Relationship between raindrop erosion and runoff erosion under simulated rainfall in the Sudano-Sahel: consequences for the spread of nematodes by runoff
This paper presents a rainfall simulation experiment carried out on three 50 m2 plots in the Senegalese groundnut belt. One plot was not cultivated. Groundnut and millet had previously been grown in the other two. The experiment consisted of three rain events applied over 5 days at the end of the dr...
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Published in | Earth surface processes and landforms Vol. 25; no. 7; pp. 729 - 741 |
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Main Authors | , , , , |
Format | Journal Article |
Language | English |
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Chichester, UK
John Wiley & Sons, Ltd
01.07.2000
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Abstract | This paper presents a rainfall simulation experiment carried out on three 50 m2 plots in the Senegalese groundnut belt. One plot was not cultivated. Groundnut and millet had previously been grown in the other two.
The experiment consisted of three rain events applied over 5 days at the end of the dry season. Erosion was monitored inside the plots by the use of a relief meter and, at their outlets, by sampling the discharge. The number of indigenous nematodes, and an exotic species introduced before the first rain event, was monitored in the soil and in the discharge. This experiment allows, for the first time, a set of simple hypotheses to be proposed to explain the spread of nematodes by the runoff: raindrop impacts on the soil surface set them in suspension; then, their low bulk density and their relatively large size do not allow them to settle when the raindrops shake the water surface. Thus, nematodes follow the flow path where they are as far as its velocity remains significant. The biological aspects are decisive in the mobility of nematodes, which can vary by a factor of 100 depending on the trophic groups. A very high raindrop erosion occurred during the experiment, up to 60 tons per hectare for the first rain event after hoeing. This represents more than 40 per cent of the volume of soil previously moved by soil work. The geometric properties of the plough, and their hydraulic consequences, appear very ephemeral. And yet these large movements of soil inside the plots are little related to the sediment load at the outlet, which follows its own rules.
Analysis of the results indicates that the carrying capacity of the runoff at the scale of 10 m2, on gentle slopes ploughed perpendicular to the slope, could not be directly calculable from the discharge. It could depend on the history of past discharges because the shape of the flow paths, which condition their carrying capacity, permanently interacts with the discharge. These interactions could explain the great difficulties encountered by the erosion models in the case of low discharges on non‐cohesive soils. Copyright © 2000 John Wiley & Sons, Ltd. |
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AbstractList | This paper presents a rainfall simulation experiment carried out on three 50 m super(2) plots in the Senegalese groundnut belt. One plot was not cultivated. Groundnut and millet had previously been grown in the other two. The experiment consisted of three rain events applied over 5 days at the end of the dry season. Erosion was monitored inside the plots by the use of a relief meter and, at their outlets, by sampling the discharge. The number of indigenous nematodes, and an exotic species introduced before the first rain event, was monitored in the soil and in the discharge. This experiment allows, for the first time, a set of simple hypotheses to be proposed to explain the spread of nematodes by the runoff: raindrop impacts on the soil surface set them in suspension; then, their low bulk density and their