David A. Holway’s research while affiliated with University of California System and other places

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Publications (136)


Argentine ant workers on coralline algae in intertidal marine wrack at Tourmaline Beach, San Diego County, California. Photo by Craig Chaddock
A Argentine ant activity and B arthropod biomass at eight spatially-paired coastal (beach) and inland (scrub) sites. Box plots show median (bold line), first and third quartiles, and minimum and maximum; unfilled circles represent outliers
Natural values of δ¹³C and δ¹⁵N of plants, algae, and arthropods collected at eight pairs of coastal (beach; open symbols) and inland (scrub; closed symbols) sites (Table 1). For each organism at each type of site, δ¹³C and δ¹⁵N values are averaged across summer and fall sampling periods. Central points indicate joint means; lines show standard errors. Code names are as follows: Buc = California buckwheat (Eriogonum fasciculatum), Lau = laurel sumac (Malosma laurina), Lem = lemonade berry (Rhus integrifolia), Sil = silverfish (Thysanura), Dar = darkling beetles (Eleodes spp.), Rol = isopods (Armadillidium vulgare), Spi = spiders (Araneae), Arg = Argentine ant (Linepithema humile), Wee = weevils (Coleoptera), Fly = seaweed flies (Fucellia sp.), Amp = sandhoppers (Megalorchestia sp.), Kel = giant kelp (Macrocystis pyrifera), Sur = surf grass (Phyllospadix sp.)
Natural values of (A) δ¹⁵N and (B) δ¹³C for the Argentine ant at coastal (beach) and inland (scrub) sites. Box plots show median (bold line), first and third quartiles, and minimum and maximum; unfilled circles represent outliers
Exploitation of a marine subsidy by a terrestrial invader
  • Article
  • Full-text available

December 2024

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9 Reads

Biological Invasions

Christopher Winters

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Grace Jurgela

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David Holway

Intertidal environments receive energy from marine ecosystems in the form of marine wrack, which makes up the base of a food web that includes both intertidal and terrestrial consumers. Consumption of wrack by terrestrial consumers can elevate their abundance and alter how they interact with organisms in adjacent terrestrial environments. Although rarely documented, terrestrial invaders may exploit marine wrack subsides and potentially disrupt intertidal and terrestrial food webs. Here, we examine consumption of marine wrack resources by the introduced Argentine ant (Linepithema humile), which occurs commonly on beaches in southern California. In controlled trials the Argentine ant readily scavenged arthropod detritivores (amphipods and flies) abundant in wrack. In spite of obvious risks (e.g., exposure to tides, desiccation, thermal stress) associated with intertidal foraging, Argentine ant activity on beaches was comparable to that in spatially-paired, scrub environments. Foraging on beaches allowed ants to access higher densities of arthropod prey and carrion compared to those found in scrub environments. Stable isotope analyses provide evidence for extensive assimilation of marine-derived resources. Values of δ¹⁵N and δ¹³C for the Argentine ant were higher at beach sites than at scrub sites, and Argentine ant δ¹⁵N values broadly overlapped those of intertidal consumers at beach sites. Although ants are known to forage in intertidal environments, this study provides a novel example of an introduced ant species exploiting a cross-boundary subsidy.

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An assemblage-level comparison of genetic diversity and population genetic structure between island and mainland ant populations

July 2024

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45 Reads

Evolution

Island biotas provide unparalleled opportunities to examine evolutionary processes. Founder effects and bottlenecks, for example, typically decrease genetic diversity in island populations, while selection for reduced dispersal can increase population structure. Given that support for these generalities mostly comes from single-species analyses, assemblage-level comparisons are needed to clarify how (i) colonization affects the gene pools of interacting insular organisms, and (ii) patterns of genetic differentiation vary within assemblages of organisms. Here, we use genome-wide sequence data from ultraconserved elements (UCEs) to compare genetic diversity and population structure of mainland and island populations of nine ant species in coastal southern California. As expected, island populations (from Santa Cruz Island) had lower expected heterozygosity and Watterson’s theta compared to mainland populations (from the Lompoc Valley). Island populations, however, exhibited smaller genetic distances among samples, indicating less population subdivision. Within the focal assemblage, pairwise Fst values revealed pronounced interspecific variation in mainland-island differentiation, which increases with gyne body size. Our results reveal population differences across an assemblage of interacting species, and illuminate general patterns of insularization in ants. Compared to single-species studies, our analysis of nine conspecific population pairs from the same island-mainland system offers a powerful approach to studying fundamental evolutionary processes.


