Water Use Efficiency of Grain Crops Dataset in Hebei
Province of China (1995–2019)
Pan, P. P.1,2,3,4* Miao, J. X.1,2,3,4 Wang, X. X.5* Li, L. S.1,2,3,4 Wen, J. Y.6 Wang, X. Y.7
1. School of Geographical Science, Hebei Normal University,
Shijiazhuang 050024, China;
2. Hebei Key Research Institute of Humanities and Social
Sciences at Universities ??GeoComputation and Planning Center of Hebei Normal
University??, Shijiazhuang 050024, China;
3. Hebei Key Laboratory of Environmental Change and Ecological
Construction, Shijiazhuang 050024, China;
4. Hebei Technology
Innovation Center for Remote Sensing Identification of Environmental Change,
Shijiazhuang 050024, China;
5. The Bureau of Natural Resources and Planning of Hebei
Xiong??an New District Management Committee, Baoding 070001, China;
6. Beijing Capital Planning and Design Engineering
Consulting and Development Co., Beijing 100045, China;
7. School of Ecology and Environmental Sciences, Ningxia
University, Yinchuan 750021, China
Abstract: Water scarcity
is a crucial factor limiting crop yields in Hebei Province, which is a typical
grain-producing region in China. Improving the efficiency of water use of grain
crops on farmland is essential for ensuring regional food security and
achieving sustainable agricultural development. Author base on dataset of the
efficiency of water use of grain crops in Hebei Province of China (1995–2019)
was developed by integrating data from the meteorological database of China,
the United Nations Food and Agriculture Organization??s (FAO) CROP database,
field surveys, rural statistical yearbooks, and the super-efficiency SBM model,
spatial econometric model, and GTWR model. The dataset contains the following:
(1) data on boundaries of the study area; (2) data on the blue water, green
water, and gray water footprints of grain crops in 1995, 2000, 2005, 2010,
2015, and 2019; (3) data on the trends of changes in the water footprints of
food crops from 1995 to 2019; (4) efficiency of water use of grain crops at the
county and regional scales in 1995, 2000, 2005, 2010, 2015, and 2019; (5)
spatial effects, spillover effects, and spatial heterogeneity of the factors
influencing the efficiency of water use of grain crops; and (6) the Theil
coefficient and the rates of contribution of the four partitions. The dataset
has been archived in .xlsx and .shp data formats, and consists of 65 data files
with a total size of 4.09 MB (compressed into one file with a size of 2.36 MB).
Keywords: Hebei Province; SBM; water footprint; water use efficiency
of grain crops; influential factors
DOI: https://doi.org/10.3974/geodp.2024.01.01
CSTR: https://cstr.escience.org.cn/CSTR:20146.14.2024.01.01
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.2024.02.04.V1 or
https://cstr.escience.org.cn/CSTR:20146.11.2024.02.04.V1.
1
Introduction
Water resources constitute the core element of food
production, and the highly efficient use of water for grain crops on farmland
in major food-producing areas that are also scarce in water has a direct impact
on national food security and regional ecological security[1]. The
National 14th Five-Year Plan for the Construction of a Water-saving Society in
China notes that the shortage of water resources is an important bottleneck in
the country??s socio-economic development. In particular in the context of
global changes and the increasing demand for food, agricultural water shortages
in China are becoming increasingly severe[2]. Moreover, inefficient
methods of irrigation for agricultural production, the serious pollution of
major water bodies in the country, and unreasonable use of the available water
resources have accentuated the problem of China??s agro-ecological security[3].
Hebei Province is a traditional region of agricultural production in China that
suffers from a serious shortage of water resources, because of which the
sustained growth in its production of food crops comes at the expense of the
large-scale exploitation of groundwater that has led to a continual decline in
the water table. ??Water for food?? has gradually emerged as the feature of
regional food production, and the high intensity of water use not only
significantly disturbs the recycling of water resources, but also triggers a
series of problems including ground subsidence, soil salinization, and water
pollution[4]. This poses a serious threat to sustainable food
production and the ecological environment[5].
