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中国城镇化对农业生态效率的影响——基于中国13个粮食主产区2009—2018年面板数据

本站小编 Free考研考试/2022-01-01

尚杰,
吉雪强,
陈玺名
东北林业大学经济管理学院 哈尔滨 150040
基金项目: 国家自然科学基金项目71573036

详细信息
作者简介:尚杰, 主要从事农业经济、环境科学与资源利用研究。E-mail:13576274061@163.com
中图分类号:F323.22

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出版历程

收稿日期:2020-02-27
录用日期:2020-05-26
刊出日期:2020-08-01

Study on the impact of China's urbanization on agricultural ecological effi-ciency:Based on panel data of 13 major grain-producing regions in China from 2009 to 2018

SHANG Jie,
JI Xueqiang,
CHEN Ximing
School of Economics and Management, Northeast Forestry University, Harbin 150040, China
Funds: the National Natural Science Foundation of China71573036



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摘要
摘要:城镇化对农业生态效率会产生重要影响。为更全面和准确分析城镇化对农业生态效率的影响,本文基于中国13个粮食主产区2009-2018年面板数据,利用3阶段非期望产出SBM-DEA模型、熵值法、Tobit回归等多种模型和方法,在理论分析基础上从多个角度就城镇化对农业生态效率的影响进行研究。结果表明:1)外生环境影响和随机干扰对农业生态效率测度会产生显著影响,并进一步作用于城镇化对农业生态效率的影响。2)中国13个粮食主产区2009-2018年间农业生态效率呈现持续增长趋势,剔除外生环境影响和随机干扰后,年度效率均值由2009年的0.53提升至2018年的0.80;但不同地区间存在较大差距,2018年河北等地区农业生态效率达到前沿面,但是内蒙古农业生态效率只有0.45。3)城镇化发展整体上能够促进农业生态效率的提高,城镇化综合指数在1%的水平上显著正向影响农业生态效率,影响系数为0.60。4)城镇化各指标对农业生态效率的影响存在差异,从各指标情况来看,人口城镇化率负向影响农业生态效率,但不显著;城镇居民人均可支配收入、城镇经济密度正向影响农业生态效率;二三产业产值占GDP比重、建成区面积比重、人均建成区面积等指标负向影响农业生态效率。为进一步发挥城镇化对农业生态效率的促进作用,本文根据研究结果从人口、经济、土地城镇化3个方面提出了政策建议。
关键词:城镇化/
农业生态效率/
粮食主产区/
DEA/
Tobit
Abstract:Urbanization is an important factor to impact agricultural ecological efficiency. However, most of the existing studies have discussed the impact of urbanization on agricultural ecological efficiency from a single perspective. Further, these studies are often affected by the impact of exogenous environment or other random factors during the measurement of agricultural ecological efficiency. To analyze the impact of urbanization on agricultural ecological efficiency more comprehensively and accurately, the present study used the three-stage SBM-DEA model, which provides simultaneously evaluation of both the undesirable and desirable outputs, entropy value method, and Tobit model, based on panel data obtained from 13 major grain-producing regions in China from 2009 to 2018. Various models and methods were used to study the impact of urbanization on agricultural ecological efficiency from multiple perspectives based on theoretical analysis. Our results showed that: 1) the impact of exogenous environment and random interference significantly impacted the agricultural ecological efficiency. After excluding these impacts, the agricultural ecological efficiency of the 13 major grain-producing regions in China changed significantly. Additionally, unlike the existing studies, the impact of urbanization on agricultural ecological efficiency too changed, after the effects of exogenous environment and random interference were removed. 2) The agricultural ecological efficiency of China's 13 major grain-producing regions showed a continuous growth trend from 2009 to 2018. The average annual efficiency, after excluding the impact of exogenous environment and random interference, increased from 0.53 in 2009 to 0.80 in 2018. However, there was a big gap in the agricultural ecological efficiency among different regions. For example, in 2018, the agricultural ecological efficiency of Hebei and other regions reached the frontier (1.00), but that of Inner Mongolia was only 0.45. 3) Urbanization as a whole improved the agricultural ecological efficiency. The comprehensive index of urbanization significantly affected agricultural ecological efficiency (at a level of 1%, impact coefficient: 0.60). 4) Various indicators of urbanization differently impacted the agricultural ecological efficiency. The population urbanization rate showed an insignificant negative impact on the agricultural ecological efficiency. The per capita disposable income of urban residents and urban economic density significantly positively affected the agricultural ecological efficiency. The output value of the secondary and tertiary industries, proportion of built-up area and per capita built-up area had significantly negative effect on the agricultural ecological efficiency. To further elucidate the role of urbanization in promoting agricultural eco-efficiency, this article proposed suggestions to modify the relevant policies, based on the research results from three aspects of population, economy, and land urbanization.
Key words:Urbanization/
Agro-ecological efficiency/
Main grain production areas/
DEA/
Tobit

