Climate Effect on the Radial Growth of Populus Simonii
Dataset in Bashang Area of Hebei Province of China
Liu, Y. L.1 Xin, Z. B.1* Li, Z. S.2 Keyimu, M.2
1. College of Water and Soil
Conservation, Beijing Forestry University, Beijing 100083, China;
2. Research Center for
Eco-Environmental Sciences, Chinese Academy of Sciences, Beijing 100085, China
Abstract: Tree-rings are
considered an important record of the influence of the environment on plant
growth. In July and August 2018, we collected and analyzed healthy and
declining poplar tree rings in Bashang area of Hebei province, China. The
dataset includes the following: (1) basic information on the Populus simonii
shelterbelt plot in Bashang area of Hebei province; (2) standard chronologies
of healthy and declining poplars and the main characteristic parameters and
common interval spans; (3) correlations between healthy/declining poplars and
climate factors: correlation analysis between healthy and declining poplars and
monthly and seasonal climate factors (mean temperature, maximum temperature,
minimum temperature, precipitation, mean relative humidity, and Palmer drought
severity index) and moving correlation function analysis between the two
chronologies and the seasonal and monthly climate factors for the most
important months; and (4) time series and cross-dating test results for the
healthy and declining Populus simonii forest. The dataset is archived in
.txt, .xlsx, .out formats and consists of 4 data files with a data size of 404
KB (compressed into one single file with 152 KB).
Keywords: Bashang area of Hebei
province; Populus simonii; declining; tree growth; climate response
DOI: https://doi.org/10.3974/geodp.2022.01.09
CSTR: https://cstr.escience.org.cn/CSTR:20146.14.2022.01.09
Dataset Availability Statement:
The dataset
supporting this paper was published and is accessible through the Digital Journal of
Global Change Data Repository at: https://doi.org/10.3974/geodb.2021.08.01.V1 or
https://cstr.escience.org.cn/CSTR:20146.11.2021.08.01.V1.
1 Introduction
The Beijing-Tianjin sandstorm source ecological plantation
is an important ecological barrier[1]. In recent years, poplar
plantations in Bashang area of Hebei have experienced different degrees of
degradation, which has attracted widespread attention from industry and the
public. The degradation mechanism is a scientific issue that must be resolved[2,3].
The factors underlying the degradation of the poplar shelterbelt in Bashang
area are mainly summarized into three types: (1) In terms of tree physiology, Populus
simonii has reached the mature stage 30 years after planting, and the
physiological functions and vitality of the trees have been gradually degraded,
leading to death[3]. (2) Poplars show poor growth due to the hard
environmental conditions in Bashang area. The root system of deep-rooted poplar
cannot penetrate the deep calcite layer in Bashang area and cannot obtain
sufficient water. As the degree of degradation deepens, the leaf fall of Populus
simonii is intensified, and more soil water is needed to maintain its
normal photosynthesis. However, the Bashang area is arid and rainless, and the
lack of water aggravates the degradation and death of poplars[4,5].
(3) Poplars are susceptible to pests and diseases after drought, which has
accelerated the degradation of poplar shelterbelts in Bashang area[6?C8].
However, the growth response of healthy and declining poplars under different
climate factors has not been investigated.
Tree rings can record
the historical growth process of trees[9], thus providing a rare
opportunity to detect the relationship between tree growth and climate. The
reasons for tree decline can be found by studying the differences between
healthy and declining poplars in response to climate change. This study
examined healthy and declining poplars of the Boluosu Forest Farm in Zhangbei
county, Hebei province, as the research object. Dendroclimatic methods have
been used to establish standard chronologies for healthy and the declining
poplars. Correlation analyses were conducted between these chronologies and
local climate factors. Data on the effect of climate on the radial growth of Populus
Simonii provide theoretical support for the management of poplar
plantations in Bashang area under climate warming.
2 Metadata
of the Dataset
The metadata of Climate effect on the radial growth of Populus
Simonii in Bashang area of Hebei province[10] are summarized in
Table 1, including the dataset full name, short name, authors, year of the
dataset, temporal resolution, spatial resolution, data format, data size, data
files, data publisher, and data sharing policy, etc.