Evaluating the efficiency of water use of grain crops, and
identifying and regulating the factors influencing it provides an important
foundation for optimizing the regional planting structure and efficiently
managing the water resources. It can also help alleviate the conflict between
the supply of agricultural water resources and the demand for them to ensure
regional water and food security[6]. The indicators of water input
used in prevalent studies in the area ignore the effective precipitation such
that the output of the relevant models does not fully reflect the negative
impacts of agricultural production on water resources and the water
environment. The multi-perspective measurement of the efficiency of water use
of grain crops and the evaluation of factors influencing it are essential for
optimally using water resources[1]. In this study we consider wheat
and maize, the two major grain crops grown in Hebei Province, as the objects of
research, apply improved methods to measure the efficiency of water use and
unexpected outputs, and introduce the water footprint, as an indicator that can
comprehensively measure the water use and food output, to the SBM model (Slacks-based Measure of Super-efficiency Model)[7]. We then systematically construct a system of indicators that
uses the blue water and green water footprints, planting area, application of
discounted fertilizer, total power consumed by agricultural machinery, and
agricultural labor as the input indicators, generates the agricultural GDP as
the desired output indicator, and uses the gray water footprint as the
non-desired output indicator. We use data from meteorological stations, rural
statistical yearbooks, the FAO CROP database, and field surveys in a water
footprint-based super-efficiency SBM model to calculate the multi-scale
efficiency of water use of grain crops in Hebei Province by determining their
blue, green, and gray water footprints from 1995 to 2019. Following this, we
construct a system of indices of the factors influencing the efficiency of
water use of grain crops by considering the actual situation in the study area,
and use a spatial measurement model and the GTWR model (Geographically and Temporally
Weighted Regression Model) to
identify the key elements driving the efficiency of water use of grain crops
and their spatial heterogeneity. This study provides a basis for subsequent
research in the area as well as for decision-making to improve the efficiency
of water use of grain crops in Hebei Province and other major grain-producing
areas. This can in turn lead to the efficient use of agricultural water
resources, and can ensure regional hydro-ecological security as well as the
green and sustainable development of agriculture.
2 Metadata
of the Dataset
The metadata for the dataset of the efficiency of water use
of grain crops in Hebei Province of China (1995–2019)[8] are
summarized in Table 1. They include the full name of the dataset, its short
name, authors, year in which it was published, data format, data size, data
files, data publisher, and data sharing policy, etc.
Table 1 Metadata summary of the Water
use efficiency of grain crops dataset in Hebei Province of China (1995–2019)
Items
|
Description
|
Dataset full name
|
Water use efficiency of grain crops dataset in Hebei
Province of China (1995–2019)
|
Dataset short name
|
WaterUseEfficiencySBM_Hebei_1995_2019
|
Authors
|
Pan, P. P. S-5072-2016, Hebei Normal University,
panpeipei626@163.com
Miao, J. X. Hebei Normal University, miao_jia_xin@163.com
|
|
Wang, X. X. S-6861-2017, The Bureau of Natural Resources
and Planning of Hebei Xiong'an New District Management Committee, Baoding,
18931179072@163.com
Li, L. S., Hebei Normal University, lilinsi9360@163.com
Wen, J. Y., Beijing Capital Planning and Design
Engineering Consulting and Development Co. Beijing, wenjiayu329@163.com
Wang, X. X., School of Ecology and Environmental Sciences,
Ningxia University, wxy_whu@163.com
|
Geographical region
|
Hebei Province: 36??05??N–42??37??N, 113??11??E–119??45??E
|
Year
|
1995–2019
|
Data format
|
.xlsx, .shp
|
|
|
Data size
|
2.36 MB (after compression)
|
|
|
Data files
|
65 data files
|
Foundation
|
Hebei Provincial Social Science Foundation (HB20GL042)
|
Data computing environment
|
CROPWAT model; super-efficiency SBM model; spatial
econometric model; ArcGIS
|
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
|
(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[9]
|
Communication and searchable system
|
DOI,
CSTR, Crossref, DCI, CSCD, CNKI, SciEngine, WDS/ISC, GEOSS
|
3 Methods
of Data Development
Dataset development included the following work: (1) The
green and blue water footprints of the grain crops were calculated based on the
acquired meteorological data, data on the area of planting of food crops, and
the demand for water in the growing period. The gray water footprint was
calculated based on the application of discounted fertilizer to the grain
crops. This yielded data on the blue, green, and gray water footprints of grain
crops in the county units of Hebei Province in 1995, 2000, 2005, 2010, 2015,
and 2019 as well as the trends of changes in them. (2) Statistical data and
measurements of the water footprint were used in the super-efficiency SBM model
to calculate the efficiency of water use of grain crops at the two scales of
counties and subdivisions in Hebei Province in 1995, 2000, 2005, 2010, 2015,
and 2019. (3) Regional differences in the efficiency of water use of grain
crops were analyzed based on the Theil coefficient. Values of the Theil
coefficient and the rates of contributions of the four major subregions in Hebei
Province to it were obtained. (4) The causes and spatial effects of differences
in the efficiency of water use of grain crops were examined based on the
spatial econometric model, and the spatio-temporal geographical- weighted
regression (GTWR) model was used to analyze the spatial distribution of the
main factors in this regard.
