Optimal Conditions for the Embryonic Development of Sea Urchin, Strongylocentrotus intermedius for Using the Bioassay

북쪽말똥성게, Strongylcentrotus intermedius를 이용한 생물검정 최적 발생조건

  • 류태권 (한국해양연구원 남해연구소) ;
  • 성찬경 (㈜네오엔비즈 환경안전연구소) ;
  • 한기명 (한국해양연구원 남해연구소) ;
  • 황인영 (인제대학교 자연과학대학 환경공학부) ;
  • 이택견 (한국해양연구원 남해연구소) ;
  • 이창훈 (㈜네오엔비즈 환경안전연구소)
  • Published : 2007.09.30

Abstract

Even though some standard developmental bioassay protocols for environmental assessment using sea urchins have already been described, there have not been many attempts to apply and modify these protocols with Korean species. Therefore, there is a strong need to establish standard bioassay protocols using sea urchins commonly found in Korea. Prior to developing a new protocol, it is essential to know the optimal conditions for the bioassay procedures. We investigated the optimal conditions (temperature, salinity, and embryo density) of the sea urchin Strongylocentrotus intermedius. The ideal temperature for developmental bioassay of S. intermedius was determined to be $15^{\circ}C$ and the time required for the embryo to become pluteus larva was 72 hr. The optimal range of salinity for the embryo toxicity using S. intermedius was between 30 to 32 psu, which is similar to the range found in the natural habitats of adult populations. The optimum density of embryos at the beginning of bioassays was 100 embryos/mL. When the assays were carried out at higher densities, the proportion of normally developed larvae decreased significantly.

Keywords

References

  1. ASTM. Standard guide for conducting acute toxicity tests starting with embryos of four species of saltwater bivalve molluscs, ASTM E724-94. 1994; pp. 334-351. American Society for Testing and Materials, Philadelphia
  2. Beiras R and Albentosa M. Inhibition of embryo development of the commercial bivalves Ruditapes decussatus and Mytilus galloprovincialis by trace metals; Implication for the implementation of seawater quality criteria, Aquaculture 2004; 230: 205-213 https://doi.org/10.1016/S0044-8486(03)00432-0
  3. Chapman GA. Sea urchin fertilization test method, Newport, OR; U.S. EPA, ERL-Narragansett, Pacific Ecosystem Branch 1992; 1-35
  4. Cherr GN, Shenker J, Lundmark C and Turner KO. Toxic effects of selected bleached kraft mill effluent constituents on the sea urchin sperm cell, Environ. Toxicol. Chem. 1987; 6: 561-569 https://doi.org/10.1897/1552-8618(1987)6[561:TEOSBK]2.0.CO;2
  5. Dinnel PA and Stober VJ. Application of the sea urchin sperm bioassay to sewage treatment efficiency and toxicity in marine waters, Mar. Environ. Res. 1987; 21: 121-133 https://doi.org/10.1016/0141-1136(87)90046-8
  6. Fichet D, Radenac G and Miramand P. Experimental studies of impacts of harbour sediments resuspension to marine invertebrates larvae: Bioavailability of Cd, Cu, Pb and Zn and toxicity, Mar. Pollut. Bull. 1998; 36: 509-518 https://doi.org/10.1016/S0025-326X(97)00190-2
  7. Garman GD, Anderson SL and Cherr GN. Developmental abnormalities and DNA-protein crosslinks in sea urchin embryos exposed to three metals. Aquat. Toxicol. 1997; 39: 247-265 https://doi.org/10.1016/S0166-445X(97)00033-7
  8. Geffard OE His H, Budzinski JF, Chiffoleau A, Coynel and Etcheber H. Effects of storage method and duration on the toxicity of marine sediments to embryos of Crassostrea gigas oysters, Environmental Pollution 2004; 129; 457-465 https://doi.org/10.1016/j.envpol.2003.11.014
  9. His E, Heyvang I, Geffard O and Montaudouin X. A comparison between oyster (Crassostrea gigas) and sea urchin (Paracentrotus lividus) larval bioassays for toxicological studies, Water Research 1999; 33(7): 1706-1718 https://doi.org/10.1016/S0043-1354(98)00381-9
  10. His E, Seaman MNL and Beiras R. A simplification the bivalve embryogenesis and larval development bioassay method for water quality assessment. Water Research, 1996; 31(2): 351-355
  11. Naomasa k and Okamura k. Effects of heavy metals on sea urchin embryo development. 1.Tracing the cause by the effects, Chemosphere, 2004; 55: 1403-1412 https://doi.org/10.1016/j.chemosphere.2003.11.052
  12. Martin M, Osborn KE, Bilig P and Glicksten N. Toxicities of ten metals to Crassostrea gigas and Mytilus edulis embryos and Cancer magister larvae. Mar. Pollu. Bull. 1981; 12 (9): 305-308 https://doi.org/10.1016/0025-326X(81)90081-3
  13. Nacci D, Jackim E and Walsh R. Comparative evaluation of three rapid marine toxicity test: Sea urchin early embryo growth test, sea urchin sperm cell toxicity test and Microtox. Environ. Toxicol. Chem., 1986; 5: 521-526 https://doi.org/10.1897/1552-8618(1986)5[521:CEOTRM]2.0.CO;2
  14. Radenac G, Fichet D and Maramand P. Bioaccumulation and toxicity of four dissolved metals in Paracentrotus lividus sea-urchin embryo. Mar. Environ. Res. 2001; 51: 151-166 https://doi.org/10.1016/S0141-1136(00)00092-1
  15. Ramachandran S, Patel TR and Colbo MH. Effect of copper and cadmium on three Malaysian tropical estuar-ine invertebrate larvae. Ecotoxicol. Environ. Saf., 1997; 36: 183-188 https://doi.org/10.1006/eesa.1996.1508
  16. Riveros A, Zun - iga M, Larrain A and Becerra J. Relationships between fertilization of the southeastern pacific sea urchin Arbacia spatuligera and environmental variables in polluted coastal waters. Mar. Ecol. Prog. Ser., 1996; 134: 159-169 https://doi.org/10.3354/meps134159
  17. U.S. EPA. Short-term methods for estimating the chronic toxicity of effluents and receiving water to marine and estuarine organisms. Second edition. 1994; EPA-600/4-91/003. Environmetal monitoring systems laboratory, Cincinnati, Ohio
  18. U.S. EPA. Short-term methods for estimating the chronic toxicity of effluents and receiving waters to west coast marine and estuarine organisms. 1995; EPA-600/R95/136. National exposure reseach, laboratory, Cincinnati, Ohio
  19. Zar JH. Biostatistical analysis, 2nd ed. 718 pp. Prentice-Hall International, Inc., Engelwood Dliffs, NJ. 1984