Tropical Zoology 23: 75-89, 2010 Feeding habits and digestive enzymes in the gut of Mormyrus rume (Valenciennes 1846) (Osteichthyes Mormyridae) D.O. Odedeyi 1 and O.A. Fagbenro 2,3 Department of Environmental Biology and Fisheries, Adekunle Ajasin University, Akungba, Nigeria 2 Department of Fisheries and Aquaculture Technology, Federal University of Technology, Akure, Nigeria 1 Received 6 August 2009, accepted 29 April 2010 The feeding habits of 436 elephant snout fish, Mormyrus rume (Valenciennes 1846), from River Ose were investigated. Stomach contents were identified and analyzed by occurrence and volumetric methods, and the prominence of individual food items was determined by the ranking index I. Only 3.2% of the specimens had empty stomachs while the others had stomachs in varying degrees of fullness. Food items included plant and animal matter, mainly arthropods. A preponderance of insects, crustaceans and detritus, which accounted for 100% occurrence and > 16% of total volume in the stomachs of M. rume specimens, suggests a benthic feeding habit. The high percentage occurrence of detritus and its high I value established M. rume as a detritivore. Assays were conducted to determine the occurrence, distribution and specific activities of digestive enzymes in different gut regions of juvenile (SL < 35.0 cm) and adult (SL > 35.0 cm) M. rume. Alphaamylase, maltase, lactase, sucrase, chitinase, pepsin, trypsin and lipase were present in the different gut regions at varying quantities and with specific activities. The wide distribution of enzymes in both juvenile and adult M. rume reflects its ability to digest the carbohydrate, protein and lipid portions of its foods. There were no differences (P > 0.05) in specific activities of digestive enzymes between wet and dry seasons. key words: feeding habits, stomach contents, digestive enzymes, gut, Mormyrus rume. Introduction .................................................................................. 76 Materials and methods ................................................................... 77 3 Corresponding author: O.A. (Dapo) Fagbenro, Tel: + 234-(0)8077788688 (E-mail: [email protected]). 76 D.O. Odedeyi and O.A. Fagbenro Results ........................................................................................... 80 Discussion ..................................................................................... 82 References ...................................................................................... 87 INTRODUCTION The food and feeding habits of different fishes often differ widely. The same fish also may show a preference for different types of food as it grows or at different times of the year (Maar et al. 1983). The stomachs of many tropical fishes have been studied to ascertain their feeding habits in natural habitats and the relationship between the fishes and their biotic environments (Ugwumba et al. 1990). Fagbenro et al. (2000) established Heterotis niloticus (Cuvier 1829) as a benthic feeder in River Oluwa and a planktonic feeder in Owena Reservoir and Mahin Lagoon. Kouamelan et al. (1999) reported that M. rume stomach contents from a man-made lake on River Bia (Côte d’Ivoire) comprised mainly chironomid larvae and bacillariophyceae in young fish, while Chaoborus Lichtenstein 1800 species formed the main food item in larger specimens. Fawole (2002) reported that the major food items in stomachs of M. rume in Lekki Lagoon (Nigeria) were detritus and plants. Omotosho (1993) reported that M. rume fed on detritus, algae and macrophytes in Oyun mini-dam (Nigeria) while Ipinjolu et al. (2005) reported that M. rume in River Rima and Goronyo reservoir (Nigeria) fed on items of both plant and animal origin. Assays of enzymes in the gut of a fish provide information about its nutritional physiology. The quality of a given food item is directly proportional to its ability to support growth and its nutritional value is determined by the ability