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ORIGINAL RESEARCH article

Front. For. Glob. Change, 13 January 2022
Sec. Temperate and Boreal Forests
This article is part of the Research Topic The Varying Responses of Vegetation Activity to Climate Change in Northern Hemisphere Forests View all 8 articles

Different Radial Growth Responses to Climate Change of Three Dominant Conifer Species in Temperate Forest, Northeastern China

\r\nHui WangHui Wang1Yangcui NingYangcui Ning1Chunlan LiuChunlan Liu1Peng XuPeng Xu2Wentao Zhang,*\r\nWentao Zhang3,4*
  • 1Beijing Municipal Research Institute of Environmental Protection, Beijing, China
  • 2School of Geography and Planning, Sun Yat-sen University, Guangzhou, China
  • 3Qingdao Institute of Humanities and Social Sciences, Shandong University, Qingdao, China
  • 4Center for Ecosystem Products Value Realization, Yellow River National Strategic Research Institute, Shandong University, Qingdao, China

We conducted dendroclimatological study on three dominant conifer tree species, Pinus koraiensis, Larix olgensis, and Picea jezoensis, in northeastern China for a better understanding of climate change impacts on temperate forest growth, by discussing the radial growth relationships of these tree species and projecting their radial growth trends under the future climate change scenarios. Based on the tree-ring samples collected from the upper altitude of Changbai Mountain, ring width chronologies were built to examine the growth relationships, and regression equations were established to project the future growth of the species under future climate change projected by the five general circulation models (GCMs) and four representative concentration pathway (RCP) scenarios. Although both temperature and precipitation showed varying degrees of relationships with growth of these three tree species, the limiting climate factors were species-specific. The tree-ring growth of P. koraiensis was limited by the summer temperature and precipitation at the end of growth, namely, significant positive correlations with the current July temperature and the previous September precipitation. Growth of L. olgensis was limited by the temperature before growing season, for its chronology was negatively correlated with the current February and previous December temperature (p < 0.05). The climatic conditions before and after growing season seemed to be the limiting factors of P. jezoensis growth, which was negatively correlated with the current February to April temperature and the current September temperature (p < 0.05), and positively correlated with the current August precipitation (p < 0.05). Under the gradual increasing of temperature predicted by the five GCMs and four RCP scenarios, the radial growth of P. Koraiensis will relatively increase, while that of L. olgensis and P. jezoensis will relatively decrease comparing to the base-line period (1981–2010). The specific growth–climate relationships and the future growth trends are species dependent. P. Koraiensis was the more suitable tree species for the forestation to maintain the sustainable forest in Changbai Mountain.

Introduction

Global warming and its influences on the structure, function, and growth of the forest ecosystem have been observed and recognized (Lindner et al., 2010; IPCC, 2013; Rahman et al., 2017; Russell and Parton, 2020). The annual mean temperature in China has increased 0.9 to 1.5°C during the last 100 years (1909–2011) larger than the global average (Editorial Commission of Northeast Regional Climate Change Assessment Report, 2013), and different climate models under different scenarios all predict that climate warming will continue in future in China (Xu et al., 2006; Xu et al., 2016; Zhang et al., 2017). A better understanding of how forest ecosystem in response to climate change is of great significance for maintaining productive and sustainable forest, and this requires more precise tree growth-climate relationships.

Tree-ring can be used as an important data source to study impacts of climate change on tree growth, for tree-ring recording the tree growth process and reflecting the effect of tree growth climate conditions. In addition, tree-ring material has many advantages, such as a wide range distribution, high resolution, accurate dating, and easy access to multiple copies (Hughes, 2002; Cook et al., 2004; Breitenmoser et al., 2014). Accordingly, many studies on tree growth-climate relationships have been widely carried out by dendroclimatological method using this proxy data (Fritts, 1976; Lebourgeois et al., 2012; Housset et al., 2018; Zhang et al., 2018).

