Abstract

Lumbricid earthworms are often exposed to polluted soil. They are also commonly subjected to various stimuli and attacks by predators that induce extrusion of coelomocyte-containing coelomic fluid and/or the loss of body segments followed by the renewal of immune-competent cells and regeneration of tissues/organs. The aim of our investigations was to test the effects of exposure of the earthworm Eisenia andrei to cadmium-polluted soil, combined with electrostimulation-induced depletion of coelomocytes (i.e. amoebocytes and chloragocyte-derived eleocytes) or the surgical amputation of posterior segments, on earthworm maturation, reproductive output, and regenerative processes. Experimental worms were maintained up to 7 weeks either in unpolluted soil or in soil spiked with cadmium chloride (500 mg/kg air-dried soil). In juvenile worms, sexual maturation (measured by clitellum formation) was delayed and cocoon production was inhibited in Cd-exposed worms. Coelomocytes were significantly depleted by electrostimulation and the kinetics of their recovery was similar in worms kept in clean and cadmium polluted soils, in both exposure conditions amoebocyte recovery was faster than recovery of riboflavin-storing eleocytes. In adult worms, soil cadmium exposure inhibited reproduction but, at macroanatomical level, had a negligible effect on regeneration of amputated posterior segments, visible only on histological cross-sections.

Highlights

  • MethodsEarthworms were maintained in commercial soil (PPUH BIOVITA, Tenczynek) of the organic type, with 51.7% organic matter, pH=6.1, with low Cd concentration (0.5±0.3), as established previously (PLYTYCZ et al 2011)

  • CHEN X., WANG X., GU X., JIANG Y., JI R. 2017

  • Untreated worms kept in clean or polluted soil comprised the control groups, cC and pC, 6-worms each. They were inspected at weekly intervals for cocoon production and tail segment regeneration expressed as numbers of blastema segments

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Summary

Methods

Earthworms were maintained in commercial soil (PPUH BIOVITA, Tenczynek) of the organic type, with 51.7% organic matter, pH=6.1, with low Cd concentration (0.5±0.3), as established previously (PLYTYCZ et al 2011). Air-dried soil was sieved and soaked either with cadmium chloride (CHEMPUR, Piekary Slaskie, Polska) dissolved in distilled water to concentrations of cadmium 500 mg/kg air-dried soil (polluted soil, “p”) or with an equivalent volume of distilled water (control clean soil, “c”). This cadmium concentration was well tolerated by composting earthworms in a former study (KWADRANS et al 2008), and was previously used for juvenile earthworms Eisenia fetida (ÞALTAUSKAITË & SODIENË 2014). Cadmium concentrations in soil and in whole earthworm bodies were measured by atomic absorption spectrometry (AAS) described in a previous study (KWADRANS et al 2008)

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