3 Study Area
and Data Development Methods
3.1
Study Area and Plot Information
3.1.1 Study Area
The Boluosu Forest Farm (41??03¢N-41??27¢N, 114??20¢E-115??58¢E) in Ertai town, Zhangbei county, is located in
a typical agro-pastoral zone with an altitude of 1,370-1,390 m. The climate belongs to the
mid-temperate continental monsoon climate zone. Affected by the high pressure
in Inner Mongolia, the main climate characteristics of this area are heavy
wind, limited rain, severe drought, and variable climate. The mean annual
temperature is 3.67 ºC, the highest temperature is 24.84 ºC, the lowest
temperature is ‒20.01 ºC, the annual accumulated temperature is 2,100-2,800 ºC, and
the frost-free period is 64-90 days (1975- 2017). The annual precipitation is
approximately 400 mm, and 64% is concentrated in summer. The annual evaporation
is 4 to 5 times the annual precipitation. Gale days are common in this area,
and approximately 30 days per year experience strong winds of level 7 and
above. The soil-forming parent materials in this area mainly include gneiss,
granite, basalt, and aeolian sandy soil. Soil erosion is serious, and it is
mainly caused by wind erosion. The main soil type is chestnut soil. Meadow soil
is distributed in low-lying areas, and brown soil is distributed in natural
secondary forest areas. The soil texture is mainly sand, loamy sand and sandy
loam[12]. The bulk density of the soil is 1.60-1.65 g/cm3,
and the total porosity is 29.97%-38.57%[12,13]. There are different
degrees of calcium deposits in the chestnut soil in this area, the depth of
which is generally 30-50 cm, and the thickness is roughly 20-60 cm. The soil is
a solid powder, and the hardness of the calcified layer is relatively high[8].
There are abundant tree species in the shelterbelt in the study area, including
Populus simonii, Populus davidiana, Populus cathayana, Pinus
sylvestris var. mongolica, Ulmus pumila, Picea asperata,
Larix gmelini, Pinus tsbulaeformis, etc. The shrubs mainly
include Caragana korshinskii, Hippophae rhamnoides, Syringa
reticulata, Salix microstachya, Salix psammophila, etc.
Herbaceous plants are mainly perennial cold-tolerant xerophytes, mainly
including Medicago sativa, Potentilla chinensis, Convolvulus
arvensis, Artemisia argyi, etc[14].
Table
1 Metadata summary of
the Climate effect on the radial growth of Populus Simonii in Bashang
area of Hebei province
Items
|
Description
|
Dataset
full name
|
Climate
effect on the radial growth of Populus Simonii in Bashang area of
Hebei province
|
Dataset
short name
|
Climate&PopulusSimoniiBashang
|
Authors
|
Liu,
Y. L., Beijing Forestry University, liuyaling0720@126.com
Xin,
Z. B. 0000-0002-1653-8679, Beijing Forestry University, xinzhongbao@126.com
|
|
Li,
Z. S., Chinese Academy of Sciences, zsli_st@rcees.ac.cn
Keyimu,
M., Chinese Academy of Sciences, mktrees@126.com
|
Geographical
region
|
Boluosu
Forest Farm, China (41??03¢N-41??27¢N??114??20¢E-115??58¢E)
|
Year
|
Healthy
poplars (1975-2017),
Declining poplars (1982-2017)
|
Data
format
|
.txt,
.xlsx, .out
|
|
|
Data
size
|
404
KB
|
|
|
Data
files
|
(1)
Basic information of Populus simonii shelterbelt plot in Bashang area
of Hebei province
(2)
Standard chronologies of healthy and declining poplars and the main
characteristic parameters and common interval spans
(3) Correlations
hetween the healthy and declining poplars and climate factors
(4) Time
series and cross-dating test results for the healthy and declining Populus
simonii forest
|
Foundations
|
National
Natural Science Foundation of China (41877539, 42177319); Ministry of
Education of P. R. China (2017ZY02)
|
Data
publisher
|
Global Change Research Data Publishing &
Repository, http://www.geodoi.ac.cn
|
Address
|
No.