3.1
Algorithmic
The above-mentioned dataset mainly uses methods to measure
the water footprint, the super-efficiency SBM model, kernel density estimation,
Thiel coefficient, spatial econometric model, and GTWR model[10].
The water footprint can describe the occupancy of water resources based on
consumption[11], and includes blue, green, and gray water
footprints. It is a more comprehensive method for measuring the occupancy of
water resources than the traditional means of water measurement[12].
The super-efficiency SBM model was proposed by Tone based on the data
envelopment analysis (DEA) model[13]. The dataset uses the
super-efficiency SBM model based on the water footprint to measure the
efficiency of water use of grain crops, and compensates for the lack of
consideration of undesirable outputs in the DEA method that may lead to
deviations in the results[14]. Kernel density estimation uses a
continuous curve of density to represent the characteristics of distribution of
efficiency[15]. The Theil coefficient is used to analyze differences
in the efficiency of regional water use and their main sources[16].
These indicators are used to analyze the trends of change and regional differences
in the efficiency of water use of grain crops in Hebei Province. Finally, the Spatial
Dubin model (SDM model), spatial econometric model, and GTWR model are used to
explore the spatial and spillover effects of the efficiency of water use of
grain crops as well as the spatial-temporal characteristics of the distribution
of the factors influencing it in the study area.
3.2
Technical Route
We used meteorological data, crop-related data, data on
agricultural production and administrative divisions, the super-efficiency SBM
model, spatial econometric model, and GTWR model from the above-mentioned
dataset to calculate the efficiency of water use of grain crops in 139 county
units of Hebei Province from 1995 to 2019. The steps are as follows (Figure 1).
(1) Basic data collection and collation
The basic data used in this study are
provided in Table 2.
Data on administrative divisions: The 139
county units of Hebei considered in this study were based on the division of
administrative regions in the province in 2015, in which the municipal
districts were merged into one county unit. We used the literature[17]
to divide Hebei Province into four regions: northwest Hebei (Zhangjiakou and
Chengde), coastal areas (Cangzhou, Tangshan, and Qinhuangdao), areas
surrounding Beijing and Tianjin (Baoding and Langfang), and south-central Hebei
(Shijiazhuang, Hengshui, Xingtai, and Handan).
Meteorological data, coefficients of
grain crops, and data on growth period: Meteorological data
were obtained from the regional data center for resources and environmental
science,
and included the temperature, humidity, precipitation, wind speed, and hours of
sunshine in cities in Hebei Province. Data on the coefficients and period of
growth of the grain
crops were
obtained by adjusting information obtained from the CROP database of the FAO by
using data obtained from field surveys in various areas as well as past
research, as shown in Table 3. This information was then used along with the
CROPWAT model, developed by the FAO, to calculate the evapotranspiration of
blue and green water (mm) during crop growth.
Figure 1 Technological
roadmap of the dataset development
Table 2 Basic data
information
Data source
|
Data type
|
Time (date)
|
Scale bar or resolution
|
National Catalogue Service For Geographic Information
|
Data on administrative divisions
|
2015
|
1:1 million
|
China Meteorological Administration
|
Meteorological data
|
1995, 2000, 2005, 2010, 2015, 2019
|
Municipal units
|
The UN FAO CROP database/field work
|
Grain crops coefficient and fertility period
|
Field work on July 7–8, 2021
|
County units
|
Hebei Province Rural Statistical Yearbook
|
Economic and social statistics
|
1995, 2000, 2005, 2010, 2015, 2019
|
County units
|
Table 3 Data
on the coefficients of grain crops and their fertility period in Hebei Province
Grain
crop
|
Fertility
period
|
Grain
crop coefficient
|
Initial
|
Development
|
Mid-season
|
Late
season
|
Wheat
|
9.28–6.13
|
0.43
|
0.90
|
1.10
|
0.49
|
Maize
|
6.16–9.25
|
0.40
|
0.81
|
1.17
|
0.88
|
Statistical economic and social
data: We obtained the relevant economic and social data from rural statistical
yearbooks of Hebei Province to calculate the efficiency of water use of grain
crops and determine the factors influencing it. Of the variables used to assess
the efficiency of water use[10] (excluding the blue, green, and gray
water footprints), the planting area was obtained from the statistical data,
while data on the other variables could not be directly obtained were refer to
the processing method of relevant research[18]. The variables used
to identify the factors influencing the efficiency of water use are shown in
Table 4, and included the annual precipitation, effective area of irrigation,
area over which the crops were sown, their primary industrial output value, per
capita net income of the rural residents in each county, urban population,
total population, and the amount of chemical fertilizer applied to the grain
crops.