relatively large size do not allow them to settle when the raindrops shake the water surface. Thus, nematodes follow the flow path where they are as far as its velocity remains significant. The biological aspects are decisive in the mobility of nematodes, which can vary by a factor of 100 depending on the trophic groups. A very high raindrop erosion occurred during the experiment, up to 60 tons per hectare for the first rain event after hoeing. This represents more than 40 per cent of the volume of soil previously moved by soil work. The geometric properties of the plough, and their hydraulic consequences, appear very ephemeral. And yet these large movements of soil inside the plots are little related to the sediment load at the outlet, which follows its own rules. Analysis of the results indicates that the carrying capacity of the runoff at the scale of 10 m super(2), on gentle slopes ploughed perpendicular to the slope, could not be directly calculable from the discharge. It could depend on the history of past discharges because the shape of the flow paths, which condition their carrying capacity, permanently interacts with the discharge. These interactions could explain the great difficulties encountered by the erosion models in the case of low discharges on non-cohesive soils. This paper presents a rainfall simulation experiment carried out on three 50 m2 plots in the Senegalese groundnut belt. One plot was not cultivated. Groundnut and millet had previously been grown in the other two. The experiment consisted of three rain events applied over 5 days at the end of the dry season. Erosion was monitored inside the plots by the use of a relief meter and, at their outlets, by sampling the discharge. The number of indigenous nematodes, and an exotic species introduced before the first rain event, was monitored in the soil and in the discharge. This experiment allows, for the first time, a set of simple hypotheses to be proposed to explain the spread of nematodes by the runoff: raindrop impacts on the soil surface set them in suspension; then, their low bulk density and their relatively large size do not allow them to settle when the raindrops shake the water surface. Thus, nematodes follow the flow path where they are as far as its velocity remains significant. The biological aspects are decisive in the mobility of nematodes, which can vary by a factor of 100 depending on the trophic groups. A very high raindrop erosion occurred during the experiment, up to 60 tons per hectare for the first rain event after hoeing. This represents more than 40 per cent of the volume of soil previously moved by soil work. The geometric properties of the plough, and their hydraulic consequences, appear very ephemeral. And yet these large movements of soil inside the plots are little related to the sediment load at the outlet, which follows its own rules. Analysis of the results indicates that the carrying capacity of the runoff at the scale of 10 m2, on gentle slopes ploughed perpendicular to the slope, could not be directly calculable from the discharge. It could depend on the history of past discharges because the shape of the flow paths, which condition their carrying capacity, permanently interacts with the discharge. These interactions could explain the great difficulties encountered by the erosion models in the case of low discharges on non‐cohesive soils. Copyright © 2000 John Wiley & Sons, Ltd. |
Author | Silvera, Norbert Lapetite, Jean-Marc Cadet, Patrice Esteves, Michel Planchon, Olivier |
