1.2 参与该技术评估和文件编制的资源人员和机构的联系方式

有助于对技术进行记录/评估的项目名称（如相关）

DESIRE (EU-DES!RE)

有助于对技术进行记录/评估的机构名称（如相关）

EEZA-CSIC (EEZA-CSIC) - 西班牙

1.3 关于使用通过WOCAT记录的数据的条件

（现场）数据是什么时候汇编的？:

12/06/2008

编制者和关键资源人员接受有关使用通过WOCAT记录数据的条件。:

是

1.4 所述技术的可持续性声明

这里所描述的技术在土地退化方面是否存在问题，导致无法被认为是一种可持续的土地管理技术？:

否

1.5 请参阅有关SLM方法的问卷

2.1 技术简介

技术定义:

Reduced contour tillage in a rotational system of winter cereals and fallow land.

2.2 技术的详细说明

说明:

This technology is a type of conservation tillage with minimal economic effort and is adapted to semi-arid conditions. Tillage is reduced to a maximum of three times surface tillage (20-30cm) in two years with a disc- or a chisel-plough. The disc-plough is only used where there is a dense weed or crop residue cover. The disc-plough breaks-up the soil top layer better than the chisel-plough, while the chisel tends to plough slightly deeper (~30cm) than the disc-plough (~20cm). The advantage of the chisel-plough is that it leaves a higher surface roughness and is less destructive to soil aggregates. Under conventional tillage, fields are ploughed up to five times every two years, once with a mouldboard plough. In both systems, cereals are cropped in a rotational system with fallow land. Cereals are sown in autumn (October) and harvested in June followed by a fallow year. Under reduced tillage the crop residues are left on the field throughout the autumn and winter periods. This provides increased protection against soil erosion. Tillage is performed on fallow land in early spring (March-April) to prepare the land for sowing in October. With conventional tillage, fields are ploughed with a mouldboard plough in autumn. Traditional sowing machinery can be used so no investments are needed in specialised equipment. Tillage is performed parallel to the contour lines to prevent rill and gully formation. No herbicides are required since annual weeds are mixed with the upper soil layer during ploughing. Owing to increased organic matter content and a better infiltration capacity, soil water retention capacity, soil humidity and crop yields will increase within 3-5 years after implementation.
The aim of this technology is to increase the soil organic matter content by retaining it in soil aggregates and to reduce soil erosion by water and tillage. The higher infiltration capacity and better surface cover with crop residues in autumn and winter protects the soil against water erosion, reducing soil erosion by over 50% and runoff by 30%. In addition, the better organic matter content increases overall soil quality in terms of soil structure and water holding capacity. Compared to traditional multiple tillage operations with a mouldboard plough, under reduced tillage, tillage erosion is reduced by having fewer tillage operations, but also through tillage of fallow land resulting in lower tillage erosion rates than secondary tillage operations of already loosened soil. Fuel use by tractors is decreased, leading to a reduction of 40% in production costs and reduced CO2 emissions. Some studies showed that in first 2-3 years after implementation, the soil can be denser and have a lower infiltration capacity than under traditional tillage regimes. Yet, when the organic matter content and soil structure have increased, infiltration rates are higher than under traditional ploughing and result in increased soil water content and crop yields.
The technology is applied on loamy soils with a calcareous substrate, of shallow to medium depth, and slopes are gentle to moderate (5-15%). The climate is semi-arid with a mean annual rainfall of around 300 mm. Droughts, centred in summer commonly last for more than 4-5 months. Annual potential evapotranspiration rates greater than 1000 mm are common. The production system is highly mechanised and market oriented but depends strongly on agricultural subsidies.

2.3 技术照片

2.5 已应用该技术的、本评估所涵盖的国家/地区/地点

2.6 实施日期

如果不知道确切的年份，请说明大概的日期:

• 不到10年前（最近）

2.7 技术介绍

详细说明该技术是如何引入的:

• 通过土地使用者的创新
• 在实验/研究期间

注释（项目类型等）:

Conservation tillage is well-known from other areas around the world. Here, it was adapted to the semi-arid and low productivity conditions of this area.

3.1 该技术的主要目的

• 减少、预防、恢复土地退化

3.2 应用该技术的当前土地利用类型

注释:

Major land use problems (compiler’s opinion): There is a lack of water for irrigation of crops limiting the crop types that can be planted as well as the crop yield of dryland farming. A lack of water availability seriously limits the production potential of the soil and results in a low vegetation/crop cover. The relatively high soil erosion rates cause various off-site related problems (i.e. flooding, reservoir siltation) and on-site problems (i.e. gully formation and reduced soil depth).
Major land use problems (land users’ perception): Lack of water for irrigation of crops limiting the crop types that can be planted as well as the crop yield of dryland farming.

