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Ingestion of charcoal by the Amazonian earthworm Pontoscolex corethrurus: a potential for tropical soil fertility

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Abstract

It is now attested that a large part of the Amazonian rain forest has been cultivated during Pre-Colombian times, using charcoal as an amendment. The incorporation of charcoal to the soil is a starting point for the formation of fertile Amazonian Dark Earths, still selected by Indian people for shifting cultivation. We showed that finely separated charcoal was commonly incorporated in the topsoil by Pontoscolex corethrurus, a tropical earthworm which thrives after burning and clearing of the rain forest, and that this natural process could be used to improve tropical soil fertility. Our paper is a contribution to the present debate about (i) the origin of black carbon in fertile Dark Earths, (ii) the detrimental vs favourable role of Pontoscolex corethrurus in tropical agriculture, (iii) natural processes which might be used to increase tropical soil fertility
Type of contribution: Letter to the Editor 1
Date of preparation: 19 December 2005 2
Number of text pages: 5 3
4
Title: Ingestion of charcoal by the Amazonian earthworm Pontoscolex corethrurus: a 5
potential for tropical soil fertility 6
7
Jean-François Ponge1, Stéphanie Topoliantz1, Sylvain Ballof2, Jean-Pierre Rossi3, Patrick 8
Lavelle4, Jean-Marie Betsch5, Philippe Gaucher6 9
10
1Muséum National d’Histoire Naturelle, CNRS Unité Mixte de Recherches 5176, 91800 11
Brunoy, France 12
2Office National des Forêts, 97370 Maripasoula, Guyane Française 13
3Institut National de la Recherche Agronomique, INRA, Unité Mixte de Recherches 14
BIOGECO, 33612 Cestas Cédex, France 15
4Institut de Recherche pour le Développement, Unité Mixte de Recherches BIOSOL 137, 16
93143 Bondy Cédex, France 17
5Muséum National d’Histoire Naturelle, Unité Scientifique 306, 91800 Brunoy, France 18
6Mission pour la Création du Parc de la Guyane, 97326 Cayenne Cédex, Guyane Française 19
20
Correspondence: Jean-François Ponge, Muséum National d‟Histoire Naturelle, CNRS UMR 5176, 4 avenue du
Petit-Château, 91800 Brunoy, France, E-mail: jean-francois.ponge@wanadoo.fr
Abstract 1
2
It is now attested that a large part of the Amazonian rain forest has been cultivated 3
during Pre-Colombian times, using charcoal as an amendment. The incorporation of charcoal 4
to the soil is a starting point for the formation of fertile Amazonian Dark Earths, still selected 5
by Indian people for shifting cultivation. We showed that finely separated charcoal was 6
commonly incorporated in the topsoil by Pontoscolex corethrurus, a tropical earthworm 7
which thrives after burning and clearing of the rain forest, and that this natural process could 8
be used to improve tropical soil fertility. Our paper is a contribution to the present debate 9
about (i) the origin of black carbon in fertile Dark Earths, (ii) the detrimental vs favourable 10
role of Pontoscolex corethrurus in tropical agriculture, (iii) natural processes which might be 11
used to increase tropical soil fertility 12
13
Keywords: Tropical earthworms, Tropical soil fertility, Slash-and-burn agriculture, Charcoal 14
15
Pontoscolex corethrurus (Annelida: Oligocheata: Glossoscolecidae) is a small 16
terrestrial earthworm which commonly inhabits rain forest soils over the whole Amazonian 17
basin (Römbke et al., 1999). Its important burrowing activity through the topsoil, associated 18
with its efficient digestive system (Zhang et al., 1993; Barros et al., 2001), allows it to thrive 19
in soils poor in organic matter, such as those found in areas now deforested for the need of 20
agriculture. In the absence of organic input to the soil, excessive casting activity of this 21
species may cause damage to permanent pastures through the coalescence of earthworm casts, 22
leading to appearance of a thick compact surface crust (Chauvel et al., 1999). However, the 23
detrimental influence of this species may be questioned when the agricultural use of the land 24
is only temporary, as in slash-and-burn shifting agriculture, or when available carbon is 25
regularly added to the soil. We hypothesized that P. corethrurus could be responsible for the 1
observed increase in soil fertility which has been reported to occur in Amazonian Dark Earths 2
formed during Pre-Colombian times (Myers et al., 2003; Steiner et al., 2004). 3
4
Using a quantitative optical method (Topoliantz et al., 2000), we investigated the 5