of the animal to digest and absorb it (Akintunde 1985). Tengjaroenkul et al. (2000) reported that the distribution and specific activity of digestive enzymes along the gut change with feeding habits. Tramati et al. (2005) noted that the age and/or stage of development influence the anatomical and physiological development of the digestive organs, and the digestive processes are correlated with the size and type of food items in fishes, thus explaining different feeding habits at various stages of the life cycle (Kuz’mina et al. 2002). Under natural conditions, adults tend to capture larger prey, which demands a greater digestive effort due to the smaller surface area exposed to enzymatic action. Uys & Hecht (1987) reported that knowledge of the digestive enzymes enhances the development of more efficient diets and rearing techniques. Studies have been conducted on digestive enzymes of various tropical fishes in sub-Saharan Africa (Olatunde & Ogunbiyi 1977; Uys & Hecht 1987; Fagbenro 1990; Fagbenro et al. 1993, 2000, 2001, 2005; Ugwumba 1993) but no such information is available for M. rume. The objectives of this study were to determine the feeding habits and the occurrence, distribution and specific activities of digestive enzymes in different regions of the gut of juvenile (SL < 35.0 cm) and adult (SL > 35.0 cm) specimens of M. rume. Feeding habits and digestive enzymes in Mormyrus rume 77 MATERIALS AND METHODS River Ose is a major perennial river in southwestern Nigeria (Fig. 1). Its source is in the Apata hills and it flows through savannah, rainforest, mangrove forest before discharging into the Atlantic Ocean through a series of creeks and lagoons. The river lies between longitudes 5°20’E to 6°10’E and latitudes 6°20’N to 8°00’N. It flows approximately 300 km from its source before breaking into a series of creeks and lagoon. M. rume specimens (436) were obtained from artisanal fishermen using gill nets set daily at 18:00 hr and recovered at dawn (06:00 hr) in River Ose. The specimens Fig. 1. — Location of River Ose, southwestern Nigeria. 78 D.O. Odedeyi and O.A. Fagbenro were collected over 24 months. The total and standard lengths (cm) and weight (g) of each specimen were taken using a fish measuring board and Ohaus Triple Beam Balance (Model 610), respectively. The specimens were dissected on the ventral side from the anal opening to the pectoral fin region. The stomach was removed and the degree of fullness was assessed visually and recorded as empty, ¼ full, ½ full, ¾ full, and full. The stomach of each specimen was opened and the contents emptied into a Petri dish containing a known volume of water for subsequent identification and estimation of food items under a binocular dissecting microscope. For the quantification of microscopic food items, a drop of the food mixture was placed on a glass slide for identification and counting with a binocular light microscope. The various food items were analyzed by occurrence and volumetric methods (Arawomo 1976). The prominence of individual food items was determined by the ranking index I (Oda & Parrish 1981): I = (% occurrence × % volume) × 10-2 . Forty live M. rume were obtained from fishermen in River Ose. The total and standard lengths (cm) and weight (g) of each fish were taken using a fish measuring board and Ohaus Triple Beam Balance, respectively. The specimens were kept for 48 hr in glass tanks without feeding to bring them to similar physiological conditions and to ensure the emptiness of their guts. The entire gut was removed, measured on ice, and then separated into oesophagus, stomach, pyloric caeca, anterior intestine, posterior intestine and rectum. Tissues from 10 specimens each of juvenile and adult fish were pooled and preserved separately in a chest freezer. Each of the regions was weighed after thawing, homogenized in an all-glass homogenizer with 10 times its weight of ice-cold neutralized 1% KOH to give a 1:10 homogenate. The homogenates were