Abstract

Exploring the impacts of climate change on agriculture is one of important topics with respect to climate change. We quantitatively examined the impacts of climate change on winter wheat yield in Northern China using the Cobb–Douglas production function. Utilizing time-series data of agricultural production and meteorological observations from 1981 to 2016, the impacts of climatic factors on wheat production were assessed. It was found that the contribution of climatic factors to winter wheat yield per unit area (WYPA) was 0.762–1.921% in absolute terms. Growing season average temperature (GSAT) had a negative impact on WYPA for the period of 1981–2016. A 1% increase in GSAT could lead to a loss of 0.109% of WYPA when the other factors were constant. While growing season precipitation (GSP) had a positive impact on WYPA, as a 1% increase in GSP could result in 0.186% increase in WYPA, other factors kept constant. Then, the impacts on WYPA for the period 2021–2050 under two different emissions scenarios RCP4.5 and RCP8.5 were forecasted. For the whole study area, GSAT is projected to increase 1.37°C under RCP4.5 and 1.54°C under RCP8.5 for the period 2021–2050, which will lower the average WYPA by 1.75% and 1.97%, respectively. GSP is tended to increase by 17.31% under RCP4.5 and 22.22% under RCP8.5 and will give a rise of 3.22% and 4.13% in WYPA. The comprehensive effect of GSAT and GSP will increase WYPA by 1.47% under RCP4.5 and 2.16% under RCP8.5.

1. Introduction

In recent years, the frequency of various meteorological disasters such as drought, flood, and frost has increased due to climate change, which seriously impaired many climate-sensitive sectors [1]. It is understood that agriculture is likely to be affected most by climate change and variability because of its high dependence and sensitivity to climatic conditions [25]. Nevertheless, the impacts of climate change on crops in different regions are not the same [6]. Previous studies have shown that the warming caused by greenhouse gases is more pronounced at higher latitudes [7], which could lengthen growing seasons and reduce the risk of freezing injury due to low temperature and have positive effects on crops here [8, 9]. In contrast, higher temperature will adversely affect growing conditions in lower latitudes, especially in areas where temperatures are close to or at the optimal level for crop growth to begin with [10, 11]. Impacts on agriculture are likely to be especially severe in developing countries because of their low agricultural investment, technological levels, and capability to cope with climate change [12, 13]. China is the most populous developing country as well as one of the largest agricultural production countries. Agriculture in China feeds 22% of the global population with only 7% of the world’s arable lands [14]. However, some studies have shown that China’s agriculture might suffer from climate change. The loss in yield for each degree Celsius increase in global mean temperature is about 8.0% for maize and 2.6% for wheat [15]. It is urgent for us to understand the possible impacts of climate change on China’s agriculture production, so that the planting strategies can be provided timely to avoid or mitigate the negative impacts from climate change.

There is now a substantial number of assessment studies demonstrating the link between climate change and agriculture, with the study methods ranging from simple equations to complex models, the study scope ranging from single sector to multiple sectors, and the study core ranging from intuitive phenomenon to mechanism analysis [16]. Crop models and statistical models are two main tools for quantitatively assessing the effects of climate change on crop yields [17]. Crop models such as DSSAT (America), APSIM (Australia), and CCSODS (China) can integrate knowledge on physiology, agronomy, soil science, and agrometeorology to the models using mathematical equations to quantitatively and dynamically describe the process of crop growth, development, and yield formation. Crop models are dominant tools for the Third and Fourth Assessment Reports of the IPCC to assess the impacts of climate change on agricultural sector because of their relatively clear ecological mechanism [18]. However, the results of crop models are highly sensitive to soil, meteorology, and field management and require extensive input data. These models also can be very difficult to calibrate because of complex model structures and a large number of uncertain parameters [1922]. Statistical models such as time-series models, panel data models, and cross section models can predict crop indicators by using historical data on crop indicators and weather data to develop a regression equation [23]. However, the statistical data of Food and Agriculture Organization of the United Nation (FAO) showed that global wheat yield did not reduce with climate warming in the premise of stable planting areas (http://www.fao.org/faostat/zh/#data/QC/visualize), which indicated that with the development of agricultural technology, agricultural production is not only related to meteorological factors such as temperature and precipitation but also to economic factors such as labor and fertilizer. Therefore, researchers combined meteorological factors and economic factors as independent variables to establish regression models so as to explore the impacts of climate change on agricultural production [2427]. Chou et al. [28, 29] developed a new model (C-D-C) for assessing and predicting the effect of climate change on grain yield by introducing climatic factors into the C-D (Cobb–Dauglas) production function, and the preliminary simulation and verification of the model were performed.