Table 4 Factors
influencing the efficiency of water use of grain crops
|
Variable
name
|
Variable
code
|
Variable
interpretation
|
Independent
variables
|
Annual
precipitation
|
AP
|
Annual
precipitation (mm)
|
Effective
irrigation degree
|
EID
|
Effective
irrigated area/area of crops sown (%)
|
Agricultural
farming structure
|
AFS
|
Maize
sown area/area of grain crops sown (%)
|
Industrial
structure
|
IS
|
Agricultural output value/Primary industrial output
value (%)
|
Per
capita net income of rural residents
|
CDI
|
Per
capita net income of rural residents in all counties (Yuan)
|
Urbanization
level
|
UL
|
Urban
population/total population (%)
|
Density
of agricultural machinery
|
AGM
|
Farm
machinery production/area of crops sown (%)
|
Fertilizer
application intensity
|
FAI
|
Amount
of chemical fertilizer used/area of crops sown (%)
|
(2) Calculation of water
footprint of grain crops
The gray water footprint was
calculated based on the wheat–maize rotation in the study area. We used past
research to set the maximum allowable concentration and the rate of leaching of
nitrogen fertilizer to 10 mg/L (national maximum) and 10%, respectively[17],
and their minimum value (zero) was set to be that in nature.
(3) Calculation of efficiency of
water use of grain crops
We considered the water used for
irrigation and the effective precipitation, and set the gray water footprint as
the index of the undesired output[7]. The water footprint was
introduced to the super-efficiency SBM model to measure
the efficiency of water use of the grain crops. The water footprint in the
input index was calculated while the planting area was obtained from the
statistical data. Because the other input indicators could not be directly
obtained, we consulted past research[18], for them, and used the
weight coefficient method to calculate the relevant data for the two crops.
(4) Analyzing the spatio-temporal
variations in efficiency of water use of grain crops at different scales
We used kernel density
estimation, the Theil coefficient, and GIS-based spatial analysis to analyze
the spatio-temporal variations in the efficiency of water use of grain crops at
different scales (provincial, regional, and county) in Hebei Province. Data on
the administrative divisions of Hebei Province and the efficiency of water use
of grain crops in each county were required for this.
(5) Analyzing causes and effects
of spatial differences in efficiency of water use of grain crops
We used the actual status of
grain planting in Hebei Province in combination with prevalent research[2,19–21]
to identify eight indicators (Table 4) influencing the efficiency of water use
of grain crops. We then examined the causes of spatial differences in the
efficiency of water use and their spatial effects by using the spatial
econometric model. Given that there are three types of spatial econometric
models[22], we subjected them to tests of spatial autocorrelation
and model tests to determine the optimal model for representing the efficiency
of water use. The SDM model was finally chosen. This model required data on the
administrative divisions and input indicators of Hebei Province, and the
expected output and the undesired output of each indicator.
(6) Analyzing the spatio-temporal
heterogeneity of influential factors
We analyzed the spatio-temporal heterogeneity of various factors
influencing the efficiency of water use of crops in Hebei Province by using the
spatio-temporal geographically weighted model of regression. The main process
consisted of a multi-collinearity test, selection of influential factors, and
the execution of the GTWR model. The required data included the administrative
divisions of Hebei Province, efficiency of water use of grain crops, and the
factors influencing it (Table 4).
4 Data
Results and Validation
4.1
Data Composition
The dataset used to assess the efficiency of water use of
grain crops in Hebei Province (1995–2019) consisted of six parts: (1) data on
boundaries of the study area; (2) data on the blue water, green water, and gray
water footprints of grain crops in 1995, 2000, 2005, 2010, 2015, and 2019; (3)
data on the trends of changes in the water footprints of food crops from 1995
to 2019; (4) efficiency of water use of grain crops at the county and regional
scales in 1995, 2000, 2005, 2010, 2015, and 2019; (5) spatial effects,
spillover effects, and spatial heterogeneity of the factors influencing the
efficiency of water use of grain crops; and (6) the Theil coefficient and the
rates of contribution of the four partitions.