centrifuged at 2500 rpm for 20 min at 4 oC in a refrigerated centrifuge. The precipitant was discarded and the clear supernatant was used as a crude enzyme solution without further purification. Specific activities of proteases The specific activities of proteases in the digestive tract of M. rume were determined in triplicate samples using the method of Rinderknecht et al. (1968) and Balogun & Fisher (1970). Trypsin was determined in a reaction mixture consisting of 1 ml/10 mg egg-albumin solution, 2 ml phosphate buffer (pH 8.0) and 0.5 ml enzyme solution. The enzyme in the control was boiled at 37 oC for 20 min in a water bath. The reaction mixture for the determination of pepsin was like that of trypsin but the phosphate buffer for the pepsin was pH 2.0. Both the test and control samples were incubated for 1 hr at 100 oC. During incubation, there was regular shaking of the tubes to ensure uniform reaction. At the end of incubation, 3 ml of ice-cold phosphate buffer was added to the test tubes. The mixture was filtered immediately through Whatman No. 1 filter paper and the absorbance of the filtrate was determined at 595 nm with a Gallenkamp color-spec colorimeter (model COJ-580010N). The blank was used to adjust the colorimeter to zero. Specific activities of glycosidases Glycosidases were determined in triplicate samples by the dinitrosalicylate (DNS) methods described by Plummer (1978) and Olatunde et al. (1988). The presence of free reducing sugars was initially determined and the amounts of DNS Feeding habits and digestive enzymes in Mormyrus rume 79 reduced in the presence of appropriate substrate and extracts were compared. The substrates used for the assays were starch, maltose, sucrose, lactose, chitin and cellulose. The reaction mixture consisted of 0.4 ml of 1% substrate, 0.2 ml phosphate buffer pH 8.0, 1.6 ml DNS and 0.1 ml of enzyme extract. The enzyme extract in the control was replaced with distilled water. The control and test samples were allowed to stand at room temperature for 3 min, then 1.0 ml (DNS) was added to each sample and they were placed in boiling water for 5 min. The samples were removed and left to cool for 30 min, after which 1.8 ml of distilled water was added to each sample to bring it up to 4.0 ml (for dilution) and it was mixed properly. The amount of reducing sugar produced in the enzymatic reaction was estimated with a colorimeter at 540 nm. Specific activities of lipases Specific activities of lipases were determined at 37 oC in triplicate samples as described by OgunbiyI & Okon (1976). The reaction mixture consisted of 1.0 ml of 25% olive oil emulsion pH 7.0 and 0.2 ml of enzyme extract. The test and control samples were incubated for 1 hr at 37 oC in a water bath, after which 3.0 ml of 95% ethanol and two drops of phenolphthalein were added to each test tube including the control. The reaction mixture was titrated against 0.05 M NaOH to a similar pink colour. An increase in the titre value of the test sample was compared with the control to confirm the presence of lipase in the test sample. Preparation of the calibration curve for protein The stock consisted of 100 µg/ml egg-albumin (10 mg of egg-albumin dissolved in 100 ml of water). Serial dilutions of stock solution were prepared, ranging from 20-100 µg/ml egg-albumin. Each concentration was prepared in duplicate tubes, each tube containing 1 ml of the dilution and 3 ml of biuret. The egg-albumin in the blank tube was replaced with distilled water. Both the test samples and controls were incubated for ten minutes at 37 oC in a water bath for colour development. The optimal density of the solution was determined with a colorimeter at 540 nm, and was used in the preparation of a calibration curve for determination of protein using egg-albumin. Absorbance was converted to enzyme activity: Unit of enzyme activity = Amount of amino acid released (µg/ml) Time Preparation of the calibration curve for glucose The stock solution