The experiment was performed at the Grassland Ecological Research Station of Northeast Normal University, Jilin Province, China (44°40′-44°44′N, 123°44′-123°47′E). The research station has a semi-arid, continental climate with mean annual temperature ranged from 4.6 to 6.4°C (1950–2004). Mean annual precipitation ranged from 280 to 644 mm (1950–2014) with over 70% of the precipitation occurs from June to August. Potential evapotranspiration is approximately three times that of the annual precipitation. Vegetation is dominated by L. chinensis, a C3 perennial rhizomatous grass; Phragmites australis, C. virgata and H. altissima are also abundant. Soil is classified as a chernozem soil, with 2.0% soil organic carbon content and 0.15% soil total nitrogen content (Wang et al., 2015 (link)).
One C3 perennial grass (L. chinensis) and two C4 grasses (annual: C. virgata; perennial: H. altissima) that co-occur in the meadow steppe of the study area were selected as experimental plants. L. chinensis is a widespread dominant grass of arid and semi-arid steppe in northern China, eastern Mongolia and Transbaikalia, Russia (Wang and Ba, 2008 (link)) and has an ability to resist drought, cold and alkaline conditions (Shi and Wang, 2005 (link)). C. virgata is widely distributed on the Northeast China Plain and is ecologically and economically important because of its high protein content and seed production. In addition, it also grows rapidly and is highly tolerant of alkaline conditions (Yang et al., 2008 (link); Lin et al., 2016 (link)). H. altissima is a perennial rhizomatous grass and is distributed in tropical, subtropical and temperate regions, especially in China and Southeast Asia. It has strong adaptability and stress resistance and can be used as a good soil and water conservation crop (Han et al., 2016 (link)).
On DOY 135 in 2013, seedlings of L. chinensis and H. altissima were transplanted to plastic pots (23.5 cm in diameter and 20 cm in height) filled with chernozem soil (8 kg soil pot−1). For C. virgata, plants were germinated from seeds and transplanted to plastic pots. All species were planted as monocultures (five individuals per pot). Before the initiation of the drought treatment, all the transplanted plants were manually watered (to field capacity) every 3 days. To ensure that plant growth was not limited by nutrient elements, each pot received 2 mg of nitrogen fertilizer in the form of NH4NO3 every week. All the pots were watered thoroughly on the date (DOY 165) prior to the initiation of the drought treatment. During the drought experiment period (DOY 166–172), we stopped watering the plants. Moreover, all the pots were placed under a plastic shed to exclude natural precipitation. Variations in the soil water content for the studied grasses are provided in the supplementary information (FigureS1 ). The measurements of leaf gas exchange and collection of both leaf dark-respired CO2 and fresh materials were conducted on DOY 166 (day 1 of the experiment), DOY 168 (day 3 of the experiment), DOY 170 (day 5 of the experiment) and DOY 172 (day 7 of the experiment). Before the initiation of the drought treatment, the studied grasses were in the stem elongation stage with average heights of 51.6, 62.9 and 42.4 cm for C. virgata, H. altissima and L. chinensis, respectively. The tiller densities of the studied grasses were 36 pot−1, 19 pot−1 and 17 pot−1 for C. virgata, H. altissima and L. chinensis, respectively. Each pot had total leaf areas of 1,045 cm2 pot−1, 618 cm2 pot−1 and 648 cm2 pot−1 for C. virgata, H. altissima and L. chinensis, respectively.
One C3 perennial grass (L. chinensis) and two C4 grasses (annual: C. virgata; perennial: H. altissima) that co-occur in the meadow steppe of the study area were selected as experimental plants. L. chinensis is a widespread dominant grass of arid and semi-arid steppe in northern China, eastern Mongolia and Transbaikalia, Russia (Wang and Ba, 2008 (link)) and has an ability to resist drought, cold and alkaline conditions (Shi and Wang, 2005 (link)). C. virgata is widely distributed on the Northeast China Plain and is ecologically and economically important because of its high protein content and seed production. In addition, it also grows rapidly and is highly tolerant of alkaline conditions (Yang et al., 2008 (link); Lin et al., 2016 (link)). H. altissima is a perennial rhizomatous grass and is distributed in tropical, subtropical and temperate regions, especially in China and Southeast Asia. It has strong adaptability and stress resistance and can be used as a good soil and water conservation crop (Han et al., 2016 (link)).
On DOY 135 in 2013, seedlings of L. chinensis and H. altissima were transplanted to plastic pots (23.5 cm in diameter and 20 cm in height) filled with chernozem soil (8 kg soil pot−1). For C. virgata, plants were germinated from seeds and transplanted to plastic pots. All species were planted as monocultures (five individuals per pot). Before the initiation of the drought treatment, all the transplanted plants were manually watered (to field capacity) every 3 days. To ensure that plant growth was not limited by nutrient elements, each pot received 2 mg of nitrogen fertilizer in the form of NH4NO3 every week. All the pots were watered thoroughly on the date (DOY 165) prior to the initiation of the drought treatment. During the drought experiment period (DOY 166–172), we stopped watering the plants. Moreover, all the pots were placed under a plastic shed to exclude natural precipitation. Variations in the soil water content for the studied grasses are provided in the supplementary information (Figure
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