Effects of temperature and soil moisture on flower size (a, b), nectar production (c, d), nectar concentration (e, f), and pollen production (g) for male (a, c, e, g) and female (b, d, f) flowers on bee‐pollinated Cucurbita pepo from Experiment I. Regression lines in (a)–(f) and asterisk (*) in (g) represent significant relationships; see Results and Table 1 for additional statistical information. For (g), box plots include the interquartile range with median line and whiskers that show quartiles ±1.5× interquartile range; points represent extreme values.
Effects of soil moisture on Cucurbita pepo reproductive success in Experiment I. (a) Seed set versus plant soil moisture (VWC%, mean percentage volumetric water content) in bee‐pollinated plants. (b) Pollen limitation versus plant soil moisture. Regression lines represent significant relationships; see Results for additional statistical information. The regression in (b) remains significant when the datum in the bottom right portion of the figure is excluded from analysis.
Effect of stigmatic fluorescent pigment deposition from plants grown in the low‐irrigation treatment on seed set in bee‐pollinated Cucurbita pepo in Experiment II. The regression line represents a significant relationship; see Results for additional statistical information.
Temperature and soil moisture manipulation yields evidence of drought‐induced pollen limitation in bee‐pollinated squash

June 2024

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39 Reads

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1 Citation

Climate change alters environmental conditions in ways that directly and indirectly affect plants. Flowering plants, for example, modify reproductive allocation in response to heat and drought stress, and such changes can in turn affect pollinator visitation and, ultimately, plant reproduction. Although the individual effects of warming and drought on plant reproductive allocation are well known, these factors may interact to influence reproduction. Here, we conducted a fully crossed temperature by irrigation manipulation in squash (Cucurbita pepo) to test how temperature and soil moisture variation affect pollinator‐mediated reproduction. To tease apart the direct and indirect effects of temperature and soil moisture, we compared hand‐pollinated plants to bee‐pollinated plants and restricted bee foraging (i.e., pollen transfer) to one experimental group per day. Temperature and soil‐moisture limitation acted independently of one another: warming decreased flower size and increased pollen production, whereas the effects of soil‐moisture limitation were uniformly inhibitory. While treatments did not change squash bee (Xenoglossa spp.) behavior, floral visitation by the honey bee (Apis mellifera) increased with temperature in male flowers and decreased with soil moisture in female flowers. Pollen deposition by bees was independent of plant soil moisture, yet reducing soil moisture increased pollen limitation. This result stemmed at least in part from the effects of soil‐moisture limitation on pollen viability; seed set declined with increasing deposition of fluorescent pigment (a proxy for pollen) from plants experiencing decreased soil moisture. These findings suggest that the transfer of lower‐quality pollen from plants experiencing soil‐moisture limitation led to drought‐induced pollen limitation. Similar effects may occur in a wide variety of flowering plant species as climate warming and drought increasingly impact animal‐pollinated systems.


PERMANOVA ordination depicting habitat characteristics between plots with (1–18) and without (19–44) San Bernardino flying squirrel (SBFS; Glaucomys oregonensis californicus) detections in the San Bernardino Mountains. Comparisons of sites with and without SBFSs in the San Bernardino Mountains revealed considerable overlap in terms of grouped habitat characteristics. The larger trapezoid encompasses plots where no squirrels were detected; the smaller polygon encompasses plots where flying squirrels were detected. Stress = 0.103.
Relationship between the area of down woody material (DWM) touching the ground and the detection of San Bernardino flying squirrels (Glaucomys oregonensis californicus) on a plot (total of 63 plots). The flying squirrels selected plots with higher areas of DWM touching the ground (p ≤ .01). Squirrel detections favored habitat with ≥60 m² DWM on a 30 m² radius plot.
PERMANOVA ordination depicting habitat characteristics between plots in the San Jacinto Mountains (left polygon), where no San Bernardino flying squirrels (SBFS; Glaucomys oregonensis californicus) were detected, and plots in the San Bernardino Mountains (right polygon), where SBFS were detected. Stress = 0.093. Forest habitats on the two mountain ranges differed significantly from one another in terms of grouped habitat characteristics.
Relationship between the detection of San Bernardino flying squirrels (SBFS; Glaucomys oregonensis californicus) and percent of canopy closure at each plot (total of 63 plots). Sixty meter transects were randomly positioned along an azimuth in each plot, and closure was measured every 15 m. SBFS selected habitats with a narrow range of percent canopy closure, 58%–77%, as shown in the smaller box/whisker plot on the left.
Average monthly temperature in the San Bernardino Mountains for 2000–2009 compared to the average monthly temperature in the San Jacinto Mountains for 1960–1969. The San Jacinto Mountains maintain higher temperatures. Data were downloaded from the NOAA database.
Habitat parameters influencing the distribution of a geographically isolated flying squirrel