consisted of 0.1 g D-glucose/100 ml. Serial dilutions ranging from 0 to 0.8 mg/ml were prepared from the stock. Each dilution was brought to 1 ml by the addition of distilled water. A blank tube that contained 1 ml of distilled water was used to adjust the colorimeter to 0. Each concentration was prepared in duplicate test tubes; 1.6 ml of alkaline 3.5-DNS reagent was added to each test tube and the sample was mixed properly. The samples were placed in a boiling water bath for 10 min. One millilitre of each sample of diluted stock was further diluted by the addition of 1 ml of distilled water. The absorbance of the reaction mixture was read at 540 nm against a blank containing buffer on the digital colorimeter. Unit of enzyme activity = Amount of glucose released (mg/ml) Time 80 D.O. Odedeyi and O.A. Fagbenro Statistical analyses All data obtained from the analyses were analyzed in terms of means and standard deviation. The data were also subjected to analysis of variance (ANOVA) with size and gut region as sources of variation. RESULTS The stomach fullness values for the specimens are presented in Table 1. M. rume in River Ose fed mainly on insects and crustaceans, which were found in all the stomachs containing food. Plant parts and detritus were also present in all stomachs containing food. Other food items were rotifers, diatoms, algae, nematodes, annelids, and protozoans. Insects, crustaceans, detritus and plant parts were widely consumed by the small (15.0-20.0 cm), medium (20.1-35.0 cm) and large (35.1-50.0 cm) M. rume individuals. Insects and crustaceans occurred in all the stomachs. By volume, insects and crustaceans (arthropods) accounted for 23 and 18%, 21 and 20%, 15 and 22% of the food of large, medium and small M. rume specimens, respectively (Table 2). According to the ranking index, insects were the prominent food item for large and medium specimens, with values of 23 and 21%, respectively, while crustaceans were the prominent food items for small fishes, making up 22% of the stomach contents (Table 2). As the fish size increased, the preference for insects increased and the preference for protozoans, rotifers and diatoms decreased. Detritus and plant materials occurred in 100% of the stomachs of large specimens, while the respective values were 98 and 92% in medium specimens and 93 and 96% in small specimens. According to the ranking index values (Table 2), detritus was more prominent among the food items consumed by smaller fish. Rotifers were significant food items consumed by small specimens and occurred in all the stomachs examined; however, they showed a low occurrence and low ranking index in large specimens. Table 1. Number of Mormyrus rume specimens examined and the degree of stomach fullness. Stomach fullness Full 15.0-20.0 1 25 9 4 1 Size (cm) 20.1-35.0 10 187 67 26 10 35.1-50.0 3 60 22 8 3 14 (3.2%) 272 (62.4%) 98 (22.5%) 38 (8.7%) 14 (3.2%) Total 40 300 96 436 Empty 1/4 1/2 3/4 Total Feeding habits and digestive enzymes in Mormyrus rume 81 Table 2. Food items in the stomachs of small, medium and large Mormyrus rume specimens. SL 15.0-20.0 cm SL 20.1-35.0 cm SL 35.1-50.0 cm Food items % volume % occurrence RI % volume % occurrence RI % volume % occurrence RI Protozoa 0.6 7.1 0.0 0.5 4.3 0.0 0.3 5.7 0.0 Crustacea 22.0 100.0 22.0 20.0 100 20.0 18.0 100.0 18.0 Insecta 15.0 100.0 15.0 21.0 100 21.0 23.0 100.0 23.0 Algae 2.0 11.1 0.2 1.5 70.2 1.1 1.3 57.1 0.7 Rotifera 5.0 100.0 5.0 4.0 51.0 2.0 3.0 65.7 2.0 Nematoda 0.3 3.7 0.0 0.2 2.1 0.0 0.3 5.7 0.0 Annelida 0.5 3.7 0.0 0.4 2.1 0.0 0.5 8.6 0.0 Arthropoda 11.0 100.0 11.0 12.0 95.7 11.5 18.0 100.0 18.0 Detritus 22.0 92.6 20.4 18.0 97.9 17.5 16.0 100.0 16.0 Sand grains 0.5 66.7 0.3 0.3 68.1 0.2 0.2 68.6 0.1 Plant parts 16.0 96.3 15.4 18.0 91.5 16.5 14.9 100.0 14.9 Unidentified mass 5.1 81.5 4.2 4.1 78.7 3.2 4.5 88.6 4.0 Total 100 100 100 The specific activities of digestive enzymes in the gut of M. rume juveniles and adults are presented in Table 