自然资源学报 ›› 2021, Vol. 36 ›› Issue (6): 1505-1520.doi: 10.31497/zrzyxb.20210612
收稿日期:
2020-07-17
修回日期:
2021-01-25
出版日期:
2021-06-28
发布日期:
2021-08-28
通讯作者:
刘畅(1988- ),女,吉林辽源人,研究助理,研究方向为农业政策和农村发展等。E-mail: liuchang@jlau.edu.cn作者简介:
于晓华(1979- ),男,江苏如东人,博士,教授,博士生导师,研究方向为环境经济学、农业经济学等。E-mail: xyu@gwdg.de
基金资助:
YU Xiao-hua1(), LIU Chang2(
), ZHANG Guo-zheng3
Received:
2020-07-17
Revised:
2021-01-25
Online:
2021-06-28
Published:
2021-08-28
摘要:
贸易自由化和区域经济一体化不仅会通过比较优势整合市场、提升效率,还会带来农产品贸易中虚拟资源的流动。以中国—巴基斯坦大米贸易为研究对象,使用两国大米贸易数据,首先检验中巴粮食市场整合程度,其次分析中巴大米贸易带来的虚拟水和虚拟土地的流动。结果表明:(1)中巴之间大米市场已经高度整合,且价格存在长期均衡,但巴基斯坦大米价格比中国波动大,其对中国大米的价格弹性为1.097;“一带一路”倡议带来了巴方大米价格7.8%的下降,增加了穷人的福利。(2)贸易带来了虚拟水土资源的流动。中国累计从巴基斯坦净进口大米354万t,相当于净进口国内52万hm2、巴基斯坦96.4万hm2耕地,以及国内34.4亿t、巴基斯坦101.7亿t水资源。中国应加大技术支持和扩散的力度,具有促进粮食安全,节约全球资源的意义。
于晓华, 刘畅, 张国政. 国际粮食贸易背景下的市场整合与虚拟资源流动——以中国巴基斯坦大米市场为例[J]. 自然资源学报, 2021, 36(6): 1505-1520.
YU Xiao-hua, LIU Chang, ZHANG Guo-zheng. Market integration and virtual flow of resources under the background of international food trade: Evidence from China-Pakistan rice market[J]. JOURNAL OF NATURAL RESOURCES, 2021, 36(6): 1505-1520.
表5
中巴大米进出口及引致虚拟土地数量"
年份 | 进口大米/t | 出口大米/t | 净进口/t | 净进口虚拟土地/hm2 | ||
---|---|---|---|---|---|---|
中方土地 | 巴方土地 | |||||
中与巴各年进出口情况 | 1988 | 0 | 750.00 | -750.00 | -141.86 | -319.00 |
1989 | 53017.50 | 0 | 53017.50 | 9624.67 | 23126.50 | |
1990 | 0 | 0 | 0 | 0 | 0 | |
1991 | 6251.25 | 0 | 6251.25 | 1108.34 | 2694.62 | |
1993 | 0 | 22.50 | -22.50 | -3.85 | -8.21 | |
1996 | 15000.00 | 0 | 15000.00 | 2414.60 | 5229.21 | |
1997 | 73.75 | 10.00 | 63.75 | 10.09 | 22.73 | |
2001 | 0 | 3.75 | -3.75 | -0.61 | -1.36 | |
2002 | 0 | 31.25 | -31.25 | -5.05 | -10.35 | |
2003 | 0 | 91.25 | -91.25 | -15.06 | -30.88 | |
2004 | 0 | 26.25 | -26.25 | -4.16 | -8.78 | |
2005 | 113.75 | 175.00 | -61.25 | -9.78 | -19.30 | |
2006 | 157.50 | 470.00 | -312.50 | -49.76 | -98.88 | |
2007 | 342.50 | 1328.75 | -986.25 | -153.31 | -297.28 | |
2008 | 577.50 | 2683.75 | -2106.25 | -320.95 | -598.38 | |
2009 | 455.00 | 3993.75 | -3538.75 | -537.37 | -988.23 | |
2010 | 532.50 | 7146.25 | -6613.75 | -1009.27 | -2162.20 | |
2011 | 10835.00 | 6722.50 | 4112.50 | 614.97 | 1144.30 | |
2012 | 724478.75 | 9280.00 | 715198.75 | 105534.79 | 198854.13 | |
2013 | 521275.00 | 6730.00 | 514545.00 | 76599.97 | 137109.62 | |
2014 | 508400.00 | 8775.00 | 499625.00 | 73331.91 | 137490.02 | |
2015 | 553266.25 | 6182.50 | 547083.75 | 79387.60 | 146907.56 | |
2016 | 879707.50 | 11657.50 | 868050.00 | 126432.85 | 230154.31 | |
2017 | 340972.50 | 9315.00 | 331657.50 | 47948.17 | 86086.67 | |
累计 | 3615456.25 | 75395.00 | 3540061.25 | 520756.93 | 964276.83 |
表6
中国从巴基斯坦净进口大米的引致虚拟水资源"
年份 | 中国大米净进口量/t | 净进口中国水资源量/万m³ | 净进口巴基斯坦水资源量/万m³ | |||||||
---|---|---|---|---|---|---|---|---|---|---|
绿水 | 蓝水 | 灰水 | 合计 | 绿水 | 蓝水 | 灰水 | 合计 | |||
1988 | -750.00 | -27.53 | -36.53 | -8.78 | -72.84 | -31.58 | -177.30 | -6.60 | -215.48 | |
1989 | 53017.50 | 1945.74 | 2581.95 | 620.30 | 5147.99 | 2232.04 | 12533.34 | 466.55 | 15231.93 | |