Livestock is grazing on crop residues.

3.3 有关土地利用的更多信息

该技术所应用土地的供水:

• 雨养

每年的生长季节数:

• 1

具体说明:

Longest growing period in days: 220 (Nov - Jun)

3.4 该技术所属的SLM组

• 最小的土壤扰动

3.5 技术传播

具体说明该技术的分布:

• 均匀地分布在一个区域

如果该技术均匀地分布在一个区域上，请注明覆盖的大致区域。:

• 10-100 平方千米

注释:

The exact area is not known, but the technology is widely applied throughout the province of Murcia and the district of the upper Guadalentin.

3.6 包含该技术的可持续土地管理措施

注释:

Type of agronomic measures: rotations / fallows, breaking crust / sealed surface, breaking compacted topsoil, minimum tillage, non-inversion tillage, contour tillage

3.7 该技术强调的主要土地退化类型

注释:

Main type of degradation addressed: Wt: loss of topsoil / surface erosion, Pk: sealing and crusting, Ha: aridification. Secondary types of degradation addressed: Wg: gully erosion / gullying.

Main causes of degradation: soil management (Crust formation, loss of soil organic matter, loss of soil structure, loss of available soil water and finally soil loss .), disturbance of water cycle (infiltration / runoff) (Reduced infiltration capacity causing runoff and soil erosion), inputs and infrastructure: (roads, markets, distribution of water points, other, …) (Low market price of cereals)
Secondary causes of degradation: Heavy / extreme rainfall (intensity/amounts) (High intensity erosive rainfall is common), droughts (Dry periods and dry years require higher water availability), governance / institutional (Spatial planning of land use and control of soil management)

3.8 防止、减少或恢复土地退化

具体数量名该技术与土地退化有关的目标:

• 防止土地退化
• 减少土地退化

4.1 该技术的技术图纸

4.2 技术规范/技术图纸说明

Photo of the disc-plough used for superficial ploughing (~20cm depth) where there is a large amount of crop residue and/or perennial vegetation. Bottom: Chisel-plough

Technical knowledge required for field staff / advisors: moderate. Technical knowledge required for land users: moderate.

Main technical functions: control of raindrop splash, control of dispersed runoff: retain / trap, control of dispersed runoff: impede / retard, control of concentrated runoff: impede / retard, improvement of ground cover, improvement of surface structure (crusting, sealing), improvement of topsoil structure (compaction), improvement of subsoil structure (hardpan), increase in organic matter, increase of infiltration, increase / maintain water stored in soil. Secondary technical functions: increase of surface roughness, increase in nutrient availability (supply, recycling,…)

Rotations / fallows: cereals are followed by 1-2 years of fallow

Breaking crust / sealed surface / compacted topsoi: Disc-plough or chisel-plough

Minimum tillage: Disc-plough or chisel-plough

Non-inversion tillage: Disc-plough or chisel-plough

Contour tillage: Disc-plough or chisel-plough

4.3 有关投入和成本计算的一般信息

其它/国家货币（具体说明）:

Euro

注明美元与当地货币的汇率(如相关):1美元=:

0.63

4.5 技术建立所需要的费用和投入

	对投入进行具体说明	单位	数量	单位成本	每项投入的总成本	土地使用者承担的成本%
劳动力	Disc plough	piece	1.0	397.0	397.0	100.0
技术建立所需总成本					397.0

注释:

The disc plough costs USD 7937, but assuming an average farm size of 10 ha, this means a per ha cost of $794 (Prices are for spring 2008). Two parties are sharing the costs. Initial investment per party = USD 397

4.6 维护/经常性活动

	活动	措施类型	时间/频率
1.	Tillage with disc-plough	农业学的	Before seeding once every 2 years in a rotational fallow system

4.7 维护/经常性活动所需要的费用和投入（每年）

	对投入进行具体说明	单位	数量	单位成本	每项投入的总成本	土地使用者承担的成本%
劳动力	Labour		1.0	12.0	12.0	100.0
设备	Machine hours		1.0	50.0	50.0	99.0
技术维护所需总成本					62.0

注释:

Machinery/ tools: Disc-plough and/or chisel-plough and tractor

The costs are indicated per ha of land where the technology is implemented.

4.8 影响成本的最重要因素

描述影响成本的最决定性因素:

Fuel price is the most determinate factor affecting the costs.

5.1 气候

5.2 地形

说明该技术是否专门应用于:

• 不相关

5.3 土壤

5.4 水资源可用性和质量

关于水质和水量的注释和进一步规范:

There is a lowering of groundwater table due to overexploitation for irrigation purposes.