distribution of humus components in soils under shifting cultivation, still practised by 6
Wayana and Aluku people settled along the Maroni river, French Guiana (Topoliantz et al., 7
2005b). This method allowed us to estimate the relative volume of components of the soil 8
matrix, including plant tissues at varying stages of decomposition, mineral particles of 9
varying size and nature, aggregates of varying colour, size and shape. 10
11
The untouched old forest exhibited low contents of both charcoal and charred material, 12
representing 2% and 7% of the volume of the soil matrix, respectively. We showed that six 13
months after burning of the same forest for cultivation, the contents of charcoal and charred 14
material increased to 10% and 20% of the soil matrix, respectively, in the top 3 cm. After 15
three years of cultivation these amounts decreased to 6% and 15%, respectively. During the 16
cultivation period the amount of dark humus (mixture of charcoal and mineral soil in varying 17
proportion) increased steadily. The examination of dark humus revealed that it was mainly 18
comprised of faecal pellets of P. corethrurus, which contained a multitude of small charcoal 19
fragments of 10-100 µm admixed in a mineral paste. 20
21
Charcoal, ingested together with soil particles, is mixed with mucus secreted in the 22
oesophagus then finely ground in the muscular gizzard of earthworms. It is excreted as a 23
muddy paste which is further stabilized by Van der Wals forces after drying, thus forming 24
dark humus (Hayes, 1983). We also showed by laboratory experiments that P. corethrurus did 25
not ingest charcoal alone but rather added it to mineral soil. A mixture of charcoal and soil 1
was preferred to either pure charcoal or pure soil (Topoliantz and Ponge, 2003, 2005a). This 2
points to a positive feed-back which improves the habitat of P. corethrurus by increasing the 3
carbon content of the soil. 4
5
It has been demonstrated that finely divided charcoal (also called black carbon) was a 6
source of stable humus (Tryon, 1948; Chan et al., 1999). Slow oxidation and hydroxylation 7
increase donor/acceptor charges, giving the soil strong exchangeable properties. The positive 8
impact of charcoal in ameliorating the physical and chemical properties of tropical soils has 9
been reported in various situations (Glaser et al., 2002). To the light of our results we expect 10
the peregrine earthworm P. corethrurus to be the main agent for the incorporation of charcoal 11
to the topsoil in the form of fine particles of silt size, which favoured the formation of stable 12
humus in Amazonian Dark Earths or „Terra Preta‟ during Pre-Colombian times (Glaser et al., 13
2000). 14
15
The natural development of P. corethrurus, able to feed and reproduce in tropical soils 16
poor in organic matter, opens avenues for new agricultural practices better adapted to 17
permanent settlements, using charcoal in mixture with nutrient-rich amendment (Steiner et al., 18
2004). In situ experiments were conducted with the help of a local agriculturist at Maripasoula 19
(French Guiana), using waste products of slash-and-burn agriculture (charcoal and manioc 20
peels) as an amendment. We demonstrated that the addition of charcoal together with manioc 21
peels, known to be rich in phosphorus (a limiting nutrient in tropical soils), increased yard-22
long bean production at the natural population size of P. corethrurus, thus allowing 23
diversification of family agriculture without any additional cost (Topoliantz et al., 2002;; 24
Topoliantz et al., 2005). 25
1
Acknowledgements 2
3
This work was supported by the French Ministry of Ecology and Sustainable Development 4
(SOFT program) and by a grant from the Commission for the Creation of the Guiana Natural 5
Park. The authors warmly acknowledge Dr. C. Kerdelhué (INRA, Pierroton, France) and Dr. 6
L. Greenfield (Canterbury University, Christchurch, New Zealand) for language editing. 7
8
References 9
10
Barros, E., Curmi, P., Hallaire, V., Chauvel, A., Lavelle, P., 2001. The role of macrofauna in 11
the transformation and reversibility of soil structure of an Oxisol in the process of 12
forest to pasture conversion. Geoderma 100, 193-213. 13
14
Chan, M.L., Jones, J.M., Pourkashanian, M., Williams, A., 1999. The oxidative reactivity of 15
coal chars in relation to their structure. Fuel 78, 1539-1552. 16
17
Chauvel, A., Grimaldi, M., Barros, E., Blanchart, E., Desjardins, T., Sarrazin, M., Lavelle, P., 18
1999. Pasture damage by an Amazonian earthworm. Nature 398, 32-33. 19
20
