Our results showed that Q. rehderiana leaves and roots in forests with rocky desertification have higher N:P ratio but lower K and P concentrations than in forests with non-rocky desertification, which was consistent with our first hypothesis (Figs. 1 and 2). In addition, we find that Q. rehderiana leaves and roots in forests with rocky desertification have higher Mg and Ca concentrations than in forests with non-rocky desertification, which was consistent with our second hypothesis (Figs. 1 and 2).
Compared with other studies, the results of this study demonstrate that C concentration of Q. rehderiana leaves both in forests with rocky desertification (498.0 mg g−1) and non-rocky desertification (494.8 mg g−1) had higher than those of global terrestrial plant species (464.0 mg g−1) [44], 10 species in the Maolan forests with karst rocky desertification (386.6 mg g−1) [36], 10 dominant species in Guiyang forests with karst rocky desertification (438.96 mg g−1) [29], but similar to the study of Guangxi forests with karst rocky desertification (496.1 mg g−1) and Quercus Sect. Heterobalanus shrubs in the Henduan Mountain region (477.9 mg g−1) [37], indicating that Q. rehderiana have higher C storage capacity both in forests with rocky desertification and non-rocky desertification. Leaf N and P concentrations of Q. rehderiana in forests with rocky desertification (15.01 mg g−1, 0.82 mg g−1) and non-rocky desertification (15.34 mg g−1, 0.97 mg g−1) had lower than those reported by Han et al. (2005) [23] and Ren et al. (2007) [45] for large-scale plant species in China (19.7 mg g−1, 1.5 mg g−1), indicating that the distribution region of Quercus Sect. Heterobalanus was deficiency in nitrogen. Similar result has been reported by Li et al. (2018) in Hengduan Mountain region [39]. Leaf P concentration of Q. rehderiana in forests with non-rocky desertification had higher than those in forest with rocky desertification. This may be due to the high rock exposure rate, severe wind erosion, and heavy rainfall in the study area greatly weakened the retention of N and P in soil, resulting in poor soil N and P [46−48]. Therefore, the concentrations of N and P of Q. rehderiana leaves were relatively low. We find that leaf Ca and Mg concentrations of Q. rehderiana in forests with rocky desertification was significantly higher than those in forests with non-rocky desertification, and the leaf K concentration was significantly lower than those in forest with rocky desertification. The results are consistent with the comparative study of leaf nutrient concentrations between in forests with rocky desertification and non-rocky desertification in Guangxi and Guizhou Provence [49]. Compared with other studies, the results of our study showed that leaf K concentration of Q. rehderiana both in forests with rocky desertification (3.67 mg g−1) and non-rocky desertification (6.15 mg g−1) were significantly lower than those of Maolan forests with karst rocky desertification (11.58 mg g−1) [20] and Guiyang forests with karst rocky desertification (12.25 mg g−1) [50]. This may be that plants selectively absorb and enrich more K to improve their resistance to adapt to the harsh habitat, shallow soil layer, and poor water and nutrient conservation ability in forests karst rocky desertification [50, 51]. K concentration of Q. rehderiana leaves in our study was lower than those in other forests with rocky desertification, which may be due to the degree of rocky desertification in this study was lower than other forests. Ca concentration of Q. rehderiana leaves in forests with rocky desertification (9.29 mg g−1) had higher than the average Ca concentration of terrestrial plant species in China (8.81 mg g−1) [23], opposite in forests with non-rocky desertification (6.61 mg g−1). Mg concentration of Q. rehderiana leaves both in forests with rocky desertification (1.33 mg g−1) and non-rocky desertification (1.05 mg g−1) were significantly lower than Maolan forests with karst rocky desertification (5.29 mg g−1) [28], but significantly higher than that Liu et al. (2024) reported (0.33 mg g−1) [49]. Ca and Mg concentrations of Q. rehderiana leaves in forests with rocky desertification were significantly higher than those in forests with non-rocky desertification. The chemical dissolution of soluble carbonate rocks by ground water and surface water in karst rocky desertification area makes calcium and magnesium enrichment in soil and then accumulation in plants [52].