3. The assay of enzymes showed that the strength of lipase activity was different in the different gut regions of both the juveniles and adults. Lipase activity was very strong in the anterior intestine, strong in the posterior intestine and pyloric caeca but weak in the oesophagus, stomach and rectum of both juveniles (SL < 35.0 cm) and adults (SL > 35.0 cm) in both seasons. The highest lipase activity occurred in the anterior intestine and was significantly different (P < 0.05) from the other regions, while the lowest activity was recorded in the oesophagus (Table 3). Lipase activity was higher in adults than in juveniles and particularly significant in the rectum (Table 3). 82 D.O. Odedeyi and O.A. Fagbenro Pepsin was present in the stomach, pyloric caeca and anterior intestine; it was strong in the stomachs of both juveniles and adults but weak in the pyloric caeca and anterior intestine, and absent in the oesophagus, posterior intestine and rectum (Table 3). Trypsin was present in the anterior and posterior intestine and was strong in the posterior intestine (Table 3). Proteases were not detected in the oesophagus and rectum of juveniles and adults (Table 3). Protease activity was higher in the stomach and posterior intestine than in the other gut regions. Pepsin activity was very high in the stomach and low in both the pyloric caeca and anterior intestine, with significant differences (P < 0.05) between juveniles and adults. Trypsin activity was high in the posterior intestine, low in the anterior intestine, and there were significant differences (P < 0.05) between juveniles and adults. Proteolytic activity was not recorded in the oesophagus and rectum of either juveniles or adults. Glycosidases (a-amylase, maltase, lactase, sucrase, chitinase, and cellulase) were present in all the gut sections except the rectum (Table 3). Alpha-amylase was very strong in both the pyloric caeca and anterior intestine and strong in the stomach, while the other glycosidases detected were weak in the various gut regions. Chitinase and cellulase were detected in the stomach, pyloric caeca and anterior intestine of juveniles and adults. Glycosidase activities in different gut regions of juveniles and adults varied somewhat between the wet and dry seasons but the differences were not significant (P > 0.05). The highest activity was in the pyloric caeca and anterior intestine and the lowest activity in the oesophagus (Table 3). There were significant differences (P < 0.05) between sizes. DISCUSSION The low incidence of full stomachs, coupled with the high incidence of ¼ full stomachs, uggests poor feeding activity in River Ose but may also be attributed to the method of catching, as many of the specimens were caught using gill nets. Arawomo (1976) reported > 67% empty stomachs for Citharinus Cuvier 1816 species caught with gill nets in Lake Kainji. Ipinjolu et al. (2005) reported that 48.1% of M. rume specimens caught in River Rima and Goronyo Dam (Nigeria) had empty stomachs and no sample had 100% fullness. This may have been due to the food items having been regurgitated or digested as the fish struggled during the gill net catches. M. rume in River Ose fed mainly on benthic insects (Notonectidae, Belastomatidae, Hydrometridae, Nepidae, Corixidae, Chironomidae, and Chaoboridae) and crustaceans (Potamonidae, Hydracarina spp., remains of decapods), which were found in all the stomachs containing food. This observation agrees with Ugwumba et al. (1990) that the mormyrids of Lekki Lagoon (Nigeria) fed mainly on insects and crustaceans. It also agrees with Kouamelan et al. (1999) who reported that M. rume in River Bia consumed invertebrates. There were also plant parts, sand grains and detritus in all stomachs containing food. Sand grains and detritus were probably ingested along with food items during feeding at the river bottom. This observation revealed that M. rume is a bottom dweller, feeding on benthic organisms. PaugY (2002) also