1School of Economics, Ocean University of China, Qingdao 266100, China 2Institute of Marine Development, Ocean University of China, Qingdao 266100, China 3School of Foreign Languages, Ocean University of China, Qingdao 266100, China 4Xinjiang Institute of Ecology and Geography, Chinese Academy of Sciences, Urumqi 830011, China 5University of Chinese Academy of Sciences, Beijing 100049, China
There are eight provinces and autonomous regions (Gansu Province, Ningxia Hui Autonomous Region, Xinjiang Uygur Autonomous Region, Inner Mongolia Autonomous Region, Tibet Autonomous Region, Qinghai Province, Shanxi Province, and Shaanxi Province) in Northwest China, most areas of which are located in arid and semi-arid regions (northwest of the 400 mm precipitation line), accounting for 58.74% of the country's land area and sustaining approximately 7.84×106 people. Because of drought conditions and fragile ecology, these regions cannot develop agriculture at the expense of the environment. Given the challenges of global warming, the green total factor productivity (GTFP), taking CO2 emissions as an undesirable output, is an effective index for measuring the sustainability of agricultural development. Agricultural GTFP can be influenced by both internal production factors (labor force, machinery, land, agricultural plastic film, diesel, pesticide, and fertilizer) and external climate factors (temperature, precipitation, and sunshine duration). In this study, we used the Super-slacks-based measure (Super-SBM) model to measure agricultural GTFP during the period 2000-2016 at the regional level. Our results show that the average agricultural GTFP of most provinces and autonomous regions in arid and semi-arid regions underwent a fluctuating increase during the study period (2000-2016), and the fluctuation was caused by the production factors (input and output factors). To improve agricultural GTFP, Shaanxi, Shanxi, and Gansu should reduce agricultural labor force input; Shaanxi, Inner Mongolia, Gansu, and Shanxi should decrease machinery input; Shaanxi, Inner Mongolia, Xinjiang, and Shanxi should reduce fertilizer input; Shaanxi, Xinjiang, Gansu, and Ningxia should reduce diesel input; Xinjiang and Gansu should decrease plastic film input; and Gansu, Shanxi, and Inner Mongolia should cut pesticide input. Desirable output agricultural earnings should be increased in Qinghai and Tibet, and undesirable output (CO2 emissions) should be reduced in Inner Mongolia, Xinjiang, Gansu, and Shaanxi. Agricultural GTFP is influenced not only by internal production factors but also by external climate factors. To determine the influence of climate factors on GTFP in these provinces and autonomous regions, we used a Geographical Detector (Geodetector) model to analyze the influence of climate factors (temperature, precipitation, and sunshine duration) and identify the relationships between different climate factors and GTFP. We found that temperature played a significant role in the spatial heterogeneity of GTFP among provinces and autonomous regions in arid and semi-arid regions. For Xinjiang, Inner Mongolia, and Tibet, a suitable average annual temperature would be in the range of 7°C-9°C; for Gansu, Shanxi, and Ningxia, it would be 11°C-13°C; and for Shaanxi, it would be 15°C-17°C. Stable climatic conditions and more efficient production are prerequisites for the development of sustainable agriculture. Hence, in the agricultural production process, reducing the redundancy of input factors is the best way to reduce CO2 emissions and to maintain temperatures, thereby improving the agricultural GTFP. The significance of this study is that it explores the impact of both internal production factors and external climatic factors on the development of sustainable agriculture in arid and semi-arid regions, identifying an effective way forward for the arid and semi-arid regions of Northwest China.