11A, Datun Road, Chaoyang District, Beijing 100101, China
|
Data sharing policy
|
Data from the Global
Change Research Data Publishing & Repository includes metadata, datasets (in the Digital Journal of Global Change Data Repository), and
publications (in the Journal of Global Change Data & Discovery). Data sharing policy
includes: (1) Data are openly
available and can be free downloaded via the Internet; (2) End users are
encouraged to use Data subject to
citation; (3) Users, who are by definition also value-added service
providers, are welcome to redistribute Data
subject to written permission from the GCdataPR Editorial Office and the
issuance of a Data redistribution
license; and (4) If Data are used
to compile new datasets, the ??ten per cent principal?? should be followed such
that Data records utilized should
not surpass 10% of the new dataset contents, while sources should be clearly
noted in suitable places in the new dataset[11]
|
Communication and searchable system
|
DOI, CSTR, Crossref, DCI, CSCD,
CNKI, SciEngine, WDS/ISC, GEOSS
|
3.1.2 Basic Information of the Plot
Tree cores were collected in the Boluosu Forest Farm (with
an area of 6.4 km2) in July and August 2018. Combining Landsat TM8
and Google Earth, 52 poplar plantation plots with relatively consistent sites
and relatively concentrated spaces were selected to collect healthy and
declining poplar cores[15]. The study divides healthy and declining
poplars by the withered rate, which refers to the percentage of the length of
the withered tree tops to the height of the tree. When the withering rate is
less than 20%, the tree is defined as a healthy poplar, and when the withering
rate is above 20%, the tree is defined as a declining poplar[15]. In
the sample plot, good-growing trees were selected for core collection, and a
Swedish haglof 300 mm growth cone (with an inner diameter of 5.15 mm) was
drilled along the east-west direction at a diameter of 1.3 m at breast height
of the tree. A total of 278 poplar tree cores were collected, including 202
healthy poplars and 76 declining poplars. After numbering, the cores were brought
back to the laboratory, and at the same time, the forest sample plot
investigation method was used to investigate and count the ecological structure
characteristics of each sample plot, such as vegetation type, diameter at
breast height, tree height, crown density, herb coverage, etc (Table 2).
Table 2
Basic information of Poplus simonii shelterbelt plot in Bashang,
Hebei province (excerpt)
Sample number
|
Shelter Forest types
|
Longitude (??E)
|
Latitude (??N)
|
Altitude (m)
|
Density (n/hm2)
|
Crown density
|
Herb coverage (%)
|
DBH
(cm)
|
Average height (m)
|
1
|
Farmland
shelterbelt
|
114.868
|
41.340
|
1,380.8
|
1,000
|
0.60
|
0.49
|
20.6
|
14.1
|
2
|
Farmland
shelterbelt
|
114.866
|
41.342
|
1,378.7
|
550
|
0.38
|
0.57
|
20.7
|
12.4
|
??
|
??
|
??
|
??
|
??
|
??
|
??
|
??
|
??
|
??
|
54
|
Farmland Protective forest
|
114.872
|
41.340
|
1,378.8
|
1,400
|
0.73
|
0.56
|
15.8
|
11.9
|
56
|
Plantation for wind protection and sand fixation
|
114.871
|
41.336
|
1,379.0
|
1,275
|
0.47
|
0.48
|
16.8
|
10.3
|
3.2 Data Processing
3.2.1 Sample Pretreatment
The collected tree cores were pretreated according to the
standard dendrochronology method[16]. First, the core number was
written down, and then the tree core was placed on wooden sample holders in a
position similar to the original position of the samples in the tree. If the
tree core was slightly twisted, the core can be broken off and pasted
separately with white latex. Then, a rope was wrapped around the pasted sample
and used to secure the sample to the wooden holder to prevent the tail of the
core from lifting. The samples were placed in a ventilated place to dry
naturally and then cut into individual sample cores. The samples were gradually
polished with 400, 800 and 1,200 mesh sandpaper until the annual ring boundary
of the samples could be clearly distinguished under the microscope.
3.2.2
Tree-ring Width Measurement and
Cross-dating
For preprocessed samples that met the requirements of
dendrochronological analysis, they were scanned by a high-definition digital
scanner, and the high-definition images with 1,200 dpi resolution were saved by
the scanner in *.tif format. Win DENDROTM (Regent Instrument Inc. Canada,
accuracy of 0.001 mm) was used to import the images and obtain the original
tree ring width time series. The COFECHA program was used to verify and
calibrate the cross dating and measurement results, and tree-ring width
sequences with poor correlations with the main sequence were eliminated[17].
Finally, 104 cores of healthy poplars and 35 cores of declining poplars were
eventually used for the tree-ring width chronology.