reported that M. rume in Baoule Feeding habits and digestive enzymes in Mormyrus rume 83 River was insectivorous and that it was a benthic dweller. However, Omotosho (1993) reported that M. rume fed on detritus, algae and macrophytes in Oyun mini-dam, Ilorin (Nigeria), which agrees with Fawole (2002) who reported that the major food items of M. rume in Lekki Lagoon were detritus and plant parts. According to Ugwumba & Ugwumba (2007), these differences can be attributed to differences in food availability between the different habitats. All the food items were encountered in the stomachs of specimens irrespective of size and season. This agrees with Kouamelan et al. (1999) who reported that there were no significant variations in the food composition of M. rume from River Bia (Cameroon). However, during the dry season, chironomid larvae dominated the insect fauna while chaoborid larvae became more abundant in the rainy season. Moreover, during the rainy season, there is a continuous input of materials of allochthonous origin, notably insects (coleopterans, dipterans, ants, termites), seeds, leaves and pollen from flooded/inundated forests into River Ose, which settle at the bottom where they are decayed by bacterial and fungal activities. The high percentage occurrence of detritus coupled with the high ranking index of detritus suggest that M. rume is a bottom dweller and a detritivore; indeed, the trunk-like snout coupled with the small terminal mouth of M. rume encourages detritivory. Crustaceans and phytoplankton dominated the plankton found in the environment. However, insects were more prominent than rotifers in the stomachs of M. rume despite the relatively low occurrence in the open waters and benthos of the river, showing that M. rume has a higher preference for insects than for rotifers. This is evident since fish tend to optimize the energy content of prey ingested by maximizing their size in relation to their mouth gape. There was high glycosidase activity, an indication that M. rume is capable of digesting carbohydrates in its food. The presence of cellulase was also reported in the gut of the catfish, Heterobranchus bidorsalis Geoffroy St. Hilaire 1809 by FAgbenro et al. (1993) who noted that the occurrence of cellulase is a rather unusual development because it occurs in few vertebrates and that when it occurs the source is usually traced to the microflora inhabiting their guts. Tramati et al. (2005) also reported cellulase activities in the stomach, pyloric caeca, foregut, midgut and hindgut of Diplodus puntazzo Cetti 1777 juveniles and adults. The digestion of starch appears to have started in the oesophagus and continued to the posterior intestine. The high glycosidase activity in the pyloric caeca and anterior intestine ensured complete digestion of carbohydrates in these regions. The presence of lactase was also reported by Fagbenro et al. (1993) in H. bidorsalis and by Lagler et al. (1977) in the pyloric caeca of trout, though lactase is known to be associated with milk digestion in mammals. The strong activities of chitinase in the stomach of adult M. rume specimens and average activities in both the pyloric caeca and anterior intestine (Table 3) showed that as the fish size increased the preference for insects increased as well; this agrees with the increasing specificity of feeding habits of the adult fish (SL > 35.0 cm) which had benthic insects and crustaceans as the prominent food items (Ugwumba et al. 1990, Ipinjolu et al. 2005). This finding agrees with Fagbenro et al. (2000) who recorded high chitinase activity in both the stomach and anterior intestine of the electric catfish, Malapterurus electricus Gmelin 84 D.O. Odedeyi and O.A. Fagbenro Table 3. Specific activities of enzymes in the gut of juveniles and adults of Mormyrus rume from River Ose. Proteases2 Gut regions Lipases1 Pepsin Trypsin Juveniles (SL < 35.0 cm) Oesophagus 0.84+0.15a* 0 0 Stomach 2.33+0.15b* 0.15+0.02a* 0 Pyloric caeca 