Prolonged drought duration, not intensity, reduces growth recovery and prevents compensatory growth of oak trees
Graphical abstract
Introduction
Droughts caused widespread tree growth decline and/or mortality across all forest types (Keen et al., 2022; Powers et al., 2020; Choat et al., 2018). The influences of droughts on tree growth can vary with drought intensity, duration, and frequency. Tree radial growth during droughts decreased significantly with increasing drought intensity (Zhang et al., 2021a; Gazol et al., 2017) . Increased drought duration has also been shown to result in cumulative effects amplifying impacts on growth and reducing the drought resistance of multiple tree species (Kannenberg et al., 2019; Gao et al., 2018). In the long term, drought may overstrain trees’ acclimation potential and make them less resistant to future droughts (Bose et al., 2020). Frequent drought conditions led to serious growth declines for Pinus ponderosa (Szejner et al., 2020). As species-specific adaptations to drought determine their growth performance during drought periods, these adaptions can lead to shifts in species composition of forests (Zhang et al., 2022; Werner et al., 2021; Senf et al., 2020; Zhang et al., 2019a). Given that the frequency and severity of droughts will continue to increase in the future (Pokhrel et al., 2021; Ault,2020; DeSoto et al., 2020; Yuan et al., 2019), major uncertainties remain with regard to the impact of different drought regimes on tree growth and forest restoration (Liu et al., 2022; D'Orangeville et al., 2018; Panetta et al., 2018). While it has been reported that growth of Quercus mongolica is generally related to site aridity throughout a large part of its distribution (Zhang et al., 2021b), the exact effects of drought characteristics on growth during the drought are still unknown.
Growth recovery from drought is affected by both drought intensity and duration. Picea abies showed lower recovery and resilience to mild drought, but higher recovery to severe drought (Bottero et al., 2021). Drought intensity had greater influence on recovery of Picea glauca than drought timing (Mood et al., 2021). However, recovery and resilience of Pinus halepensis, P. nigra and P. sylvestris were lower after multiple droughts (Serra-Maluquer et al., 2018), indicating that recovery dynamics can change with multiple drought exposure. In fact, multi-year drought was a better predictor of post-drought tree growth of P. halepensis than drought intensity (Helluy et al., 2020). Long-term drought has also been reported to delay and limit post-drought recovery for P. sylvestris (Dang et al., 2019). Important differences in post-drought recovery seem to exist between differing wood types with ring-porous species tending towards a quicker recovery than diffuse-porous species (Kannenberg et al., 2019). Overall, recovery dynamics vary by species and there is less work on angiosperm species, such as Q. mongolica, making it very difficult to anticipate their reaction to future droughts.
Some species can even grow more after drought than before, presumably to compensate for reduced growth during the drought (Li et al., 2021; Alfaro-Sánchez et al., 2019). Such rapid recovery associated with compensatory growth has been observed in several tree species (Ovenden et al., 2021; Seidel et al., 2019; Minucci et al., 2017). The compensatory mechanisms has been hypothesized to mitigate some of the otherwise lasting effects of drought on the tree physiology (Balducci et al., 2016). Q. petraea and Q. robur recovered quickly to the pre-drought growth level after summer drought (Bose et al., 2021), while P. sylvestris showed rapid growth in the next year after spring and summer drought, which weakened the overall negative impact of drought (Seidel et al., 2019). However, increased drought frequency caused the compensatory effect on growth to fade for Larix sibirica, L. gmelinii, and P. sylvestris (Xu et al., 2022), suggesting that compensatory growth is limited to isolated drought events. Whether this effect of multi-year drought on compensatory growth is also evident in oaks remains an open question.