Author_xml | – sequence: 1 givenname: Olivier surname: Planchon fullname: Planchon, Olivier email: Oliver.Planchon@ird.sn organization: Institut de Recherche pour le Développement (IRD), BP 1386, Dakar, Senegal – sequence: 2 givenname: Patrice surname: Cadet fullname: Cadet, Patrice organization: South African Sugar Association Experiment Station, Private Bag X02, Mount Edgecombe, 4300 KwaZulu Natal, South Africa – sequence: 3 givenname: Jean-Marc surname: Lapetite fullname: Lapetite, Jean-Marc organization: Laboratoire d'étude des transferts en hydrologie et environnement (LTHE), BP 53, 38041 Grenoble Cedex 9, France – sequence: 4 givenname: Norbert surname: Silvera fullname: Silvera, Norbert organization: Institut de Recherche pour le Développement (IRD), BP 1386, Dakar, Senegal – sequence: 5 givenname: Michel surname: Esteves fullname: Esteves, Michel organization: Laboratoire d'étude des transferts en hydrologie et environnement (LTHE), BP 53, 38041 Grenoble Cedex 9, France |
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References | Gilley JE, Kincaid DC, Elliot WJ, Laflen JM. 1992. Sediment delivery on rill and interrill areas. Journal of Hydrology 140: 313-341. Nearing MA, Norton LD, Bulgakov DA, Larionov GA, West LT, Dontsova KM. 1997. Hydraulics and erosion in eroding rills. Water Resources Research 33: 865-876. Cogo NP, Moldenhauer WC, Foster GR. 1983. Effect of crop residue, tillage-induced roughness and runoff velocity on size distribution of eroded soil aggregates. Soil Science Society of America Journal 47: 1005-1008. Luc M, Sikora RA, Bridge J. 1990. Plant Parasitic Nematodes in Subtropical and Tropical Agriculture. CAB International: Wallingford. Bielders CL, Baveye P, Wilding LP, Drees LR, Valentin C. 1996. Tillage-induced spatial distribution of surface crusts on a sandy Paleustult from Togo. Soil Science Society of America Journal 60: 843-855. Planchon O, Esteves M, Silvera N, Lapetite JM. 2000. Raindrop erosion of tillage induced microrelief: possible use of the diffusion equation. Soil and Tillage Research. in press. Abrahams AD, Parsons AJ, Luk SH. 1986. Resistance to overland flow on desert hillslopes. Journal of Hydrology 88: 343-363. Mwendera EJ, Feyen J. 1992. Estimation of depression storage and Manning's resistance coefficient from random roughness measurements. Geoderma 52: 235-250. Seinhorst JW. 1962. Modifications of the elutriation method for extracting nematodes from soil. Nematologica 8: 117. Murthy GVGK, Elias NA. 1970. Vertical distribution pattern of plant parasitic nematodes in Tobacco fields in Mysore. Indian Phytopathology XXII: 252-254. Nearing MA. 1998. Why soil erosion models over-predict small soil losses and under-predict large soil losses. Catena 32: 15-22. Prosser IP, Dietrich WE. 1995. Field experiments on erosion by overland flow and their implication for à digital terrain model of channel initiation. Water Ressources Research. 31(11): 2867-2876. Baujard P, Martiny B. 1995. Ecology and pathogenicity of the Hoplolaimidae (Nemata) from the sahelian zone of West Africa. 2. Laboratory studies on Scutellonema cavenessi Sher, 1964. Fundamental and Applied Nematology 18: 335-345. Cadet P, Albergel J. 1998. Passive transport of phytoparasitic nematodes by runoff water in the sudano-sahelian climatic area. Journal of Hydrology 214: 91-102. Govers G. 1992. Relationship between discharge, velocity, and flow area for rills eroding loose, non-layered materials. Earth Surface Processes and Landforms 17: 515-528. Demeure YD, Freckman W, Van Gundy SD. 1979. Anhydrobiotic coiling of nematodes in soil. Journal of Nematology 11(2): 189-195. Demeure Y. 1980. Biology of the plant parasitic nematode Scutellonema cavenessi Sher, 1964; anhydrobiosis. Revue de Nématologie 3: 283-289. Jetten V, de Roo A, Favis-Mortlock D. 1999. Evaluation of field-scale and catchment-scale soil erosion models. Catena 37(3-4): 521-541. Masse D, Cadet P, Chotte JL, Diatta M, Floret C, NDiaye-Faye N, Pate E, Pontanier R, Thioulouse J, Villenave C. 1998. L'exploitation des jachères naturelles compromet la restauration de la fertilité du milieu semi-aride au Sénégal. Agriculture et Développement 18: 31-38. Roth CH, Helming K. 1992. Dynamics of surface sealing, runoff formation and interrill soil loss as