May 2024

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79 Reads

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1 Citation

Clark S. Winchell

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David A. Holway

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[...]

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The San Bernardino flying squirrel (SBFS) is an isolated subspecies of Humboldt's flying squirrel, occurring in montane sky islands in the San Bernardino and San Jacinto Mountains in Southern California, USA. Recent small mammal surveys in the San Jacinto Mountains suggest the squirrel is extirpated. Our objectives were (1) determine habitat features, including forest metrics and topographical factors, that influence SBFS presence, in the San Bernardino Mountains; (2) use information collected in the San Bernardino Mountains to confirm squirrel occurrence and habitat preference in the San Jacinto Mountains; and (3) assess habitat and climatic differences between the two mountain ranges that could explain species persistence in one mountain range but not the other. We surveyed for SBFS using camera traps at 54 sites in the San Bernardino Mountains and 34 sites in the San Jacinto Mountains using both camera traps and acoustics. In the San Bernardino Mountains, we detected squirrels in sites that were more mesic, had higher structural heterogeneity, and had greater amounts of downed woody material compared to non‐detection sites. Habitat parameters were similar between the two ranges; however, squirrels were not detected in the San Jacinto Mountains. Conditions in the San Jacinto Mountains were hotter and drier. Increased temperatures due to climate change could potentially explain the absence of flying squirrels in the San Jacinto Mountains.


Effects of experimentally manipulated soil moisture on pollinator behavior in female flowers of Cucurbita pepo. (a) Visitation rate, (b) cumulative time spent nectaring per minute per flower, and (c) cumulative time spent in contact with the stigma per minute per flower for honey bees (Apis mellifera) and squash bees (Eucera spp.) versus plant soil moisture (VWC%, mean percentage volumetric water content). Each data point represents a separate plant for which we video‐recorded a female flower. Regression lines shown are for Apis behaviors only and are statistically significant; see Results and Appendix S1: Table S2 for additional information. Photos by Jess Gambel.
Seed set in bee‐pollinated and hand‐pollinated Cucurbita pepo as a function of plant soil moisture (VWC%, mean percentage volumetric water content) for (a) all bee‐pollinated and hand‐pollinated plants and (b) only those plants for which stigmatic pollen deposition overlapped in the two pollination groups (i.e., between 1490 and 3797 deposited total pollen grains per stigma per plant, averaged across the flowering season). Solid regression lines indicate bee‐pollinated plants, whereas dashed regression lines indicate hand‐pollinated plants. Data points represent mean values for individual plants. See Results for additional information.
Effects of fluorescent pigment deposition, pollen deposition, and soil moisture on seed set in bee‐pollinated Cucurbita pepo. Seed set versus (a) fluorescent pigment deposition from plants grown in the high‐irrigation treatment and (b) pollen deposition. Data points represent mean values for individual plants. Residuals of seed set for the model in Figure 3b versus (c) the proportion of fluorescent pigment deposition from plants grown in the high‐irrigation treatment and (d) soil moisture (VWC%, mean percentage volumetric water content of the recipient plant). Regression lines shown are statistically significant; see Results for additional information.
Divergent responses of generalist and specialist pollinators to experimental drought: Outcomes for plant reproduction

