The sulfide tolerance of milkfish and tilapia in relation to fish kills in farms and natural waters in the Philippines

被引:39
作者
Bagarinao, T [1 ]
Lantin-Olaguer, I [1 ]
机构
[1] SE Asian Fisheries Dev Ctr, Iloilo 5021, Philippines
关键词
hypoxia tolerance; acid tolerance; intensive farming; sediments; Chanos chanos; Oreochromis mossambicus;
D O I
10.1023/A:1003420312764
中图分类号
Q17 [水生生物学];
学科分类号
071004 ;
摘要
Fish kills of milkfish Chanos chanos and tilapia Oreochromis spp. now occur frequently in brackish, marine, and freshwater farms (ponds, pens, and cages) in the Philippines. Aquafarms with high organic load, limited water exchange and circulation, no aeration, and high stocking and feeding rates can become oxygen-depleted and allow sulfide from the sediments to appear in the water column and poison free-swimming fish. The sulfide tolerance of 2-5 g milkfish and 5-8 g O. mossambicus was determined in 25-liter aquaria with flow-through sea water (100 ml min(-1)) at 26-30 degrees C and sulfide stock solutions pumped in at 1 ml min(-1). Total sulfide concentrations in the aquaria were measured by the methylene blue method and used in the regression against the probits of % survival. Four experiments showed that the two species have similar sulfide tolerance. In sea water of pH 8-8.5, about 163 +/- 68 mu M or 5.2 +/- 2.2 mg l(-1) total sulfide (mean +/- 2 se) or 10 mu M or 313 mu g l(-1) H2S was lethal to 50% of the fish in 4-8 h, and 61 +/- 3 mu M total sulfide or 4 mu M H2S in 24-96 h (to convert all sulfide concentrations: 1 mu M = 32 mu g l(-1)). Earthen pond bottoms had 0-382 mu M total dissolved sulfide (mean +/- sd = 54 +/- 79 mu M, n = 76); a tenth of the samples had >200 mu M. The water column may have such sulfide levels under hypoxic or anoxic conditions. To simulate some of the conditions during fish kills, 5-12 g milkfish were exposed to an abrupt increase in sulfide, alone or in combination with progressive respiratory hypoxia and decreasing pH. The tests were done in the same flow-through set-up but with sulfide pumped in at 25 ml min(-1). The lethal concentration for 50% of the fish was 197 mu M total sulfide or 12 mu M H2S at 2 h, but 28-53 mu M sulfide allowed fish to survive 6-10 h. Milkfish in aquaria with no aeration nor flow-through sea water died of respiratory hypoxia in 5-8 h when oxygen dropped from 6 to 1 mg l(-1). Under respiratory hypoxia with 30-115 mu M sulfide, the fish died in 2.5-4 h. Tests with low pH were done by pumping a weak sulfuric acid solution at 25 ml min(-1) into aquaria with flow-through sea water such that the pH dropped from 8 to 4 in 5 h. Under these conditions, milkfish died in 7-9 h when the pH was 3.5. When 30-93 mu M sulfide was pumped in with the acid, the fish died in 2-6 h when the pH was still 4.5-6.3. Thus, sulfide, hypoxia, and low pH are each toxic to milkfish at particular levels and aggravate each other's toxicity. Aquafarms must be well oxygenated to prevent sulfide toxicity and fish kills.
引用
收藏
页码:137 / 150
页数:14
相关论文
共 52 条
[21]   DAILY OXYGEN VARIATIONS IN MARINE FISH PONDS, ELAT, ISRAEL [J].
EREZ, J ;
KROM, MD ;
NEUWIRTH, T .
AQUACULTURE, 1990, 84 (3-4) :289-305
[22]   EFFECTS OF WATER DEPTH AND ARTIFICIAL MIXING ON DYNAMICS OF PHILIPPINES BRACKISHWATER SHRIMP PONDS [J].
FAST, AW ;
CARPENTER, KE ;
ESTILO, VJ ;
GONZALES, HJ .
AQUACULTURAL ENGINEERING, 1988, 7 (05) :349-361
[23]   INHIBITORY EFFECTS OF MICROCYSTIS-AERUGINOSA TOXIN ON ION PUMPS OF THE GILL OF FRESH-WATER FISH [J].
GAETE, V ;
CANELO, E ;
LAGOS, N ;
ZAMBRANO, F .
TOXICON, 1994, 32 (01) :121-127
[24]   MECHANISMS OF HYDROGEN-SULFIDE RELEASE FROM COASTAL MARINE-SEDIMENTS TO ATMOSPHERE [J].
HANSEN, MH ;
INGVORSEN, K ;
JORGENSEN, BB .
LIMNOLOGY AND OCEANOGRAPHY, 1978, 23 (01) :68-76
[25]  
*IFP, 1974, IFP TECHNICAL REPORT, V5, P21
[26]   CAUSES OF FISH MORTALITIES IN SEMI-INTENSIVELY OPERATED SEAWATER PONDS IN EILAT, ISRAEL [J].
KROM, MD ;
PORTER, C ;
GORDIN, H .
AQUACULTURE, 1985, 49 (02) :159-177
[27]   PHENOL AND SULFIDE INDUCED CHANGES IN THE OVARY AND LIVER OF SEXUALLY MATURING COMMON CARP, CYPRINUS-CARPIO [J].
KUMAR, V ;
MUKHERJEE, D .
AQUATIC TOXICOLOGY, 1988, 13 (01) :53-59
[28]  
MAEDA H, 1988, NIPPON SUISAN GAKK, V54, P1623
[29]   ASSOCIATION BETWEEN PORE WATER SULFIDE CONCENTRATIONS AND THE DISTRIBUTION OF MANGROVES [J].
NICKERSON, NH ;
THIBODEAU, FR .
BIOGEOCHEMISTRY, 1985, 1 (02) :183-192
[30]  
Ochumba P.B.O., 1987, Water Quality Bulletin, V12, P119