In terms of planting area and yield, wheat is the third most important crop in China, only behind rice and maize, and winter wheat accounts for approximately 95% of the total (winter and spring) wheat yields. The northern winter wheat production areas (NWPA) are the main areas that produce winter wheat and make up approximately 80.1% of the wheat production (National Bureau of Statistics of China, http://data.stats.gov.cn/easyquery.htm?cn=E0103). Winter wheat is mainly used for food in this region because of its high quality and flour yield. The goal of this paper was to quantitatively study the impacts of climate change on the winter wheat yield per unit area (WYPA) in NWPA by introducing growing season average temperature (GSAT) and precipitation (GSP) for winter wheat into the C-D production function, so as to provide reference for planting strategies and wheat import and export trade strategies in the future.

2. Materials and Methods

2.1. Study Area and Data

Our study area covers Jing-Jin-Ji region (including Beijing, Tianjin, and Hebei provinces), Shanxi, Shaanxi, Shandong, and Henan provinces (Figure 1), located in the midlatitude temperate zones of northern hemisphere (32–42°N) and influenced by East Asian monsoon climate. Crops are harvested twice a year or three times every two years. The climatic conditions in the region are suitable for planting winterness or strong-winterness wheat varieties with an annual precipitation of 440–980 mm, annual average temperature of 9–15°C, and active accumulated temperature ranges from 2750 to 4900°C. The growing season of winter wheat in this area is from this September to next June [30, 31].

The data used in this study included meteorological data and agricultural data. The meteorological data consisted of observations data for estimating the parameters of models and scenario data for forecasting future climate change. Observations data were available from China Meteorological Administration (CMA), which provided time series on the daily temperature and precipitation of meteorological stations (black dots in Figure 1) across the study area from 1981 to 2016, so as to calculate the GSAT and GSP for winter wheat. Greenhouse gas emission scenarios are the basis for future climate change projections, and one of the most important scenarios is RCPs (representative concentration pathways). RCPs include four greenhouse gases concentration trajectories adopted by the IPCC AR5, which represent integrated socioeconomic standards, emissions, and climate scenarios to construct the definite mitigation scenario. The four RCPs including RCP2.6, RCP4.5, RCP6.0, and RCP8.0 stabilized the radiative forcing at approximately 490, 650, 850, and 1370 ppm CO2-equivalent in 2100, respectively [32]. RCP4.5, a medium emissions scenario, is possibly consistent with the future economic development of China and meets the mitigation plan for responding to climate change [33]. RCP8.5 corresponds to a high greenhouse gas emissions pathway and also to the upper bound of the four RCPs. The greenhouse gases emissions and concentrations in this scenario increase considerably over time, and there is not any specific climate mitigation target [34]. Therefore, the RCP4.5 and RCP8.5 were used in this study. Climate scenario data from the RCP4.5 and RCP8.5 for 2021–2050 were downloaded from the Inter-Sectoral Impact Model Intercomparison Project (ISI-MIP). The data include 5 climate models simulation outputs: HadGEM2-ES (MOHC, England), IPSL-CM5A-LR (IPSL, France), MIROC-ESM-CHEM (MIROC, Japan), GFDL-ESM2M (GFDL, America), and NorESM1-M (NCC, Norway), which have been bias-corrected based on the raw data from the 5 CMIP5 models listed above. The variability of the simulated data about their monthly means is modified to match the observed data to preserve the long-term absolute or relative trend of the simulated data. Then, these data are bilinearly interpolated in space to 0.5° × 0.5° grid [35]. The multimodel ensemble (MME) of the climate variables was used in this paper, including daily mean temperature and precipitation.

Agricultural data were available from the National Bureau of Statistics of the People’s Republic of China and an agricultural statistical datasets [36], which included provincial WYPA and related inputs from 1981 to 2016, that is, fertilizer use, machinery, labor, and irrigated area for winter wheat.