3.2.3 Development of Chronologies
Besause this research focuses on the relationship between
poplar growth and climate factors, the growth trends of trees with age and
other nonclimate factors were eliminated[18]. The cross-dated ring
width series were standardized using a negative exponential model in the ??dplR??
package in the R statistical software[19], and the standard
chronology (STD), Residual chronology (RES) and Arstan chronology (ARS) were
developed using the double-weighted average method[20].
This study used the standard chronologies of healthy and declining poplars to
analyze the correlation between tree growth and climate factors.
3.2.4
Climate Data
The monthly average data (1975-2017) of the Zhangbei Count Meteorological
Station, which is the closest station to the sampling plot at a straight-line
distance of 47.2 km, were selected from the China Meteorological Data Network.
Climate factors included the mean temperature (TMP), minimum temperature (TMN),
maximum temperature (TMX), precipitation (PRE) and mean relative humidity (RH).
To study the relationship between tree growth and the effective use of soil
moisture, Palmer drought severity index (PDSI) gridded data were obtained from
the Global Climate Database of the Royal Meteorological Institute of the
Netherlands[21] for the whole study region (114.50??E-115.00??E, 41.00??N-1.50??N) from 1975
to 2017.
3.2.5
Climate Response Analysis
In this study, a bootstrap correlation analysis was
performed using the DendroClim 2002 program[22] to study the
relationship between healthy and declining poplar growth and climate factors to
identify the climate factors that limit the growth of healthy and declining
poplars. Considering that the growth of poplars was affected not only by the
climate conditions of the current year but also by the climate conditions of
the previous year, the climate data from June of the previous year to October
of the current year (17 months in total) were selected as the window for the
climate correlation analysis. Seasonal climatic conditions have a more
representative influence on the radial growth of trees and the growth habits
and climatic change characteristics of the local shelter forest tree species. A
monthly combination of climate factors for a single month[23] was
used to analyze the influence of seasonal climate factors on the radial growth
of healthy and declining poplars. Since 1975, the warming of the Bashang area
of Hebei province has been significant. To understand the dynamic relationship
between healthy and declining poplar growth and major climatic factors, a moving
correlation analysis was performed in DendroClim 2002 to reveal the temporal
stability of healthy and declining poplar growth-climate relationships (moving
interval of 20 a).
3.3 Data Development
Flowchart
This study took the Populus simonii shelterbelt in
Bashang area of Hebei province, which is the source of sandstorms in Beijing
and Tianjin, as the research object. Based on the local historical climate
data, the dendroclimatic method was used to study the differences in the
response of healthy and declining poplars to climate change, thus providing
theoretical support for the management of the poplar shelterbelt in Bashang
area. The specific technical flowchart of this research is shown in Figure 1.
4 Data Results and Validation
4.1 Data Composition
(1) Basic information on the Populus simonii
shelterbelt plot in Bashang area of Hebei province, including the shelterbelt
types, latitude, longitude, altitude, crown density, herb density, DBH, tree
height, dieback rate and other basic information;
(2) Standard chronologies of healthy and declining poplars
and the main characteristic parameters and common interval spans, including the
standard deviation, mean inter-series correlation coefficient, first-order
autocorrelation coefficient, signal-to-noise ratio, express population siginal,
etc.
Figure 1 Data development technical
flowchart
(3) Correlation analysis between healthy and declining
poplars and climate factors, including: 1) Correlation analysis of healthy and
declining poplars with monthly and seasonal climate factors and 2) 20-year
moving correlation function analysis computed between the two chronologies and
the seasonal and monthly climate factors for the most important months.
(4) Time series and cross-dating test results of healthy
and declining poplars, including healthy and declining poplars tree-ring width
time series, and cross-dating test results of healthy and declining poplars
tree-ring width time series.
4.2 Data Results
Standard
chronologies of healthy and declining poplars were established, and the lengths
of the chronologies were 43 years and 36 years, respectively. The chronology of
healthy poplars showed an upward trend, and the chronology of declining poplars
showed a downward trend (Figure 2). According to the main characteristic parameters
of the chronology and the results of the public interval analysis, the
chronology of declining poplars was of high quality and contained abundant
climate signals (Table 3).
