Elsevier

Geoderma Regional

Volume 22, September 2020, e00293
Geoderma Regional

Termite mound soil properties in West Bengal, India

https://doi.org/10.1016/j.geodrs.2020.e00293Get rights and content

Highlights

  • Properties of termite mounds are directly proportional to the surrounding surface soil.

  • Termites significantly affect the physiochemical properties of soil

  • Mound soils are physio chemically and morphologically distinct from surrounding surface soil.

  • Termite mounds have greater nutrient concentration than surrounding surface soil.

  • Height, mass of material, abundance and regeneration rate of termite mounds are higher in dense vegetation.

Abstract

Termites are ecosystem engineers, they play a major role in the biotransformation and modification of soil physicochemical and morphological properties. This study was conducted to evaluate the explored and compared physicochemical and morphological characteristics of soil between termite mounds and surrounding surface soil. Therefore, this study, especially emphasizes the impacts of the mound soil on the surrounding surface soil properties and also to find out the difference between the mound soil properties and surrounding surface soil properties at different soil depth, and characteristic of termite mounds. This study unveils that mound soil properties are directly proportional to the surrounding surface soil properties except for porosity and dispersion ratio. But mound soil properties are not significantly affecting all surface soil properties. The termites have a significant role to change soil physicochemical and morphological properties and there is a significant difference in soil physicochemical properties between mound and surrounding surface soil. However, relatively greater bulk density, clay content, soil pH, organic carbon, nitrogen, exchangeable calcium, exchangeable magnesium, exchangeable sodium, total exchangeable base cations and cation exchange capacity in mound soil than surrounding surface soil. But the relatively lesser value of porosity, dispersion ratio, exchangeable potassium, phosphorus, exchangeable acidity, and C: N ratio is found in mound soil than surrounding surface soil. Conical shaped mounds have greater nutrient concentration than surrounding surface soil. It also highlighted that most of the termite mound consists of trees and bushes containing 8–21 hole or chamber. The termite mounds have granular structure and particle shape are rounded to subrounded, which make them different from surrounding areas. This study suggests and statistically prove that termites have a significant effect on soil properties, they produce physicochemically more quality soil and have an influence on surrounding soil properties.