Oak Ridge National Laboratory (ORNL), United States
Pesticide (kg CE/kg)
4.9341
Oak Ridge National Laboratory (ORNL), United States
Plastic film (kg CE/kg)
5.1800
Institute of Resource, Ecosystem and Environment of Agriculture of Nanjing Agricultural University (IREEA), China
Diesel (kg CE/kg)
0.5927
Intergovernmental Panel on Climate Change (IPCC), United Nations
Irrigation (kg/km2)
266.4800
Duan et al. (2011), China
Plowing (kg/km2)
312.6000
China Agricultural University (CAU), China
Variable type
Variable
Mean
Standard deviation
Input factors
Number of agricultural labor force (×104 persons)
1165.3802
787.6478
Total power of agricultural machinery (×104 kW)
1424.8896
960.7656
Volume of effective component of fertilizer (×104 t)
89.1750
71.8066
Use of agricultural diesel (×104 t)
32.3338
25.3809
Use of agricultural plastic film (×104 t)
5.1745
6.0462
Use of agricultural pesticide (×104 t)
1.5174
1.6592
Total sown area of farm crops (×103 hm2)
3121.5603
2140.6714
Output factors
Gross output value of agriculture (×108 CNY, at 2000 constant price)
306.0458
234.7596
CO2 emissions (×104 t)
217.4791
157.7604
Region
Province/ Autonomous region
Labor Force (×104 persons)
Machinery (×104 kW)
Fertilizer (×104 t)
Diesel (×104 t)
Plastic Film (×104 t)
Pesticide (×104 t)
Land (×103 hm2)
Earnings (×108 CNY)
CO2 Emissions (×104 t)
Arid
Gansu
1799.4180
1752.1940
81.5529
26.8824
11.3788
4.1811
3909.8470
388.6244
273.9565
Ningxia
355.0647
627.2294
33.3706
17.2529
1.0324
0.2182
1179.5180
96.6187
78.3374
Xinjiang
1136.8940
1530.3290
151.1882
59.6412
16.1241
1.8047
4461.7940
531.6966
383.4737
Semi-
Tibet
226.8471
345.2588
4.4353
2.7294
0.0859
0.0929
239.1765
25.8114
12.9417
arid
Shanxi
2001.4290
2470.2410
103.7412
27.6823
3.8182
2.4718
3781.5060
380.3657
243.2440
Qinghai
323.8235
365.8294
8.0941
5.8235
0.3171
0.1871
522.7882
37.3417
27.3607
Shaanxi
2289.5120
1773.7060
180.0824
65.1411
3.1341
1.1465
4217.3530
525.5955
335.4848
Inner Mongolia
1190.0530
2534.3290
150.9353
53.5177
5.5053
2.0365
6660.5000
462.3124
385.0342
Average
1165.3802
1424.8896
89.1750
32.3338
5.1745
1.5174
3121.5603
306.0458
217.4791
Region
Province/ Autonomous region
Growth rate (%)
Labor force
Machinery
Fertilizer
Diesel
Plastic film
Pesticide
Land
Earnings
CO2 emissions
Arid
Gansu
-28.9125
80.1400
44.8062
183.3333
203.8941
513.1579
14.4511
145.9105
74.5302
Ningxia
-24.0474
52.5223
72.4576
95.6522
214.5833
62.5000
21.0231
232.7867
57.0062
Xinjiang
35.6767
199.8355
215.9091
121.1587
202.1566
102.9412
80.6876
134.5649
148.8370
Semi-
Tibet
7.4723
454.6725
136.0000
785.7143
1700.0000
57.1428
10.6880
-13.6474
86.7169
arid
Shanxi
-30.5950
2.5275
34.5977
28.6344
77.1739
74.8571
-6.3576
174.4045
18.5313
Qinghai
-14.7356
79.0008
22.2222
8.4746
1216.6670
0.0000
-0.7585
117.6976
20.6629
Shaanxi
-38.4843
108.2558
77.6677
66.3082
72.7273
28.1553
-6.7415
168.9692
39.7402
Inner Mongolia
-28.9657
146.6933
213.6364
170.9030
176.3006
262.9213
29.2709
119.9713
98.7764
Statistic
Temperature
Precipitation
Sunshine duration
q statistic
0.2442
0.0173
0.0203
P value
0.9817
1.0000
1.0000
Temperature
Precipitation
Sunshine duration
Temperature
Precipitation
Y
Sunshine duration
Y
N
Temperature
Precipitation
Sunshine duration
Temperature
0.2442
Precipitation
0.3004
0.0173
Sunshine duration
0.2981
0.0550
0.0203
Climate factor
Graphical representation
Interaction
Temperature∩Precipitation
Enhances, nonlinear
Temperature∩Sunshine duration
Enhances, nonlinear
Precipitation∩Sunshine duration
Enhances, nonlinear
Temperature
5°C-7°C
7°C-9°C
9°C-11°C
11°C-13°C
13°C-15°C
15°C-17°C
Average GTFP
0.3960
0.6615
0.4857
0.6785
0.5673
0.6748
5°C-7°C
7°C-9°C
Y
9°C-11°C
Y
Y
11°C-13°C
Y
N
Y
13°C-15°C
Y
N
N
N
Over 15°C
Y
N
Y
N
N
Precipitation
0-200 mm
200-400 mm
400-600 mm
600-800 mm
Over 800 mm
Average GTFP
0.5073
0.5749
0.5911
0.5772
0.4411
0-200 mm
200-400 mm
N
400-600 mm
N
N
600-800 mm
N
N
N
Over 800 mm
N
N
N
N
Sunshine
1000-1500 h
1500-2000 h
2000-2500 h
Average GTFP
0.5803
0.5827
0.5804
1000-1500 h
1500-2000 h
N
2000-2500 h
N
N
[1]
Andersen P, Petersen N C. 1993. A procedure for ranking efficient units in data envelopment analysis. Management Science, 39(10): 1261-1264.