2.2. Model Specification and Evaluation

Cobb–Douglas production function is a multifactor analysis model, which can effectively describe the relationship between production factors and output. The production factors used in this study included both agricultural inputs and climatic factors, and we introduced climatic factors GSAT and GSP into the Cobb–Douglas production function to quantitatively investigate the impacts of climate change on wheat yield for the five provinces (region) in Northern China. We specified the empirical production function where the WYPA was a function of the meteorological variables and agricultural inputs for any province (region) i at year t:

We linearized the equation by taking the logarithm of both sides:where Y was the WYPA (kg/ha) and the agricultural inputs F, M, L, and I were fertilizers used (10,000 tons), machinery (10,000 kw), labor (10,000 persons), and irrigated area (1000 ha) for winter wheat, respectively. More importantly, we introduced average temperature (T, °C) and precipitation (P, 100 mm) during winter wheat growing season (from this September to next June) as climatic factors to the model. Additionally, we allowed for time varying effects on winter wheat production, represented by a time series, Te, and intended to capture the factor of technological progress influence. ε was white noise. The , , and were the coefficients to be estimated.

One should note that the agricultural inputs for winter wheat were included in the total agricultural inputs and needed to be calculated by some formulas. They can take the following form:where TF was total fertilizer use of farm crops; TM was total power of agricultural machinery; TL was total labor of agriculture, forestry, animal husbandry, and fishery; TI was total agricultural irrigated area; RA was sown area of winter wheat/total sown area of farm crops; RG was gross output of agriculture/gross output of agriculture, forestry, animal husbandry, and fishery.

Panel data involved two dimensions: a cross-sectional dimension and a time-series dimension [37], which required testing the temporal stability of variables before establishing a regression model to avoid spurious regressions. The approaches of LLC that assumes common unit root process [38] and ADF-Fisher that assumes individual unit root process [39] were used in this study to test for a unit root. The regression analysis can be carried out when all of the variables are stationary time series. However, as analyzed by Zhao [40], we can also establish a regression model if the variables pass the cointegration criterion in the premise that the integrated order of dependent variable is not more than that of independent variables and there are at least two independent variables having the integrated orders more than that of dependent variable, although some of the variables are nonstationary time series.

We adopted “leave-one-out cross validation” [41], the measures of “normalized root mean square error” (NRMSE), and “index of agreement” (IA) [42] to evaluate model performance. The two measures, NRMES and IA, summarize the average difference and agreement between observed and model-predicted values, respectively. They can take the following form:where Pi is the model-predicted value, Oi is observed value, n is the number of cases, and is the average of observed values. Following Yang et al. [43], we considered NRMSE ≤ 15% as “good” agreement; 15–30% as “moderate” agreement; and ≥30% as “poor” agreement. IA is intended to be a descriptive measurement, and it is both a relative and bounded measure [42], with IA = 0 indicating no agreement and IA = 1 indicating perfect agreement or zero error. Also as recommended by Yang et al. [43], when IA ≥ 0.9, it is considered as “excellent” agreement; 0.8 ≤ IA < 0.9 as “good” agreement; 0.7 ≤ IA < 0.8 as “moderate” agreement; and IA < 0.7 as “poor” agreement.

The impacts of climate trends and agricultural inputs changes on the WYPA were calculated in the following processes. First, we set three scenarios: (i) actual climatic factors and actual agricultural inputs for each province (region) for the period 1981–2016; (ii) detrended climatic factors and actual agricultural inputs; (iii) actual climatic factors and fixed agricultural inputs. We obtained the detrended datasets of GSAT and GSP for winter wheat in the five provinces (region) by the method of “linear detrending” [44]. For the agricultural inputs, we fixed them at the values in 1980. They can take the following form:where Ci,t is the climatic variable for province (region) i at year t, including GSAT and GSP; si is the slope of one climatic variable for province (region) i, based on linear fit for 1981–2016; and Ai,1980 is the agricultural inputs for province (region) i in 1980, including fertilizer use, machinery, labor, irrigated area, and technological progress. We then used the “Climate-Economy” model F(C, A) to compute the following:(i)F(C, A) = predicted WYPA with observed climatic data and agricultural inputs(ii)F(Cd, A) = predicted WYPA with detrended climatic data and observed agricultural inputs(iii)F(C, AF) = predicted WYPA with observed climatic data and fixed agricultural inputs

We computed the trends of (i)-(ii) and (i)–(iii) to quantify the yield effects of climate trends and agricultural inputs changes, respectively.