related to rainfall intensity, microrelief and slope. Zeitschrift fur Pflanzenernahrung und Bodenkunde 155: 209-216. Magunda MK, Larson WE, Linden DR, Nater EA. 1997. Changes in microrelief and their effects on infiltration and erosion during simulated rainfall. Soil Technology 10(1): 57-67. Abrahams AD, Parsons AJ. 1994. Hydraulics of interrill overland flow on stone-covered desert surfaces. Catena 23: 111-140. Esteves M, Planchon O, Lapetite JM, Silvera N, Cadet P. 2000. The EMIRE large rainfall simulator: design and field testing. Earth Surface Processes and Landform 25: XXX-XXX. 1995; 31 1992; 140 2000; 25 1962; 8 1994; 23 1992; 17 1998 1997 1998; 214 1995; 18 1970; XXII 1979; 11 1978 1992; 52 1998; 18 1990 1997; 33 1997; 10 2000 1986; 88 1992; 155 1999; 37 1980; 3 1996; 60 1998; 32 1983; 47 Masse (10.1002/1096-9837(200007)25:7<729::AID-ESP128>3.0.CO;2-C-BIB17) 1998; 18 Magunda (10.1002/1096-9837(200007)25:7<729::AID-ESP128>3.0.CO;2-C-BIB16) 1997; 10 Abrahams (10.1002/1096-9837(200007)25:7<729::AID-ESP128>3.0.CO;2-C-BIB2) 1994; 23 Gilley (10.1002/1096-9837(200007)25:7<729::AID-ESP128>3.0.CO;2-C-BIB12) 1992; 140 Luc (10.1002/1096-9837(200007)25:7<729::AID-ESP128>3.0.CO;2-C-BIB15) 1990 Cogo (10.1002/1096-9837(200007)25:7<729::AID-ESP128>3.0.CO;2-C-BIB7) 1983; 47 Bjorneberg (10.1002/1096-9837(200007)25:7<729::AID-ESP128>3.0.CO;2-C-BIB5) 1997 Demeure (10.1002/1096-9837(200007)25:7<729::AID-ESP128>3.0.CO;2-C-BIB10) 1980; 3 Cadet (10.1002/1096-9837(200007)25:7<729::AID-ESP128>3.0.CO;2-C-BIB6) 1998; 214 Prosser (10.1002/1096-9837(200007)25:7<729::AID-ESP128>3.0.CO;2-C-BIB25) 1995; 31 Nearing (10.1002/1096-9837(200007)25:7<729::AID-ESP128>3.0.CO;2-C-BIB21) 1997; 33 Planchon (10.1002/1096-9837(200007)25:7<729::AID-ESP128>3.0.CO;2-C-BIB24) 2000 Jetten (10.1002/1096-9837(200007)25:7<729::AID-ESP128>3.0.CO;2-C-BIB14) 1999; 37 Pate (10.1002/1096-9837(200007)25:7<729::AID-ESP128>3.0.CO;2-C-BIB22) 1997 Abrahams (10.1002/1096-9837(200007)25:7<729::AID-ESP128>3.0.CO;2-C-BIB1) 1986; 88 Demeure (10.1002/1096-9837(200007)25:7<729::AID-ESP128>3.0.CO;2-C-BIB8) 1978 Murthy (10.1002/1096-9837(200007)25:7<729::AID-ESP128>3.0.CO;2-C-BIB18) 1970; XXII Esteves (10.1002/1096-9837(200007)25:7<729::AID-ESP128>3.0.CO;2-C-BIB11) 2000; 25 Bielders (10.1002/1096-9837(200007)25:7<729::AID-ESP128>3.0.CO;2-C-BIB4) 1996; 60 Mwendera (10.1002/1096-9837(200007)25:7<729::AID-ESP128>3.0.CO;2-C-BIB19) 1992; 52 Demeure (10.1002/1096-9837(200007)25:7<729::AID-ESP128>3.0.CO;2-C-BIB9) 1979; 11 Roth (10.1002/1096-9837(200007)25:7<729::AID-ESP128>3.0.CO;2-C-BIB26) 1992; 155 Seinhorst (10.1002/1096-9837(200007)25:7<729::AID-ESP128>3.0.CO;2-C-BIB27) 1962; 8 Nearing (10.1002/1096-9837(200007)25:7<729::AID-ESP128>3.0.CO;2-C-BIB20) 1998; 32 Govers (10.1002/1096-9837(200007)25:7<729::AID-ESP128>3.0.CO;2-C-BIB13) 1992; 17 Baujard (10.1002/1096-9837(200007)25:7<729::AID-ESP128>3.0.CO;2-C-BIB3) 1995; 18 Planchon (10.1002/1096-9837(200007)25:7<729::AID-ESP128>3.0.CO;2-C-BIB23) 1998 |
References_xml | – reference: Abrahams AD, Parsons AJ, Luk SH. 1986. Resistance to overland flow on desert hillslopes. Journal of Hydrology 88: 343-363. – reference: Gilley JE, Kincaid DC, Elliot WJ, Laflen JM. 1992. Sediment delivery on rill and interrill areas. Journal of Hydrology 140: 313-341. – reference: Murthy GVGK, Elias NA. 1970. Vertical distribution pattern of plant parasitic nematodes in Tobacco fields in Mysore. Indian Phytopathology XXII: 252-254. – reference: Cadet P, Albergel J. 1998. Passive transport of phytoparasitic nematodes by runoff water in the sudano-sahelian climatic area. Journal of Hydrology 214: 91-102. – reference: Nearing MA. 1998. Why soil erosion models over-predict small soil losses and under-predict large soil losses. Catena 32: 15-22. – reference: Baujard P, Martiny B. 1995. Ecology and pathogenicity of the Hoplolaimidae (Nemata) from the sahelian zone of West Africa. 