Research Article |
Corresponding author: Aaron C. Rhodes ( aaronrhodes@utexas.edu ) Academic editor: Matt Hill
© 2022 Aaron C. Rhodes, Robert M. Plowes, Dino J. Martins, Ivy Ng’Iru, Lawrence E. Gilbert.
This is an open access article distributed under the terms of the Creative Commons Attribution License (CC BY 4.0), which permits unrestricted use, distribution, and reproduction in any medium, provided the original author and source are credited.
Citation:
Rhodes AC, Plowes RM, Martins DJ, Ng’Iru I, Gilbert LE (2022) The invasiveness of Guinea grass (Megathyrsus maximus) is characterized by habitat and differing herbivore assemblages in its native and invaded range. NeoBiota 78: 25-44. https://doi.org/10.3897/neobiota.78.87069
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A significant challenge of global change is the human-mediated movement of pasture grasses and their subsequent impact on ecosystem processes when they become invasive. We must understand invasive grass ecology and their natural enemies in native and introduced ranges to mitigate these impacts. Guinea grass (Megathyrsus maximus) is a pantropically introduced pasture grass that escapes intended areas and invades native ecosystems – threatening biodiversity and ecosystem function. The success of invasive plants has often been attributed to ecological release from stressors, including natural enemies and resource availability. Our objective was to assess Guinea grass functional traits across three different habitat types in native and invaded ranges by documenting ungulate and arthropod abundance, diversity, and feeding guilds. Guinea grass functional traits were assessed in three habitat types: grassland, riparian, and woody thickets around nitrogen-fixing Prosopis glandulosa in its introduced range in Texas, USA, and Senegalia mellifera in its native range in Kenya. We characterized Guinea grass functional traits by measuring plant height, cover, biomass, root-to-shoot ratios, and reproductive traits. We then examined the phytophagous arthropod and ungulate abundance and feeding guild diversity across the three habitat types. We hypothesized that functional trait expression related to invasiveness would be associated with Guinea grass in its introduced range. Also, we hypothesized that the abundance and diversity of phytophagous arthropods and ungulates would be lower in the invaded range. Finally, we hypothesized that Guinea grass functional traits would differ between the three habitat types, given the habitat types’ innate differences in resource availability. We found that Guinea grass was 2.5 times taller and 3.3 times more productive and covered 2.5 times more area in its invaded versus native ranges. Introduced Guinea grass had higher reproduction rates with 2.5 times more reproductive tillers, while habitat type drove vegetative reproduction with 15 times more stoloniferous establishment in wooded and riparian sites than grasslands. Texan ungulate communities were less species-rich, less functionally diverse, and less abundant than the Kenyan ungulate community. The phytophagous arthropod diversity on plants was twice as high on Kenyan Guinea grass than on Texan Guinea grass. Total arthropod family richness was nearly double, with 15 families represented in Kenya and 8 in Texas. These results suggest that Guinea grass has escaped a rich assemblage of arthropods and ungulates and likely explains some of its spread in introduced ranges. This study demonstrates how the invasive success of Guinea grass can be understood in terms of its competitive ability and interaction with natural enemies in the introduced and native ranges and may inform future biological control.