4.62+0.34c* 0.100+01b* 0 Anterior intestine 6.64+0.40d* 0.10+0.01b* 0.08+0.03a* Posterior intestine 5.04+0.07e* 0 0.16+0.02b* Rectum 1.30+0.10f* 0 0 Oesophagus 0.90+0.10a** 0 0 Stomach 2.50+0.37b** 0.19+0.01a** 0 Pyloric caeca 5.10+0.46c** 0.11+0.01b** 0 Anterior intestine 7.23+0.11d** 0.11+0.01 c** 0.10+0.01a** Posterior intestine 5.27+0.14e** 0 0.18+0.01b** Rectum 2.90+0.20f** 0 0 Adults (SL > 35.0 cm) (continued) Feeding habits and digestive enzymes in Mormyrus rume 85 Table 3. (continued) Glycosidases3 a-Amylase Maltase Lactase Sucrase Cellulase Chitinase 0.04+0.00a* 0.01+0.00a* 0 0 0 0 0.14+0.02b* 0.09+01b* 0.07+0.01a* 0.07+0.01a* 0.02+0.01a* 0.03+0.00a* 0.50+0.03c* 0.09+0.00c* 0.08+0.01b* 0.05+0.01b* 0.03+0.00b* 0.03+0.00a* 0.36+0.03d* 0.06+0.01d* 0.05+0.02c* 0.04+0.01c* 0.02+0.00c* 0.02+0.00b* 0.03+0.00e* 0.02+0.00e* 0.02+0.00d* 0.02+0.00d* 0 0 0 0 0 0 0 0 0.11+0.01a** 0.02+0.00a** 0 0 0 0 0.34+0.02b** 0.10+01b** 0.08+0.01a** 0.08+0.02a** 0.02+0.00a** 0.05+0.00a** 0.53+0.03c** 0.13+0.02c** 0.06+0.01b** 0.07+0.01b** 0.05+0.02b** 0.06+0.01a** 0.39+0.02d** 0.07+0.02d** 0.05+0.02c** 0.05+0.01c** 0.04+0.01c** 0.04+0.00b** 0.04+0.01e** 0.03+0.00e** 0.03+0.00d** 0.02+0.00d** 0 0 0 0 0 0 0 0 a-f = for each enzyme, data in the same column with different superscript letters are significantly different (P < 0.05); *,** = for each enzyme, data along the same row with different asterisks are significantly different (P < 0.05); 1 milliequivalents of fatty acids/mg protein at 37 o C, 2 change in optical density at 595 nm/hr/mg of L-tyrosine/hr at 37 oC, 3 mg glucose/min/ mg protein at 37 oC. 86 D.O. Odedeyi and O.A. Fagbenro 1789, and associated this with its chitin-eating habit (feeding on crustaceans and insects). Similarly high chitinase activities were detected in the stomachs and intestines of Atlantic cod fed on whole crustaceans (Danulat 1986). Lindsay (1984) suggested that the primary function of gastric chitinase in fishes is to chemically disrupt the chitin envelope of the prey. Digestion of protein in M. rume started in the stomach. The absence of proteases in the oesophagus showed that this region only serves for the passage of food items to the stomach while the rectum retains undigested food materials or waste prior to being voided from the body (Olatunde & Ogunbiyi 1977, Olatunde et al. 1988). The high peptic activities recorded in the stomach of both juvenile and adult M. rume suggest the consumption of protein-rich food items by this species. High peptic activity was also reported in the stomach of the electric catfish by Fagbenro et al. (2001). Smith (1980) reported that peptic activity in fishes occurs in acid conditions (pH 2.0-4.0) as in higher vertebrates and is about 150 times greater than the activity of mammalian pepsin in the affinity for the substrate (Ananichev 1959). The high activity of trypsin, an alkaline protease, in the posterior intestine of M. rume agrees with Fagbenro et al. (2001) who also recorded high trypsin activity in the posterior intestine of the electric catfish, M. electricus. Olatunde & Ogunbiyi (1977) attributed high trypsin activities in Schilbe mystus Linnaeus 1758 to the large amounts of fish and insect materials in the food of the species. Pepsin activity was high in both juveniles and adults of M. rume. The high pepsin and trypsin activities recorded in this study can be attributed to M. rume consuming protein-rich food items, in a similar manner to H. bidorsalis (Fagbenro et al. 1993, 2001) and other tropical catfishes, Parailia (Physailia) pellucida Boulenger 1901, Eutropius niloticus Rüppell 1829 and S. mystus (Olatunde & Ogunbiyi 1977). Protein digestion was initiated by pepsin and completed by trypsin; Uys & Hecht (1987) and Fagbenro et al. (1993) reported that partial hydrolysis of protein is subsequently completed by the combined action of trypsin and chymotrypsin when food reaches the intestine. Lipase activity was detected in all the regions of the M. rume