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Journal of Zhejiang University (Agriculture and Life Sciences)  2019, Vol. 45 Issue (3): 355-364    DOI: 10.3785/j.issn.1008-9209.2018.10.220
Resource utilization & environmental protection     
Allocation analysis of natural and cultivated grassland resources of eco-family pasture based on the theory of grassland agro-ecosystem discordance
Li FU1,2(),Yingzhong XIE1(),Hongbin MA1,Ende XING3,Xiumin TIAN3
1. College of Agriculture, Ningxia University, Yinchuan 750021, China
2. College of Xinhua, Ningxia University, Yinchuan 750021, China
3. Institute of Water Resources for Pastoral Area, Ministry of Water Resources, Hohhot 010020, China
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Abstract  

In order to achieve sustainable development in pastoral areas, based on the theory of grassland agro-ecosystem discordance, we selected the meteorological factors in the study area of Otog Front Banner in recent 30 years and the water, soil, grass, and livestock in the area in recent years as the objects of study to discuss how to make a grassland resource allocation plan. The result showed that the natural environment in the study area was harsh and the annual precipitation was very limited; the groundwater resources were abundant but unevenly distributed, and the water consumption for agriculture and animal husbandry exceeded the expected limit. The proportion of natural grassland was obvious, but the overgrazing was serious, and the ecosystem was fragile, and the contradiction of herbage resources was prominent. The most important problem was time paradox, followed by space paradox, and finally by species paradox in the development of family ranches. Meanwhile, in the time paradox, it was necessary to reasonable matching cultivation of grassland resources according to the shortage period and surplus period of natural grassland; in the space paradox, on the one hand, developing high-yielding and high-quality cultivated grasslands to replace natural grassland functions in the towns of Aolezhaoqi and Chengchuan, and on the other hand, it was necessary to strictly control over the stock capacity of natural grassland, develop short-term fattening and improve turnover efficiency in the towns of Aangsu and Shanghaimiao.



Key wordssystem discordance      desert steppe      ecology      family pasture      resource allocation     
Received: 22 October 2018      Published: 25 June 2019
CLC:  S 812.8  
Corresponding Authors: Yingzhong XIE     E-mail: fuli39501793@163.com;xieyz@nxu.edu.cn
Cite this article:

Li FU,Yingzhong XIE,Hongbin MA,Ende XING,Xiumin TIAN. Allocation analysis of natural and cultivated grassland resources of eco-family pasture based on the theory of grassland agro-ecosystem discordance. Journal of Zhejiang University (Agriculture and Life Sciences), 2019, 45(3): 355-364.

URL:

http://www.zjujournals.com/agr/10.3785/j.issn.1008-9209.2018.10.220     OR     http://www.zjujournals.com/agr/Y2019/V45/I3/355


基于系统相悖理论的生态家庭牧场天然与栽培草地资源配置探析

选取鄂托克前旗研究区近30年气象因子及近年来的水、土、草、畜为研究对象,以草地农业生态系统相悖理论为基础,探讨生态家庭牧场天然与栽培草地资源配置方案,实现牧区可持续发展。结果表明:研究区自然环境恶劣,年降水量非常有限,地下水资源丰富但分布不均,农牧业用水量超过预期限额;天然牧草地比重优势明显,但过度放牧严重,生态脆弱,牧草资源极其短缺;发展生态家庭牧场,时间相悖问题最为关键,空间相悖次之,种间相悖居后。其中:在时间相悖中,需要根据天然草场的亏缺和盈余期,合理配套栽培饲草料;在空间相悖中,在敖勒召其镇和城川镇可发展高产优质栽培草地,置换天然草地的功能,而在昂素镇和上海庙镇,需要严格控制天然草地载畜量,发展短期育肥,提高周转效率。


关键词: 系统相悖,  荒漠草原,  生态,  家庭牧场,  资源配置 
Fig. 1 Annual precipitation in research area over the past 30 years
Fig. 2 Time series of meteorological factors in research area over the past 30 years