3. Results

3.1. Panel Regression and Model Evaluation

The results of unit root test suggested that a cointegration test should be carried out, and the variables passed the cointegration criterion (Table 1), which indicated that we can establish a regression model and the model will not be spurious. F test suggested us to choose a fixed-effects model, and the estimation results are presented in Table 2. We also reported the adjusted R2, F statistic, NRMSE, and IA used to evaluate the model performance in Table 2. The value of adjusted R2 was 0.91, and F statistic was significant at the 1% level, which indicated that the model had the feature of high fitting precision. NRMSE and IA were 8.14% and 0.98, respectively, showing a high extrapolating performance of the model. The coefficients on all of the agricultural inputs were positive and significant as expected for WYPA, except the labor with a negative coefficient. This indicated that WYPA increased with more fertilizer use, machinery, and irrigation but decreased with more labor. The reason why labor had a negative impact on YWPA was explicable that, since 1980, the agricultural mechanization improved rapidly, which resulted in a large surplus of agricultural labor. For climatic factors, the sign was negative for GSAT and was positive for GSP. This suggested that WYPA increased with more precipitation and decreased with higher temperature during the growing season.

3.2. Impacts of Climate Change on the Fluctuation of Winter Wheat Yield

From Table 2, the elastic coefficient of temperature was −0.109, which indicated that the WYPA will decrease 0.109% for each 1% increase in GSAT. Higher temperature negatively affect winter wheat yield, both directly and indirectly. With the increase of temperature, wheat tends to overgrow due to excessive accumulated temperatures before the winter, which makes wheat seedlings weak and lack resistance to the cold [45]. Higher temperature will also shorten winter wheat growing season, leading to the decrease of 1000-grain weight and damaging the quality of grain [46]. In addition, the occurrence probability of extreme high temperature events in the later stage of winter wheat growing season will increase, which is not conducive to the formation of wheat yield. However, due to the large demand of winter wheat for water and the low precipitation in study area, GSP had a positive and significant impact on WYPA, with the elastic coefficient of 0.186, that is, each 1% increase in GSP will increase WYPA by 0.186%. However, in the terms of the whole study area, GSAT for winter wheat experienced a significant increase by 0.49°C per decade since 1980; yet, the GSP had a slight but inconspicuous increasing trend with the slope of 1.138 (Figure 2).

Figure 3 showed the model-simulated results of F(C, A), F(Cd, A), and F(C, AF) for each province (region), so as to measure the impacts of climatic factors and agricultural inputs on WYPA. From Figure 3, agricultural inputs and technological progress played an important role in the formation of wheat yield. If these variables have remained at the values of the 1980s, the WYPA would be stagnant (green arrows). We computed the differences of F(C, A) and F(C, AF) for each province (region) to quantify the impacts of agricultural inputs on wheat yield variability and found that Shandong province was most influenced by agricultural inputs, followed by Jing-Jin-Ji region and Henan province, with the WYPA increase rate of 60.438%, 59.279%, and 56.369%, respectively. The effects of agricultural inputs on WYPA for Shanxi and Shaanxi provinces were less, and the WYPA only increased by 28.448% for Shanxi province and by 27.193% for Shaanxi province. However, the effects of climate trend on wheat yield were relatively low, and the degree of the effects was different within the five provinces (region). The actual climate change in Jing-Jin-Ji region and Shandong province, that is relatively weak rise in temperature (Jing-Jin-Jislope = 0.032; Shandongslope = 0.034) and large increase in precipitation (Jing-Jin-Jislope = 1.775; Shandongslope = 1.116), positively affected the wheat yield in the two regions during 1981–2016. The WYPA increased by 1.884% for Jing-Jin-Ji region and by 0.762% for Shandong province, relative to those without the climate trend. On the contrary, due to relatively rapid temperature rise and insignificant or negative precipitation change trend, wheat yield exhibited negative impacts for Shaanxi (GSATslope = 0.04; GSPslope = −0.013), Shanxi (GSATslope = 0.063; GSPslope = 0.92), and Henan (GSATslope = 0.039; GSPslope = 0.071), with the loss of 0.917%, 1.316%, and 1.921%, respectively. If just from the aspect of quantitative values above, agricultural inputs were likely to be more important factors contributing to the formation of wheat yield. Nevertheless, one should note that agricultural inputs changes are mainly controlled by technological development level, and the impacts of agricultural inputs on crops can be stable in the premise that social and technological development are stable and the government pays more attention to the agricultural harvests, whereas climate change itself and its impacts on crops are both more complicated. Short-term extreme weather events such as flood, drought, and frost will directly exert deadly effects on crops and sharply decrease their yield, while the effects of long-term trend of climate change is gradual and potential. Long-term climate changes can greatly influence the cropping system, planting boundary, and planting structure and further influence the allocation and trade of national agricultural products. Therefore, the impacts of climatic factors on crops cannot be ignored, although apart from extreme climate events, it may be small in the short term.