arthropod diversity, biological control, ecological stressor release, function, invasion, natural enemy, ungulate
Introducing perennial grasses for rangeland improvement has led to the pantropical distribution of highly invasive grasses (
Life histories and functional traits are important indicators of plant success and often correlate with their invasiveness and dominance in a community (
Guinea grass (Megathyrsus maximus syn. Panicum maximum (Jacq.) B.K. Simon & S.W.L. Jacobs) is consistently ranked among the most ecologically damaging invasive plant species globally (
This dichotomy of Guinea grass is its economic success and ecological damage, which can be attributed to several core traits; its ability to grow in variable precipitation (400 mm – 1700 mm), high tolerance to herbivory (
Invasive plants alter the structure and function of arthropod communities (
Ungulates may be used to manage invasive plants, improving ecological restoration and maintenance outcomes with the added benefit of contributing to livestock yields (
The primary objective of this project was to evaluate Guinea grass functional traits across three habitat types in the native and invaded ranges and document the arthropod and ungulate herbivore community assemblages. To achieve this objective, we; first quantified Guinea grass functional traits and reproductive output across three habitat types. Second, we measured the richness and diversity of phytophagous arthropods and ungulate herbivores on Guinea grass in native ranges versus the invaded range. Third, we characterized these communities by their relative abundance and feeding guild diversity. Fourth, we developed a list of the arthropod community attached to Guinea grass to understand their impact. We hypothesized that functional trait expression related to invasiveness would be associated with Guinea grass in its introduced range. We hypothesized that functional traits would differ between the three habitat types, given the habitat types’ innate differences in resource availability. Finally, we hypothesized that the abundance and diversity of phytophagous arthropods and ungulates would be lower in the invaded range, consistent with the Enemy Release Hypothesiss.
We established field sites to examine Guinea grass occurring naturally in two savanna systems; 1) the native range in Laikipia Province, Kenya, and 2) the invaded range in South Texas, where Guinea grass is spreading rapidly. Ten locations were selected in both Kenya and Texas. Each location had three habitat types: woody mottes (thickets), open grassland, and riparian zones. Three 1 × 1 m subplots were randomly established within each habitat type for 180 subplots. Mottes were under woody legumes with higher soil moisture and soil nitrogen. We selected two major tree species, each native to the study area; Senegalia mellifera (Benth.) Seigler & Ebinger, common in the red soils of Laikipia, and P. glandulosa in Texas a common species. The grassland sites for each grouping were approximately halfway between the thicket (motte) and riparian habitat types. Riparian areas were defined as the upland portion of ephemeral creeks that fed into the main waterway (Los Olmos Creek in Texas and Ewaso Ng’iro River in Kenya).
In Kenya, field sites were selected along the Ewaso Ng’iro River. West of the river is Mpala Research Centre, an active cattle ranch with approximately 3000 livestock grazing at low to moderate stocking intensities on 19,500 hectares, including Zebu/Boran mix-breed of cattle, camel, goat, and sheep. Mottes were maintained naturally by large ungulate and fire disturbances. In Texas, the study was conducted at two ranches with active brush and cattle management activities in the semi-arid mesquite thorn tree savanna of the South Texas Plains ecoregion. A 1600-ha ranch pasture in Kenedy, Kleberg & Brooks Counties on Palobia loamy fine sand was brush-chained in the 1970s and then partly root-plowed in 1998 to form residual stands of P. glandulosa in a grassland matrix and a 1000-ha ranch pasture in Brooks County, on Padrones fine sand. Cattle regularly graze both sites and feed on Guinea grass. Stocking densities were generally low to moderate using resident longhorn cattle (Bos primigenius) and common stocker cattle (Bos taurus).
Within each 1 × 1 m subplot, we measured Guinea grass height to the highest leaf and visually estimated the percent foliar cover at each site to understand how functional traits vary across habitat types and invaded vs. native range. We used the height as a functional indicator that provides a relative indicator of the competitive potential of Guinea grass in its native and invaded range across habitat types. We uprooted one Guinea grass clump from each subplot by tossing the quadrat and selecting the central individual to estimate productivity and resource allocation to above and belowground tissues (three in total from each site). The plants were cut to separate aboveground tissues (leaves, culms, and inflorescences) from the belowground tissues (roots and rhizomes). Belowground tissue was soaked in water overnight and then washed over a 1 mm sieve to remove soil and soil organic matter. The aboveground tissue was dried in a drying oven for 72 hours at 50 °C. Root clumps were broken up over a sieve to remove the remaining soil. The above and belowground tissue was summed to calculate total biomass, and then root tissue biomass (mg) was divided by shoot biomass (mg) to calculate root to shoot ratio. Finally, in each of the three 1 m2 plots, the total numbers of seed heads and stolons were recorded. The mean of the three plots was then used in the analyses. Seedheads were defined as panicles with mature seeds, noted by the ease of dislodging seeds. Stolons were characterized by lateral shoots that had established a rooted node with at least five leaves and a height of 20 cm. These definitions ensured that the stolon had been successfully established.