Table 3
Standard chronology statistics and results of common interval span
analysis of healthy and declining poplars
Statistics
|
Healthy poplar
|
Declining poplar
|
Latitude
and longitude
|
114.88??E, 41.34??N
|
114.88??E, 41.34??N
|
Altitude
(m)
|
1,379
|
1,379
|
Time span (A.D.)
|
1975-2017
|
1982-2017
|
Sample size
|
104
|
35
|
Average growth rate (mm/a)
|
2.533
|
2.570
|
Standard deviation
|
1.544
|
1.900
|
Correlation between trees
|
0.306
|
0.445
|
First-order autocorrelation
|
0.590
|
0.609
|
Signal-to-noise ratio
|
33.995
|
20.617
|
Express population signal
|
0.971
|
0.954
|
4.3 Data Validation
The correlation between the chronologies of healthy and
declining poplars and climate factors, shows that the growth of poplars is
mostly negatively correlated with temperature factors, and mostly positively
correlated with precipitation, relative humidity, and PDSI (Table 4). This
result is more consistent with the response of poplar growth to climate in
semi-arid area (southern part of the Greater Xing??an Mountains)[24].
The chronology of declining poplars contains more climate signals than that of
healthy poplars, which is consistent with the standard deviation in the
characteristic parameters of the standard chronology. A larger standard
deviation corresponds to a greater amount of climate information, and a larger
first-order autocorrelation coefficient corresponds to a greater number of
climatic signals included in the previous year. The statistical characteristics
showed that the growth of declining poplars were more affected by the climate
factors of the previous year while the growth of healthy poplars were significantly
correlated with the temperature factors in December of the previous year and
the precipitation and relative humidity in September of the previous year (P<0.05).
Declining poplars were significantly positively correlated with the
precipitation in September and November of the previous year, relative humidity
in September of the previous year, and the PDSI from September to December of
the previous year (P<0.05).
Figure 2 Standard tree-ring
chronologies of healthy and declining Populus simonii forest
|
The
growth of healthy and declining poplars in this area has a stronger response to
monthly temperature factors and the PDSI than seasonal temperature factors.
Seasonal precipitation and relative humidity had a greater impact on healthy
and declining poplars than on the single-month scale. The accumulated
precipitation and relative humidity have a greater effect on the growth of
poplars. As the temperature in this area increases and precipitation decreases,
the factors that affect the growth of declining poplars have changed from
temperature to moisture, which is consistent with the changes in local climate
factors[15].
Table 4 Correlations between chronologies of
healthy and declining poplars and climate factors
Month
|
Healthy poplars
|
Declining poplars
|
TMP
|
TMX
|
TMN
|
PRE
|
RH
|
PDSI
|
TMP
|
TMX
|
TMN
|
PRE
|
RH
|
PDSI
|
‒6
|
0.10
|
0.08
|
0.14
|
0.02
|
0.00
|
‒0.03
|
‒0.21
|
‒0.19
|
‒0.21
|
0.10
|
0.01
|
0.04
|
‒7
|
0.08
|
0.07
|
0.08
|
‒0.07
|
‒0.02
|
‒0.02
|
‒0.06
|
‒0.09
|
0.02
|
0.16
|
0.12
|
0.07
|
‒8
|
‒0.07
|
‒0.06
|
‒0.11
|
0.24
|
0.09
|
0.03
|
‒0.06
|
0.02
|
‒0.21
|
‒0.01
|
0.00
|
0.09
|
‒9
|
0.06
|
0.00
|
0.09
|
0.28*
|
0.35*
|
0.09
|
‒0.21
|
‒0.30
|
‒0.07
|
0.37*
|
0.31*
|
0.32*
|
‒10
|
‒0.11
|
‒0.15
|
‒0.06
|
0.17
|
0.31
|
0.20
|
‒0.25
|
‒0.26
|
‒0.25
|
0.09
|
0.18
|
0.38*
|
‒11
|