Compared with boreal forests, temperate forests are characterized by high precipitation, high humidity, and more deciduous tree species, indicating more complex growth-climate relationships and potential growth trends under climate change (Castagneri et al., 2014; Han et al., 2019; Prislan et al., 2019; Wu et al., 2019). Some dendroecological studies were conducted on the radial growth of Pinus sylvestriformis, Picea jezoensis, and Pinus koraiensis in the temperate forest of Changbai Mountain, showing comprehensive influence of temperature and precipitation (Yu et al., 2016, 2021). If the global temperature continues to increase in the future, growth of P. jezoensis will undergo an adverse impact (Yu et al., 2021). At the same time, the climate conditions related to growing seasons have been found to be limiting factor for temperate forest growth usually, especially summer temperature (Castagneri et al., 2014; Chen et al., 2017; Wu et al., 2019), spring, and winter temperatures before growing season (Pederson et al., 2004; Yan et al., 2017; Prislan et al., 2019). Above all, although many studies have already addressed the unstable relationships between radial growth and climate, the climatic responses still need to dig deeper.

Changbai Mountain in Northeastern China is covered by a large area of undisturbed temperate forest and characterized by a vertical zonation of forest ecosystems along the altitudinal gradient (Editorial Committee for Forestry of Jilin, 1988). P. koraiensis, Larix olgensis, and P. jezoensis are its three dominant conifer tree species. The climate warming in Changbai Mountain has been obvious since the 1950s (Wang et al., 2010; Jia et al., 2017; Jiang et al., 2019). Under this background, many studies were carried out in this region to discuss the influence of climate change on the forest ecosystem using dendroclimatological method. Some revealed that elevation differences exerted a strong influence on the growth-climate relationships for the individual conifer tree species (Wang et al., 2013; Shen et al., 2016; Wang H. et al., 2017; Wang X. C. et al., 2017), but the difference among the tree species growth-climate relationships was rarely compared, which is also important for examining the regional growth-climate precisely and thoroughly.

This study chose the three main conifer tree species of P. koraiensis, L. olgensis, and P. jezoensis in Changbai Mountain to discuss the radial growth relationships of the three tree species and to project their radial growth trends under the future climate change scenarios.

Materials and Methods

Study Area and Field Sampling

The study area is located on the north slope of the Changbai Mountain Natural Reserve in northeastern China (Figure 1). This area is characterized by a temperate continental monsoon climate. The meteorological data of the Donggang and Erdao stations (data from the National Meteorological Information Center of China) showed that the mean annual temperature was 3.2°C, with a mean temperature of −16.8°C in January and 20.1°C in July during the period 1958–2007 (Figure 2). The mean annual precipitation was 746.4 mm, and mainly occurred from May to September. The vegetation in this area has the characteristic of vertical zonality. Korean pine and broad-leaved mixed forest are located from 500 to 1,100 m. A spruce-fir forest continues from 1,100 to 1,800 m. The soil in the coniferous forest zone is mountainous brown forest soil (Editorial Committee for Forestry of Jilin, 1988).

FIGURE 1
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Figure 1. Locations of sample sites and meteorological stations in the study area.

FIGURE 2
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Figure 2. Monthly total precipitation and mean temperature at Changbai Mountain based on the Donggang and Erdao meteorological stations (1958–2007).

Tree-ring cores of P. koraiensis, L. olgensis, and P. jezoensis were all sampled at their upper altitudinal limit in the mountain dark coniferous forest zone distributed from 1,100 to 1,800 m a.s.l. For each site, approximately 20–30 trees were selected and two cores were sampled per tree.

Chronology Development

Cores were dried and sanded to produce clearly visible tree-ring boundaries, and then cross-dated (Stokes and Smiley, 1968). The ring width was measured using the LINTAB-station (Frank Rinn, Heidelberg, Germany) at a 0.01 mm resolution. The COFECHA program (Holmes, 1983) was used to check the quality of cross-dating and measurements.

