TRADE-OFFS BETWEEN BIOMASS USE AND SOIL COVER. THE CASE OF RICE-BASED CROPPING SYSTEMS IN THE LAKE ALAOTRA REGION OF MADAGASCAR

SUMMARY Farmers in the Lake Alaotra region of Madagascar are currently evaluating a range of conservation agriculture (CA) cropping systems. Most of the expected agroecological functions of CA (weed control, erosion control and water retention) are related to the degree of soil cover. Under farmers’ conditions, the grain and biomass productivity of these systems is highly variable and the biomass is used for several purposes. In this study, we measured biomass production of cover crops and crops in farmers’ fields. Further, we derived relationships to predict the soil cover that can be generated for a particular quantity of mulch. We used these relationships to explore the variability of soil cover that can be generated in farmers’ fields, and to estimate how much of the biomass can be removed for use as livestock feed, while retaining sufficient soil cover. Three different kinds of cropping systems were investigated in 91 farmers’ fields. The first two cropping sequences were on the hillsides: (i) maize + pulse (Vigna unguiculata or Dolichos lablab) in year 1, followed by upland rice in year 2; (ii) the second crop sequence included several years of Stylosanthes guianensis followed by upland rice; (iii) the third crop sequence was in lowland paddy fields: Vicia villosa or D. lablab, which was followed by rice within the same year and repeated every year. The biomass available prior to rice sowing varied from 3.6 t ha−1 with S. guianensis to 7.3 t ha−1 with V. villosa. The relationship between the mulch quantity (M) and soil cover (C) was measured using digital imaging and was well described by the following equation: C = 1 − exp(−Am × M), where Am is an area-to-mass ratio with R2 > 0.99 in all cases. The calculated average soil cover varied from 56 to 97% for maize + V. unguiculata and V. villosa, respectively. In order to maintain 90% soil cover at rice sowing, the average amount of biomass of V. villosa that could be removed was at least 3 t ha−1 for three quarters of the fields. This quantity was less for other annual or biennial cropping systems. On average the V. villosa aboveground biomass contained 236 kg N ha−1. The study showed that for the conditions of farmers of Malagasy, the production and conservation of biomass is not always sufficient to fulfil all the above-cited agroecological functions of mulch. Inventory of the soil cover capacity for different types of mulch may help farmers to decide how much biomass they can remove from the field.

[1]  K. Giller,et al.  Conservation agriculture and smallholder farming in Africa: The heretics' view , 2009 .

[2]  Éric Scopel,et al.  Le semis direct avec paillis de résidus dans l'ouest mexicain : une histoire d'eau ? , 1999 .

[3]  M. Bernoux,et al.  Soil Carbon stocks under no-tillage mulch-based cropping systems in the Brazilian Cerrado: an on-farm synchronic assessment , 2010 .

[4]  K. Naudin,et al.  Stockage de carbone dans les sols sous systèmes de culture en semis direct sous couvert vègètal (SCV) dans diffèrents contextes pèdoclimatiques à Madagascar , 2010 .

[5]  A. Wezel,et al.  Resource conservation strategies in agro-ecosystems of semi-arid West Africa , 2002 .

[6]  Fernando-Antonio Macena Da Silva,et al.  Modelling crop residue mulching effects on water use and production of maize under semi-arid and humid tropical conditions , 2004 .

[7]  P. Hobbs,et al.  Conservation Agriculture : What Is It and Why Is It Important for Future Sustainable Food Production ? , 2006 .

[8]  D. Reicosky Carbon sequestration and environmental benefits from no-till systems , 2008 .

[9]  J. Teasdale,et al.  Light transmittance, soil temperature, and soil moisture under residue of hairy vetch and rye , 1993 .

[10]  Upendra M. Sainju,et al.  Tillage, cover crops, and nitrogen fertilization effects on soil nitrogen and cotton and sorghum yields , 2006 .

[11]  James M. Gregory,et al.  Soil Cover Prediction with Various Amounts and Types of Crop Residue , 1982 .

[12]  Keith D. Shepherd,et al.  Rapid characterization of Organic Resource Quality for Soil and Livestock Management in Tropical Agroecosystems Using Near Infrared Spectroscopy. , 2003 .

[13]  C. Thierfelder,et al.  ROTATION IN CONSERVATION AGRICULTURE SYSTEMS OF ZAMBIA: EFFECTS ON SOIL QUALITY AND WATER RELATIONS , 2010, Experimental Agriculture.

[14]  B. Govaerts,et al.  Influence of permanent raised bed planting and residue management on physical and chemical soil quality in rain fed maize/wheat systems , 2007, Plant and Soil.

[15]  Kazuki Saito,et al.  Combined effects of Stylosanthes guianensis fallow and tillage management on upland rice yield, weeds and soils in southern Benin , 2010 .

[16]  K. Giller,et al.  Future benefits from biological nitrogen fixation: An ecological approach to agriculture , 1995, Plant and Soil.

[17]  J. Deckers,et al.  Stable high yields with zero tillage and permanent bed planting , 2005 .

[18]  J. Poesen,et al.  Spatial scale effects on the effectiveness of organic mulches in reducing soil erosion by water , 2008 .

[19]  B. Stinner An Ecological Approach to Agriculture , 1993 .

[20]  N. P. Cogo,et al.  Erosão hídrica influenciada por condições físicas de superfície e subsuperfície do solo resultantes do seu manejo, na ausência de cobertura vegetal , 2004 .

[21]  K. Giller,et al.  Yield gaps, nutrient use efficiencies and response to fertilisers by maize across heterogeneous smallholder farms of western Kenya , 2008, Plant and Soil.

[22]  E. Gozé,et al.  Impact of no tillage and mulching practices on cotton production in North Cameroon: A multi-locational on-farm assessment , 2010 .

[23]  G. Roberge,et al.  Cultures fourragères tropicales , 1999 .

[24]  Dimitrios Bilalis,et al.  Effect of Different Levels of Wheat Straw Soil Surface Coverage on Weed Flora in Vicia faba Crops , 2003 .

[25]  John R. Teasdale,et al.  The quantitative relationship between weed emergence and the physical properties of mulches , 2000, Weed Science.

[26]  E. Scopel,et al.  Cover Crop and Nitrogen Effects on Maize Productivity in No‐Tillage Systems of the Brazilian Cerrados , 2009 .

[27]  P. Unger,et al.  Biomass and residue cover relationships of fresh and decomposing small grain residue. , 2000 .

[28]  John E. Gilley,et al.  Runoff and Erosion as Affected by Corn Residue: Part I. Total Losses , 1986 .

[29]  Olaf Erenstein,et al.  Smallholder conservation farming in the tropics and sub-tropics: a guide to the development and dissemination of mulching with crop residues and cover crops , 2003 .

[30]  P. Lecomte,et al.  Species, climate and fertilizer effects on grass fibre and protein in tropical environments , 2009, The Journal of Agricultural Science.

[31]  M. Rufino,et al.  Nitrogen cycling efficiencies through resource-poor African crop-livestock systems , 2006 .