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表1城镇化综合指数评价指标体系
Table1.Evaluation indicator system of comprehensive index of urbanization
目标层
Target level
系统层指标
System-level indicator
评价指标
Evaluating indicator
计算方法
Computational method
城镇化
Urbanization
人口城镇化
Population urbanization
人口城镇化率
Population urbanization rate
统计年鉴查询
Statistical Yearbook queries
城镇居民人均可支配收入
Per capita disposable income of urban residents
统计年鉴查询
Statistical Yearbook queries
经济城镇化
Economicurbanization
城镇经济密度
Urban economic density
第二三产业产值/土地面积
Output value of secondary and tertiary industries/land area
第二三产业占GDP的比重
Proportion of secondary and tertiary industries in GDP
第二三产业产值/GDP
Output value of secondary and tertiary industries/GDP
土地城镇化
Land urbanization
建成区面积比重
Proportion of built-up area
建成区面积/土地面积
Built-up area/total area
人均建成区面积
Per capita built-up area
辖区建成区面积/辖区总人口
Built-up area/total population


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表2农业生态效率投入-产出指标体系
Table2.Agricultural eco-efficiency input-output index system
指标类型
Index type
分类指标
Sub index
变量及说明
Variables and descriptions
投入指标
Input index
劳动力Labour force农业从业人员Number of employees in farm (×104person)
土地Land农作物总播种面积Planting area of crops (khm2)
化肥Chemical fertilizer化肥施用量Fertilizers consumption (×104t)
农药Pesticide农药使用量Pesticides usage (t)
农膜Agricultural film农膜使用量Agricultural film consumption (t)
农业机械动力
Agricultural machinery power
农业机械总动力
Total power of agricultural machinery (×104kW)
灌溉Irrigation有效灌溉面积Effective irrigation area (khm2)
期望产出指标
Output index
农业总产值
Total output value of farm
农业总产值Total output value of farm (×108¥)
非期望产出指标
Undesirable output index
碳排放
Carbon emission
化肥、农药、农膜、农用柴油、灌溉、播耕碳排放总和
Total carbon emissions from fertilizers, pesticides, agricultural films, agricultural diesel, irrigation and sowing (×104t)
污染排放
Pollution emissions
化肥污染量、农药污染量、农膜残留量总和
Total quantity of chemical fertilizer and pesticide pollutions, and total residues of agricultural film (×104t)


