TY - JOUR
T1 - A water acquisition strategy may regulate the biomass and distribution of winter forage species in cold Asian rangeland
AU - Tanaka-Oda, Ayumi
AU - Endo, Izuki
AU - Ohte, Nobuhito
AU - Eer, Deni
AU - Yamanaka, Norikazu
AU - Hirobe, Muneto
AU - Nachinshonhor, G. U.
AU - Koyama, Asuka
AU - Jambal, Sergelenkhuu
AU - Katsuyama, Masanori
AU - Nakamura, Takashi
AU - Matsuo, Naoko
AU - Jamsran, Undarmaa
AU - Okuro, Toshiya
AU - Yoshikawa, Ken
N1 - Funding Information:
The authors thank Dr. K. Sakamoto of Okayama University, Dr. T. Okayasu, Dr. K. Fukuda, Dr. K. Kojima and Dr. M. Norisada of Tokyo University, Dr. Higuchi of Chiba University, Dr. T. Kenzo and the members of Department of Forest Soils of Forestry and Forest Products Research Institute, and students of Mongolian State University for their kind support of this study. This research was partly funded by the Global Environmental Fund of the Ministry of the Environment of Japan (D-1105 “Biodiversity of dryland ecosystem and sustainability of nomadic production in Northeast Asia”) and the Japan Society for Promotion of Science (JSPS) Research Fellowships for Young Scientists to A. T-O. by KAKENHI Grant (No. JP2410102). This study was partly funded by the Joint Research Program of Arid Land Research Center, Tottori University (No. 28C2029). We thank Lesley Benyon, PhD, from Edanz Group (www.edanzediting.com/ac) for editing a draft of this manuscript.
Publisher Copyright:
© 2018 The Authors.
PY - 2018/12
Y1 - 2018/12
N2 - Aboveground biomass is often restricted by water availability; therefore, water acquisition strategies have important roles in determining biomass volume and distribution under arid conditions. In cold Asian rangelands, the large tussock grass Achnatherum splendens is the most important forage for maintaining livestock under severe winter conditions. However, A. splendens distribution is restricted to the middle of the slopes of ephemeral streams, making it difficult to manage winter foraging. To understand the mechanisms behind the specific distribution and maintenance of a large A. splendens biomass under arid conditions, we established four typical vegetative plots along a riverside slope with different A. splendens density levels and elevations: river bottom with no A. splendens, riverbank with a large A. splendens community, upper slope with an isolated A. splendens community, and flat plain with no A. splendens. We measured the soil pH and electric conductivity (EC) of the plots and investigated the vertical biomass and root distribution of A. splendens. We also investigated the water source for the A. splendens communities using isotope techniques. The soil pH was not different among plots, while the soil EC was significantly higher in the river bottom because of salt accumulation. However, low soil EC levels were found under the A. splendens communities. In the ground below the A. splendens communities, plant stems were buried deeply. The belowground biomass and buried stem depths decreased at the sites of the isolated A. splendens communities in the upper slope. The aboveground biomass of A. splendens increased as the stem burial depths and, therefore, the adventitious roots depths increased. The water source of A. splendens was estimated to be at a depth of more than 30 cm. Thus, A. splendens prefers a habitat with a low level of soil salinity and a high level of water availability, which may increase with the sand burial depth because of the increasing accessibility of a substantial water source in the deeper soil layer. Sand burial may affect the water acquisition strategy and maintenance of large biomasses of tussock grass species that act as important winter forage in cold Asian rangelands.
AB - Aboveground biomass is often restricted by water availability; therefore, water acquisition strategies have important roles in determining biomass volume and distribution under arid conditions. In cold Asian rangelands, the large tussock grass Achnatherum splendens is the most important forage for maintaining livestock under severe winter conditions. However, A. splendens distribution is restricted to the middle of the slopes of ephemeral streams, making it difficult to manage winter foraging. To understand the mechanisms behind the specific distribution and maintenance of a large A. splendens biomass under arid conditions, we established four typical vegetative plots along a riverside slope with different A. splendens density levels and elevations: river bottom with no A. splendens, riverbank with a large A. splendens community, upper slope with an isolated A. splendens community, and flat plain with no A. splendens. We measured the soil pH and electric conductivity (EC) of the plots and investigated the vertical biomass and root distribution of A. splendens. We also investigated the water source for the A. splendens communities using isotope techniques. The soil pH was not different among plots, while the soil EC was significantly higher in the river bottom because of salt accumulation. However, low soil EC levels were found under the A. splendens communities. In the ground below the A. splendens communities, plant stems were buried deeply. The belowground biomass and buried stem depths decreased at the sites of the isolated A. splendens communities in the upper slope. The aboveground biomass of A. splendens increased as the stem burial depths and, therefore, the adventitious roots depths increased. The water source of A. splendens was estimated to be at a depth of more than 30 cm. Thus, A. splendens prefers a habitat with a low level of soil salinity and a high level of water availability, which may increase with the sand burial depth because of the increasing accessibility of a substantial water source in the deeper soil layer. Sand burial may affect the water acquisition strategy and maintenance of large biomasses of tussock grass species that act as important winter forage in cold Asian rangelands.
KW - adventitious root
KW - community development
KW - dryland
KW - key resource
KW - sand burial
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U2 - 10.1002/ecs2.2511
DO - 10.1002/ecs2.2511
M3 - Article
AN - SCOPUS:85059073266
SN - 2150-8925
VL - 9
JO - Ecosphere
JF - Ecosphere
IS - 12
M1 - e02511
ER -