4.2
Data Results
(1) Spatio-temporal variations in water footprint of grain
crops in Hebei Province
The
blue, green, and gray water footprints represent the consumption of water for
irrigation, precipitation water used for irrigation, and the emission of
pollutants during crop growth, respectively. From 1995 to 2019, the total water
footprint of grain crops in Hebei Province was influenced by an increase in the
planting area, and exhibited an overall trend of increased with an annual
growth rate of 1.03%. The change in the blue water footprint of the crops was
relatively stable, their green and gray water footprints increased slightly,
and the rate of growth of the latter was higher and began to decrease in 2000.
On the whole, the proportion of blue and green water footprints of the crops
decreased while the proportion of their gray water footprint increased
significantly. Data on the spatial distribution of the blue, green, and gray
water footprints of the grain crops in Hebei are shown in Figures 2–4. The
high-value areas were concentrated in central and southern Hebei, and the
coastal areas, while low-value areas were distributed in the northwest Hebei,
and in areas northwest of Beijing and Tianjin. The overall pattern was low in
the northwest and high in the southeast. This is because the spatial occupation
of the main grain crops in Hebei Province gradually decreases from south to
north. The distribution of planted wheat decreased from southwest to northeast, while that of planted corn exhibited
a regular distribution of central > southern > northern[23].
In addition, the high-yield areas for grain crops consumed large amounts of
blue and green water while emitting large volumes of pollutants, because of which
their gray water footprint was large.
(2) Spatio-temporal heterogeneity of efficiency of water
use of grain crops at different spatial scales
There were spatial
differences in the efficiency of water use of the grain crops at the
provincial, regional, and county scales in Hebei. The differences in the
distributions of the efficiency of water use of grain crops was prominent at
the provincial scale, and exhibited trends of decrease and increase in
1995–2000 and 2000–2015, respectively. By 2019, the
Figure 2 Maps of the blue water
footprint of grain crops in Hebei Province (1995–2019)
Figure 3 Maps of the
green water footprint of grain crops in Hebei Province (1995–2019)
Figure 4 Maps of the
gray water footprint of grain crops in Hebei Province (1995–2019)
efficiency of water use in most counties had decreased
while the polarization of its regional efficiency had increased.
Figure 5 shows that the spatial pattern of the efficiency
of water use of grain crops in the four major regions of Hebei changed
significantly from 1995 to 2019. Northwest Hebei exhibited a downward trend, while the coastal areas, and
areas surrounding Beijing and Tianjin as well as south-central Hebei exhibited
a fluctuating downward trend. The range of change in each region was narrow
from 2000 to 2015 and the spatial distribution was relatively stable,
exhibiting a pattern of low in northwest Hebei and high in areas surrounding
Beijing and Tianjin. The efficiency of water use in northwest Hebei
significantly improved in 2019 while that of the other regions significantly
decreased. It gradually decreased from north to south, which was consistent
with its spatial distribution in 1995. An analysis of the regional Theil
coefficient and the rates of contribution of the four regions[10]
yielded clear regional differences in the overall efficiency of water use of
grain crops in Hebei that mainly originated from within each region.
Differences in the efficiency of water use of grain crops within south-central
Hebei decreased from 1995 to 2019. This difference was large within northwest
Hebei, the rate of contribution of which to the overall regional differences in
the efficiency of water use increased. The coastal areas as well as areas
surrounding Beijing and Tianjin made minor contributions to the difference in
the efficiency of water use of grain crops, and the range of changes in
efficiency within these regions was narrow.
Figure 6 shows that
the efficiency of water use of food crops as well as its spatial pattern
changed significantly at the county level, while its spatial distribution in
plain areas was relatively stable. Zones with high and median efficiencies
increased from 2000 to 2015, but the patterns of a significant expansion in
low-value areas and a significant decrease in median-values areas were evident
from 2015 to 2019. The high-value areas in the western and northern mountainous
and hilly areas decreased. Overall, the range of spatial
Figure 5 Maps of
efficiency of water use of grain crops in the four regions of Hebei Province (1995–2019)
Figure 6 Maps of
efficiency of water use of grain crops in Hebei Province (1995–2019)
distribution of low-value areas in Hebei Province expanded
from 1995 to 2019 while that of high- and median-value areas decreased.