The tree-ring chronologies was developed using the ARSTAN program (Cook, 1985). A cubic smoothing spline with 67% of the series length was used to remove the age-related growth trends of raw ring-width chronologies. The resulting ratio series were then computed as a biweight robust mean of the detrended and standardized individual series (Cook et al., 1990). To show the strength of common signals in the chronologies, a within-chronology common interval analysis for each chronology was performed. The statistical quality of each chronology was measured using several coefficients commonly used in dendrochronology. We calculated the standard deviation (SD) to estimate the variability of ring width series, and the mean sensitivity (MS) to indicate the relative changes in ring width index variance between consecutive years, and the first-order autocorrelation (AC1) to measure the influence of the previous year’s growth on the current ring, and the mean correlation between trees (R) and the first principal component (PC1) to indicate the common signal strength. The expressed population signal (EPS) was also calculated to indicate the chronology confidence level (Briffa and Jones, 1990), and a threshold value of 0.85 is often used to evaluate the useful and valid time span of the final chronologies (Wigley et al., 1984).

Gleichläufigkeit index was calculated to measure level of agreement between consecutive ring width slopes. The degree of similarity between two series based on the positive (upward) or negative (downward) trends of each width was expressed as a percentage of the number of intervals (Schweingruber, 1988; Schweingruber et al., 1993). Gleichläufigkeit index (GLK) was computed according to the formula (Feliksik and Wilczyński, 2009):

G L K = 100 m ( n - 1 ) - 1 [ % ]

where m is the number of concordant (as to the direction) chronology sections, and n is the length of the period under comparison in years.

Pearson correlation coefficient was calculated to measure the consistence of variation amplitude correlated with the sensitivity of the chronology.

Growth-Climate Relationships

There are three meteorological stations named Erdao (591 m a.s.l.), Donggang (774 m a.s.l.), and Tianchi (2623 m a.s.l.) in the study area (Figure 1). Among them, Tianchi station data were not used in our study because winter observations have been terminated since 1989. The monthly temperature and precipitation correlation coefficients at Erdao and Donggang from 1958 to 2007 were 0.95 (p < 0.01) and 0.79 (p < 0.01), respectively. Therefore, we averaged the recorded climate data from the Erdao and Donggang to improve the regional representation when used to analysis the growth-climate relationships.

Pearson correlation coefficients between the tree-ring width and monthly mean temperature and total precipitation were calculated between 1958 and 2007 to identify the growth-climate relationships (Fritts, 1974) throughout 13 months from the previous September to the current September.

Future Projection of the Radial Growth Trends

The future climatological data were projected by five general circulation models (GCMs) (HadGEM2-ES, IPSL-CM5A-LR, GFDL-ESM2M, MIROC-ESMCHEM, and NorESM1-M) (Yin et al., 2015) and four representative concentration pathway (RCPs) (RCP2.6, RCP4.5, RCP6.0, and RCP8.5) scenarios (Moss et al., 2010) used in the Intergovernmental Panel on Climate Change (IPCC) Fifth Assessment Report. To evaluate the simulation capacity of the models for the study area, Pearson correlation coefficients between the observed and the simulated monthly temperature and precipitation were calculated during 1981–2010. To reduce uncertainty in GCMs performance, an average of the five GCMs under each emission scenario was used in this study. The future projection was predicted between 2011 and 2100.

The regression equations between ring width and climatic factors were established by stepwise regression method to calculate tree-ring index. The regression equations, passing the significance test at 0.005 levels and explaining variances all over 20%, were used for the growth projections. Sum of square error (SSE) and mean squared error (RMSE) were calculated to measure the fitting effect of the equations. The relative variation rate (RVI) was used to evaluate the impacts of future climate change on the radial growth of the three tree species.

RVI = Y ( X + X ) - Y ( X ) Y ( X ) × 100 %

RVI: the variation rate of tree-ring index; Y: the tree-ring width index; X: the monthly total precipitation and mean temperature; △X: the variable quantity of monthly total precipitation and mean temperature.

Results

Chronology Characteristics

Three ring-width chronologies were built for the three conifer tree species. Table 1 shows the statistical characteristics of the three chronologies. P. jezoensis had the higher statistical indices than the other two tree species, except for L. olgensis’ SD. P. koraiensis had the lowest statistics of the three tree species. The EPS of the three chronologies all exceeded the recommended threshold of 0.85; according to Wigley et al. (1984), they were all suitable for dendroclimatological studies.

TABLE 1
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Table 1. The sampling site information, the standard chronology statistics, and the results of the common period analysis.