Six camera trap locations along the south, central, and northern portions of Mpala Research Centre and ten camera trap locations were used at the Texas ranch. The camera survey was conducted from January 2019 to June 2019 until the Guinea grass sampling was completed. At each study site, we placed a trail camera (HyperFire 2 Professional Covert Camera Trap) (Reconyx, Holmen, WI, USA) to estimate relative use by ungulate species (
Three Guinea grass plants from each site were uprooted and transported back to the lab. Three culms and the associated roots from each grass clump were examined for arthropods under a microscope, the stem was dissected, and the leaf, inflorescence, culm, and roots. We assumed that arthropods still attached to the plant after this process were more likely to be associated with this plant rather than transient. Arthropod abundance was estimated by recording the number of arthropods per gram of wet plant tissue measured for each morphospecies recognized by morphological differences. Specimens were collected, cataloged, and stored in ethanol in a 2 ml microtube. Each morphospecies was barcoded at the CO1 locus. A region of approximately 450 bp targeting the CO1 locus was amplified with degenerate primers (ZBJ-ArtF1c, ZBJ-ArtR2c (
The height of the tallest culm, total biomass, foliar cover (%), root-to-shoot ratio, stolon count, and reproductive tiller counts were analyzed using mixed-effects regressions. Arthropod morphospecies counts were also analyzed using a mixed-effects regression. For all regressions, the fixed effects were the habitat type and invasion status and their interaction. The heterogeneity of variance was assessed by visually assessing the distribution of model residuals. Invasion status (native vs. invaded) was used as an identity variance structure to deal with variance heterogeneity and site as a random effect to account for spatial autocorrelation. Normality was assessed by visually inspecting a histogram of model residuals and was analyzed as normally distributed data. Feeding guilds for ungulates and arthropods are reported as the raw averages with their standard error. Ungulate camera data is presented as descriptive, given that no direct correlation could be made between ungulate abundance and specific use of Guinea grass. All regression analyses were done in R (
Guinea grass in its invaded range had productivity and functional traits consistent with a successful invader. Guinea grass in its invaded range was taller, had 3.3 times higher biomass per plant, covered 2.5 times more area, and had twice as much shoot production over root production (Fig.
Guinea grass’s morphological and physiological traits across three habitat types in native and invaded ranges. The morphological and physiological traits of Guinea grass are presented in four panels A height (cm) B Biomass dry weight (g) C percent foliar cover, and D root-to-shoot ratio. The bar’s colors represent the ephemeral riparian, grassland, and motte portions of the matrix. Habitat type is nested within invaded (Texas) or native range (Kenya). The bar heights are calculated from the model predictions, and the error bars are the standard error.
Seedborne reproduction by Guinea grass, measured by seedhead count, was nearly three times as abundant in the invaded range (F(1,10) = 14, p = 0.004). Still, it did not vary significantly across habitat types or the interaction between native and invaded provenance and by habitat type (F1,42) = 1.3 and F2,42) = 0.6, respectively) (Fig.
Guinea grass’s reproductive output and mode across three habitat types in native and invaded ranges. The reproductive outputs by seedhead and stolon counts of Guinea grass are presented in two panels A seedhead count and B stolon count. The bar’s colors represent the ephemeral riparian, grassland, and motte (woody portion) for each vegetation type, which is nested within invaded (Texas) or native range (Kenya). The bar heights are calculated from the model predictions, and the error bars are the standard error.