Introduction

Termite mounds, a micro landform feature generally found in the lateritic landscapes of the tropical and subtropical regions (Dangerfield et al., 1998; Levick et al., 2010). Termite mounds have distinct morphology compared with the surrounding topsoil (de BRUYN and Conacher, 1990; Abe et al., 2009). Generally, termite mounds are stable, erosion resistant, (Léonard and Rajot, 2001; Jouquet et al., 2004; Ackerman et al., 2007), and increase nutrient concentration and mineral reserves (Kebede, 2004). Diets of termites are based on wood, grasses, litter, and nutrient-rich soil, so most of the termite's nest grows on wood soil interface and high biomass regions (Eggleton et al., 1996; Mora et al., 2006). Termite mound's growth, abundance and volume vary regionally due to variation in climate, vegetation cover, soil properties, biomass abundance, slope and groundwater depth etc. (Gathorne-Hardy and Eggleton, 2001; Cancello et al., 2014; Davies et al., 2014; Jamilu Bala Ahmed et al., 2019). Biological agents like termites are important for pedological processes hence are termed as bioengineers (Holt and Lepage, 2000); Millogo et al., 2011; Whitford and Eldridge, 2013; Jouquet et al., 2016). Termites have great impact on soil properties including redistribution of soil particles with nutrient and minerals, nest building, repacking and cementing, feeding activity, interaction with the organism, organic matter (OM) decomposition, nutrient recycling, foraging behaviour and decaying (Holt and Lepage, 2000). They also effects on soil properties by their chemical secretions (Prestwich, 1979; Hanus et al., 2010) and by bringing up subsoil to the soil surface for construction of mounds (Lee and Wood, 1971; Holt and Lepage, 2000; Jouquet et al., 2011; Mujinya et al., 2014). Termites are the most important soil fauna which help to modify physicochemical properties of soil (de BRUYN and Conacher, 1990; Lee and Foster, 1991; Holt and Lepage, 2000; Millogo et al., 2011; Jouquet et al., 2011; Rückamp et al., 2012; Jouquet et al., 2016; Lavelle et al., 2016), and built stable, microstructural and morphological features which are distinct from surrounding soil (Lee and Wood, 1971; Eschenbrenner, 1986; Lal et al., 1992; Dangerfield et al., 1998; Jungerius et al., 1999; Turner, 2000; Sarcinelli et al., 2009). The effects of termites are not limited to their living area, they also effect inside the mound and surrounding foraging area (Rückamp et al., 2012). Quantifying the distribution of termite mounds, regeneration, volume and mass of mound provide useful information on nutrient and minerals, the good productive capacity of the soil and groundwater resource (Turner, 2000; Kaschuk et al., 2006; Ackerman et al., 2007; Mège and Rango, 2010). Research on termite mounds historically concentrated on physicochemical and geomorphological properties (Lee and Wood, 1971; Wood et al., 1983; Abe et al., 2009; Dowuona et al., 2012), and their stability, erodibility, runoff, infiltration rate (Léonard and Rajot, 2001; Jouquet et al., 2012) and physicochemical properties of termite's mound (as a whole) in relation to adjacent topsoil (Hesse, 1955; Brian, 1978; Asawalam et al., 1999; López-Hernández, 2001; Jouquet et al., 2005; Ackerman et al., 2007; Kawaguchi and Nishi, 2007; Asawalam and Johnson, 2007; Jiménez et al., 2008; Okullo and Moe, 2012). As termites bring up soil not only from topsoil but also from subsoil (Jouquet et al., 2002),mound soils are affected by rainfall and thus eroded materials may also affect associated surface soils surrounding the mounds (Arshad, 1982; Lal et al., 1992).This study emphasizes the effect of the mound soil properties on the surrounding surface soil properties and makes a comparison between physicochemical properties of mound soil (at different depth) and surrounding surface soil (non-mound affected soil at different depth). The hypothesis was whether there is significant difference between mound soil properties and surrounding surface soil properties and the mound soil properties that may affect the surrounding surface soil properties. Therefore, the aims of this study were 1) to assess the effects of the mound soil properties on the surrounding surface soil properties, 2) to find out the difference between termite mound and surrounding surface soil properties in the study area and 3) to analyse the characteristics of mounds with their abundance, mass of materials (mass of termite mounds) and rate of regeneration.

Section snippets

Location of the study area

The study sites were situated in the lateritic soils of Paschim Medinipur district. Which is located in the southwestern part of West Bengal, India. The locational extent of this area is 22°25′40″ N to 22°26′4″ N and 87°17′40″ E to 87°18′14″ E (Fig. 1). Samples were collected from 20 termite mounds and 20 surrounding surface soils from different position of the study area at random and at different depth (Table 1). Average distance between sampling mound and the surface soil is 4 m. Ten mounds

Characteristics of mound

Termite mounds (as a whole) were approximately conical shaped with a height range from 33.22 cm to 241.30 cm and diameter range from 111.76 cm to 314.96 cm. The average height of termite mound was 252 cm, 184 cm and 161 cm in dense vegetation, dispersed vegetation and grassland area, respectively. In the study area, most of the mounds are conical in shape but few others cathedral configuration. Most of the termite mounds were compact and sealed with trees and bushes (Fig. 4) and some internal

Conclusion

After the study, it is found that most of the termite mounds have developed on the trees and bushes, where canopy cover is dense. Mound height, the mass of material, abundance and regeneration rate are high in dense vegetation (dense vegetation < dispersed vegetation < grassland). Soil properties of termite mounds positivly correlated with the surrounding surface soil properties except porosity and dispersion ratio. But soil properties of termite mounds have no significant effects on all

Declaration of competing interest

None.

Acknowledgements

The authors are grateful to Vidyasagar University Science Instrument Centre (USIC) especially, Dipankar Sir and Anindita Madam for their valuable guidance with soil testing and for technical assistance in laboratory analysis. Finally, the authors would like to thank to all the researcher of our lab for their encouragement, and valuable suggestion for undertaking this study.

Funding

This research did not receive any specific grant from funding agencies in the public, commercial, or not-for-profit sectors.

References (73)

  • P. Jouquet et al.