5.5 生物多样性

5.6 应用该技术的土地使用者的特征

说明土地使用者的其他有关特征:

Land users applying the Technology are mainly common / average land users.
Difference in the involvement of women and men: Traditionally most agriculture is done by men in this region.

Population density: 10-50 persons/km2
Annual population growth: < 0.5%

15% of the land users are rich and own 20% of the land. 80% of the land users are average wealthy and own 75% of the land. 5% of the land users are poor and own 5% of the land.

Off-farm income specification: There is no difference in the ones who apply the technology and those who do not. Most farmers do have an off-farm income for example from hunting, work in a factory or office.

5.7 应用该技术的土地使用者拥有或租用的平均土地面积

5.8 土地所有权、土地使用权和水使用权

土地所有权:

• 个人，有命名

土地使用权:

• 个人

用水权:

• 个人

注释:

All cropland is privately owned. Water use is organised by permits to water extraction from aquifers on individual basis. Water rights are provided and controlled by the Water authority of the Segura river basin (CHS).

5.9 进入服务和基础设施的通道

6.1 该技术的现场影响

社会经济效应

生产

收入和成本

社会文化影响

生态影响

水循环/径流

土壤

减少气候和灾害风险

6.2 该技术的场外影响已经显现

6.3 技术对渐变气候以及与气候相关的极端情况/灾害的暴露和敏感性（土地使用者认为的极端情况/灾害）

渐变气候

渐变气候

	季节	气候变化/极端天气的类型	该技术是如何应对的？
年温度		增加	不好

气候有关的极端情况（灾害）

气象灾害

	该技术是如何应对的？
局地暴雨	好
局地风暴	好

气候灾害

	该技术是如何应对的？
干旱	不好

水文灾害

	该技术是如何应对的？
比较和缓的（河道）洪水	好

其他气候相关的后果

其他气候相关的后果

	该技术是如何应对的？
缩短生长期	好

注释:

The crop type is sensitive to changes in water availability under the semi arid conditions.

6.4 成本效益分析

技术收益与技术建立成本相比如何（从土地使用者的角度看）？

技术收益与技术维护成本/经常性成本相比如何（从土地使用者的角度看）？

注释:

When a disc-plough was not already used in normal farming operations, this implies a slightly negative influence on farm income during establishment.

6.5 技术采用

在所有采用这项技术的人当中，有多少人是自发地采用该技术，即未获得任何物质奖励/付款？:

• 0-10%

注释:

Reduced tillage is not subsidised and so is implemented 100% voluntary. However, there are subsidies for parts of the technology such as contour ploughing and rotational farming allowing a fallow period (1-2 years) after cereals. Practically 100 % of farmers use these subsidies.

There seems to be a growing public awareness of the fact that frequent deep rotational ploughing is not always necessary.

6.7 该技术的优点/长处/机会

土地使用者眼中的长处/优势/机会

The technology is low cost and even generates more farm income due to lower fuel use. The increased soil cover through winter and the contour ploughing have a notable positive effect on rill and gully formation in the fields. (How to sustain: The tillage between two fallow periods might be avoided to further reduce fuel use and maintain surface cover intact. However, in order to apply for subsidies for agricultural extensification, farmers are obliged to plough fallow land once a year in order to eliminate weeds.)

编制者或其他关键资源人员认为的长处/优势/机会
This is a low-cost technology that requires limited initial investments in equipment and potentially results in a slightly increased farm income, as well as a decrease in land degradation and an increase in soil quality and water-holding capacity. (How to sustain: In some higher areas with sufficient rainfall, the technology might be adapted to conservation tillage with direct sowing, reducing the tillage operations even more. However, this implies an important investment in machinery and a high level of organisation at the agricultural cooperation level.)
An increased soil surface cover throughout autumn and winter provides a good protection against soil erosion reducing rill and gully formation. (How to sustain: Sometimes a field is left fallow for two consecutive years, but it is still ploughed between them. This ploughing might be avoided as well.)

6.8 技术的弱点/缺点/风险及其克服方法

土地使用者认为的弱点/缺点/风险	如何克服它们？
In order to apply for subsidies for cereal cultivation in a rotation system with fallow, farmers are obliged to plough after each fallow period to control weeds, even when two consecutive years of fallow are applied. This is considered unnecessary	It might be worthwhile to test the need for this and look for alternatives without ploughing.

编制者或其他关键资源人员认为的弱点/缺点/风险	如何克服它们？
The most important weakness of this technology is that it does not significantly improve farm income and so may not be stimulating enough for farmers to apply	Provide information on all the advantages of good soil management that include many costs for society (including floods, reservoir siltation, etc.) and stress the fact that reduced tillage will lead to less work for the same or slightly higher profit.