The roots absorb water, minerals and nutrients and transport them to the leaves, ensuring the normal metabolism of the leaves [53]. In the present study, we find that roots N, Ca and Mg concentrations of Q. rehderiana had significant greater in forests with rocky desertification than those in forests with difference between in forests with non-rocky desertification, P and K concentrations showed opposite. Compared with other studies, C concentration of roots of Q. rehderiana both in forests with rocky desertification (466.7 mg g−1) and non-rocky desertification (469.7 mg g−1) was similar to terrestrial plant roots of China (473.9 mg g−1) [54], but higher than those in Quercus Sect. Heterobalanus shrubs in the Henduan Mountain region (431.4 mg g−1) [39] and Guanling forests with karst rocky desertification in Guizhou Province (445.6 mg g−1) [30], indicating that Q. rehderiana roots have higher C storage capacity. N concentration of Q. rehderiana roots both in forests with rocky desertification (4.56 mg g−1) and non-rocky desertification (3.73 mg g−1) had lower than terrestrial plant roots in China (9.16 mg g−1) [54] and Guanling forest with karst rocky desertification in Guizhou Province (5.98 mg g−1) [30]. P concentration of Q. rehderiana roots in forests with non-rocky desertification (0.97 mg g−1) was similar to terrestrial plant roots in China (0.95 mg g−1) [54] and Guanling forests with karst rocky desertification in Guizhou Provence (0.95 mg g−1) [30], but lower in forests with rocky desertification (0.82 mg g−1). On the one hand, plants growing in forests with rocky desertification had lower ability to acquire N and P from soil than plants growing in forests with non-rocky desertification [33]. On the other hand, the high rock exposure rate, severe wind erosion, and heavy rainfall in the study area greatly weakened the soil retention of N and P elements, resulting in relatively poor soil N and P [46, 55]. K concentration of Q. rehderiana roots both in forests with rocky desertification (1.37 mg g−1) and non-rocky desertification (2.34 mg g−1) had lower than those observed in Guanling forests with karst rocky desertification (2.71 mg g−1) [30], and in Hunan forests with non-rocky desertification (2.57 mg g−1) [56]. Moreover, we find that K concentration of roots in forests with rocky desertification was significantly higher than those of non-rocky desertification. Karst rocky desertification areas are poor-soil and soil erosion serious, therefore plant roots and leaves will selectively absorb and enrich more K element to increase the resistance to the severe environment [51]. Similar to leaves, Ca and Mg concentrations of roots in forests with rocky desertification was significantly higher than those in forests with non-rocky desertification. It may be due to soils are enrichment in Ca and Mg in forests with rocky desertification, which are absorbed by the roots and enriched them in plant roots [52].
The C, N, and P stoichiometry of plants can indicate the C accumulation dynamics, growth rate, and N and P nutrient limitation patterns of the terrestrial ecosystem [57, 58]. To a certain extent, C:N and C:P ratios of mature leaves reflect the growth rate of plants, that is, plants with higher C:N and C:P ratios have higher N and P utilization efficiency but low growth rate [59]. In this study, C:N and C:P ratios of Q. rehderiana leaves in forests with rocky desertification (33.25, 612.6) and non-rocky desertification (32.44, 520.6) were significantly higher than the global terrestrial plant (30.9, 374.7) [44]. The results are consistent with those of the Quercus Sect. Heterobalanus shrubs in Hengduan Mountain area [39] and other Quercus in karst peak-cluster depression in Guizhou Provence [41]. In this study, both C:N and C:P ratios were higher in forests with rocky and non-rocky desertification, indicating higher N and P utilization efficiency, but lower growth rate. This may be one of the important reasons for the wide distribution of Q. rehderiana in rocky desertification and non-rocky desertification environment [41]. The N:P ratio as an indicator of nutrient limitation, which divided into three level: N:P > 16 (P limitation), N:P < 14 (N limitation), 14 < N:P < 16 (limitation of N and P or both not) [3]. In this study, N:P ratio was higher than 16 both in forests with rocky desertification (18.47) and non-rocky desertification (16.04), indicating that the growth of Q. rehderiana was mainly limited by P. Interestingly, studies of Quercus in the Hengduan Mountain area found that the growth of Quercus Sect. Heterobalanus shrubs were mainly limited by N [39], while Quercus semicarpifolia was not limited by N and P [40]. The N:K and K:P ratios are indicators that plant growth was limited by K or N + K, N:K < 2.1 and K:P < 3.4 indicate that plant growth was limited by K or N + K, and the opposite was not limited [8]. We find that N:K and P:K ratios both in forests with rocky desertification (4.33, 4.51) and non-rocky desertification (2.53, 6.48) were higher than 2.1 and 3.4, respectively. Therefore, the growth and development of Q. rehderiana both in forests with rocky desertification and non-rocky desertification was not limited by K, which consistent with reported by Liu et al. (2024) [49].