‒0.16
|
‒0.16
|
‒0.19
|
0.15
|
0.20
|
0.20
|
‒0.09
|
‒0.11
|
‒0.13
|
0.40*
|
0.18
|
0.42**
|
‒12
|
‒0.27*
|
‒0.30*
|
‒0.26*
|
0.16
|
0.21
|
0.15
|
‒0.08
|
‒0.11
|
‒0.14
|
0.23
|
0.27
|
0.37*
|
1
|
‒0.14
|
‒0.17
|
‒0.12
|
‒0.20
|
0.18
|
0.17
|
‒0.19
|
‒0.21
|
‒0.20
|
0.08
|
0.22
|
0.41*
|
2
|
‒0.04
|
0.02
|
‒0.06
|
‒0.01
|
‒0.20
|
0.16
|
‒0.10
|
‒0.05
|
‒0.12
|
‒0.20
|
0.00
|
0.36*
|
3
|
‒0.12
|
‒0.14
|
‒0.06
|
0.09
|
0.04
|
0.17
|
‒0.04
|
‒0.10
|
0.07
|
0.08
|
0.14
|
0.33*
|
4
|
‒0.44**
|
‒0.45**
|
‒0.37**
|
0.06
|
0.06
|
0.16
|
‒0.46**
|
‒0.44**
|
‒0.47**
|
‒0.30
|
‒0.20
|
0.18
|
5
|
0.01
|
0.03
|
0.05
|
‒0.01
|
0.16
|
0.15
|
‒0.05
|
‒0.04
|
‒0.11
|
‒0.07
|
0.03
|
0.18
|
6
|
‒0.02
|
‒0.08
|
0.09
|
0.10
|
0.23
|
0.27
|
‒0.18
|
‒0.21
|
‒0.13
|
0.23
|
0.12
|
0.45**
|
7
|
‒0.18
|
‒0.17
|
‒0.16
|
0.14
|
0.13
|
0.26
|
‒0.26*
|
‒0.33*
|
‒0.07
|
0.51**
|
0.45**
|
0.44**
|
8
|
0.03
|
0.00
|
0.11
|
‒0.04
|
0.16
|
0.30
|
0.09
|
0.06
|
0.11
|
‒0.07
|
0.17
|
0.51**
|
9
|
‒0.24
|
‒0.14
|
‒0.34
|
‒0.02
|
0.03
|
0.14
|
‒0.34*
|
‒0.30*
|
‒0.34*
|
0.11
|
0.10
|
0.34*
|
10
|
‒0.04
|
0.00
|
‒0.06
|
0.13
|
0.16
|
0.20
|
‒0.41*
|
‒0.35*
|
‒0.38*
|
0.05
|
0.20
|
0.35*
|
Notes:
TMP, mean temperature; TMN, minimum temperature; TMX, maximum temperature; PRE,
precipitation; RH, mean relative humidity; PDSI, Palmer drought severity index;
* P < 0.05, ** P < 0.01.
5 Conclusion
The standard
chronologies of healthy and declining poplars in Bashang area of Hebei province
was established. The data for healthy and declining poplars were collected from
1975-2017 and 1982-2017 respectively. Through correlation and moving correlation
analyses, the responses of healthy and declining poplars to climate change were
compared. Finally, it was concluded that drought is the main driving factor for
the degradation and even death of poplars in the region. This dataset enriches
the international tree ring database, provides a better understanding of the
temporal variations in the growth of healthy and declining poplars in response
to climate, and can provide basic data for the field of global climate change.
Author Contributions
Xin, Z. B., and Li, Z. S. made the overall design the
algorithms of the dataset. Liu, Y. L. and Keyimu, M. finished the data
processing and analysis. Li, Z. S. provided WINDENDRO, a tree ring analysis
platform, and performed data verification. Liu, Y. L. wrote the paper.
Conflicts
of Interest
The authors declare no conflicts of interest.
References
[1]
Zheng, C.
Y., Xu, Z. Q., Ma, C. M., et al. Soil properties of degraded shelter
forests in Bashang Plateau of northwestern Hebei province [J]. Journal of
Soil and Water Conservation, 2016, 30(1): 203‒207.
[2]
Xing, H. F.
Analysis on the cause of death of Bashang poplar shelter forest [J]. The
Journal of Hebei Forestry Science and Technology, 2015, (1): 76‒77.
[3]
Miao, B.,
Meng, P., Zhang, J. S., et al. Difference of water relationships of poplar
trees in Zhangbei county, Hebei, China based on stable isotope and thermal
dissipation method [J]. Chinese Journal of Applied Ecology, 2017, 28(7):
2111‒2118.
[4]
Zhang, H.,
Cao, J., Wang, H. B., et al. Water utilization characteristics of the
degraded poplar shelterbelts in Zhangbei, Hebei, China [J]. Chinese Journal
of Applied Ecology, 2018, 29(5): 1381‒1388
[5]
Cheng, M.
Y., Zhang, Y., Cui, S., et al. Study on poplar degeneration in Zhangbei
county, Hebei province??a case study in Panchengying [J]. Forest Resources
Management, 2015, (1): 152‒155, 167.
