Effects of sodium azide on sea urchin embryos and gametes

Factors affecting R6 fungicide toxicity on sea urchin fertilization and early development: roles of exposure routes and mixture components

A technical fungicide mixture, R6 and its components, cymoxanil (CYM) and cupric oxychloride (Cu-OCl), were tested by sea urchin bioassays (Paracentrotus lividus and Sphaerechinus granularis). A set of toxicity endpoints was evaluated including both lethal and sublethal effects with the following endpoints: (a) acute embryotoxicity, (b) developmental defects, (c) changes in sperm fertilization success, (d) transmissible damage from sperm to the offspring, and (e) cytogenetic abnormalities. Acute effects on developing embryos were observed as early (prehatch) mortality at R6 levels > or =25 microg/ml. The pesticide mixture R6 was tested at realistic concentrations, ranging from 25 ng/ ml to 2.5 microg/ml, and the two components, CYM and Cu-OCl, were tested, either alone or in mixture, at concentrations equal to their levels in the corresponding R6 solutions. R6 was either dissolved in filtered seawater (water only, W-O), or spiked in "pristine" silt-clay sediment or soil samples before bioassays. Developmental toxicity of R6, following W-O dissolution, displayed a significant dose-related increase of larval malformations and differentiation arrest at concentrations of 750 ng/ml to 2.5 microg/ml both in P. lividus and in S. granularis larvae. Developmental toxicity was removed in spiked sediment up to R6 nominal levels (25 microg/ml), 10-fold above the embryotoxic R6 levels in W-O exposure. No significant developmental toxicity was exerted by CYM or Cu-OCl (W-O exposure) up to their concentrations equivalent to 2.5 microg/ml R6. The laboratory-prepared mixture of CYM and Cu-OCl, in the same concentration range, only resulted in minor effects, as larval retardation, suggesting the presence of toxic impurities (or additional components) in the R6 formulation. When sperm from either P. lividus or S. granularis were exposed to R6 before fertilization, a W-O exposure resulted in a dose-related decrease in fertilization of P. lividus sperm (up to 250 microg/ml R6), whereas S. granularis sperm underwent a significant increase of fertilization rate at the highest R6 nominal levels (up to 25 microg/ml). Equivalent CYM or Cu-OCl levels were ineffective on sperm fertilization success in both species. The offspring of S. granularis sperm exposed to 25 microg/ml R6 showed a significant increase in larval malformations, which were not detected in the offspring of R6-exposed P. lividus sperm. Again, CYM or Cu-OCl was unable to exert any transmissible damage from sperm to the offspring in either species. The present study raises the case of possible discrepancies between toxicity of a technical mixture and of its analytical-grade components, also providing evidence for a loss of pesticide toxicity following dispersion in an environmental matrix such as sediment or soil.

Alteration of Ca2+ homeostasis of sea urchin embryos by retinoid CD 367, dual effect on egg cleavage and embryonic development

The effect of a light stable retinoid (CD 367) was studied on sea urchin embryos. CD 367 did not affect sperm-egg interaction. In a range of concentrations between 10 and 100 microM, CD 367 delayed the first and the second cleavages. When added after fertilization, micromolar amounts of CD 367 delayed hatching and produced embryonic abnormalities in a dose-dependent manner. Mesodermal cells, primary (PMC) and secondary (SMC) mesenchyme cells migration was particularly disturbed, leading to exogastrulations and calcified spicules malformations. Concentrations of CD 367 higher than 8 microM were embryolethal. Micromolar amount of CD 367 increased plasmalemma Ca2+ permeability of fertilized eggs but not of unfertilized eggs. CD 367 inhibited ATP-dependent intracellular sequestration of Ca2+ in a range of concentrations similar to those affecting egg cleavage and embryonic structures. Since we were unable to detect nuclear receptors for CD 367 in sea urchin eggs and ovocytes, these effects probably are not related to interaction of the retinoid with members of the RAR family, to which CD 367 has a high affinity, but rather to its toxicity by the means of some unknown mechanisms.

Stage-specific effects of teratogens on sea urchin embryogenesis

The effect of direct (chlorambucil and allopurinol) and indirect (cyclophosphamide) teratogens on the fertilization and early development of sea urchin embryos has been investigated. Fertilization was affected by none of the drugs tested. Continuous exposure of embryos to chlorambucil (10(-6) to 3 x 10(-4) M) starting after fertilization delayed the first cleavage and hatching. Developmental defects in chlorambucil-treated embryos consisted mainly of blastula and gastrula-arrested embryos and in a limited number (25%) of plutei with malformed gut or skeleton. Post-hatching exposure to chlorambucil led to malformed plutei only. Early (pre-hatching) exposure to allopurinol (10(-6) to 10(-3) M) did not affect cleavage but induced developmental defects in a ratio comparable to chlorambucil. Post-hatching exposure to allopurinol failed to affect the embryogenesis. The indirect teratogen cyclophosphamide (10(-6) to 3 x 10(-5) M) had no effect on the early embryogenesis. Results were discussed in view of using sea urchin embryos to detect and analyze the early mechanisms of teratogenic action.