Effects of nitrogen application, warming, and their interaction on S. alopecuroides seed germination
As shown in Fig. 2, for S. alopecuroides seeds, in comparison to the control group, nitrogen application alone resulted in significant decreases in germination rate, germination potential, and germination index of 13%, 16.5%, and 20.6%, respectively (P < 0.05). However, there were no significant differences in germination rate, germination potential, and germination index compared to the control group under either the warming treatment alone or the combined treatment of warming and nitrogen application (P > 0.05). This indicates that nitrogen application negatively affects the germination performance of S. alopecuroides seeds, whereas warming treatment alone or in combination with nitrogen application has no significant effect on germination.
Effects of nitrogen application, warming, and their combination on the growth of S. alopecuroides seedlings
In this study, following the application of the different treatments to S. alopecuroides, several changes in root diameter, stem diameter, plant height, and primary root length were observed Table 1. Compared to the control group, nitrogen application resulted in significant reductions in stem diameter, plant height, and primary root length of 33.3%, 19.4%, and 24%, respectively (P < 0.05). However, root diameter exhibited no significant change (P > 0.05). In contrast, under the interaction of warming and nitrogen application, stem diameter and plant height increased significantly compared to the control group (P < 0.05). Under the combined treatment of warming and nitrogen application, root diameter exhibited a 7.2% and 28.5% increase, stem diameter exhibited a 23.6% and 19% increase, plant height exhibited a 20.3% and 13.2% increase, and primary root length exhibited a 19.5% and 13.8% increase, respectively. A comparison of the different treatment groups revealed that warming could promote to varying degrees increases in stem diameter, plant height, and primary root length of S. alopecuroides seedlings, whereas nitrogen application could inhibit these effects to varying degrees.
Table 1
Effects of nitrogen addition, warming, and their interactions on growth parameters of S. alopecuroides seedlings groups
Group
|
Root diameter/mm
|
Stem diameter/mm
|
Height/cm
|
Root length/cm
|
CK
|
0.358 ± 0.0303b
|
0.537 ± 0.026b
|
19.05 ± 0.533c
|
6.933 ± 0.416b
|
N
|
0.373 ± 0.0191b
|
0.358 ± 0.0251c
|
15.347 ± 0.357d
|
5.263 ± 0.254c
|
W
|
0.384 ± 0.0188ab
|
0.664 ± 0.0204a
|
23.023 ± 0.337a
|
8.287 ± 0.247a
|
WN
|
0.460 ± 0.0238a
|
0.639 ± 0.0154a
|
21.57 ± 0.264b
|
7.89 ± 0.235ab
|
Notes: All data in the table are average values ± standard error (SE). Values of different lowercase letters indicate significant difference at the P < 0.05 level (the same below). |
Effects of nitrogen application, warming, and their combination on biomass accumulation and allocation in S. alopecuroides
Table 2 indicates that the combined treatment of warming and nitrogen application significantly increased the root biomass of seedlings by 257.7% and 351.3%, respectively. Furthermore, the leaf area increased by 17.9% and 11.4%, leaf biomass increased by 70.2% and 56.2%, and stem biomass increased by 114.9% and 92%, respectively (P < 0.05). However, in the independent nitrogen application treatment, there were no significant changes in root biomass and stem biomass compared to the control group (P > 0.05). in contrast, leaves exhibited 87.0% increase in biomass of, but leaf area and leaf number significantly decreased (P < 0.05). These findings indicated that S. alopecuroides seedlings exhibited a positive response in root growth and leaf development under warming and the combined treatment of warming and nitrogen application, indicating both promoting and interaction effects.
Table 2
Biomass accumulation of S. alopecuroides seedlings under nitrogen and warming treatments (mean ± SE).
group
|
Root Biomass / g
|
Stem Biomass / g
|
Leaf Biomass / g
|
Leaf Area / cm2
|
Number of Leaves
|
CK
|
0.0078 ± 0.0005b
|
0.0771 ± 0.0207b
|
0.0185 ± 0.0014b
|
7.63 ± 0.273b
|
1.2993 ± 0.1040b
|
N
|
0.0168 ± 0.0020b
|
0.0491 ± 0.0055b
|
0.0346 ± 0.0046a
|
6.63 ± 0.242c
|
0.9369 ± 0.0566c
|
W
|
0.0279 ± 0.0017a
|
0.1657 ± 0.0076a
|
0.0315 ± 0.0018a
|
9.00 ± 0.267a
|
2.2415 ± 0.1038a
|
WN
|
0.0352 ± 0.0070a
|
0.1481 ± 0.0043a
|
0.0289 ± 0.0015a
|
8.50 ± 0.196a
|
2.0716 ± 0.0860a
|
Figure 3 illustrates that sole nitrogen application treatment showed no significant changes in root biomass ratio and stem biomass ratio of seedlings in compared to the control group (P > 0.05). However, the leaf biomass ratio and root-to-shoot ratio increased significantly (P < 0.05). This indicates that nitrogen application can promote photosynthesis and nutrient absorption in S. alopecuroides seedlings, resulting in improved efficiency of leaf tissue and spatial utilization. Under the warming treatment alone, the root biomass ratio and stem biomass ratio increased significantly (P < 0.05) compared to the control group, whereas, the leaf biomass ratio and root-to-shoot ratio did not show significant changes (P > 0.05). This indicated that the warming treatment could enhance plant root growth and increase plant biomass. Under the combined treatment of warming and nitrogen application, the root biomass ratio and stem biomass ratio increased significantly (P < 0.05); however, the leaf biomass ratio and root-to-shoot ratio did not show significant changes compared to the control group (P > 0.05). These findings indicate that the combined treatment of warming and nitrogen application promotes plant growth and significantly increases biomass accumulation in both roots and above ground stems.
Effects of nitrogen application, warming, and their combination on physicochemical indicators of S. alopecuroides
Figure 4 indicates that nitrogen application significantly reduced the soluble sugar content (P < 0.05) compared to the control group. However, no significant changes were observed in protein, chlorophyll, and MDA contents (P > 0.05). However, the warming treatment resulted in a significant increase in soluble sugar content (P < 0.05), while protein, chlorophyll, and MDA contents did not show significant changes (P > 0.05). The combined treatment of warming and nitrogen application resulted in a significant decrease in the protein and chlorophyll contents of S. alopecuroides seedlings compared to the control group (P < 0.05). However, no significant differences were observed in soluble sugar content or MDA content (P > 0.05). These findings suggest that nitrogen application, warming, and their combined effects have a limited impact on the biochemical indicators of S. alopecuroides seedlings.
The enzyme activities of NR and SOD in S. alopecuroides seedlings exhibited significant differences among the different treatment groups (P < 0.05) (Fig. 5). Under the combined treatment of warming and nitrogen application, the activity of NR was significantly higher than those of the control group and the other treatment groups (P < 0.05). Compared to the control group, both the sole nitrogen application and sole warming treatments demonstrated a significant increase in NR activity (P < 0.05). The combined treatment of warming and nitrogen application exhibited the greatest increase in NR activity, followed by sole nitrogen application and sole warming treatments. Concerning sSOD, all treatment groups exhibited a significant reduction in enzyme activity compared to the control group. The control group exhibited the highest SOD enzyme activity, followed by the sole nitrogen application treatment, and the combined treatments of warming and nitrogen application showed the lowest activity (P < 0.05). The combined treatments of warming and nitrogen application significantly increased NR activity in S. alopecuroides seedlings, while exerting a substantial inhibitory effect on SOD activity. The sole nitrogen application and sole warming application also significantly affected enzyme activity, although to a lesser extent than the combined application of warming and nitrogen.