[2]
Blancard S, Martin E. 2014. Energy efficiency measurement in agriculture with imprecise energy content information. Energy Policy, 66: 198-208.
[3]
Chen P C, Yu M M, Chang C C, et al. 2008. Total factor productivity growth in China's agricultural sector. China Economic Review, 19(4): 580-593.
[4]
Chen Z, Huffman W E, Rozelle S. 2009. Farm technology and technical efficiency: Evidence from four regions in China. China Economic Review, 20(2): 153-161.
[5]
Cheng G. 2014. Data Envelopment Analysis: Methods and MaxDEA Software. Beijing: Intellectual Property Right Press, 180-189. (in Chinese)
[6]
Dai A G. 2011. Drought under global warming: a review. Climate Change, 2(1): 45-65.
[7]
Deng X Z, Gibson J, Wang P. 2017. Management of trade-offs between cultivated land conversions and land productivity in Shandong Province. Journal of Cleaner Production, 142: 767-774.
[8]
Duan H P, Zhang Y, Zhao J B, et al. 2011. Carbon footprint analysis of farm land ecosystem in China. Journal of Soil and Water Conservation, 25(5): 203-208. (in Chinese)
[9]
Feng C P, Chu F, Ding J J, et al. 2015. Carbon Emissions Abatement (CEA) allocation and compensation schemes based on DEA. Omega-International Journal of Management Science, 53: 78-89.
[10]
Feng Z M, Yang Y Z, Zhang Y Q, et al. 2005. Grain-for-green policy and its impacts on grain supply in West China. Land Use Policy, 22(4): 301-312.
[11]
Fischer G, Winiwarter W, Ermolieva T, et al. 2010. Integrated modeling framework for assessment and mitigation of nitrogen pollution from agriculture: concept and case study for China. Agriculture, Ecosystems & Environment, 136(1-2): 116-124.
[12]
Fuinhas J A, Marques A C, Almeida P, et al. 2016. Two centuries of economic growth: international evidence on deepness and steepness. Transformations in Business & Economics, 15(3): 192-206.
[13]
Gan Y T, Kadambot H M S, Turner N C, et al. 2013. Ridge-furrow mulching systems—an innovative technique for boosting crop productivity in semiarid rain-fed environments. Advances in Agronomy, 118: 429-476.
[14]
Gollin D, Parente S L, Rogerson R. 2007. The food problem and the evolution of international income levels. Journal of Monetary Economics, 54(4): 1230-1255.
[15]
He F, Wang K, Li X L, et al. 2012. Effects of ridge and furrow rainfall harvesting system of on soil hydrothermal condition and yields of Elymus Sibiricus L. in arid and semiarid regions. Transactions of the Chinese Society of Agricultural Engineering, 28(12): 122-126. (in Chinese)
[16]
Heidari M D, Omid M, Mohammadi A. 2012. Measuring productive efficiency of horticultural greenhouses in Iran: a data envelopment analysis approach. Expert Systems with Applications, 39(1): 1040-1045.