1991 | 6251.25 | 229.42 | 304.44 | 73.14 | 607.00 | 263.18 | 1477.80 | 55.01 | 1795.99 | |
1993 | -22.50 | -0.83 | -1.10 | -0.26 | -2.19 | -0.95 | -5.32 | -0.20 | -6.47 | |
1996 | 15000.00 | 550.50 | 730.50 | 175.50 | 1456.50 | 631.50 | 3546.00 | 132.00 | 4309.50 | |
1997 | 63.75 | 2.34 | 3.10 | 0.75 | 6.19 | 2.68 | 15.07 | 0.56 | 18.31 | |
2001 | -3.75 | -0.14 | -0.18 | -0.04 | -0.36 | -0.16 | -0.89 | -0.03 | -1.08 | |
2002 | -31.25 | -1.15 | -1.52 | -0.37 | -3.04 | -1.32 | -7.39 | -0.28 | -8.99 | |
2003 | -91.25 | -3.35 | -4.44 | -1.07 | -8.86 | -3.84 | -21.57 | -0.80 | -26.21 | |
2004 | -26.25 | -0.96 | -1.28 | -0.31 | -2.55 | -1.11 | -6.21 | -0.23 | -7.55 | |
2005 | -61.25 | -2.25 | -2.98 | -0.72 | -5.95 | -2.58 | -14.48 | -0.54 | -17.60 | |
2006 | -312.50 | -11.47 | -15.22 | -3.66 | -30.35 | -13.16 | -73.88 | -2.75 | -89.79 | |
2007 | -986.25 | -36.20 | -48.03 | -11.54 | -95.77 | -41.52 | -233.15 | -8.68 | -283.35 | |
2008 | -2106.25 | -77.30 | -102.57 | -24.64 | -204.51 | -88.67 | -497.92 | -18.54 | -605.13 | |
2009 | -3538.75 | -129.87 | -172.34 | -41.40 | -343.61 | -148.98 | -836.56 | -31.14 | -1016.68 | |
2010 | -6613.75 | -242.72 | -322.09 | -77.38 | -642.19 | -278.44 | -1563.49 | -58.20 | -1900.13 | |
2011 | 4112.50 | 150.93 | 200.28 | 48.12 | 399.33 | 173.14 | 972.20 | 36.19 | 1181.53 | |
2012 | 715198.75 | 26247.79 | 34830.18 | 8367.83 | 69445.80 | 30109.87 | 169072.98 | 6293.75 | 205476.60 | |
2013 | 514545.00 | 18883.80 | 25058.34 | 6020.18 | 49962.32 | 21662.34 | 121638.44 | 4528.00 | 147828.78 | |
2014 | 499625.00 | 18336.24 | 24331.74 | 5845.61 | 48513.59 | 21034.21 | 118111.35 | 4396.70 | 143542.26 | |
2015 | 547083.75 | 20077.97 | 26642.98 | 6400.88 | 53121.83 | 23032.23 | 129330.60 | 4814.34 | 157177.17 | |
2016 | 868050.00 | 31857.44 | 42274.04 | 10156.19 | 84287.67 | 36544.91 | 205207.02 | 7638.84 | 249390.77 | |
2017 | 331657.50 | 12171.83 | 16151.72 | 3880.39 | 32203.94 | 13962.78 | 78403.83 | 2918.59 | 95285.20 | |
累计 | 3540061.25 | 129920.23 | 172400.99 | 41418.72 | 343739.94 | 149036.57 | 836870.47 | 31152.54 | 1017059.58 |
表7
中巴两国水资源规模"
水资源规模 | 1988—1992年 | 1993—1997年 | 1998—2002年 | 2003—2007年 | 2008—2012年 | 2013—2017年 |
---|---|---|---|---|---|---|
中国 | ||||||
长期年平均降水量深度/(mm/年) | 645 | 645 | 645 | 645 | 645 | 645 |
长期年平均降水量体积/(10亿m3/年) | 6192 | 6192 | 6192 | 6192 | 6192 | 6192 |
人均可再生水资源总量/(m3/人/年) | 2307 | 2206 | 2139 | 2077 | 2020 | 1971 |
农业平均用水量/(10亿m3/年) | 415 | 407.7 | 378.4 | 360 | 388 | 385.2 |
农业用水量占总用水量百分比/% | 83 | 77.6 | 68.83 | 63.01 | 64.31 | 64.4 |
人均年用水总量/(m3/人/年) | 406.2 | 408.1 | 414 | 417.9 | 429 | 415 |
巴基斯坦 | ||||||
长期年平均降水量深度/(mm/年) | 494 | 494 | 494 | 494 | 494 | 494 |
长期年平均降水量体积/(10亿m3/年) | 393.3 | 393.3 | 393.3 | 393.3 | 393.3 | 393.3 |
人均可再生水资源总量/(m3/人/年) | 2170 | 1912 | 1706 | 1539 | 1387 | 1253 |
农业平均用水量/(10亿m3/年) | 150.6 | — | 162.7 | — | 172.4 | — |
农业用水量占总用水量百分比/% | 96.79 | — | 94.26 | — | 93.95 | — |
人均年用水总量/(m3/人/年) | 1368 | — | 1193 | — | 1031 | — |
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