June 2023

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61 Reads

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5 Citations

Drought is an increasingly important consequence of climate change. Drought often causes plants to alter patterns of resource allocation, which in turn can affect how plants interact with other species. How these altered interactions subsequently influence plant reproductive success remains incompletely understood and may depend on the degree of specialization exhibited by antagonists and mutualists. Specialist pollinators, for example, are dependent on floral resources from their obligate hosts and under drought conditions may thus indiscriminately visit these hosts (at least in certain circumstances). Generalist pollinators, in contrast, may only forage on host plants in good condition, given that they can forage on other plant species. We tested this hypothesis and its consequences for plant reproduction in squash (Cucurbita pepo) grown along an experimental moisture gradient ranging from dry (growth and flowering compromised) to wet conditions. Floral visitation increased with plant soil moisture for generalist honey bees but was independent of plant soil moisture for specialist squash bees. Pollen production increased with plant soil moisture, and fluorescent pigments placed on flowers revealed that pollinators primarily moved pollen from male flowers on well‐watered plants to the stigmas of female flowers on well‐watered plants. Seed set increased with increasing plant soil moisture but, notably, was higher in bee‐pollinated plants compared to plants pollinated by hand with an even mix of pollen from plants grown at either end of the experimental moisture gradient. These results suggest that superior pollen rewards, perhaps combined with selective foraging by generalists, enhanced reproductive success in C. pepo when plant soil moisture was high and more generally illustrate that pollinator behavior may contribute to how drought conditions affect plant reproduction.


Argentine ant δ¹⁵N values from Rice Canyon (San Diego Co., CA) in 2003 and 2019. Lines connect δ¹⁵N values of ants collected at the same transect position in each of these two years
Plant and ant δ¹⁵N values from samples collected in 2019 from Rice Canyon (San Diego Co., CA). Note that there is no replication at the level of transect position for plant and ant δ¹⁵N values
Argentine ant δ¹⁵N values from an invasion chronosequence in the Sacramento River Valley (Solano and Yolo Cos., CA)
Argentine ant δ¹⁵N values from transects oriented perpendicular to known contact zones between the Argentine ant and native ants on San Nicolas Island (Ventura Co., CA)
Variation in Argentine ant (Linepithema humile) trophic position as a function of time

September 2022

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61 Reads

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3 Citations

Biological Invasions

The ecological effects of species introductions can change over time, but an understanding of how and why they do remains hindered by the lack of long-term data sets that permit investigation into underlying causes. We employed stable isotope analysis to estimate how trophic position changes as a function of time for the Argentine ant, a widespread, abundant, and ecologically disruptive introduced species. Previous research at a site in southern California (Rice Canyon, San Diego Co.) found that Argentine ant δ15N values were higher at the leading edge of invasion than at those same sites in years subsequent to invasion (i.e., after the invasion front had advanced). To assess if a reduction in relative trophic position over time is a typical feature of Argentine ant invasions, we expanded the temporal and spatial scale of sampling and measured δ15N values of the Argentine ant at three locations with a known or inferred history of invasion: Rice Canyon (the location of the original study), the Sacramento River Valley (Yolo and Solano Cos., CA), and San Nicolas Island (Ventura Co., CA). Resampling Rice Canyon in 2019, 16 years after the original survey, revealed a significant increase in Argentine ant δ15N values. At the two other locations, Argentine ant δ15N values were independent of time since invasion (Sacramento River Valley) or position relative to the invasion front (San Nicolas Island). These findings suggest that post-invasion reductions in trophic position may not be a general phenomenon or could reflect transitory ecological processes that require finer-scale temporal sampling than was possible to achieve in the present study. Our findings are nonetheless consistent with the results of recent studies, which found that the effects of Argentine ant invasions persist over decadal time scales.


The two focal plant species considered in this study: Santa Cruz Island Buckwheat (L; Eriogonum arborescens) and non-native fennel (R; Foeniculum vulgare). a Both individuals in this picture are in bloom. b Santa Cruz Island Buckwheat pollen and fennel pollen grains at 100 μm magnification
Visits per minute made by a all insects and b bees to individual buckwheat plants on control (C, dark-colored boxes) and removal (R, light-colored boxes) plots before (Pre Removal) and after (Post 1, Post 2, Post 3) fennel removal. Boxes indicate central 50% of data; bold horizontal lines represent medians, and white diamonds are means. Whiskers extend from the quartiles to 1.5× the interquartile range (or the most extreme values, whichever is closest to the median). Points are outliers
NMDS ordinations based on the community matrix of insect visitation on native Santa Cruz Island Buckwheat (Eriogonum arborescens) and non-native fennel (Foeniculum vulgare). a Pollinator composition based on presence or absence of pollinators. Ordination stress equals 0.09. b Pollinator composition based on the visitation rates of pollinators. Ordination stress equals 0.09. Points are labelled by plot and plant (B = buckwheat, F = fennel)
Interspecific pollen transport between non-native fennel and an island endemic buckwheat: assessment of the magnet effect