参量

Parameter

统计量

Statistic

月平均降水量

Monthly average

precipitation

月平均相对湿度

Monthly average

relative humidity

月平均日照时数Monthly average

sunshine hours

月平均风速

Monthly average

wind speed

月平均相对湿度

Monthly average relative humidity

Pearson相关 0.445**
显著性(单侧) 0

月平均日照时数

Monthly average sunshine hours

Pearson相关 0.187** -0.470**
显著性(单侧) 0 0

月平均风速

Monthly average wind speed

Pearson相关 -0.005 -0.477** 0.407**
显著性(单侧) 0.463 0 0

月平均气温

Monthly mean temperature

Pearson相关 0.596** 0.035 0.644** 0.243**
显著性(单侧) 0 0.252 0 0
Table 1 Correlation matrix in research area over the past 30 years

地点

Location

供水量 Water supply

农牧业用水及其占比

Water for agriculture and livestock husbandry and its proportion

总量Total/(104 m3) 地下水Groundwater/(104 m3) 地下水占比Proportion of groundwater/%

农业灌溉

Agricultural irrigation/(104 m3)

家畜饮水Livestock drinking water/(104 m3)

占比

Proportion/%

方正汇总行合计

Total

13 691.0 12 327.0 90.0 12 144.0 478.0 92.2

敖勒召其镇

Aolezhaoqi Town

2 556.0 2 555.0 100.0 2 177.0 101.0 89.1

上海庙镇

Shanghaimiao Town

2 778.0 1 863.0 67.1 2 054.0 79.0 76.8

城川镇

Chengchuan Town

6 076.0 5 628.0 92.6 5 774.0 208.0 98.5

昂素镇

Aangsu Town

2 281.0 2 281.0 100.0 2 139.0 90.0 97.7
Table 2 Water supply and use in research area (2015)

地点

Location

耕地 Farmland 林地 Woodland 牧草地 Meadow

总面积

Total area/(104 hm2)

面积

Area/(104 hm2)

百分比

Percentage/%

面积

Area/(104 hm2)

百分比

Percentage/%

面积

Area/(104 hm2)

百分比

Percentage/%

方正汇总行合计

Total

2.2 1.8 25.4 20.8 75.2 61.6 122.2

敖勒召其镇

Aolezhaoqi Town

0.4 2.8 4.0 25.1 8.6 53.8 16.0

上海庙镇

Shanghaimiao Town

0.3 0.7 6.4 16.3 28.7 73.8 38.9

城川镇

Chengchuan Town

1.0 4.1 5.6 23.2 11.4 46.8 24.3

昂素镇

Aangsu Town

0.5 1.1 9.4 22.0 26.5 61.8 42.9
Table 3 Survey of agricultural land in research area

参量

Parameter

统计量

Statistic

牧草地

Meadow

总供水量

Water supply

耕地

Farmland

林地

Woodland

农业灌溉

Agricultural irrigation

总供水量

Water supply

Pearson相关 -0.474
显著性 0.526

耕地

Farmland

Pearson 相关 -0.487 0.929
显著性 0.513 0.071

林地

Woodland

Pearson 相关 0.767 -0.287 -0.071
显著性 0.233 0.713 0.929

农业灌溉

Agricultural irrigation

Pearson 相关 -0.500 0.991** 0.970* -0.227
显著性 0.500 0.009 0.030 0.773

家畜饮水

Livestock drinking water

Pearson 相关 -0.595 0.974* 0.974* -0.283 0.992**
显著性 0.405 0.026 0.026 0.717 0.008
Table 4 Correlation analysis between land use and water resources in research area
Fig. 3 Supply and demand relationship between natural and artificial forage in research area

年份

Year

Sheep & goat

大牲畜

Large animals

年末牲畜存栏头数

Total livestock at the year-end

总量 Total 距平 Anomaly 总量 Total 距平 Anomaly 总量 Total 距平 Anomaly
2007 73.7 -3.3 3.7 0.2 82.3 -3.3
2008 69.3 -7.7 3.7 0.2 78.3 -7.3
2009 72.3 -4.7 3.6 0.1 81.5 -4.1
2010 70.7 -6.3 3.1 -0.4 79.2 -6.4
2011 76.0 -1.0 3.2 -0.3 84.8 -0.8
2012 79.6 2.6 3.7 0.2 89.0 3.4
2013 80.7 3.7 3.5 0.0 90.1 4.5
2014 82.0 5.0 3.5 0.0 91.2 5.6
2015 83.7 6.7 3.4 -0.1 92.5 6.9
2016 82.3 5.3 3.9 0.4 87.3 1.7
Table 5 Structure of livestock in research area104 heads
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