3.3. Scenario Simulation Analysis of Climate Change

Figure 4 and Table 3 show the differences of GSAT and GSP projected for 2021–2050 relative to the baseline period of 1981–2005 for the medium emission scenario (RCP4.5) and high emission scenario (RCP8.5). The GSAT will increase by 1.33–1.44°C under RCP4.5 and by 1.43–1.68°C under RCP8.5 for the five provinces (region), relative to the baseline period. Shanxi province will experience the most warming. In terms of the whole study area, GSAT is projected to experience a rise of about 1.37°C for RCP4.5°C and 1.54°C for RCP8.5. The results also suggested that there will be an increasing trend in GSP for the majority of the regions under the two RCP scenarios, except for a slight decrease in western Shaanxi province. Shandong province will experience the most precipitation increasing. The precipitation increment under high emissions scenario is much more than that under medium emissions scenario. The GSP increment for the five provinces (region) under RCP4.5 and RCP8.5 are 2.72–31.82% and 4.53–33.0%, respectively. In terms of the whole study area, precipitation is projected to increase by 17.31% for RCP4.5 and by 22.22% for RCP8.5.

Finally and for perspective, we used the estimates of climate change under RCP4.5 and RCP8.5 (Table 3) to obtain estimates of the effects of projected GSAT and GSP changes on WYPA variance in the five provinces (region) (Table 4). The change tendency of WYPA is opposite to GSAT but is consistent with GSP. For RCP4.5, temperature rising gives a decrease of 1.75% in average WYPA for the whole study area and a decrease of 1.46% (Jing-Jin-Ji region) to 2.71% (Shanxi province) for the selected five provinces (region). However, precipitation increasing is beneficial to the improvement of WYPA, with the increase of 3.22% for the whole study area and 0.51% (Shaanxi province) to 5.92% (Shandong province) for the five provinces (region). For RCP8.5, WYPA decreases by 1.97% for the whole study area and by 1.51% (Jing-jin-ji region) to 3.16% (Shanxi province) for the selected five provinces (region). Precipitation increasing gives a rise of 4.13% in WYPA for the whole study area, and 0.84% (Shaanxi province) to 6.14% (Shandong province) for the five provinces (region). In terms of the comprehensive effect of GSAT and GSP, the majority of study area experiences a WYPA increase, due to the substantial increase of GSP counteracting the negative effect of GSAT rising. However, the small increase in Shaanxi’s GSP is not enough to offset the negative effects driven by the large increase in GSAT, which causes Shaanxi to be the only province whose WYPA suffering from the projected changes of GSAT and GSP. For RCP4.5, WYPA increases by 1.47% for the whole study area and by 0.47–4.13% for Shanxi, Henan, Jing-Jin-Ji, and Shandong provinces, but decreases by 1.3% for Shaanxi province. For RCP8.5, WYPA increases by 2.16% for the whole region and by 0.43–4.16% for Shanxi, Henan, Jing-Jin-Ji, and Shandong provinces, while Shaanxi province experiences a wheat yield decrease of 1.37%.