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表32009—2018年第1、3阶段中国主要粮食产区农业生态效率
Table3.Agricultural ecological efficiencies in the main grain-producing regions of China in the first and third stagesfrom 2009 to 2018
省份Province2009201020112012201320142015201620172018
阶段Stage
13131313131313131313
河北Hebei0.460.630.490.660.500.710.510.720.530.740.560.750.590.750.610.810.760.891.001.00
内蒙古Inner Mongolia0.400.350.420.360.440.390.440.400.470.420.460.410.480.420.490.420.500.430.550.45
辽宁Liaoning0.590.430.600.430.650.470.680.490.770.510.750.521.000.550.810.540.950.551.000.56
吉林Jilin0.460.380.480.400.500.420.510.430.550.450.570.470.580.480.590.480.850.511.000.52
黑龙江Heilongjiang0.460.500.480.510.520.550.520.560.540.600.540.630.590.660.650.720.680.781.001.00
江苏Jiangsu0.620.650.680.670.700.680.710.650.750.650.790.670.850.760.880.810.810.931.001.00
安徽Anhui0.350.430.360.440.360.440.360.430.360.440.380.460.400.480.420.500.460.530.470.55
江西Jiangxi0.370.340.370.340.380.350.390.360.460.400.480.410.500.420.530.450.590.470.660.50
山东Shandong0.520.720.540.730.570.750.600.760.650.790.710.840.780.870.881.001.001.001.001.00
河南Henan0.440.680.460.720.470.730.480.740.490.760.510.800.540.850.580.940.671.001.001.00
湖北Hubei0.510.540.520.550.540.580.570.610.600.640.620.670.670.710.780.830.870.921.001.00
湖南Hunan0.520.620.550.650.580.680.570.700.570.710.610.730.660.750.700.770.780.810.850.86
四川Sichuan0.570.680.600.710.620.740.650.770.670.790.700.810.720.820.840.940.901.001.001.00
均值Mean0.480.530.500.550.530.580.540.590.570.610.590.630.640.660.670.710.760.760.890.80


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表4第2阶段环境变量对农业生态效率冗余变量影响分析结果
Table4.Analysis of effects of environmental variables on redundant variables of agricultural ecological efficiency in the phase 2
冗余来源
Redundant source
变量
Variable
估计系数
Estimated coefficient
标准误差
Standard error
冗余来源
Redundant source
变量
Variable
估计系数
Estimated coefficient
标准误差
Standard error
劳动投入
Labour input
β0-1.65E+01-2.23E+01农膜投入
Agricultural film input
β3-1.64E-03***4.80E-04
β11.92E-021.18E-02σ21.89E+09***1.00E+00
β2-8.22E-06**-3.70E-06γ9.11E-01***1.18E-02
β3-9.45E-07-1.72E-06农业机械动力投入
Power input for agricultural machinery
β0-1.12E+03*6.23E+02
σ22.20E+04***2.37E+00β19.20E-01***2.95E-01
$\gamma $9.16E-01***1.11E-02β2-1.52E-04*9.08E-05
土地投入
Land input
β01.78E+03***5.23E+02β3-1.30E-04***4.21E-05
β1-2.40E-012.53E-01σ26.10E+06***1.09E+00
β2-1.60E-04*8.47E-05$\gamma $8.56E-01***1.89E-02
β3-1.78E-074.33E-05灌溉投入
Irrigation input
β01.49E+03***6.83E+00
σ26.15E+06***1.00E+00β1-2.77E-014.79E-01
γ8.95E-01***1.37E-02β2-1.78E-042.11E-04
化肥投入
Fertilizer input
β03.52E+012.23E+01β32.56E-04***9.26E-05
β13.93E-02***1.35E-02σ21.03E+07***1.00E+00
β2-1.42E-05***3.75E-06γ7.51E-021.21E-01
β3-9.43E-06***2.07E-06碳排放
Carbon emission
β01.55E+02***3.87E+01
σ21.59E+04***1.03E+00β14.93E-02*2.49E-02
γ9.16E-01***1.09E-02β2-2.68E-05***7.96E-06
农药投入
Pesticide input
β02.90E+04***2.55E+00β3-1.30E-05***3.34E-06
β17.75E+00**3.45E+00σ23.01E+04***1.00E+00
β2-4.91E-03***1.05E-03γ8.63E-01***1.79E-02
β3-2.67E-03***5.89E-04面源污染排放
Non-point source pollution emission
β02.52E+01*1.49E+01
σ21.41E+09***1.00E+00β12.61E-02***8.95E-03
γ9.10E-01***1.18E-02β2-9.51E-06***2.51E-06
农膜投入
Agricultural film input
β0-8.59E+03***1.01E+00β3-6.33E-06***1.37E-06
β1-1.95E+002.83E+00σ26.81E+03***1.04E+00
β22.95E-03***1.03E-03γ9.14E-01***1.16E-02
*、**和***表示在10%、5%和1%水平显著; β0为模型截距项, β1是第一产业产值参数估计值, β2是财政支农支出参数估计值, β3是研究经费支出参数估计值, σ2是模型中由随机噪声和无效效应符合作用造成的偏差, γ是无效影响因素对个体效率差异的解释程度。*, ** and *** represent significant difference at levels of 10%, 5%, 1%, respectively. β0 is the model intercept term; β1 is the first industry output value parameter estimate; β2 is the financial expenditure parameter estimate; β3 is the research expenditure parameter estimate. σ2 is the deviation caused by the coincidence of random noise and invalid effect in the model, and γ is the explanation degree of invalid influence factors to individual efficiency difference.