2. Laboratory studies on Scutellonema cavenessi Sher, 1964. Fundamental and Applied Nematology 18: 335-345. – reference: Planchon O, Esteves M, Silvera N, Lapetite JM. 2000. Raindrop erosion of tillage induced microrelief: possible use of the diffusion equation. Soil and Tillage Research. in press. – reference: Mwendera EJ, Feyen J. 1992. Estimation of depression storage and Manning's resistance coefficient from random roughness measurements. Geoderma 52: 235-250. – reference: Prosser IP, Dietrich WE. 1995. Field experiments on erosion by overland flow and their implication for à digital terrain model of channel initiation. Water Ressources Research. 31(11): 2867-2876. – reference: Luc M, Sikora RA, Bridge J. 1990. Plant Parasitic Nematodes in Subtropical and Tropical Agriculture. CAB International: Wallingford. – reference: Demeure YD, Freckman W, Van Gundy SD. 1979. Anhydrobiotic coiling of nematodes in soil. Journal of Nematology 11(2): 189-195. – reference: Esteves M, Planchon O, Lapetite JM, Silvera N, Cadet P. 2000. The EMIRE large rainfall simulator: design and field testing. Earth Surface Processes and Landform 25: XXX-XXX. – reference: Jetten V, de Roo A, Favis-Mortlock D. 1999. Evaluation of field-scale and catchment-scale soil erosion models. Catena 37(3-4): 521-541. – reference: Nearing MA, Norton LD, Bulgakov DA, Larionov GA, West LT, Dontsova KM. 1997. Hydraulics and erosion in eroding rills. Water Resources Research 33: 865-876. – reference: Seinhorst JW. 1962. Modifications of the elutriation method for extracting nematodes from soil. Nematologica 8: 117. – reference: Bielders CL, Baveye P, Wilding LP, Drees LR, Valentin C. 1996. Tillage-induced spatial distribution of surface crusts on a sandy Paleustult from Togo. Soil Science Society of America Journal 60: 843-855. – reference: Govers G. 1992. Relationship between discharge, velocity, and flow area for rills eroding loose, non-layered materials. Earth Surface Processes and Landforms 17: 515-528. – reference: Masse D, Cadet P, Chotte JL, Diatta M, Floret C, NDiaye-Faye N, Pate E, Pontanier R, Thioulouse J, Villenave C. 1998. L'exploitation des jachères naturelles compromet la restauration de la fertilité du milieu semi-aride au Sénégal. Agriculture et Développement 18: 31-38. – reference: Abrahams AD, Parsons AJ. 1994. Hydraulics of interrill overland flow on stone-covered desert surfaces. Catena 23: 111-140. – reference: Roth CH, Helming K. 1992. Dynamics of surface sealing, runoff formation and interrill soil loss as related to rainfall intensity, microrelief and slope. Zeitschrift fur Pflanzenernahrung und Bodenkunde 155: 209-216. – reference: Magunda MK, Larson WE, Linden DR, Nater EA. 1997. Changes in microrelief and their effects on infiltration and erosion during simulated rainfall. Soil Technology 10(1): 57-67. – reference: Cogo NP, Moldenhauer WC, Foster GR. 1983. Effect of crop residue, tillage-induced roughness and runoff velocity on size distribution of eroded soil aggregates. Soil Science Society of America Journal 47: 1005-1008. – reference: Demeure Y. 1980. Biology of the plant parasitic nematode Scutellonema cavenessi Sher, 1964; anhydrobiosis. 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Snippet | This paper presents a rainfall simulation experiment carried out on three 50 m2 plots in the Senegalese groundnut belt. One plot was not cultivated. Groundnut... This paper presents a rainfall simulation experiment carried out on three 50 m super(2) plots in the Senegalese groundnut belt. One plot was not cultivated.... |
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SubjectTerms | microrelief Nematoda nematodes rainfall simulation runoff Senegal splash erosion |
Title | Relationship between raindrop erosion and runoff erosion under simulated rainfall in the Sudano-Sahel: consequences for the spread of nematodes by runoff |
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