Glaser, B., Balashov, E., Haumaier, L., Guggenberger, G., Zech, W., 2000. Black carbon in 21
density fractions of anthropogenic soils of the Brazilian Amazon region. Organic 22
Geochemistry 31, 669-678. 23
24
Glaser, B., Lehmann, J., Zech, W., 2002. Ameliorating physical and chemical properties of 1
hughly weathered soils in the tropics with charcoal. A review. Biology and Fertility of 2
Soils 35, 219-230. 3
4
Hayes, M.H.B., 1983. Darwin‟s “vegetable mould” and some modern concepts of humus 5
structure and soil aggregation. In: Satchell, J.E. (Ed.), Earthworm Ecology from 6
Darwin to Vermiculture. Chapman and Hall, London, pp. 19-33. 7
8
Myers, T.P., Denevan, W.M., Winklerprins, A., Porro, A., 2003. Historical perspectives on 9
Amazonian Dark Earths. In: Lehmann, J., Kern, D.C., Glaser, B., Woods, W.I. (Eds.), 10
Amazonian Dark Earths. Origin, Properties, Management. Kluwer, Dordrecht, pp. 15-11
28. 12
13
Römbke, J., Meller, M., García, M., 1999. Earthworm densities in central Amazonian primary 14
and secondary forests and a polyculture forestry plantation. Pedobiologia 43, 518-522. 15
16
Steiner, C., Teixeira, W.G., Zech, W., 2004. Slash and char: an alternative to slash and burn 17
practiced in the Amazonian Basin. In: Glaser, B., Woods, W.I. (Eds.), Amazonian 18
Dark Earths: Explorations in Space and Time. Springer, Berlin, pp. 183-193. 19
20
Topoliantz, S., Ponge, J.F., 2003. Burrowing activity of the geophagous earthworm 21
Pontoscolex corethrurus (Oligochaeta: Glossoscolecidae) in the presence of charcoal. 22
Applied Soil Ecology 23, 267-271. 23
24
Topoliantz, S., Ponge, J.F., 2005. Charcoal consumption and casting activity by Pontoscolex 1
corethrurus (Glossoscolecidae). Applied Soil Ecology 28, 217-224. 2
3
Topoliantz, S., Ponge, J.F., Arrouays, D., Ballof, S., Lavelle, P., 2002. Effect of organic 4
manure and the endogeic earthworm Pontoscolex corethrurus (Oligochaeta: 5
Glosscoscolecidae) on soil fertility and bean production. Biology and Fertility of Soils 6
36, 313-319. 7
8
Topoliantz, S., Ponge, J.F., Ballof, S., 2005a. Manioc peel and charcoal: a potential organic 9
amendment for sustainable soil fertility in the tropics. Biology and Fertility of Soils 10
41, 15-21. 11
12
Topoliantz, S., Ponge, J.F., Lavelle, P., 2005b. Humus components and biogenic structures 13
under tropical slash-and-burn agriculture. European Journal of Soil Science doi: 14
10.1111/j.1365-2389.2005.00736.x (on line first). 15
16
Topoliantz, S., Ponge, J.F., Viaux, P., 2000. Earthworm and enchytraeid activity under 17
different arable farming systems, as exemplified by biogenic structures. Plant and Soil 18
225, 39-51. 19
20
Tryon, E.H., 1948. Effect of charcoal on certain physical, chemical, and biological properties 21
of forest soils. Ecological Monographs 18, 81-115. 22
23
Zhang, B.G., Rouland, C., Lattaud, C., Lavelle, P., 1993. Activity and origin of digestion 1
complexes in gut of the tropical earthworm Pontoscolex corethrurus. European 2
Journal of Soil Biology 29, 7-11. 3
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Rapid turnover of organic matter leads to a low efficiency of organic fertilizers applied to increase and sequester C in soils of the humid tropics. Charcoal was reported to be responsible for high soil organic matter contents and soil fertility of anthropogenic soils (Terra Preta) found in central Amazonia. Therefore, we reviewed the available information about the physical and chemical properties of charcoal as affected by different combustion procedures, and the effects of its application in agricultural fields on nutrient retention and crop production. Higher nutrient retention and nutrient availability were found after charcoal additions to soil, related to higher exchange capacity, surface area and direct nutrient additions. Higher charring temperatures generally improved exchange properties and surface area of the charcoal. Additionally, charcoal is relatively recalcitrant and can therefore be used as a long-term sink for atmospheric CO, Several aspects of a charcoal management system remain unclear, such as the role of microorganisms in oxidizing charcoal surfaces and releasing nutrients and the possibilities to improve charcoal properties during production under field conditions. Several research needs were identified, such as field testing of charcoal production in tropical agroecosystems, the investigation of surface properties of the carbonized materials in the soil environment, and the evaluation of the agronomic and economic effectiveness of soil management with charcoal.
