Chinese Journal of Zoology 2010 45 3 102 ~ 109 ph 12 3 12* 12 1 524025 2 524025 3 524025 28. 5 ph Hemifusus tuba 11. 3 ± 0. 11 mm n = 30 1 16 19 23 28 96 h 96hLC 50 36. 5 43. 7 52. 6 58. 8 mg / L SC 3. 7 4. 4 5. 3 5. 9 mg / L 2 ph ph 7. 6 8. 0 8. 4 8. 8 96hLC 50 58. 3 54. 5 50. 6 20. 2 mg / L SC 5. 8 5. 5 5. 1 2. 0 mg / L ph 8. 8 96hLC 50 ph 7. 6 2. 9 ph S968. 31 A 0250-3263 2010 03-102-08 Toxic Effects of Ammonia to Hemifusus tuba Juveniles at Different ph and Salinity LUO Jie 1 2 DU Tao 3 LIU Chu-Wu 1 2 * CHEN Jia-Hui 1 2 1 Fishery College of Guangdong Ocean University Zhanjiang 524025 2 Key Labolatory of Aquaculture in South China Sea for Aquatic Economic Animal of Guangdong Higher Education Institute Zhanjiang 524025 3Technology Park of Guangdong Ocean University Zhanjiang 524025 China Abstract In this paper under water temperatures 28. 5 the toxic effects of ammonia to Hemifusus tuba juveniles shells high 11. 3 ± 0. 11 mm n = 30 were studied at different ph and salinity with ecological method. The result showed that salinity has significantly effect on the toxicity of ammonia. The toxicity of ammonia in water became stronger when the salinity was lower. When salinity was 16 19 23 and 28 respectively the 96hLC 50 of total ammonia to H. tuba juveniles were 36. 5 43. 7 52. 6 and 58. 8 mg / L respectively and equivalent the safe concentration SC of total ammonia to the juveniles were 3. 7 4. 4 5. 3 and 5. 9 mg / L respectively. The toxicity of ammonia in water became stronger in higher ph than in lower. The 96hLC 50 and the SC of total ammonia to H. tuba juveniles were 58. 3 54. 5 50. 6 20. 2 mg / L and 5. 8 5. 5 5. 1 and 2. 0 mg / L respectively. The 96hLC 50 of total ammonia to H. tuba juveniles fell rapidly when ph was 8. 8 and toxicity of ammonia in water became 2. 9 times higher than in ph 7. 6. Key words Hemifusus tuba Juveniles Salinity ph Ammonia Toxicity No. 2005B33201011 * E-mail liucw@ gdou. edu. cn E-mail luoj@ gdou. edu. cn 2009-11-19 2010-02-04
3 ph 103 1. 1. 2 NH 4 Cl 53. 49 10 g / L 2 000 ml 1 000 W 500 W CT-6659 ph YK-31SA NH 3 NH + 4 1. 2 ph 1 Hemifusus tuba 16 16 19 23 28 4 ph 7. 6 8. 0 8. 4 8. 8 4 ph 10 m 2 NH 4 Cl 4. 8 11. 3 18. 8 23. 6 47. 5 63. 5 85 100 150 mg / L 9 3 3-5 NH 4 Cl Babylonia areolata 2 000 ml 1 200 ml 0. 5 mm 20 28. 5 ph 6 1. 2. 2 7-15 24 h ph 100% 1 1. 1 1. 1. 1 1. 2. 3 SPSS 13. 0 11. 3 ± 0. 11 mm n = 24 h 48 h 72 h 96 h 30 LC 50 95% 16 2 d SC 17 = 0. 1 96hLC 50 28. 5 ~ 29. 2 23 ph 8. 2 0. 3 ~ 0. 5 mm 1. 2. 1 24 h 48 h 72 h 96 h