The C:N and C:P ratios of roots reflects the turnover ability of root, that is, the higher the C:N ratio which have slower turnover rate of root [60, 61]. Our study found that C:N ratio of Q. rehderiana roots in forests with rocky desertification (103.42) and non-rocky desertification (129.66) were significantly higher than the average value of terrestrial vegetation ecosystem in China (59.15) [54], in forest with karst rocky desertification (59.15) [30], and in forests with non-rocky desertification (105.33) [39]. Compared with other species of Quercus, C:N ratio of Q. rehderiana roots in forests with rocky desertification and non-rocky desertification were higher than those of other Quercus species in forests with karst rocky desertification, such as Quercus fabrei (75.67) and Quercus fabrei (77.36) [41]. We also found that C:P ratio of Q. rehderiana roots in forests with rocky desertification (1440.39) and non-rocky desertification (946.38) were significantly higher than the average value of terrestrial vegetation in China (844.07) [54], in forests with karst rocky desertification (962.06) [30], and Quercus Sect. Heterobalanus shrubs in forests with non-rocky desertification (418.15) [39], but similar to Quercus fabrei (1398.99) and Quercus fabrei (1233.43) studied in forests with karst rocky desertification [41]. Therefore, we concluded that the slow decomposition rate of roots of Q. rehderiana may be related to soil microorganisms, Quercus species heterogeneity and karst rocky desertification environment. Based on previous studies, Chen et al. (2011) suggested that the N:P threshold of 12 and 14 is also applicable to plant tissues such as roots, which divided into N:P < 12 (limitation of N), N:P > 14 (limitation of P) and 12 < N:P < 14 (limitation of N and P) [9]. In this study, root N:P ratio in forests with rocky desertification was 13.94, indicating that the root growth of Q. rehderiana was limited by both N and P. However, root N:P ratio in forests with non-rocky desertification was 7.61, indicating that the root growth of Q. rehderiana was limited by N. The results of this study are similar to those of the regional studies, that is, the N:P ratio of the roots in forests with karst non-rocky desertification were limited by N, while leaves were limited by P [36]. The N:P ratio of plants is limited by P probably may be due to the availability of active N is greater than P [21].
The distribution of nutrients in different organs varies greatly due to the function and activity of different organs of the plant, and organs that are metabolically active (leaf photosynthesis and root absorption capacity) tend to allocate more nutrients (such as N, P, K, Ca, etc.) to maintain higher function [62, 63]. The order of C, N, and P concentrations were consistent in different plant components from the forests with rocky desertification and non-rocky desertification, specifically, leaves > roots. Our study results are consistent with the research of 930 species plants in eastern of China [62], the research of 10 dominant tree species in the central of Guizhou karst region [29], the research of 3 species for Quercus in karst peak-cluster depressions in southern of Guizhou [41], the research of 6 species for Quercus Sect. Heterobalanus shrubs in the Hengduan Mountain, China [39], and research of 10 tree species in the Guizhou plateau karst secondary forest [34]. This indicates that nutrient distribution strategies in plant organs are related to the function of plant organs at regional scale, ecosystem scale and for plant individual. The order of Ca, K and Mg concentrations in our study were the consistent in different plant components from the rocky desertification forest and non-rocky desertification forest, specifically, leaves > roots. In order to ensure the growth and development of plants, plants distribute more nutrients to leaves to photosynthesis, while roots, as an absorption and transportation organ and store less nutrients [64].
For the correlation of nutrients, leaf N and P concentrations were significantly positively correlated in forests with non-rocky desertification, which was similar to the results of other studies [23, 36, 39]. This is because plants need to consume a large amount of ATP to synthesize proteins during the growth process, which reflects the synergism of plant absorption of N and P [65]. Leaf P concentration was positively related to leaf Mg concentration in forests with non-rocky desertification, which was consistent with previous studies [28, 49]. The results showed that there is a certain proportion composition and coordination relationships between these elements [28, 66]. Leaf Ca concentration was negatively related to leaf C concentration in forests with rocky desertification, which was consistent with previous studies in forests with karts rocky desertification in Yunnan Provence [67] and in Guizhou Provence [68]. Interestingly, C and Ca concentrations correlations in roots are similar to those in leaves, suggesting that the same synergistic tradeoff relationship between roots and leaves. Under the stress of high Ca environment, the chlorophyll content, stomatal conductance, transpiration rate, and the photosynthetic production of plants were reduced, which was not conducive to C storage [68–70]. We find that root C concentration in forests with rocky desertification was negatively correlated with Mg concentration, which consistent with other study in forests with karst rocky desertification [68]. The Mg concentration in leaves and roots in forests with rocky desertification are generally high, which can inhibit the phosphorylation process of photosynthesis, thereby reducing plant productivity and thus affecting carbon storage in leaves and roots [71].