(3) Spatial heterogeneity of factors influencing the
efficiency of water use grain crops at different scales
The
factors influencing the efficiency of water use of food crops included those
that had a direct impact (local effects) and others that had indirect spillover
effects (effects on surrounding areas).Our results[10] show that
CDI, UL, and AGM had positive effects and significant spillover effects, while
EID and IS had a positive effect but insignificant spillover effects. Owing to
the insufficient degree of optimization of AFS in Hebei, it had a negative
effect on the efficiency of water use of grain crops. FAI had a negative effect
and a prominent spillover effect, while AP had a minor influence on the
efficiency of water use. We also analyzed the spatial differences among the
influence of these factors on the efficiency of water use. EID and IS had a
large influence on the efficiency of water use in the north but a minor
influence in the south. The influence of UL decreased from the northeast to the
southwest, while the area under the negative influence of AGM was mainly
distributed in the northwest. The area under the negative influence of FAI and
AFS was large, and had an opposite pattern of distribution. This suggests that
reducing fertilizer use and optimizing the planting structure based on regional
differences are important ways to improve the efficiency of water consumption
of food crops.
4.3
Data Validation
There are three forms of Spatial econometric model that
need to undergo data verification to select the most suitable model. We used[10]
the SDM model with fixed spatio-temporal effects based on the test of
significance of spatial autocorrelation, Lagrange Multiplier test, Likelihood Ration
test, and Hausman test. The results showed that the model fit well and passed
the significance test, which revealed the obvious spatial effect and spillover
effect of the water use efficiency of grain crops in Hebei Province.
We
analyzed the efficiency of water use of food crops and the factors influencing
it based on statistical data. In practice, there is no specific location and
observed value that can be used for comparative analysis. We verified the
results in comparison with past work on the study area. The results showed that
the efficiency of water consumption of grain crops in Hebei Province was
generally poor, and exhibited a significant downward trend after 2015 that is
in line with the results of related studies[24]. The parameter R2 of the model of regression
was adjusted to 0.948 after applying the GTWR model, and the outcome was
consistent with that of certain past studies: That is, EID had a positive
effect on the efficiency of water use of food crops[24–26], while
AFS, AP, and FAI had a negative influence on it[3,24,25,27].
However, the results of some past studies were inconsistent with our
conclusions. They have claimed that FAI has a positive effect on the efficiency
of water use[28]. This is because these studies did not consider the
unexpected output in this scenario, because of which their results do not
reflect the actual efficiency of water use by crops. In addition, pollution due
to nitrogen fertilizers is considered to be an index of pollution of water
resources. Phosphate fertilizers and other options should be considered in
future research to reduce pollution.
5 Discussion and Conclusion
Water shortage has and will continue to restrict
sustainable regional grain production and the security of the ecological
environment. Improving the efficiency of water use for food crops in major
grain-producing areas that are also afflicted with water shortages is the key
to alleviating the tension between the supply of water resources and the demand
for them while ensuring food and ecological
security[24]. In this study, we considered 139 county units of Hebei
Province to calculate the efficiency of water consumption of grain crops under
an improved multi-factor input–output framework, and analyzed the spatial
effects of factors influencing this efficiency by integrating the model of
spatial measurement with the GTWR model. The results showed that the total
water footprint of grain crops in Hebei Province grew from 24.601 billion m3
in 1995 to 31.494 billion m3 in 2015, and the gray water footprint
had the largest rate of annual growth in this period. The overall efficiency of
water use of grain crops was poor, and exhibited a downward trend later in the
study period. The difference in the efficiency of water use of grain crops in
northwest Hebei was the largest, and made an increasing contribution to the
overall difference in efficiency across the province. The factors influencing
the efficiency of water use exhibited prominent spatial and spillover effects.
UL and AGM had a positive effect on it as well as significant spillover
effects, while EID and IS also had a positive effect but an insignificant
spillover effect. FAI and AFS had a negative effect on the efficiency of water
use, while the spillover effect of FAI was prominent.