Oak species are widely distributed in Asia, Europe and North America (Sun et al., 2020; Cavender‐Bares, 2019; Mölder et al., 2019). Most oak species can adapt to a certain degree of drought (Suseela et al., 2020; Kunz et al., 2018). Q. mongolica, an oak species that is widely distributed and a dominant species of forests in northern China, had been predicted to expand its distribution under intensified drought regimes in model simulations (Leng et al., 2008). In contrast, analysis of tree-rings suggested that the expansion of Q. mongolica would be highly restricted by increasing drought, especially in the drier portion of its distribution (Zhang et al., 2021b). Growth declines caused by drought have been reported for other oak species (Gea-Izquierdo et al., 2021; Colangelo et al., 2018) and the vulnerability of oak species to extreme drought can increase (Camarero et al., 2021; Móricz et al., 2021). Yet, few studies have reported how drought intensity and duration affect the post-drought growth recovery for oak species (Gonzalez de Andres et al., 2021; Ouyang et al., 2021).
Here, we use a network of tree-ring collections from 27 stands covering a large part of the distribution of Q. mongolica in northern China, to investigate the influences of multi-year drought on post-drought growth recovery. Our main objectives were to (1) determine whether drought was a primary factor that influences radial growth of Q. mongolica; (2) investigate the growth changes of Q. mongolica with different drought intensity; (3) assess how drought intensity and duration affect variations of post-drought recovery of Q. mongolica; and (4) reveal how compensatory growth varies with drought duration and intensity. Accordingly, we hypothesized that (1) drought is a primary factor that influences radial growth of Q. mongolica; (2) drought intensity was positively related to growth reductions during the drought year; (3) multi-year drought is a strong indicator of recovery; and (4) that both severity and duration are negatively related to post-drought compensatory growth.
Section snippets
Study region and species
The study region (115°E-132° E, 39°N-48° N) is located in North China (Fig. 1). Q. mongolica is the dominant deciduous species in the broadleaf and needleleaf mixed forests of northern China, where it can form pure oak and mixed forests (Sun et al., 2020; Lyu et al., 2018, 2017). Q. mongolica is typically found in lowlands, hillsides, and rocky sites.
The study region has a temperate monsoon climate. Mean annual temperatures ranged between 3.3 and 8.6°C (mean 6.2°C), and total annual
Growth-climate relationships
Summer temperatures (June – July) had a negative influence on tree growth at 23 of 27 sites, whereas summer precipitation and relative humidity were positively correlated for 25 and 24 sites, respectively (Fig. 2). Summer PDSI also had a positive correlation with tree growth in 27 sites (Fig. 2). The correlation between PDSI and tree growth tended to be stronger in drier sites (Figs. 2 & S1). Compared to precipitation and relative humidity, PDSI showed generally stronger correlations with tree
Q. mongolica tree growth was mainly constrained by drought
Our results reveal that drought is a major climatic constraint on growth of Q. mongolica over a large proportion of its range. PDSI integrates precipitation input and evapotranspiration loss to reflect the combined effects of precipitation and temperature. While radial growth was positively related to current June-July precipitation and negatively related to current June-July temperature, PDSI showed a stronger relationship with radial growth. The stronger correlation between PDSI and radial
Conclusion
Summer drought controls the radial growth of Q. mongolica in northern China. Post-drought recovery of Q. mongolica depends mostly on the drought duration beyond a certain threshold of drought intensity. After short-term drought, the recovery of Q. mongolica is not inhibited no matter the drought intensity, but recovery can be seriously weakened if droughts last for multiple years. Long-term drought also reduces compensatory growth and leads to the transformation of post-drought growth
Author contribution
P.L. processed the data, analyzed the results and led the writing. X.Z., and X.H. designed the experiment and methodology. X.Z. and T.R., wrote, reviewed and edited the manuscript. P.L., and B.Z. participated in data processing and data collection.
Declaration of Competing Interest
The authors declare that no conflict of interests exists.
Acknowledgments
This work was funded by the Special Project for Local Science and Technology Development Guided by the Central Government for Hebei Province (226Z6801G), the Science and Technology Project of Hebei Education Department (BJ2020025), and Talent introduction program in Hebei Agricultural University (YJ201918).
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