In Texas, we observed five ungulate species: Bos taurus Linnaeus, 1758, Odocoileus virginianus Zimmermann, 1780, Pecari tajacu Linnaeus, 1758, Sus scrofa Linnaeus, 1758, Boselaphus tragocamelus Pallas, 1766. According to their behavior and physiology, these species were classified into their respective feeding guilds, one grazer, three mixed feeders, and one browser (
Guinea grass from Texas had less than half the phytophagous morphospecies of arthropods, with an average of 1.01 morphospecies per sample. In contrast, Guinea grass samples from Kenya had 2.14 (F(1,10) = 12 p = 0.006). However, there was no significant association between habitat types or interaction between habitat type and invasion status (F(1,42) = 0.19, F(2,42) = 1.46, respectively) (Fig.
Diversity of arthropod morphospecies collected from Guinea grass in Kenya and Texas.
Kenya families | Species count* | Texas families | Species count* |
---|---|---|---|
Agaonidae | 1 | Cecidomyiidae | 1 |
Cecidomyiidae | 3 | Chloropidae | 1 |
Chloropidae | 6 | Cicadellidae | 1 |
Chrysomelidae | 2 | Haplozetidae | 3 |
Crambidae | 1 | Mordellidae | 1 |
Curculionidae | 1 | Nymphalidae | 1 |
Geometridae | 2 | Oppiidae | 1 |
Hydraenidae | 1 | Pyralidae | 1 |
Lygaeidae | 1 | ||
Noctuidae | 2 | ||
Phlaeothripidae | 1 | ||
Phycitinae | 1 | ||
Pyralidae | 3 | ||
Tenebrionidae | 1 | ||
Tortricidae | 1 | ||
Total | 27 | 10 |
Guinea grass-associated arthropod morphospecies in three habitat types in the invaded and native ranges. The bar’s colors represent the ephemeral riparian, grassland, and motte (woody) vegetation types. The habitats are nested within invaded (Texas) or native ranges (Kenya). The bar heights are calculated from the model predictions, and the error bars are the standard error.
The potential feeding guilds from the total morphospecies in native and invaded ranges. Panel A compares potential feeding guilds given a given family’s known feeding guild types. Panel B sums the total morphospecies count. The bar’s colors represent native (dark) or invaded (Texas). The bar heights are the total sum of morphospecies that potentially belong to a particular feeding guild.
In South Texas, Guinea grass has pronounced functional and reproductive traits associated with invasiveness. Our results show that Guinea grass in South Texas was taller, dominated a larger area, produced more biomass (especially aboveground), and reproduced sexually at higher rates than in its native range. These differences likely have cascading impacts on Guinea grass’s competition with native species (
The morphology and productivity of invasive plants are functional traits that can predict invasiveness (
Vegetative reproduction is associated with a higher competitive ability (
In savanna systems, woody vegetation and riparian patches integrate with a grassland matrix creating gradients of light environment, nutrient turnover, and water availability that have vital impacts on grass growth (
Losing natural enemies can increase biomass compared to native populations (
The differences between Kenya and Texas’s arthropod and ungulate communities were stark. Several arthropod species encountered in Kenya are from feeding guilds known to tend toward specialization, including stem borers and mites (
Utilizing natural enemies has formed the basis for classic biological control. The potential for classic biological control has been known for decades (
This study represents an essential step in describing the productivity and reproduction of Guinea grass in three resource environments and its association with natural enemies in its native and invaded ranges. Guinea grass achieved high productivity and reproductivity across the range of habitat types in its invaded range when released from native enemies. However, in its native range, when subjected to natural enemies, the potential of Guinea grass was significantly reduced. In addition, the diversity of specialist and generalist arthropods in Kenya is high compared to the few generalist arthropods in Texas. This information improves our understanding of opportunities to develop impactful and sustainable biological control agents (
Grasses are a critical group of organisms that make up most food crops and are translocated for pasture development, yet are also among the most pervasive invaders (
We thank the skilled and knowledgeable technicians Godfrey Amoni, Kamukunji Katero from the Mpala Research Centre, and the Centre itself for its logistical support of this research. In Texas, Jason Lawson was our lead technician and was instrumental in assisting Texas’s collection and processing of materials. We also thank Kaitlyn Williams and Shellsea Miller for their molecular contributions. The authors have declared that no competing interests exist.
This research was funded by the Lee and Ramona Bass Foundation.