[6]
Sun, S. J.,
Li, C. Y., He, C. X., et al. Retrospective analysis of the poplar
plantation degradation based on stable carbon isotope of tree rings in Zhangbei
county, Hebei, China [J]. Chinese Journal of Applied Ecology, 2017,
28(7): 2119‒2127.
[7]
Li, X. H.,
Liu, X. L. Research progress on the degradation and death of shelterbelt caused
by drought [J]. Protection Forest Science and Technology, 2016, (12):
59‒60.
[8]
Zheng, C.
Y., Xu, Z. Q., Ma, C. M., et al. The
factors influencing the poplar shelterbelt degradation in the Bashang Plateau
of Northwest Hebei province [J]. Forest Resources Management, 2018, (1):
9‒15,147.
[9]
Fritts, H. C. Tree Rings
and Climate [M]. New York: Academic Press, 1976.
[10]
Liu, Y. L.,
Xin, Z. B., Li, Z. S., et al. Climate effect on the radial growth of Populus
Simonii in Bashang area of Hebei province [J/DB/OL]. Digital Journal of
Global Change Data Repository, 2021. https://doi.org/10.3974/
geodb.2021.08.01.V1. https://cstr.escience.org.cn/CSTR:20146.11.2021.08.01.V1.
[11] GCdataPR Editorial Office. GCdataPR data sharing policy [OL].
https://doi.org/10.3974/dp.policy.2014.05 (Updated 2017).
[12] Shen, H. Y., Wang, M. M., Liang, X. Y., et al. Soil
properties of shelterbelts in the Bashang area of Hebei province [J]. Science
of Soil and Water Conservation, 2021, 19(5): 63-71.
[13]
Sun, L. B.,
Yu, X. X., Chen, L. H., et al. Degradation of litter and soil water
conservation function of poplar plantation in Bashang Plateau [J]. Journal
of Soil and Water Conservation, 2019, 33(1): 104‒110.
[14]
Su, W. X.,
Li, Z., Chen, S. Q., et al. Evolution trend of vegetation coverage and
its risk assessment in the Bashang region in Hebei province [J]. Arid Zone
Research, 2018, 35(3): 686‒694.
[15]
Liu, Y. L.,
Xin, Z. B., Li, Z. S., et al. Climate effect on the radial growth of Populus
simonii in Northwest of Hebei for last four decades [J]. Acta Ecologica
Sinica, 2020, 40(24): 9108‒9119.
[16]
Stokes, M.
A., Smiley, T. L. An Introduction to Tree Ring Dating [M]. Chicago: University
of Chicago Press, 1968.
[17]
Holmes, R.
L. Computer-assisted quality control in tree-ring dating and measurement [J]. Tree-Ring
Bulletin, 1983, 43: 51‒67.
[18] Brubaker, L. B., Fritts, H. C. Tree rings and climate [J]. Ecology,
1977, 58(6): 1400‒1401.
[19]
Bunn, A. G. A dendrochronology program library in R (dplR) [J]. Dendrochronologia,
2008, 26(2): 115‒124.
[20]
Shao, X.
M., Wu, X. D. Tree-ring chronologies for Pinus aemandi Franch from Huashan,
China [J]. Acta Geographica Sinica, 1994, 61(2): 174‒181.
[21] Harris, I., Jones, P. D., Osborn, T. J., et al. Updated
high-resolution grids of monthly climatic observations-the CRU TS3.10 dataset [J].
International Journal of Climatology, 2014, 34(3): 623-642.
[22]
Biondi, F.,
Waikul, K. DENDROCLIM2002: a C++ program for statistical calibration of climate
signals in tree-ring chronologies [J]. Computers & Geosciences,
2004, 30(3): 303‒311.
[23]
Dong, Z.
P., Zheng, H. Z., Fang, K. Y., et al. Responses of tree-ring width of Pinus
massiniana in Sanming, Fujian Province to climate change [J]. Journal of
Subtropical Resources and Environment, 2014, 9 (1): 1‒7.
[24]
He, M.,
Wei, J. S., Shi, L., et al. The response of radial growth and death of Populus
davidiana to regional climate change in southern Greater Xing??an Mountains
[J]. Chinese Journal of Ecology, 2018, 37(11): 3237‒3244.