We used the dataset to comprehensively evaluate the
efficiency of water use of grain crops from multiple perspectives, and explored
the spatial effects and spatial heterogeneity of the various factors
influencing it. This provides basic data to support decision-making on the
optimal use of water resources and making adjustments to the agricultural
planting structure of farmland in Hebei Province as well as other major
grain-producing areas that have limited water resources. The results showed
that the planting structure and intensity of use of chemical fertilizers
restrict improvements in the regional efficiency of water use, which means that
it is important to appropriately alter the planting structure and promote green
agriculture. However, we did not consider the actual impact of water-saving
irrigation in this study. A field survey from 2022 to 2023 found the
water-saving facilities in deep groundwater funnel areas of Hebei (Jizhou,
Zaoqiang, Hengshui, Cangzhou, and Nangong) have been enabled, but cannot meet
the demand of food crops irrigation. Therefore, the recognition degree and utilization
rate of farmers in some areas for this are low, affect the improvement of water
efficiency, the follow-up should be comprehensive evaluation of the actual
impact of water-saving irrigation on effective irrigation area. Moreover, due
to limitations in data acquisition, we were unable to analyze the efficiency of
water use of a wider variety of grain crops. There is also a lack of research
on the evolution of the efficiency of water use of grain crops over the long
term at the county level. Future research in the area should seek to address
these limitations.
Author Contributions
Pan, P. P., Wang, X.
X. and Wang, X. Y. designed the algorithms of dataset. Pan, P. P., Miao, J. X.,
and Wen, J. Y. contributed to the data processing and analysis of water use
efficiency for grain crops. Pan, P. P. and Wen, J. Y. designed the model and
the algorithm. Wen, J. Y. and Li, L. S. did the data verification. Pan, P. P.
and Miao, J. X. wrote the data paper.
Conflicts of Interest
The
authors declare no conflicts of interest.
References
[1]
Fang, D.
L., Wang, J., Liu, J. J., et al. Study on spatial-temporal
differentiation characteristics of agricultural water use efficiency and
influencing factors under the combination of multiple models [J/OL]. Water
Saving Irrigation, 2024: 1-18.
http://kns.cnki.net/kcms/detail/42.1420.TV.20240227.1129.024.html.
[2]
Chang, M., Wang, X. Q., Jia, B. Z. Driving factors and Spatial-temporal
differentiation of irrigation water use efficiency in China: a case study of
rice, wheat and maize [J]. Resources Science, 2019, 41(11): 2032–2042.
[3]
Wu, Z. D.,
Zhang, Y., Wu, Z. L., et al. Study on the Spatial-temporal evolution and
influencing factors of economic efficiency of generalized water use for crop production
in China??s major grain-producing area [J]. Resources and Environment in the
Yangtze Basin, 2021, 30(11): 2763–2777.
[4]
Yan, Z. X.,
Zhang, W. Y., Liu, X. W., et al. Grain yield and water productivity of
winter wheat controlled by irrigation regime and manure substitution in the
North China Plain [J] Agricultural Water Management, 2024, 295: 108731.
[5]
Li, W.,
Jiang, S., Zhao, Y., et al. Safety evaluation of water-energy-food
coupling system in Beijing-Tianjin-Hebei region [J]. Water Resources
Protection, 2023, 39(5): 39–48.
[6]
Cui, S. M., Wu, M. Y., Wang, X. J., et al.
Optimization of planting structure in pumping irrigation system based on water
footprint and water-energy-grain nexus [J]. Journal of Hydraulic Engineering,
2023, 54(8): 967–977.
[7]
Tian, J.
X., Dang, X. H., Yang, Z., et al. Analysis of water security risk of
cash forest expansion in the Loess Plateau in terms of water footprint: A case
study of apple planting [J]. Journal of Natural Resources, 2022, 37(10):
2750–2762.
[8]
Pan, P. P.,
Miao, J. X., Wang, X. X., et al. Water use efficiency of grain crops
dataset in Hebei Province of China (1995–2019) [J/DB/OL]. Digital Journal of
Global Change Data Repository, 2024. https://doi.org/ 10.3974/geodb.2024.02.04.V1.
https://cstr.escience.org.cn/CSTR:20146.11.2024.02.04.V1.
[9]
GCdataPR
Editorial Office. GCdataPR data sharing policy [OL].
https://doi.org/10.3974/dp.policy.2014.05 (Updated 2017).
[10]
Wen, J. Y.,
Pan, P. P., Wang, X. X., et al. Spatial-temporal characteristics and
influencing factors of water use efficiency of major grain crops in Hebei
Province [J]. Journal of Arid Land Resources and Environment, 2023,
37(8): 117–127.