    Influence of earthworms and termites on runoff and erosion in a tropical steep slope fallow in Vietnam: a rainfall simulation experiment

    Appl. Soil Ecol.

    (2012)
  • P.D. Jungerius et al.

    The contribution of termites to the microgranular structure of soils on the Uasin Gishu Plateau, Kenya

    CATENA

    (1999)
  • F. Kebede

    Use of termite mounds in geochemical exploration in North Ethiopia

    J. Afr. Earth Sci.

    (2004)
  • J. Léonard et al.

    Influence of termites on runoff and infiltration: quantification and analysis

    Ouquet Geoderma

    (2001)
  • S.R. Levick et al.

    The spatial extent of termite influences on herbivore browsing in an African savanna

    Biol. Conserv.

    (2010)
  • D. López-Hernández

    Nutrient dynamics (C, N and P) in termite mounds of Nasutitermes ephratae from savannas of the Orinoco Llanos (Venezuela)

    Soil Biol. Biochem.

    (2001)
  • D. Mège et al.

    Permanent groundwater storage in basaltic dyke fractures and termite mound viability

    J. Afr. Earth Sci.

    (2010)
  • Y. Millogo et al.

    Physical properties, microstructure and mineralogy of termite mound material considered as construction materials

    Appl. Clay Sci.

    (2011)
  • P. Mora et al.

    Abundance of biogenic structures of earthworms and termites in a mango orchard

    Eur. J. Soil Biol.

    (2006)
  • B.B. Mujinya et al.

    Spatial patterns and morphology of termite (Macrotermes falciger) mounds in the Upper Katanga, D.R. Congo

    CATENA

    (2014)
  • D. Rückamp et al.

    Soil genesis and heterogeneity of phosphorus forms and carbon below mounds inhabited by primary and secondary termites

    Geoderma

    (2012)
  • T.S. Sarcinelli et al.

    Chemical, physical and micromorphological properties of termite mounds and adjacent soils along a toposequence in Zona da Mata, Minas Gerais State, Brazil

    CATENA

    (2009)
  • J. Six et al.

    A history of research on the link between (micro)aggregates, soil biota, and soil organic matter dynamics

    Soil Tillage Res.

    (2004)
  • W. Whitford et al.

    Effects of ants and termites on soil and geomorphological processes

    Treatise Geomorph.

    (2013)
  • T.G. Wood et al.

    Modification of soils in Nigerian savanna by soil-feeding Cubitermes (Isoptera, Termitidae)

    Soil Biol. Biochem.

    (1983)
  • L. Abbadie et al.

    Soil fauna at the forest-savanna boundary: role of termite mounds in nutrient cycling

    Nat. Dyn. For.-Savanna Bound.

    (1992)
  • S.S. Abe et al.

    Soil-particle selection by the mound-building termite Macrotermes bellicosus on a sandy loam soil catena in a Nigerian tropical savanna

    J. Trop. Ecol.

    (2009)
  • S.S. Abe et al.

    Nutrient storage in termite (Macrotermes bellicosus ) mounds and the implications for nutrient dynamics in a tropical savanna Ultisol

    Soil Sci. Plant Nutr.

    (2011)
  • F. Adekayode et al.

    Comparative study of clay and organic matter content of termite mounds and the surrounding soils

    Afr. Crop Sci. Conf. Proc., Afr. Crop Sci. Soc.

    (2009)
  • S.G. Afolabi et al.

    Physical and chemical characteristics of mound materials and surrounding soils of different habitats of two termite species in Minna, Nigeria

    PAT

    (2014)
  • D.O. Asawalam et al.

    Physical and chemical characteristics of soils modified by earthworms and termites

    Commun. Soil Sci. Plant Anal.

    (2007)
  • D.O. Asawalam et al.

    Effects of termites on the physical and chemical properties of the acid sandy soils of southern Nigeria

    Commun. Soil Sci. Plant Anal.

    (1999)
  • G.R. Blake et al.

    Bulk density

  • R.H. Bray et al.

    Determination of total organic and available forms of phosphorus in soils

    Soil Sci.

    (1945)
  • J.M. Bremner et al.

    Nitrogen – total

  • M.V. Brian

    Production ecology of ants and termites

    Soil Sci.

    (1978)
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