104 Chinese Journal of Zoology 45 18 ρ NH3 = ρ T / 10 pka - ph + 1 ρ NH3 ρ T pka NH 4 -N pka = 0. 090 18 + 2 729. 92 / T T T = 273 + t t 50 min 28. 5 130 min ph 1 1 ph ρ T ρ NH3 Table 1 The relation with total ammonia and un-ion ammonia at difference ph ρ T ρ NH3 ph 7. 6 ph 8. 0 ph 8. 4 ph 8. 8 4. 8 0. 13 0. 32 0. 73 1. 50 11. 3 0. 31 0. 76 1. 73 3. 52 18. 8 0. 52 1. 26 2. 87 5. 85 23. 6 0. 65 1. 58 3. 60 7. 35 47. 5 1. 32 3. 18 7. 25 14. 80 63. 5 1. 76 4. 25 9. 69 19. 78 85. 0 2. 36 5. 69 12. 98 26. 48 100. 0 2. 77 6. 69 15. 27 31. 15 150. 0 4. 16 10. 03 22. 90 46. 73 200 min 2. 2 28. 5 ph 8. 2 2 ph 11. 3 mg / L 16 19 48 h 72 h 23 28 100 mg / L 16 19 96 h 2 3 16 2 19 23 28 96 h 96hLC 50 36. 5 43. 7 52. 6 58. 8 mg / 2. 1 L SC = 0. 1 96hLC 50 16 19 23 28 3. 7 4. 4 5. 3 5. 9 mg / L Table 2 2 The result of toxicity experiment of ammonia to Hemifusus tuba juveniles at difference salinities The mortality rate % ρ T Salinity 16 Salinity 19 Salinity 23 Salinity 28 24 h 48 h 72 h 96 h 24 h 48 h 72 h 96 h 24 h 48 h 72 h 96 h 24 h 48 h 72 h 96 h 0 Control 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 4. 8 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 11. 3 0 1. 7 1. 7 3. 3 0 0 1. 7 1. 7 0 0 0 0 0 0 0 0 18. 8 6. 7 10. 0 16. 7 23. 3 0 3. 3 10. 0 10. 0 1. 7 1. 7 6. 7 6. 7 0 3. 3 3. 3 3. 3 23. 6 18. 3 23. 3 31. 7 43. 3 11. 7 11. 7 26. 7 36. 7 8. 3 8. 3 15. 0 25. 0 6. 7 10. 0 13. 3 21. 7 47. 5 38. 3 43. 3 51. 7 61. 7 28. 3 41. 7 45. 0 53. 3 18. 3 33. 3 41. 7 46. 7 18. 3 26. 7 36. 7 41. 7 63. 5 41. 7 51. 7 55. 0 71. 7 36. 7 43. 3 51. 7 66. 7 31. 7 38. 3 48. 3 61. 7 31. 7 33. 3 48. 3 56. 7 85. 0 56. 7 61. 7 78. 3 86. 7 51. 7 56. 7 68. 3 83. 3 48. 3 53. 3 68. 3 78. 3 43. 3 51. 7 58. 3 63. 3 100. 0 61. 7 86. 7 98. 3 100. 0 56. 7 86. 7 93. 5 100. 0 53. 3 66. 7 78. 3 83. 3 51. 7 63. 3 80. 0 81. 7 150. 0 100. 0 100. 0 100. 0 100. 0 100. 0 100. 0 100. 0 100. 0 95. 0 100. 0 100. 0 100. 0 96. 7 100. 0 100. 0 100. 0
3 ph 105 Table 3 3 LC 50 95% The median lethal concentrations LC 50 and their 95% confidence interval of total ammonia to Hemifusus tuba juveniles at difference salinities Salinity 16 19 23 28 Time h LC 50 95% Confidence interval 24 76. 3 71. 2 ~ 80. 4 48 61. 2 58. 6 ~ 65. 3 72 44. 3 41. 6 ~ 48. 3 96 36. 5 33. 2 ~ 41. 2 24 82. 3 75. 4 ~ 88. 7 48 77. 6 72. 6 ~ 83. 4 72 61. 5 56. 3 ~ 66. 4 96 43. 7 37. 2 ~ 47. 3 24 87. 4 83. 4 ~ 92. 7 48 79. 4 75. 4 ~ 84. 2 72 66. 2 60. 8 ~ 70. 8 96 52. 6 48. 3 ~ 55. 8 24 98. 4 92. 3 ~ 101. 4 48 83. 5 76. 5 ~ 90. 7 72 68. 3 63. 2 ~ 74. 1 96 58. 8 52. 4 ~ 66. 4 Safe concentration 3. 7 4. 4 5. 3 5. 9 2. 3 ph 24 h 100% 4 4 28. 5 ph 23 LC 50 95% ph 5 ph 7. 6 8. 0 8. 4 8. 8 ph 58. 3 54. 5 50. 6 20. 2 mg / L SC = 0. 1 96hLC 50 ph 11. 3 mg / L ph 96 h 7. 6 8. 0 8. 4 8. 8 5. 8 5. 5 100 mg / L ph 8. 8 96 h 100% 150 mg / L 5. 1 2. 0 mg / L ph 8. 8 ph 7. 6 2. 9 Table 4 4 ph The result of toxicity experiment of ammonia to Hemifusus tuba juveniles at different ph The mortality rate % ρ T ph 7. 6 ph 8. 0 ph 8. 4 ph 8. 