[17]
Hu Q, Pan F F, Pan X B, et al. 2014. Effects of a ridge-furrow micro-field rainwater-harvesting system on potato yield in a semi-arid region. Field Crops Research, 166(9): 92-101.
[18]
Huang C, Santibanez-Gonzalez E D, Song M. 2018. Interstate pollution spillover and setting environmental standards. Journal of Cleaner Production, 170: 1544-1553.
[19]
Ito J. 2010. Inter-regional difference of agricultural productivity in China: distinction between biochemical and machinery technology. China Economic Review, 21(3): 394-410.
[20]
Jin G, Li Z H, Deng X Z, et al.2018. An analysis of spatiotemporal patterns in Chinese agricultural productivity between 2004 and 2014. Ecological Indicators, 2019: 591-600.
[21]
Kerstens K, Shen Z, Ignace V D W. 2018. Comparing Luenberger and Luenberger-Hicks-Moorsteen productivity indicators: how well is total factor productivity approximated? International Journal of Production Economics, 195: 311-318.
[22]
Kravchenko A N, Bullock D G. 2000. Correlation of corn and soybean grain yield with topography and soil properties. Agronomy Journal, 92(1): 75-83.
[23]
Lee E A, Tollenaar M. 2007. Physiological basis of successful breeding strategies for maize grain yields. Crop Science, 47(Suppl.): S202-S215.
[24]
Lei Y D, Zhang H L, Chen F, et al. 2016. How rural land use management facilitates drought risk adaptation in a changing climate—a case study in arid Northern China. Science of the Total Environment, 550: 192-199.
[25]
Leng G Y, Tang Q H, Rayburg S. 2015. Climate change impacts on meteorological, agricultural and hydrological droughts in China. Global and Planetary Change, 126: 23-34.
[26]
Li X Y, Gong J D. 2002. Effect of different ridge: furrow ratios and supplement irrigation on crop production in ridge and furrow rainfall harvesting system with mulches. Agricultural Water Management, 54(3): 243-254.
[27]
Liobikiene G, Mandravickaite J, Krepstuliene D, et al. 2017. Lithuanian achievements in terms of CO2 emissions based on production side in the context of the EU-27. Technological and Economic Development of Economy, 23(3): 483-503.
[28]
Liu J Y, Xu X L, Zhuang D F, et al. 2005. Impacts of LUCC processes on potential land productivity in China in the 1990s. Science in China Series D: Earth Sciences, 48(8): 1259-1269.
[29]
Liu T, Liu H, Qi Y J. 2015. Construction land expansion and cultivated land protection in urbanizing China: insights from national land surveys, 1996-2006. Habitat International, 46:13-22.
[30]
Liu Y, Zhang J B, Zhang L. 2018. Analysis of carbon emission efficiency of rice in China under different rice planting patterns based on the DEA-SBM model. Journal of China Agricultural University, 23(6): 177-186. (in Chinese)
[31]
Liu Z, Guan D B, Crawford-Brown D, et al. 2013. Energy policy: a low-carbon road map for China. Nature, 500(7461): 143-145.
doi: 10.1038/500143a
pmid: 23925225
[32]
Liu Z, Davis S J, Feng K S, et al. 2016. Targeted opportunities to address the climate-trade dilemma in China. Nature Climate Change, 6(2): 201-206.
[33]
Lobell D B, Burke M B, Tebaldi C, et al. 2008. Prioritizing climate change adaptation needs for food security in 2030. Science, 319(5863): 607-610.
doi: 10.1126/science.1152339
[34]
Ma S Z, Feng H. 2013. Will the decline of efficiency in China's agriculture come to an end? An analysis based on opening and convergence. China Economic Review, 27:179-190.
doi: 10.1016/j.chieco.2013.04.003
[35]
MacDonald D, Crabtree J R, Wiesinger G, et al. 2000. Agricultural abandonment in mountain areas of Europe: environmental consequences and policy response. Journal of Environmental Management, 59(1): 47-69.
doi: 10.1006/jema.1999.0335
[36]
Makijenko J, Burlakovs J, Brizga J, et al. 2016. Energy efficiency and behavioral patterns in Latvia. Management of Environmental Quality, 27(6): 695-707.