7.1 信息的方法/来源

7.2 参考可用出版物

标题、作者、年份、ISBN:

Angás, P., Lampurlanés, J. and Cantero-Martínez, C., 2006. Tillage and N fertilization: Effects on N dynamics and Barley yield under semiarid Mediterranean conditions. Soil and Tillage Research, 87(1): 59-71.

可以从哪里获得?成本如何?

Internet

标题、作者、年份、ISBN:

Holland, J.M., 2004. The environmental consequences of adopting conservation tillage in Europe: reviewing the evidence. Agriculture, Ecosystems & Environment, 103(1): 1-25.

可以从哪里获得?成本如何?

Internet

标题、作者、年份、ISBN:

Hoogmoed, W.B. and Derpsch, R., 1985. Chisel ploughing as an alternative tillage system in Parana, Brazil. Soil and Tillage Research, 6(1): 53-67.

可以从哪里获得?成本如何?

Internet

标题、作者、年份、ISBN:

Josa, R. and Hereter, A., 2005. Effects of tillage systems in dryland farming on near-surface water content during the late winter period. Soil and Tillage Research, 82(2): 173-183.

可以从哪里获得?成本如何?

Internet

标题、作者、年份、ISBN:

Lampurlanés, J. and Cantero-Martínez, C., 2006. Hydraulic conductivity, residue cover and soil surface roughness under different tillage systems in semiarid conditions. Soil and Tillage Research, 85(1-2): 13-26.

可以从哪里获得?成本如何?

Internet

标题、作者、年份、ISBN:

Lampurlanés, J., Angás, P. and Cantero-Martínez, C. 2002. Tillage effects on water storage during fallow, and on barley root growth and yield in two contrasting soils of the semi-arid Segarra region in Spain. Soil and Tillage Research, 65(2): 207-220

可以从哪里获得?成本如何?

Internet

标题、作者、年份、ISBN:

López-Fando, C., Dorado, J. and Pardo, M.T., 2007. Effects of zone-tillage in rotation with no-tillage on soil properties and crop yields in a semi-arid soil from central Spain. Soil and Tillage Research, 95(1-2): 266-276.

可以从哪里获得?成本如何?

Internet

标题、作者、年份、ISBN:

Martin-Rueda, I., Muñoz-Guerra, L.M., Yunta, F., Esteban, E., Tenorio, J.L. and Lucena, J.J., 2007. Tillage and crop rotation effects on barley yield and soil nutrients on a Calciortidic Haploxeralf. Soil and Tillage Research, 92(1-2): 1-9

可以从哪里获得?成本如何?

Internet

标题、作者、年份、ISBN:

Ozpinar, S., 2006. Effects of tillage systems on weed population and economics for winter wheat production under the Mediterranean dryland conditions. Soil and Tillage Research, 87(1): 1-8.

可以从哪里获得?成本如何?

Internet

标题、作者、年份、ISBN:

Van Muysen, W., Govers, G., Van Oost, K. and Van Rompaey, A., 2000. The effect of tillage depth, tillage speed and soil condition on chisel tillage erosivity. Journal of Soil and Water Conservation(355-364).

可以从哪里获得?成本如何?

Internet

标题、作者、年份、ISBN:

Van Muysen, W., Govers, G., Bergkamp, G., Roxo, M. and Poesen, J., 1999. Measurement and modelling of the effects of initial soil conditions and slope gradient on soil translocation by tillage1. Soil and Tillage Research, 51(3-4): 303-316

可以从哪里获得?成本如何?

Internet

标题、作者、年份、ISBN:

Van Oost, K., Govers, G., De Alba, S. and Quine, T.A., 2006. Tillage erosion: a review of controlling factors and implications for soil quality. Progress in Physical Geography, 30(4): 443-466.

可以从哪里获得?成本如何?

Internet

标题、作者、年份、ISBN:

CARM 2008. Programa de Desarrollo Rural de la Región de Murcia 2007-2013 Tomo I. 508pp

可以从哪里获得?成本如何?

http://www.carm.es/neweb2/servlet/integra.servlets.ControlPublico?IDCONTENIDO=4689&IDTIPO=100&RASTRO=c431$m1219

标题、作者、年份、ISBN:

Poesen, J., van Wesemael, B., Govers, G., Martinez-Fernandez, J., Desmet, P., Vandaele, K., Quine, T. and Degraer, G., 1997. Patterns of rock fragment cover generated by tillage erosion. Geomorphology, 18(3-4): 183-197.

可以从哪里获得?成本如何?

Internet