The annual and 5-year moving averaged ring width indices revealed the correlations among chronologies in high-frequency and low-frequency, respectively (Figure 3). They showed the similar variation in 1990s, circa 1885 to 1905, but they were different in circa 1975, circa 1930 to 1935. Gleichläufigkeit indices of the three chronologies were 57, 53, and 53%, all greater than 50% over 200 years. The P. koraiensis chronologies showed better relationships with the other two chronologies (R = 0.22 and 0.28, respectively) than the relationship between L. olgensis and P. jezoensis chronologies (R = 0.09) (Table 2).

FIGURE 3
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Figure 3. Ring-width index series of the chronologies (left Y-axis) and numbers of tree-ring sample cores used in the chronology development (right Y-axis). The red lines represent the 5-year moving averages.

TABLE 2
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Table 2. Gleichläufigkeit indices (GLK) and Pearson correlation coefficients (R) among the three chronologies.

Relationships Between Tree-Ring Chronologies and Climatic Factors

The growth-climate relationships were different for the three tree species (Figure 4). P. koraiensis chronology was significantly and positively correlated with temperature in the current July and precipitation in the previous September. Different from P. koraiensis, L. olgensis ring width index chronology was negatively and significantly correlated with temperature in the current February and the previous December. P. jezoensis was negatively correlated with the temperature in the current months especially with February to April and September (all p < 0.05), and it was positively correlated with the current August precipitation significantly.

FIGURE 4
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Figure 4. Pearson correlation coefficients between monthly climatic factors and ring width indices for Pinus koraiensis, Larix olgensis, and Picea jezoensis. Sizes of the circles indicate the strengths of the correlation coefficients. The gradual change of color from blue to red indicates a gradual change of correlation from negative to positive. The capitalized months mean them from the past year, and the lowercase from the current year. The “*” indicated a significance p < 0.05.

The Future Radial Growth Trends Under the Projected Climate

Figure 5 shows the future climate change predicted by five GCMs under four emission scenarios. During 1981–2010, the correlation coefficient between the observation and the simulated monthly temperature and precipitation was 0.987 (p < 0.001) and 0.721 (p < 0.001), respectively. The annual average temperature increased gradually for all RCPs, and the temperature in 2099 is 1.4, 2.1, 3.5, and 6.3°C higher than the temperature in 2011, respectively, for RCP2.6, RCP4.5, RCP6.0, and RCP8.5, respectively (Figure 5A). The annual total precipitation also had a rising trend, increased about 10 mm from 2011 to 2100 for the individual RCPs (Figure 5B).

FIGURE 5
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Figure 5. Climate changes in (A) annual temperature and (B) annual precipitation during 2011–2100 relative to the baseline period for four RCPs. Modeled and observed averages of (C) monthly temperature and (D) monthly precipitation during 1981–2010.

Three equations were chosen for prediction of the future radial growth (Table 3). They all passed the significance test at 0.005 levels and explained variances all over 20%. The correlation coefficient between observed and the modeled tree-ring width index are 0.482 (p < 0.01), 0.761 (p < 0.01), and 0.533 (p < 0.01) for P. koraiensis, L. olgensis, and P. jezoensis, respectively. Under the future climate change scenarios, compared with the baseline term of 1981–2010, the annual ring width of P. koraiensis will increase by more than 20% in the three future periods (Table 4). The ring width of L. olgensis and P. jezoensis will decrease by more than 48 and 29% in the three future periods, respectively. As carbon intensity increased from low greenhouse gas emissions scenarios (RCP2.6) to high greenhouse gas emissions scenarios (RCP8.5), the variation magnitude will be enhanced for all the three tree species.

TABLE 3
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Table 3. Statistics of equation for Pinus koraiensis, Larix olgensis, and Picea jezoensis.

TABLE 4
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Table 4. RV values for the three periods based on tree-ring climate relationship.

