J Plant Ecol ›› 2017, Vol. 10 ›› Issue (3): 426-439 .DOI: 10.1093/jpe/rtw056

• Research Articles • Previous Articles     Next Articles

Multiple ecological strategies explain the distribution of exotic and native C4 grasses in heterogeneous early successional sites in Hawai'i

Rafael de Oliveira Xavier1,* and Carla M. D'Antonio2   

  1. 1 Ecology and Conservation Lab, Department of Hydrobiology, Federal University of São Carlos, Washington Luís Highway, km 235, São Carlos, São Paulo 13565-905, Brazil; 2 Environmental Studies Program, 4312-L Bren University of California, Santa Barbara, CA 93106, USA
  • Received:2015-10-29 Accepted:2016-05-30 Published:2017-05-23
  • Contact: Xavier, Rafael

Multiple ecological strategies explain the distribution of exotic and native C4 grasses in heterogeneous early successional sites in Hawai'i

Abstract: Aims Biotic homogenization results in novel communities containing multiple exotic species. Many attributes that contribute to the dominance of invaders and increase invasibility of communities have been identified, but rarely have factors governing the dominance of co-occurring invaders been considered. Here we assess the presence and performance of five exotic and one native C4 grass species across local (microsite) and more broad-scale variation in fire history, soil age, altitude and precipitation. We ask whether species show preferences for the same conditions, whether all are constrained by poor soil development, and how their performance changes when alone versus co-occurring. In addition to providing information useful to managers who want to control some of these species, such information can help to predict how distributions might change with climate change
Methods We measured percent cover and plant height of each grass species in 64 plots in each of 15 sites, located in young volcanic substrates across environmental gradients in Hawai'i Volcanoes National Park, Hawai'i, USA. Sites varied in fire history and soil age, across altitudinal and precipitation gradients. We estimated microsite heterogeneity by measuring rock cover and soil depth, where each species was present and in plots as a whole. We analyzed effects of possible controlling variables using chi-square tests and Generalized Additive Mixed Models.
Important findings Two species (Schizachyrium condensatum and Hyparrhenia rufa) were absent in shallow soil, restricted to more mesic sites and showed increasing performance with soil depth. By contrast, two other species (Andropogon virginicus and Melinis repens) tended to occur in shallow soil with high rock cover across a wide range of sites. One additional species (Melinis minutiflora) was weakly affected by soil depth and was the dominant at higher elevation (more mesic) and on burned sites, especially in old soil. This species was largely absent from lower elevation sites, where the more widespread and opportunistic congener, M. repens, and a drought tolerant native grass, Heteropogon contortus, were more abundant. The latter was confined to this low hot zone. Introduced C4 grasses in this region of Hawai'i are distributed according to an interaction between soil requirements, climate (correlated with elevation), competitive ability and fire response. No one strategy can explain the distributions, which will likely persist unless climate changes toward warmer and drier conditions or new fires occur. The latter would promote dominance of M. minutiflora in more mesic sites, while the former would promote either native (H. contortus) or other exotic grasses (M. repens, A. virginicus).

Key words: elevation gradient, fire, invasive species, Melinis minutiflora, soil depth

摘要:
Aims Biotic homogenization results in novel communities containing multiple exotic species. Many attributes that contribute to the dominance of invaders and increase invasibility of communities have been identified, but rarely have factors governing the dominance of co-occurring invaders been considered. Here we assess the presence and performance of five exotic and one native C4 grass species across local (microsite) and more broad-scale variation in fire history, soil age, altitude and precipitation. We ask whether species show preferences for the same conditions, whether all are constrained by poor soil development, and how their performance changes when alone versus co-occurring. In addition to providing information useful to managers who want to control some of these species, such information can help to predict how distributions might change with climate change
Methods We measured percent cover and plant height of each grass species in 64 plots in each of 15 sites, located in young volcanic substrates across environmental gradients in Hawai'i Volcanoes National Park, Hawai'i, USA. Sites varied in fire history and soil age, across altitudinal and precipitation gradients. We estimated microsite heterogeneity by measuring rock cover and soil depth, where each species was present and in plots as a whole. We analyzed effects of possible controlling variables using chi-square tests and Generalized Additive Mixed Models.
Important findings Two species (Schizachyrium condensatum and Hyparrhenia rufa) were absent in shallow soil, restricted to more mesic sites and showed increasing performance with soil depth. By contrast, two other species (Andropogon virginicus and Melinis repens) tended to occur in shallow soil with high rock cover across a wide range of sites. One additional species (Melinis minutiflora) was weakly affected by soil depth and was the dominant at higher elevation (more mesic) and on burned sites, especially in old soil. This species was largely absent from lower elevation sites, where the more widespread and opportunistic congener, M. repens, and a drought tolerant native grass, Heteropogon contortus, were more abundant. The latter was confined to this low hot zone. Introduced C4 grasses in this region of Hawai'i are distributed according to an interaction between soil requirements, climate (correlated with elevation), competitive ability and fire response. No one strategy can explain the distributions, which will likely persist unless climate changes toward warmer and drier conditions or new fires occur. The latter would promote dominance of M. minutiflora in more mesic sites, while the former would promote either native (H. contortus) or other exotic grasses (M. repens, A. virginicus).