8 24 h 48 h 72 h 96 h 24 h 48 h 72 h 96 h 24 h 48 h 72 h 96 h 24 h 48 h 72 h 96 h 0 Control 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 4. 8 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 11. 3 0 0 0 1. 7 0 0 1. 7 1. 7 0 0 3. 3 5. 0 0 0 3. 3 6. 7 18. 8 0 11. 7 16. 7 16. 7 11. 7 15. 0 18. 3 18. 3 11. 7 16. 7 18. 3 23. 3 10 18. 3 28. 3 28. 3 23. 6 10 13. 3 25. 0 25. 0 16. 7 23. 3 25. 0 36. 7 21. 7 26. 7 31. 7 41. 7 31. 7 36. 7 41. 7 51. 7 47. 5 23. 3 26. 7 33. 3 38. 3 26. 7 26. 7 36. 7 43. 3 33. 3 38. 3 40. 0 48. 3 38. 3 43. 3 56. 7 63. 3 63. 5 23. 3 36. 7 45. 0 53. 3 38. 3 43. 3 48. 3 58. 3 43. 3 46. 7 51. 7 66. 7 48. 3 58. 3 66. 7 78. 3 85. 0 41. 7 50. 0 55. 0 66. 7 43. 3 51. 3 66. 7 78. 3 51. 7 61. 7 75. 0 83. 3 56. 7 78. 3 88. 3 95. 0 100. 0 51. 7 68. 3 75. 0 88. 3 55. 0 76. 7 76. 7 85. 0 63. 3 76. 7 81. 7 91. 7 86. 7 93. 3 98. 3 100 150. 0 96. 7 100. 0 100. 0 100. 0 100. 0 100. 0 100. 0 100. 0 100. 0 100. 0 100. 0 100. 0 100. 0 100. 0 100. 0 100. 0
106 Chinese Journal of Zoology 45 Table 5 5 ph LC 50 95% The median lethal concentrations LC 50 and their 95% confidence interval of total ammonia to Hemifusus tuba juveniles at difference ph ph 7. 6 8. 0 8. 4 8. 8 Time h LC 50 95% Confidence interval 24 94. 6 87. 3 ~ 98. 1 48 85. 1 80. 4 ~ 92. 5 72 71. 5 67. 3 ~ 76. 3 96 58. 3 55. 1 ~ 93. 4 24 91. 4 86. 7 ~ 96. 4 48 81. 3 77. 3 ~ 87. 5 72 68. 2 65. 4 ~ 76. 1 96 54. 5 49. 7 ~ 60. 1 24 82. 4 77. 2 ~ 85. 3 48 74. 3 70. 1 ~ 81. 3 72 58. 6 53. 6 ~ 63. 1 96 50. 6 47. 3 ~ 55. 2 24 60. 4 56. 4 ~ 64. 7 48 55. 8 51. 3 ~ 60. 1 72 42. 3 38. 5 ~ 44. 6 96 20. 2 18. 4 ~ 22. 7 Safe concentration 5. 8 5. 5 5. 1 2. 0 3 3. 1 20 21 22 23 Ruditapes philippinarum 24 19 Chlamys farreri 0. 02 mg / L 25 0. 02 ~ 0. 2 mg / L 3. 2 ph ph 0. 05 ~ 0. 15 mg / L 0. 3 mg / L 0. 5 mg / L Armstrong 4 ph
3 ph 107 ph Chen 26 28 ph 15 29 NH 3 ~ 30 ph NH 3 30 4. 8 mg / L ph 100% 11. 3 mg / L ph 16 19 96 h 3. 3% 0 150 mg / L 96 h 100% 11 Argopecteni rradians ph > 7. 99 NH 3 ph 7 ~ 8 LC 50 ph 60% 35% ph NH 3 -N ph 7. 7 ~ 8. 2 NH + 4 ph NH 3 NH 3 H 2 O ph 8. 0 ~ 8. 4 96hLC 50 54. 5 ~ 50. 6 mg / L NH + 4 NH 3 ph ph 7. 6 8. 0 8. 4 1. 7% 23 28 96 h ph 8. 8 2. 0 mg / L ph 7. 6 2. 9 6 17 Estellarca olivacea 14 11 Scapharca subcrenata 15 Coelom actra antiquata 7 ph 17 H 2 S ph 10 NH 3 27 6 96hLC 50 Table 6 Compareision of 96hLC 50 of total ammonia to several kinds of shellfish Species Shell hight mm ph 96hLC 50 Temperature Babylonia areolata 17 30 d 8. 5 100. 2 29 ~ 30 Argopecteni rradians 11 6 ~ 8 7. 99 11. 85 23 ~ 25 Estellarca olivacea 14 1. 579 ± 0. 131 8. 3 ± 0. 2 50 25 ± 0. 5 Scapharca subcrenata 15 1. 579 ± 0. 131 8. 15 ± 0. 18 20. 36 28 ± 0. 5 Coelom actra antiquata 7 6. 10 ± 0. 44 7. 90 ~ 8. 34 14. 220 25. 8 ~ 29. 2 Hemifusus tuba 11. 3 ± 0. 11 8. 0 ~ 8. 4 54. 5 ~ 50. 6 28. 5
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