Discussion

Species-Specific Growth-Climate Relationships

Pinus koraiensis, L. olgensis, and P. jezoensis chosen in this study were the three typical and representative conifer tree species of Changbai Mountain (Editorial Committee for Forestry of Jilin, 1988). The established chronologies had good statistical quality, suggesting they were suitable for dendroclimatological study. High Gleichläufigkeit indices illustrated the good overall similarity of width trends among the three chronologies, which can crossdate with each other. However, the correlation coefficients between the L. olgensis and P. jezoensis were weak, indicating that the amplitude of variation for the two chronologies had poor consistence (Shao et al., 2003). This may inform differences in the ecological information recorded by the chronologies, but the further identification of such information required a comparison of the chronologies with climate data (Wimmer and Grabner, 2000; Fonti and García-González, 2004).

According to the new climate regionalization scheme for China, Changbai Mountain belongs to the middle temperate humid climate zone located in northeastern China, where temperature is the main limiting factor for forest growth. However, further analyses showed that precipitation were the one of the limiting climate factors for the tree radial growth in Changbai Mountain as well. Due to the vertical zonality of Changbai Mountain, the microclimate (such as temperature, precipitation, and soil moisture) is different (Editorial Committee for Forestry of Jilin, 1988), which further leads to the influence of altitude on the radial growth-climate relationships for the individual tree species. In general, at low elevation site, the radial growth was positively correlated with the precipitation, while at the upper elevation, radial growth was significantly correlated with the temperature. This rule was applied to the main tree species in the region scale (Zhuang et al., 2017). On the other hand, some studies have also shown that differences in growth-climate relationships between tree species were more influential than those between sites (Yu et al., 2011), which were consistent with the results reported by Graumlich (Graumilch, 1993), but differed from some other findings in northwest China, Picea crassifolia in Qilian Mountain for example (Liang et al., 2010).

Our study suggested that the three conifer tree species’ radial growth was affected by both temperature and precipitation, and the specific responses of tree radial growth to climate were dependent on the species. The main difference was that P. Koraiensis radial growth was positively and significantly correlated with temperature, whereas L. olgensis and P. jezoensis radial growth were negatively and significantly correlated with temperature; these findings were confirmed by the other studies. With the detailed analysis, the current July temperature was the main climatic limiting factor for the growth of P. koraiensis, verified by Gao et al. (2018), because the decreasing temperature may lead to a delay of the onset of the growth period and the termination of growth before the end of the normal growing season. In addition, the previous September precipitation was another climatic limiting factor for the growth P. koraiensis, for that the concentrating period of precipitation was from May to September. Therefore, high precipitation in September was more important to the accumulation of soil moisture, which affected the growth of P. koraiensis in the next year. The radial growth of L. olgensis was negatively affected by the temperature in the current February and the previous December, while the radial growth of for P. jezoensis was negatively with temperature from February to April. Some other studies showed that the above negative correlations may be caused by the drought stress when the temperature rises for the high altitude growth of the conifer tree growth (Yu et al., 2006; Li et al., 2011). The special geological conditions in Changbai Mountain lead to the thin soil layer and poor water storage capacity in high altitude areas. With the increase of temperature, the evapotranspiration of soil water and the transpiration of plants may accelerate to inhibit the tree growth, reduce leaf area, and then affect the photosynthetic characteristics of plants, which is most obvious in spring when drought stress is prone to occur.

The Projected Future Radial Growth

The future climate change in Changbai Mountain area was predicted by different climate models with different climate scenarios (Zeng et al., 2009; Wang et al., 2013; Yu et al., 2015), and those studies all predicted temperature will increase gradually in future. However, the prediction results for precipitation are inconsistent, which indicated that the change of future precipitation is uncertain. GCMs have become the main tool in future climate change assessment and RCPs were used in IPCC Fifth Assessment Report to investigate the impact of greenhouse gasses on climate change (IPCC, 2013). They were proved to have good simulation abilities for local climate characteristics over China (Yin et al., 2015) and in Changbai Mountain (Yu et al., 2015; Wang et al., 2019).