4. Discussion

4.1. Climate Model Uncertainty

Climate models are one of the most important tools to simulate and forecast future climate change, but there exists uncertainty about the results simulated by different climate models, which represents a key challenge for adaptation planning. For example, Ding et al. [47] simulated the climate change of China by the 40 models and suggested that there is a potential significant warming in China in the twenty-first century under different emission scenarios. However, large uncertainty exists in the projection of precipitation, and further studies are needed. Xu and Xu [48] assessed the performance in simulating the climate over China based on the CMIP3 and CMIP5 experiments and found that models appeared to have a good performance on reproducing the warming tendency but showing limited skills for precipitation, and most models overestimate precipitation. Uncertainty in future climate change derives from various sources such as emission scenarios, model structure, downscaling/bias-correction methods, and impact models [49].

In this study, we dealt with the uncertainty of the model from the following three aspects. Firstly, in emissions scenarios, we selected RCP4.5 as the lower one because it is possibly most consistent with the future economic development of China and meets the mitigation plan for responding to climate change [33]. The upper bound of four RCPs, RCP8.5, was used as the contrast scenario. Secondly, the climate simulation datasets used in this study were obtained from the ISI-MIP, which have been bias-corrected in the fast-track of ISI-MIP using the trend-preserving method and can reproduce the observed climate very well [35]. Several studies have demonstrated the value of using the same projections by the 5 GCMs in climate change impact assessments for different sectors at the global and regional scales [5054]. Thirdly, we used the MME to reduce the uncertainty because combining models can generally increase the skill, reliability, and consistency of model forecasts [55]. The combined information of an equally weighted average of several models (the method used in this study) is usually found to agree better with observations than any single model [56]. These solutions can effectively reduce the uncertainty of the models and improve the accuracy of our analysis.

4.2. Food Security and Adaptation Strategies

China is a large producer and consumer of food. China’s domestic demand for food maintained a self-sufficiency rate of 95%, while the other 5% depended on the international market for balance, since joining the WTO in 1980 [57]. However, with the growing population and rising consumption levels, China needs more food to feed itself. According to the forecast of the DRC (Development Research Center of the State Council), total domestic grain demand will reach 584.87–592.02 million tons, and the gap between food supply and demand will be up to 40–50 million tons [58]. The problem of food shortage has become more and more serious in recent years, and the reasons for food shortage are various factors, among which included are the increase of population, the decrease of cultivated land area, and the degradation of cultivated land quality. In addition, climate change has altered the agrometeorological conditions and posed a certain impact on crops growth. As shown in the results of this paper, the contribution of temperature rising to winter wheat yield in Northern China was negative since 1981, and the degree of influence will increase with the temperature rising further, while precipitation had a positive impact.

It is suggested that China could take the following two aspects to ensure the supply of domestic wheat, i.e., domestic wheat production and international wheat trade. From the aspect of domestic wheat production, climate change has been a concern of policy-makers, scientists, and farmers due to its far-reaching impacts on agriculture, and appropriate adaptation strategies should be taken immediately. Because Northern China is the principal wheat production base, the climate adaptation measures proposed in the following are based on the climate change of this region. Firstly, one of the most realistic and convenient measures for the local farmers is adjusting the sowing dates of winter wheat. Studies found that the suitable sowing dates of winter wheat in the region have been delayed in the last few decades and are projected to be further delayed in the future due to the temperature rising [59, 60]. The properly delayed sowing dates could result in significant differences in environmental conditions during crop grain filling and usually help the grains grow with increasing temperatures, which will minimize the decreasing rate of wheat yield under global warming [61, 62]. It is noticeable, however, that the freeze injury before winter wheat overwintering must be considered in this region, so the sowing dates cannot be delayed too late. Secondly, the strategy that copes with the challenges of climate change is to plant new grains which have higher heat requirement and longer duration of reproductive growth period. Better adaption to warmer climatic conditions makes these new grains more favorable than old ones under climate change and significantly increases wheat yield [63, 64]. Thirdly, converting the tillage system from conventional plow tillage to rotary tillage is beneficial to improve the efficiency of local agriculture production and enhance crop yield. The conventional plow tillage is time-consuming and energy-intensive, and farmers prefer to burn crop residues in order to save time for seeding the next crop, which has some adverse impacts on soil and hinders crops growth. However, rotary tillage can chop crop residue and mix it into the soil, which will increase retention of rainfall in the soil and enhance SOC sequestration. This can enhance the ability of wheat to cope with climate change during its growing period [65]. Fourthly, it is necessary to expand irrigation infrastructure for Northern China. Although this study found that the precipitation likely increases during wheat growing season over the region, winter wheat is generally cultivated under irrigation conditions due to the small amount and large fluctuation of precipitation [66]. Optimizing irrigation facilities can ensure the water supply for wheat during the critical growth period, which is beneficial to improve its ability to cope with adverse climatic conditions and reduce the losses of wheat yield. In addition, there are many other options of agricultural adaptation to climate change for the region, such as developing crop diversity, improving fertilization, and natural resource management. Finally, we should be aware that the negative impacts of climate change could be moderated by implementing these adaptations duly and steadily rather than missing the appropriate timing to implement adaptations.