[11]
Yin, M. X.,
Zhao, X. G. Evaluation of water resource in Inner Mongolia from 1990 to 2016
based on water footprint theory [J]. Journal of Arid Land Resources and
Environment, 2018, 32(6): 120–125.
[12]
Mekonnen, M. M., Hoekstra, A. Y. The
green, blue and grey water footprint of crops and derived crop products [J]. Hydrology
and Earth System Sciences, 2011, 15(139): 1577–1600.
[13]
Tone, K. A.
slacks-based measure of super-efficiency in data envelopment analysis [J]. European
Journal of Operational Research, 2002, 143(1): 32–41.
[14]
Liu, W. B.,
Meng, W., Li, X. X., et al. DEA models with undesirable inputs and
outputs [J] Annals of Operations Research, 2010, 173(1): 177–194.
[15]
Zheng, Z. W.,
Jiang, C., Wang, J., et al. Spatiotemporal evolution of urban theft
crimes and mechanism in the context of regular COVID-19 pandemic prevention and
control: A case study of Haining, Zhejiang [J]. Progress in Geography,
2023, 42(2): 341–352.
[16]
Di, Q. B.,
Chen, X. L., Hou, Z. W. Regional differences and key pathway identification of
the coordinated governance of pollution control and carbon emission reduction
in the three major urban agglomerations of China under the ??Double-Carbon??
targets [J]. Resources Science, 2022, 44(6): 1155–1167.
[17]
Zhao, Q. S., Pan, P. P., Wang, X. X., et al. A study of cultivated
land utilization efficiency and its influencing factors in Hebei Province based
on DEA-Malmquist index [J]. Arid Zone Research, 2021, 38(4): 1162–1171.
[18]
Tan, Z. X., Guo, X. Y. Evaluation and analysis of Chinese grain
production water use efficiency based on Super-
efficiency DEA Model [J]. Transactions of the Chinese Society for
Agricultural Machinery, 2019, 50(8): 280–288.
[19]
Yan, M. T.,
Qiao, J. J., Qu, M., et al. Measurements, Spatial Spillover and
Influencing Factors of Agricultural Eco-efficiency in Henan Province [J]. Journal
of Ecology and Rural Environment, 2022, 38(11): 1396–1405.
[20]
Geng, Q. L., Ren, Q. F., Nolan, R. H., et al. Assessing China??s
agricultural water use efficiency in a green-blue water perspective: A study
based on data envelopment analysis [J]. Ecological Indicators, 2019, 96:
329–335.
[21]
Lu, W. N., Liu, J. Y., Zhao, M. J. Dynamic evolution and convergence of
agricultural water use efficiency in the Yellow River Basin [J]. Journal of
Northwest A&F University (Social Science Edition), 2022, 22(4):
123–134.
[22]
Cai, R., Tao,
S. M. Evolution characteristics of grain production distribution and spatial
mechanism decomposition in China from 1978 to 2018 [J]. Journal of Arid Land
Resources and Environment, 2021, 35(6): 1–7.
[23]
Cao, Y. Q.,
Li, W. J., Yuan, L. T. Spatio-temporal pattern variation and safety evaluation
of crops in Hebei Province [J]. Scientia Geographica Sinica, 2018,
38(8): 1319–1327.
[24]
Su, X. J., Ji,
D. H., He, H. S. Study on spatial and temporal differences and affecting
factors of agricultural water resources green efficiency in Huang-Huai-Hai
Plain [J]. Ecological Economy, 2021, 37(3): 106–111.
[25]
Zhang, Q. N.,
Zhang, F. F., Mai, Q., et al. Spatial spillover networks and enhancement
paths of grain production efficiency in China [J]. Acta Geographica Sinica,
2022, 77(4): 996–1008.
[26]
Zhao, J.,
Meng, H., Gong, J. Measurement of total factor agricultural water efficiency
and analysis of influential factors in Jing-Jin-Ji area [J]. Journal of
China Agricultural University, 2017, 22(3): 76–84.
[27] Song, H. F., Liu, Y. Z. Wheat ecological efficiency
and pollution reducing potential of major grain production areas: Based on the
perspective of storing grain in the field [J]. Journal of Arid Land
Resources and Environment, 2017, 31(7): 97–101.
[28] Cui, N. B., Yu, Z., Jiang, X. R. Study on water
resource utilization efficiency of grain production in Heilongjiang reclamation
area [J]. Agricultural Economics and Management, 2020(5): 54–63.