Under the climate change scenarios, in the future (2011–2099), the temperature in Changbai Mountain will increase obviously, and the rates of increase are 0.14°C/10 a (RCP2.6), 0.21°C/10 a (RCP4.5), 0.35°C/10 a (RCP6.0), and 0.63°C/10 a (RCP8.5), which are generally consistent with those of the whole China (Yin et al., 2015). The different growth–climate relationships dependent on tree species caused the different future radial growth under future climate warming, and this finding was verified by other studies (Li et al., 2011; Zhuang et al., 2017). For P. koraiensis, the radial growth will increase greatly when the temperature rise. But for L. olgensis and P. jezoensis, the radial growth will relatively decrease with temperature increase in future. In detail, a warming growing season will benefit growth and distribution spread of P. koraiensis, while temperature increase before growing season will restrict the growth and survival of L. olgensis and P. jezoensis. If warming continues in the future, the distribution of P. koraiensis at high altitude will very likely expand; however, the range of L. olgensis and P. jezoensis will narrow for their decline in competitiveness. These dominant tree species shift may further lead to the changes of forest composition, structure, and the potential distribution area for the mountain dark coniferous forest where they distributed.

It should be noted that the above projections based on the growth-climate relationships and future climate change may be of some uncertainty. On the one hand, some uncertainties may exist in GCMs and RCPs. On the other hand, the other environmental and biological factors affecting tree growth also may change, bringing about the future growth change.

Conclusion

The radial growth of the three main conifer tree species of P. koraiensis, L. olgensis, and P. jezoensis, distributed at their upper altitudinal limit on the north slope of Changbai Mountain, is affected by both temperature and precipitation. The specific growth–climate relationships are species dependent. Under the future climate change scenarios, the P. koraiensis growth will increase, whereas the L. olgensis and P. jezoensis radial growth will decrease relatively. In consequence, P. koraiensis in the higher attitude are more favorable for forestation compared with the other two tree species, and this finding can be used as an important basis of healthy forest management in this region.

Data Availability Statement

The original contributions presented in the study are included in the article/supplementary material, further inquiries can be directed to the corresponding author.

Author Contributions

HW and WZ were responsible for the research design and the editing coordination of the manuscript, tree-ring width measurement, and contributed in editing and reviewing the manuscript. HW, YN, and CL data preparation and analysis were partitioned as follows: site inventory and sample collection. HW, PX, and WZ tree-ring growth and climate relationship analysis. All authors contributed to the article and approved the submitted version.

Funding

This research was funded by the Fundamental Research Funds of Shandong University (Grant No. 2020GN107).

Conflict of Interest

The authors declare that the research was conducted in the absence of any commercial or financial relationships that could be construed as a potential conflict of interest.

Publisher’s Note

All claims expressed in this article are solely those of the authors and do not necessarily represent those of their affiliated organizations, or those of the publisher, the editors and the reviewers. Any product that may be evaluated in this article, or claim that may be made by its manufacturer, is not guaranteed or endorsed by the publisher.

Acknowledgments

We thank Xuemei Shao and Xiuqi Fang for their help in methodology. We also thank Zhiyong Yin, Haifeng Zhu, Li Chen, and Dongsheng Zhao for their help in materials for study.

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Keywords: climate change, radial growth, dendroclimatology, Changbai Mountain, temperate forest

Citation: Wang H, Ning Y, Liu C, Xu P and Zhang W (2022) Different Radial Growth Responses to Climate Change of Three Dominant Conifer Species in Temperate Forest, Northeastern China. Front. For. Glob. Change 4:820800. doi: 10.3389/ffgc.2021.820800

Received: 23 November 2021; Accepted: 07 December 2021;
Published: 13 January 2022.

Edited by:

Jian Tao, Shandong Institute of Business and Technology, China

Reviewed by:

Liang Jiao, Northwest Normal University, China
Zhudeng Wei, Nanjing University of Information and Science Technology, China
Yuan Jiang, Beijing Normal University, China

Copyright © 2022 Wang, Ning, Liu, Xu and Zhang. This is an open-access article distributed under the terms of the Creative Commons Attribution License (CC BY). The use, distribution or reproduction in other forums is permitted, provided the original author(s) and the copyright owner(s) are credited and that the original publication in this journal is cited, in accordance with accepted academic practice. No use, distribution or reproduction is permitted which does not comply with these terms.

*Correspondence: Wentao Zhang, zhangwt@sdu.edu.cn

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