[37]
Mueller L, Kay B D, Hu C S, et al. 2009. Visual assessment of soil structure: evaluation of methodologies on sites in Canada, China and Germany: part I: comparing visual methods and linking them with soil physical data and grain yield of cereals. Soil & Tillage Research, 103(1): 178-187.
[38]
NBSC (National Bureau of Statistical of China). 2001-2017a. China Rural Statistical Yearbook 2000-2016. Beijing: China Statistics Press. (in Chinese)
[39]
NBSC (National Bureau of Statistical of China). 2001-2017b. China Statistical Yearbook 2000-2016. Beijing: China Statistics Press. (in Chinese)
[40]
Nigussie Z, Tsunekawa A, Haregeweyn N, et al. 2017. Factors influencing small-scale farmers' adoption of sustainable land management technologies in north-western Ethiopia. Land Use Policy, 67: 57-64.
[41]
Olesen J E, Bindi M. 2002. Consequences of climate change for European agricultural productivity, land use and policy. European Journal of Agronomy, 16(4): 239-262.
[42]
Pang J X, Chen X P, Zhang Z L, et al. 2016. Measuring eco-efficiency of agriculture in China. Sustainability, 8(4): 1-15.
[43]
Peters C J, Wilkins J L, Fick G W. 2007. Testing a complete-diet model for estimating the land resource requirements of food consumption and agricultural carrying capacity: the New York State example. Renewable Agriculture and Food Systems, 22(2): 145-153.
[44]
Piao S L, Ciais P, Huang Y, et al. 2010. The impacts of climate change on water resources and agriculture in China. Nature, 467(7311): 43-51.
doi: 10.1038/nature09364
pmid: 20811450
[45]
Ponce C, Guillermo E, Moran M S, et al. 2013. Ecosystem resilience despite large-scale altered hydroclimatic condition. Nature, 470(1): 1-4.
[46]
Ren W, Tian H Q, Tao B, et al. 2012. China's crop productivity and soil carbon storage as influenced by multifactor global change. Global Change Biology, 18(9): 2945-2957.
doi: 10.1111/j.1365-2486.2012.02741.x
pmid: 24501069
[47]
Rigoberto A L, Xi H, Eleonora D F. 2017. What drives China's new agricultural subsidies? World Development, 93: 279-292.
[48]
Saleska S R, Didan K, Huete A R, et al. 2007. Amazon forests green-up during 2005 drought. Science, 318(5850): 612-612.
doi: 10.1126/science.1146663
pmid: 17885095
[49]
Seiford L M, Zhu J. 2002. Modeling undesirable factors in efficiency evaluation. European Journal of Operational Research, 142: 16-20.
[50]
Sheffield J, Wood E F. 2008. Projected changes in drought occurrence under future global warming from multi-model, multi-scenario, IPCC AR4 simulations. Climate Dynamics, 31(1): 79-105.
[51]
Shen Z Y, Baležentis T, Chen X L, et al. 2018. Green growth and structural change in Chinese agricultural sector during 1997-2014. China Economic Review, 51: 83-96.
[52]
Song M L, Wang S H, Cen L. 2015. Comprehensive efficiency evaluation of coal enterprises from production and pollution treatment process. Journal of Cleaner Production, 104: 374-379.
[53]
Song M L, Zheng W P, Wang Z Y. 2016. Environmental efficiency and energy consumption of highway transportation systems in China. International Journal of Production Economics, 181: 441-449.
[54]
Tao F L, Yokozawa M, Xu Y L, et al. 2006. Climate changes and trends in phenology and yields of field crops in China, 1981-2000. Agricultural and Forest Meteorology, 138(1-4): 82-92.
[55]
Tian X, Yu X H. 2012. The enigmas of TFP in China: a meta-analysis. China Economic Review, 23(2): 396-414.
[56]
Tone K. 2002. A slacks-based measure of super-efficiency in data envelopment analysis. European Journal of Operational Research, 143(1): 32-41.
[57]
Trenberth K E, Dai A G, Schrier G V D, et al. 2014. Global warming and changes in drought. Nature Climate Change, 4(1): 17-22.