January 2022

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117 Reads

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6 Citations

Biological Invasions

Non-native plant species can disrupt plant–pollinator interactions by altering pollinator foraging behavior, which can in turn affect levels of interspecific pollen transfer between native and non-native plant species. These processes may be amplified in cases where introduced plant species act as magnet taxa that enhance pollinator visitation to other plant species. We investigated these interactions on Santa Cruz Island (Santa Barbara Co., California) between non-native fennel (Foeniculum vulgare), a widespread and abundant invader, and the endemic Santa Cruz Island buckwheat (Eriogonum arborescens), which broadly overlaps fennel in its local distribution and blooming phenology. A fennel flower removal experiment revealed that this invader acts as a magnet species by increasing insect visitation to adjacent buckwheat flowers. Analysis of the amount of pollen carried on the bodies of insect pollinators (i.e., pollen transport) revealed that 96% of visitors to buckwheat flowers carried fennel pollen and 72% of visitors to fennel flowers carried buckwheat pollen. Pollen transport analyses and visitation rate data further suggest that members of three bee genera (primarily Augochlorella) may be responsible for the majority of fennel pollen deposited on the stigmas of buckwheat flowers (i.e., pollen transfer) and vice versa. Lastly, fennel pollen transport appeared to occur at a larger spatial scale than the magnet effect that fennel plants exert on floral visitors to neighboring buckwheat plants. The ability of fennel to act as a magnet species, coupled with the fact that it is widespread invader with known allelopathic capacities, suggests that future studies could evaluate if the transfer of fennel pollen adversely affects native plant reproduction in areas where fennel is introduced.


Figure 2
Figure 4
Changes In Argentine Ant Trophic Position As A Function of Time

September 2021

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72 Reads

The ecological effects of species introductions can change over time, but an understanding of how and why they do remains hindered by the lack of long-term data sets that permit investigation into underlying causes. We employed stable isotope analysis to estimate how trophic position changes as a function of time for the Argentine Ant, a widespread, abundant, and ecologically disruptive introduced species. Previous research at a site in southern California (Rice Canyon, San Diego Co.) found that Argentine Ant δ15N values were higher at the leading edge of invasion than at those same sites in years subsequent to invasion. To assess if a reduction in relative trophic position over time is a typical feature of ant invasions, we expanded the temporal and spatial scale of sampling and measured δ15N values of the Argentine ant at three locations with a known or inferred history of invasion: Rice Canyon (the site of the original study), the Sacramento River Valley (Yolo and Solano Cos., CA), and San Nicolas Island (Ventura Co., CA). Resampling Rice Canyon in 2019, 16 years after the original survey, revealed a significant increase in Argentine ant δ15N values. At the two other locations, Argentine ant δ15N values were independent of time since invasion (Sacramento River Valley) or position relative to the invasion front (San Nicolas Island). These findings suggest that post-invasion reductions in trophic position may not be a general phenomenon or could reflect transitory ecological processes that require finer-scale temporal sampling than was possible to achieve in the present study. Our findings are nonetheless consistent with the results of recent studies, which found that the effects of Argentine ant invasions persist over decadal time scales.


