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Frontiers of Environmental Science & Engineering

ISSN 2095-2201

ISSN 2095-221X(Online)

CN 10-1013/X

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2018 Impact Factor: 3.883

Front Envir Sci Eng    0, Vol. Issue () : 743-752    https://doi.org/10.1007/s11783-011-0385-4
RESEARCH ARTICLE
Ecosystem service tradeoff between traditional and modern agriculture: a case study in Congjiang County, Guizhou Province, China
Dan ZHANG1,2, Qingwen MIN1(), Moucheng LIU1, Shengkui CHENG1
1. Institute of Geographic Sciences and Natural Resources Research, Chinese Academy of Sciences, Beijing 100101, China; 2. Graduate School of Chinese Academy of Sciences, Beijing 100049, China
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Abstract

Besides crops, agriculture supplies all three major categories of ecosystem services (ES). However, agriculture also supplies an array of ecosystem dis-services (EDS) that may harm other ecosystems. The flows of ES and EDS are directly dependent on the management of agricultural ecosystems. The traditional method of Chinese agriculture, which supports sustainable agriculture, has been proven to increase ES and reduce EDS. However, there is a lack of a detailed understanding of the ES and EDS associated with traditional agriculture, and also of differences between traditional and modern agriculture.

In this study, an investigation was conducted on the ecosystem services (ES) and ecosystem dis-services (EDS) of traditional and modern agriculture in Congjiang County, Guizhou Province, China. Afterwards, the economic values of ES and EDS were quantified experimentally and calculated based on the market price. The results show that: the net economic value of traditional rice-fish agriculture was 3.31×104 CNY·ha-1 (6.83 CNY= 1 USD as of July, 2009) and that of rice monoculture was 1.99×104 CNY·ha-1. Significant differences existed between traditional rice-fish and rice monoculture fields for their economic values of some ES or EDS.

A benefit and cost analysis (BCA) model was used to adjust the conflict between the economic income and environmental loss from traditional and modern agriculture. The BCA model not only calculates the net income but also monetizes the EDS of the agricultural systems. The results showed that the net income of rice-fish agriculture was 1.94×104 CNY·ha-1 higher than that of rice monoculture. However, the benefit to cost ratio (BCR) of rice-fish agriculture was lower than that of rice monoculture, indicating that the traditional agricultural model was not the most optimized choice for farmers. The value of the rice-fish agriculture was much higher than that of the rice monoculture. Thus, when considering the benefits that rice-fish agriculture contributes to the large-scale society, these agricultural methods needs to be utilized. Furthermore, the labor opportunity costs were calculated and the comprehensive value of rice monoculture was negative. Finally, the compensation standard was calculated based on the comprehensive benefit analysis. The lowest level was 1.09×103 CNY·ha-1, and the highest level was 1.21×104 CNY·ha-1.

Keywords traditional agriculture      rice-fish agriculture      rice monoculture      benefit and cost analysis (BCA)      ecosystem services (ES)      ecosystem dis-services (EDS)     
Corresponding Author(s): MIN Qingwen,Email:minqw@igsnrr.ac.cn   
Issue Date: 01 October 2012
 Cite this article:   
Dan ZHANG,Qingwen MIN,Moucheng LIU, et al. Ecosystem service tradeoff between traditional and modern agriculture: a case study in Congjiang County, Guizhou Province, China[J]. Front Envir Sci Eng, 0, (): 743-752.
 URL:  
https://academic.hep.com.cn/fese/EN/10.1007/s11783-011-0385-4
https://academic.hep.com.cn/fese/EN/Y0/V/I/743
Fig.1  Study area: Congjiang County of the South-east Guizhou Miao and Dong Autonomous Prefecture, Xiaohuang is a village
Fig.2  The incidence of pests in rice-fish agriculture field (RF) and rice monoculture field (HR)
weed speciesdensity
HRRF
Ceratophyllum demirsum32a7.6b
Potamogeton distinctus12a0b
Sagittaria pygmaea12.6a0.2ac
Hydrila vercillata6.2a0b
Monochoria vaginalis7.9a0b
Rotala indica6.4a0.6b
Salvinia natans3.8a0ab
Ottelia alismoides3a0ab
Utricularia aurea2.4a1b
Eleocharis yokoscensis4a0b
Sagittaria sagittifolia.2.2a0b
Marsilea quadrifolia1.6a0.8ab
Echinochloa crusgalli0.2b0.2b
Eleoohayis plantagineif0.2a0b
Tab.1  The density of weeds in RF and HR
rice-fish agriculturerice monoculture
quantity/( kg·hm -2)value /(CNY·hm-2)quantity/(kg·hm -2)value /(CNY·hm -2)
rice7.04 × 1031.09 × 1049.08 × 1031.40 × 104
rice straw stalk6.14 × 1031.14 × 1038.46 × 1031.57 × 103
fish0.3 × 1030.90 × 104--
total-2.10 × 104-1.56 × 104
Tab.2  The economic values of primary products provided by RF and HR
treatmentbiomass/(kg·ha -1)O2 emission/(kg·ha-1)value of O2 emission/(CNY·ha-1)
rice-fish agriculture16281.6119375.116975.04
rice monoculture20252.10241008626.75
Tab.3  Biomass and O emission and their economic values from RF and HR
itemrice-fish agriculturerice monoculture
food and material productionoutput2.10×1031.56×104
input1.56×103-3.50×102
oxygen production6.98×1048.63×103
climate regulationCO2 uptake1.37×1031.11×103
CH4 emission-6.33×102-8.49×102
N2O emission-28.3-18.5
water regulation6.80×1032.27×103
waste treatmentpollution of water-2.24×103-6.44×103
absorb SO28.008.00
biologic control6070.00
recreation and culture8400.00
totalES3.76×1042.72×104
EDS-4.46×103-7.31×103
NV3.31×1041.99×104
Tab.4  The ecological (dis-)service value of rice-fish ecosystem and rice monoculture/(CNY·ha)
Fig.3  Distribution of ecosystem services (ES) function for rice-fish agriculture
itemrice-fish agriculturerice monoculture
outputrice1.09×1041.40×104
fish9.00×103-
rice straw stalk1.14×1031.57×103
subtotal2.10×1041.56×104
inputseed2.12×1021.25×102
fish fry7.34×102-
feed4.97×102-
fertilizer and pesticide1.21×1022.25×102
subtotal1.56×1033.50×102
NV1.94×1041.52×104
BCR13.444.5
Tab.5  The net income of rice-fish agriculture and rice monoculture/(CNY·ha)
itemrice-fish agriculturerice monoculture
NV/(CNY·ha-1)3.31×1041.99×104
BCR8.413.60
Tab.6  Result of benefit and cost analysis based on the ES
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