[58]
Turner N C. 2004. Sustainable production of crops and pastures under drought in a Mediterranean environment. Annals of Applied Biology, 144(2): 139-174.
[59]
Van Ittersum M K, Leffelaar P A, Van Keulen H. 2003. On approaches and applications of Wageningen crop models. European Journal of Agronomy, 18(3-4): 201-234.
[60]
Wang A H, Lettenmaier D P, Sheffield J. 2011. Soil moisture drought in China, 1950-2006. Journal of Climate, 24(13): 3257-3271.
[61]
Wang F T, Yu C, Xiong L C, et al. 2019. How can agricultural water use efficiency be promoted in China? A spatial-temporal analysis. Resources, Conservation and Recycling, 145: 411-418.
[62]
Wang J F, Li X H, Christakos G, et al. 2010. Geographical detectors-based health risk assessment and its application in the neural tube defects study of the Heshun region, China. International Journal of Geographical Information Science, 24(1): 107-127.
[63]
Wang J F, Zhang T L, Fu B J. 2016. A measure of spatial stratified heterogeneity. Ecological Indicators, 67: 250-256
[64]
Wang J F, Xu C D. 2017. Geographical detector: principles and prospects. Acta Geographica Sinica, 72(1): 116-134. (in Chinese)
[65]
Wang K, Wei Y M, Huang Z M. 2016. Potential gains from carbon emissions trading in China: A DEA based estimation on abatement cost savings. Omega-International Journal of Management Science, 63: 48-59.
[66]
Wang Y J, Xie Z K, Malhi S S, et al. 2011. Effects of gravel-sand mulch, plastic mulch and ridge and furrow rainfall harvesting system combinations on water use efficiency, soil temperature and watermelon yield in a semi-arid Loess Plateau of northwestern China. Agricultural Water Management, 10(1): 88-92.
[67]
Wu Y R. 1995. Productivity growth, technological progress, and technical efficiency change in China: A three-sector analysis. Journal of Comparative Economics, 21(2): 207-229.
[68]
Xiao G J, Zhang Q B, Zhang F J, et al. 2016. Warming influences the yield and water use efficiency of winter wheat in the semiarid regions of Northwest China. Field Crops Research, 199: 129-135.
[69]
Xu S W, Li G Q, Li Z M. 2015. China agricultural outlook for 2015-2024 based on China Agricultural Monitoring and Early-warning System (CAMES). Journal of Integrative Agriculture, 14(9): 1889-1902.
[70]
Xu Y B, Li J Y, Wan J M. 2017. Agriculture and crop science in China: innovation and sustainability. Crop Journal, 5(2): 95-99.
[71]
Yao Y B, Wang R Y, Yang J H, et al. 2011. Impact of climate warming on flax growth and water use efficiency in semiarid regions of the loess plateau. Journal of Applied Ecology, 22(10): 2635-2642.
pmid: 22263469
[72]
Zhang B C. 2008. Discussion on basic characteristics and developmental status of rainfall-harvesting technique in arid areas. Journal of Irrigation & Drainage, 27(2): 119-122.
[73]
Zhang C J, Liao Y M, Duan J Q, et al. 2016. The progresses of dry-wet climate divisional research in China. Research in Climate Change Progress, 12(4): 261-267.
[74]
Zhang L, Pang J X, Chen X P, et al. 2019. Carbon emissions, energy consumption and economic growth: Evidence from the agricultural sector of China's main grain-producing areas. Science of the Total Environment, 665: 1017-1025.
doi: 10.1016/j.scitotenv.2019.02.162
[75]
Zhao H, Wang R Y, Ma B L. 2014. Ridge-furrow with full plastic film mulching improves water use efficiency and tuber yields of potato in a semiarid rainfed ecosystem. Field Crops Research, 161: 137-148.
doi: 10.1016/j.fcr.2014.02.013
[76]
Zhou L M, Jin S L, Liu C A, et al. 2012. Ridge-furrow and plastic-mulching tillage enhances maize-soil interactions: opportunities and challenges in a semiarid agroecosystem. Field Crops Research, 126: 181-188.
doi: 10.1016/j.fcr.2011.10.010