Figure 1. Map of the study region showing the location of 1-ha study plots in large scrub reserves (squares) and scrub fragments (circles). Within each symbol, filling of distinct sectors indicates the year(s) in which the plot was sampled.
Figure 5. Nonmetric multidimensional scaling (NMDS) ordination plot of bee assemblages in reserve plots (squares) and fragment plots (circles) across four years of sampling. Points depicting sequential years of sampling at the same study plot are connected by dotted lines that terminate in an arrow at the point that depicts the last year of sampling for the plot. The ordination was constructed based on Bray-Curtis dissimilarity scores between all possible pairs of plot-year combinations. Dissimilarity scores were calculated based on relative abundances of bee species after standardizing the total abundance of each assemblage to a sum of 1. Statistical significance and R 2 value are indicated for each PERMANOVA independent variable: Y = study year, F = fragmentation status (reserves versus fragments); *** p ≤ 0.001. There was no statistically significant interaction between study year and fragmentation status.
Joint Impacts of Drought and Habitat Fragmentation on Native Bee Assemblages in a California Biodiversity Hotspot

February 2021

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192 Reads

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19 Citations

Insects

Global climate change is causing more frequent and severe droughts, which could have serious repercussions for the maintenance of biodiversity. Here, we compare native bee assemblages collected via bowl traps before and after a severe drought event in 2014 in San Diego, California, and examine the relative magnitude of impacts from drought in fragmented habitat patches versus unfragmented natural reserves. Bee richness and diversity were higher in assemblages surveyed before the drought compared to those surveyed after the drought. However, bees belonging to the Lasioglossum subgenus Dialictus increased in abundance after the drought, driving increased representation by small-bodied, primitively eusocial, and generalist bees in post-drought assemblages. Conversely, among non-Dialictus bees, post-drought years were associated with decreased abundance and reduced representation by eusocial species. Drought effects were consistently greater in reserves, which supported more bee species, than in fragments, suggesting that fragmentation either had redundant impacts with drought, or ameliorated effects of drought by enhancing bees’ access to floral resources in irrigated urban environments. Shifts in assemblage composition associated with drought were three times greater compared to those associated with habitat fragmentation, highlighting the importance of understanding the impacts of large-scale climatic events relative to those associated with land use change.


The importance of scavenging in ant invasions

February 2021

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80 Reads

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13 Citations

Current Opinion in Insect Science

Recent work underscores that ants are highly proficient and ubiquitous scavengers. These tendencies extend to numerically and behaviorally dominant introduced ants, which exhibit a suite of traits that allow them to exploit and monopolize carrion to a greater extent than is widely appreciated. We thus contend that an understanding of how introduced ants fit into food webs remains incomplete. Monopolization of carrion resources by introduced ants could increase worker production, enhance the ability of these species to compete with and prey upon other organisms, and alter the strength of direct and indirect interactions within food webs. Future work should consider how ant invasions influence energy transfer within and between green and brown food webs.


Citations (63)


... Reduced seed set in water-stressed plants may also result from the combined effects of plant physiological changes and indirect changes in pollinator behavior, which can vary with pollinator species, e.g., generalist vs. specialist pollinators [20,23]. To understand the direct and indirect effects of water stress on plant-pollinator interactions, it is crucial to study the pollinator species, pollinator behavior, and the plant's reproductive parameters. ...

Reference:

Water Deprivation and Sowing Times Alter Plant–Pollination Interactions and Seed Yield in Sunflower, Helianthus annuus L. (Asteraceae)
Divergent responses of generalist and specialist pollinators to experimental drought: Outcomes for plant reproduction

... Ants are ecologically important social insects, participating in a wide range of species interactions, for example, as predators, parasites, herbivores, granivores, prey, mutualists and hosts, across almost all terrestrial environments and all continents except Antarctica (Hölldobler & Wilson, 1990;Lach et al., 2010;Parker & Kronauer, 2021;Stadler & Dixon, 2005). Invasive ants possess adaptations such as supercoloniality and dietary generalism to establish themselves outside of their natural ranges and subsequently ecologically dominate native communities (Baratelli et al., 2023;Holway et al., 2002;Wong et al., 2023). Studies investigating native species responses to ant invasion tend to show negative consequences, but many studies cannot isolate non-native ants as the causal factor of these changes due to environmental differences between uninvaded and invaded sites or other confounding variables (Hill et al., 2003;King & Tschinkel, 2008;King & Tschinkel, 2013;Narendra et al., 2011;Sakamoto et al., 2019;Stuble et al., 2013;Vonshak et al., 2010). ...