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表52009—2018年中国粮食主产区城镇化综合指数
Table5.Comprehensive indexes of urbanization of main grain-producing regions of China in 2009–2018
省份Province2009201020112012201320142015201620172018
河北Hebei0.340.380.430.460.490.520.510.500.500.52
内蒙古Inner Mongolia0.260.280.320.340.360.370.390.410.420.43
辽宁Liaoning0.310.360.400.430.460.490.510.520.500.52
吉林Jilin0.150.170.190.190.220.240.250.280.310.33
黑龙江Heilongjiang0.150.170.190.200.200.210.220.230.230.24
江苏Jiangsu0.460.540.610.660.690.740.770.810.870.90
安徽Anhui0.230.280.330.380.410.440.480.510.560.58
江西Jiangxi0.170.220.280.310.350.390.400.410.450.48
山东Shandong0.340.390.430.480.530.560.590.620.670.70
河南Henan0.270.300.360.400.440.470.490.520.580.63
湖北Hubei0.120.160.190.230.260.300.320.350.380.42
湖南Hunan0.180.210.260.290.330.370.390.430.490.49
四川Sichuan0.140.190.230.270.300.340.310.360.400.43
均值Mean0.240.280.330.360.390.420.430.460.490.51


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表6城镇化对农业生态效率影响的估计结果
Table6.Effect of urbanization on agricultural ecological efficiency
解释变量
Explanatory variable
第1次估计First estimate第2次估计Second estimate
TobitOlsTobitOls
估计系数
Estimated coefficient
标准误差
Standard error
估计系数
Estimated coefficient
标准误差
Standard error
估计系数
Estimated coefficient
标准误差
Standard error
估计系数
Estimated coefficient
标准误差
Standard error
城镇化综合指数
Comprehensive index of urbanization
0.60***0.100.54***0.09
人口城镇化率
Population urbanization rate
-0.050.08-0.050.08
城镇居民人均可支配收入
Per capital disposable income of urban residents
0.51***0.100.48***0.10
城镇经济密度
Urban economic density
0.72***0.190.65***0.18
第二三产业占GDP的比重
Proportion of secondary and tertiary industries in GDP
-0.33***0.09-0.32***0.09
建成区面积比重Proportion of built-up area-0.26**0.13-0.23**0.12
人均建成区面积
Per capital built-up area
-0.28***0.07-0.28***0.07
cons0.42***0.040.43***0.030.67***0.040.67***0.04
sigma0.180.010.130.01
Log likelihood20.7460.74
LR chi230.23(Prod > chi2=0.00)Prod > F=0.00110.22(Prod > chi2=0.00)Prod > F=0.00
*、**、***表示在10%、5%、1%水平显著。*, **, *** represent significant effects at levels of 10%, 5%, 1%, respectively.


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