In terms of international wheat trade, China should make full use of the grain production resources in other countries and regions and expand the sources of domestic food supply through food trade and cooperation, so as to keep the balance between food supply and demand and guarantee the quantity of the grain stored. However, China’s import market of wheat in international trade mainly focuses in the United States, Canada, and Australia. For instance, China imported 99% of its wheat from the three countries in 2011, which will raise the potential risk for China’s wheat import market in the future. China should try to reduce the risk of wheat imports by analyzing the potential of wheat yield increase and export in various countries and seeking more stable sources for wheat importing. For example, from climate perspective, the United States, the largest wheat exporter to China, is projected to experience a wheat yield decrease in the future while Canada is inversed [15, 6770]. This indicates that China’s wheat import market center in North America may slowly shift from the United States to Canada. Moreover, as emerging export countries in the international wheat trade market, Russia, Ukraine, and Kazakhstan have witnessed a rapid increasing in the proportion of wheat export and a growing market influence [71]. Climate change has effectively increased their grain production potential because of the location in mid- and high-latitudes [72, 73]. The food self-sufficiency rate of the three countries has been stable at more than 100%, and the export potential is also increasing (FAOSTAT food balance sheet). Therefore, China can increase its wheat import from these countries to ensure the domestic food security in the future.

5. Conclusion

The relative contribution of climatic factors to wheat yield was about 0.762–1.921% in absolute terms for the period 1981–2016, which was smaller than the contribution of agricultural inputs and technological progress that ranged from 27.193 to 60.438%. Warming trends during winter wheat growing season had a negative effect on WYPA, whereas the increasing trend of precipitation had a positive effect in 1981–2016, and the elastic coefficients were −0.109 and 0.186, respectively. This indicated that a 1% rise in GSAT tends to lower yield of 0.109%, and a 1% increase in GSP increases yield of 0.186%, up to a point at which further rainfall becomes harmful. The GSAT and GSP are both projected to increase in the study area for the period of 2021–2050, the increment of which for high emission scenario (RCP8.5) is more than that for medium emission scenario (RCP4.5). GSAT is projected to rise 1.37°C under RCP4.5 scenario and 1.54°C under RCP8.5 scenario for the whole study area, which will lower the average WYPA by 1.75% and 1.97%, respectively. GSP is tended to increase by 17.31% under RCP4.5 scenario and 22.22% under RCP8.5 scenario for the whole region, which will give a rise of 3.22% and 4.13% in WYPA, respectively. In terms of the comprehensive effect of GSAT and GSP, average WYPA will increase by 1.47% under RCP4.5 scenario and 2.16% under RCP8.5 scenario for the whole study area. At provincial scale, the changes of climatic factors will have a positive effect on WYPA for Jing-Jin-Ji region, Shanxi, Shandong, and Henan provinces, while they will have a negative effect for Shaanxi province.

Data Availability

The meteorological observation data were taken from http://data.cma.cn/data/cdcindex/cid/6d1b5efbdcbf9a58.html. The climate scenario data were downloaded from https://esg.pik-potsdam.de/search/isimip-ft/. The agricultural data were provided by http://data.stats.gov.cn/. The other data used to support the findings of this study are available from the corresponding author upon request.

Conflicts of Interest

The authors declare that there are no conflicts of interest regarding the publication of this paper.

Acknowledgments

This research was supported by the grants (to IGSNRR) from the Ministry of Science and Technology of the People’s Republic of China (2016YFA0602704) and the National Natural Science Foundation of China (41831174 and 41671201).