Variation in Argentine ant (Linepithema humile) trophic position as a function of time

Biological Invasions

... Given the low but consistent sampling completeness at the sites, the increase in links per species can be explained by the increase in overall visits by Coleoptera taxa to invaded plots, as the richness of Coleoptera remained unchanged across treatments. Increased links per species in plant-pollinator networks have previously been recorded in response to plant invasions [29] and habitat disturbance [42]. Unexpectedly, insect visits per floral unit to Acacia were significantly fewer than to focal fynbos species, indicating that, generally, insects prefer to visit fynbos flowers over Acacia. ...

Interspecific pollen transport between non-native fennel and an island endemic buckwheat: assessment of the magnet effect

Biological Invasions

... Both experiments used dead amphipods and flies. Talitrid amphipods and adult flies can easily evade capture by ants while alive, and these resources are thus presumably obtained by scavenging rather than predation (Holway and Cameron 2021). Ants may prey on fly larvae and pupae as well as other wrack arthropods with limited mobility. ...

The importance of scavenging in ant invasions
  • Citing Article
  • February 2021

Current Opinion in Insect Science

... First, in densely wooded areas, roads open up the canopy, providing an opportunity for understory flowering plants to grow in the light (Eckerter et al., 2023;Hanula et al., 2016), similar to the effects seen with powerline corridors (Garfinkel et al., 2022;Russell et al., 2005;Wagner et al., 2014). Second, in drier environments precipitation run-off from roads creates abundant floral resource patches that do not exist elsewhere in the landscape (Dean et al., 2019); the relative importance of this affect is magnified in drought years (Hung et al., 2021). However, other studies have suggested roadside habitats could be an ecological trap leading to high levels of insect mortality (Keilsohn et al., 2018;Phillips et al., 2020;Skórka et al., 2013). ...

Joint Impacts of Drought and Habitat Fragmentation on Native Bee Assemblages in a California Biodiversity Hotspot

Insects

... humile), known for relying extensively on collective information encoded in pheromone signals rather than private information acquired through visual memory, as demonstrated by Thienen et al. (2016). While visual memory can contribute to reducing uncertainty when combined with a pheromone trail, its standalone efficacy for Argentine ants is limited Clifton et al. (2020). Previous research on Argentine ants by Aron et al. (1989) indicates that paths are marked and favored even in the absence of specific recruiting incentives. ...

Vision does not impact walking performance in Argentine ants
  • Citing Article
  • October 2020

Journal of Experimental Biology

... This is only a speculation at this stage, and future studies should measure the metabolic rate of flour beetles moving on different substrates to support or refute our suggestion. Other studies have found movement on uneven terrain to be slower, more challenging, and more energetically costly as well in various animals, such as cockroaches, ants, beetles, sea urchins, and humans (Lejeune et al., 1998;Sponberg & Full, 2008;Cho et al., 2014;Clifton et al., 2020;Knight, 2024). The common explanation for the higher energetic cost is that, owing to less stable movement on uneven terrain or rough substrates, dynamic corrections are needed while moving. ...

Uneven substrates constrain walking speed in ants through modulation of stride frequency more than stride length

... Finally, dependence on abiotic factors suggests that global climate change will affect the current distribution patterns of L. humile, retracting in tropical areas but expanding in higher latitudes (Roura-Pascual et al. 2004;Cooling et al. 2012;Bertelsmeier et al. 2016). However, some populations have persisted for a long time (Castro-Cobo et al. 2021), while others that have declined could recover with climate change (Cooling et al. 2012): in any case, the distribution of invaded areas will change according mainly to local-scale environmental conditions (Menke & Holway 2020). ...

Historical resurvey indicates no decline in Argentine ant site occupancy in coastal southern California

Biological Invasions

... These species, whether intentionally or accidentally introduced, can disrupt the ecological dynamics of endemic flora and fauna (Causton et al. 2006). In the case of introduced ant species, the displacement of local fauna is a welldocumented consequence (Lach and Hooper-Bùi 2010;Naughton et al. 2020), but indirect impacts have also been observed (Allen et al. 2004). For instance, the introduction of the fire ant Solenopsis invicta in Texas resulted in the displacement of harvester ants (genus Pogonomyrmex), the main prey of the Texas horned lizard (Phrynosoma cornutum), and potentially contributed to its geographic range reduction (Allen et al. 2004). ...

Direct evidence of native ant displacement by the Argentine ant in island ecosystems

Biological Invasions