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Darwin’s observations on earthworms can be regarded as a milestone in our understanding of soil biology and an enormous contribution to some aspects of the genesis of humus and of its role in soils. This chapter outlines Darwin’s conclusions on the role of earthworms in the formation of vegetable mould and his interpretations of its nature and properties, especially those of its organic constituents. It discusses modern concepts of the composition, structure and properties of humus substances and the role they play in soil, especially in stabilizing aggregates and retaining water and plant nutrients.
Article
Almost all cultivated soils undergo some reduction in the porosity of the surface layers, and nowhere is this more evident than in tropical rainforests that have been converted to pastures. Following deforestation in an area of Costa Rica, soil bulk density has been shown to increase rapidly after conversion to pasture, leading to poor drainage and a reduced rate of gaseous diffusion¹. These factors limit methane consumption and promote the anaerobic production of methane. A similar effect on methane flux has been found in upland soils in the Brazilian Amazonian basin after conversion from forest to pasture²,³. Increases in atmospheric methane are therefore not limited to emissions from flooded soils⁴, as forest-to-pasture conversion promotes the anaerobic mineralization of organic matter by changing the physical properties of soil.
Article
During the oxidation of porous coal chars the internal surface area can increase as a function of the degree of conversion due to pore growth and the opening up of sealed internal pores or cavities. Consequently, rate expressions for their oxidation are more accurately described in terms of the intrinsic reactivity, where differences in surface area and porosity can be taken into account.The oxidative reactivity of coal chars is complicated by a number of different factors, which are explored in this paper. These include (i) the development of the pore structure during devolatilisation of the coal, (ii) the ash content, its distribution in the carbon matrix and effect on reactivity, (iii) the extent of the H and N functional groups present in the solid matrix, and their interrelation with residual volatile species which are present, (iv) the extent of the graphitic nature of the carbon surface and (v) the active surface area available for reaction.
Article
Frequent charcoal findings together with black carbon concentrations in the soil organic matter (SOM) of up to 35% provided evidence that black carbon is important for the SOM stability in Terra Preta soils. This paper aims to investigate whether black carbon is additionally stabilised by organo-mineral complexation. For this purpose black carbon was analysed in density fractions using benzenecarboxylic acids as molecular markers. Density fractions were also studied by scanning electron microscopy and energy dispersive X-ray spectroscopy. Concentrations and total amounts of black carbon were generally highest in the light fraction indicating that a major part of black carbon is not chemically stabilised but intrinsically refractory. On the other hand, a large part of black carbon was also found in the heavier fractions, where it was partly embedded within plaques of iron and aluminium oxides on mineral surfaces. The major part of black carbon in the medium fraction seemed to be organo-mineral complexed because we found amounts of black carbon in this fraction by wet chemical analysis but not by scanning electron microscopy and energy dispersive X-ray spectroscopy. The spectroscopic analysis can only detect particulate black carbon. Black carbon was particularly enriched in 30–40 cm soil depth, and in all fractions of Terra Preta soils compared to adjacent Oxisols. The occurrence of particulate black carbon together with potsherds in the subsoil horizons of Terra Preta soils indicate that this might be due to turbation processes or the soils were covered by earthworm or termite activities. Further research, however, is needed to clarify the transport mechanisms of black carbon into deeper soil horizons.