attack of the phorid fly parasitoid Pseudacteon spp. . While ant activity only significantly increased after string placement on connected coffee plants, we also observed lesser increases in ant activity on control coffee plants and nest trees . This unexpected result could mean that strings, a novel element in the environment, acted as a form of habitat modification or disturbance, which increased overall ant activity in the local area. However, if our manipulation were the cause, we would have expected the ants to attack the jute strings , a behavior that we did not observe during the experiment. Experiments in tropical forests have shown that the long-term removal of lianas can influence ant richness on trees , and therefore may possibly also affect overall ant abundance and activity when promoted. It is also possible that other factors could potentially explain this result in control plants, such as changes in local abiotic factors that we did not measure systematically in our experiment. Future research which expands on the temporal scope of this study may be useful in assessing the long-term effects of artificial connectivity in this system. Ant activity post string placement was negatively affected by distance to the nesting tree .
This result is consistent with previous studies suggesting that within 5 meters A. sericeasur dominance in the leaf litter decreases with distance to the nesting tree . However, in our study, the effect of distance after string placement was significant only on control plants, but not on connected plants. This suggests that connections could buffer the negative effects that larger distances from the nesting tree pose to ant activity and potentially increase ant-provided biological control services in these plants. Connected coffee plants also had significantly higher CBB removal than control plants . Overall, greater ant activity on coffee plants was associated with higher CBB removal rates , suggesting that ant activity directly influenced CBB removal rates. However, while this effect was significant on control coffee plants it was only marginally significant on connected plants. While we believe that these results support the hypothesis that connectivity enhances ant foraging and bio-control services on coffee, the use of dead CBB in this experiment as a proxy to measure bio-control may explain the only marginally significant effect of ant activity on CBB removal in connected plants. It is possible that dead prey exhibit more variable recruitment responses from ants than live prey. Despite this, it is likely that strings facilitated ant movement to coffee plants by providing a smooth, linear substrate and indirectly increased CBB removal . In other systems, the leaf-cutting ant Atta cephalotes uses fallen branches to rapidly move between areas and thereby quickly discover new food resources . Similarly, these resources allow scouts to return quickly to the colony, minimizing the time taken for information transfer and recruitment of other foraging workers . The role of trunk trails and fallen branches has received extensive attention in the leaf-cutting ant system, however, fewer studies have looked at the influence of connectivity resources on foraging behavior of predatory arboreal ants. Surprisingly, CBB removal did not follow the same trend as ant activity with distance to the nesting tree. While control plants tended to have lower CBB removal rates than connected plants as distance to the tree increased, blackberry containers we did not find a significant effect of distance on CBB removal in either control or connected plant groups. Collectively, these results suggest that connections in the arboreal stratum have the potential to increase ant activity and therefore enhance plant protection from CBB attack, particularly in connected plants. Further studies should assess the effect of distance on CBB removal using plants located at distances larger than 3.5 m from the tree. It is important to note the potential for negative impacts of enhanced ant activity on coffee plants resulting from hemipteran tending behavior. While ant activity can increase the density of green coffee scale insects, which may harm coffee plants and reduce coffee productivity, the scale are not a major pest in the region of study, and are not as economically significant as the coffee berry borer . A recent study evaluating the benefits associated with the indirect Azteca–Coffea mutualism, which emerges from the Azteca-scale mutualism, found that the protective benefit ants provide to coffee plants is positively associated with high densities of the scale . Therefore, it is possible that enhanced CBB control associated with scale-tending by ants outweighs the costs associated with scale damage. However, these interactions may be context-dependent, and still need to be fully evaluated in the field to provide a holistic understanding of the impact of connectivity on scale density and coffee yield. Other ant species could also benefit from the addition of connections between coffee plants and shade trees, such as Cephalotes basalis and Pseudomyrmex simplex, which were observed using these connections during our study.
The ant P. simplex has been previously reported as an important CBB bio-control agent, acting in conjunction with other species of ants to effectively suppress CBB at various life stages . Therefore, this technique could support Azteca ants as well as other ant species that play an important role in suppressing CBB populations. Our results support the general hypothesis that connectivity, one measure of habitat complexity, can sustain important ecological processes in natural and managed ecosystems. In aquatic systems, more complex habitats with macrophytes allow for greater food capture and maintain higher levels of diversity . In terrestrial systems, higher complexity can influence trophic dynamics . In coffee agroecosystems, ants are highly sensitive to habitat change and management intensification, generally expressed as the reduction of shade, elimination of epiphytes, and use of chemical inputs . Such intensification can have a negative effect not only on vegetation connectivity and ant foraging, but may also cascade to affect ecosystem services, such as biological control. Our study supports the idea that promoting complexity at a local scale, in this case providing structural resources for ants in agroecosystems, can significantly enhance connectivity within the arboreal strata, and potentially improve biological control of coffee pests. This idea has already been successfully implemented in other agricultural systems, placing “ant bridges” made of bamboo strips or strings connecting neighboring trees in , and could be incorporated as a management strategy in coffee systems. Future research should evaluate the practical feasibility of adding connections between vegetation strata to enhance bio-control. For example,studies in timber plantations have estimated that the presence of ants increases timber production by 40%, and that ants can be maintained at lower costs by providing intra-colony host tree connections using rope, poles or lianas . It is important that future studies in coffee also consider the costs of other CBB control methods, such as the application of the pesticide endosulfan, which can lead to the development of resistance, can negatively impact natural enemies, and can have harmful impacts on human health . Further investigation into promoting ant bio-control with artificial connections in coffee should: 1) assess economic tradeoffs, management applicability, and farmers’ perceptions of this method in large and small coffee plantations, 2) compare the cost between string placement and other management approaches , and 3) assess coffee yields on connected and not connected plants to provide management recommendations. More broadly, incorporating conservation bio-control strategies in combination with vegetation connectivity is consistent with criteria identified as key for the sustainability of biological control, such as increasing local habitat quality and enhancing species’ dispersal ability . Generally, the maintenance of shade trees and natural vegetation in agroforestry systems may increase vegetation complexity and natural connectivity between plants to promote ant foraging and subsequent biological pest control. The extent to which biotic and abiotic factors shape species interactions and their distributions has been a central focus for community ecologists . Included in the wide spectrum of factors shaping community dynamics are the diversity and availability of food resources and habitat complexity; all are important determinants of species diversity, distribution and interactions . Recent theoretical advances and empirical work in community ecology suggest that further research is needed to understand how resource availability and environmental factors shape species interactions. Specifically, one research gap is in our understanding of how variation in resources along habitat complexity gradients affects species interactions . However, empirically demonstrating how resources vary and how species respond is methodologically complicated, in the sense that the manipulation of multiple resources and consumers is not always straight forward, especially in complex systems. Consequently, studies have focused primarily on one single resource and– disproportionately– on competitive species interactions. Further, the environmental context in which resources matter is also not well understood and will gain more importance as natural and managed systems continue to experience habitat simplification .