gut, indicating a uniform distribution in the entire gut system, as reported in Heterotis niloticus Cuvier 1829 by Fagbenro et al. (2000). Swarup & Goel (1975) also observed lipases along the entire gut of some teleosts. The lipase activity was lowest in the oesophagus and more abundant in the pyloric caeca, anterior and posterior intestine, which are the neutral and alkaline regions of the tract. This agrees with Tramati et al. (2005) who reported that lipase was more abundant in the neutral-alkaline gut regions of juvenile and adult D. puntazzo. Fagbenro et al. (1993) reported that lipase activity was average and restricted to the posterior regions of the H. bidorsalis gut, while Olatunde & Ogunbiyi (1977) reported that lipase activities were not detected in the guts of P. pellucida, E. niloticus and S. mystus and remarked that this was a surprise in view of the fact that the food items consumed by E. niloticus and S. mystus included fatty fishes such as clupeids. The higher values (P < 0.05) of lipase activity in the rectum of adult M. rume than of juvenile M. rume (Table 3) are unusual and can be attributed to forceful ejection of enzymes while the fish struggle immediately after being captured in the gill nets. Feeding habits and digestive enzymes in Mormyrus rume 87 According to Buddington (1985), the presence or absence of certain digestive enzymes in fishes depends on the food and feeding habits as well as the functional morphology of the various parts of the gut. In addition, the presence of some enzymes in the oesophagus might be an artefact due to reflux of the chyme and/or digestive juices caused by stress suffered when the fish are captured in gill nets and handled by the fishermen. The occurrence of various glycosidases, proteases and lipases in the gut of M. rume was correlated with detritivorous food habits. The digestive enzyme activities in the adults were higher than in the juveniles, which agrees with Tramati et al. (2005) that the digestive processes of D. puntazzo are correlated with the size and composition of the food. Lee et al. (1984) and Le François et al. (2000) also reported that the activities of glycolytic enzymes increased with fish mass. REFERENCES Akintunde E.A. 1985. Digestive enzymes in the gut of Sarotherodon galilaeus (Syn. Tilapia galilea) (Family Cichlidae) of Lake Kainji. Journal of Science 18: 22-25. Ananichev A.B. 1959. Digestive enzymes of fish and seasonal change in their activity. Biokhimiya 24: 1033-1040. Arawomo G.A.O. 1976. Food and feeding of three Citharinus species in Lake Kainji, Nigeria. Journal of Fish Biology 9: 3-10. Balogun R.A. & Fisher O. 1970. Studies on the digestive enzymes of the common African toad, Bufo regularis Boulenger. Comparative Biochemistry and Physiology 33: 813-820. Buddington R.K. 1985. Digestive secretion of sturgeon (Acipenser fulvescens) during early development. Journal of Fish Biology 26: 715-723. Danulat E. 1986. The effects of various diets on chitinase and -glucosidase activities and the condition of cod, Gadus morhua (L.). Journal of Fish Biology 28: 191-197. Fagbenro O., Adedire C.O., Ayotunde E.O. & Faminu E.O. 2000. Haematological profile, food composition and digestive enzyme assay in the gut of the African bony-tongue fish, Heterotis (Clupisudis) niloticus (Cuvier 1829) (Osteoglossidae). Tropical Zoology 13: 1-9. Fagbenro O., Adedire O., Fateru O., Owolabi I., Ogunlana O., Akanbi B., Fasanmi T. & Ayo-Amu P. 2005. Digestive enzyme assays in the gut of Oreochromis niloticus Linnaeus 1757, Parachanna (Channa) obscura Gunther 1861 and Gymnarchus niloticus Cuvier 1829. Animal Research International 2 (2): 292-296. Fagbenro O.A. 1990. Food composition and digestive enzymes in the gut of pondcultured Clarias isheriensis (Sydenham 1980), (Siluriformes: Clariidae). Journal of Applied Ichthyology 6: 91-98. Fagbenro O.A., Adedire C.O. & Aiyegbeni M.L. 2001. Food composition and digestive enzymes in the gut of the African electric catfish, Malapterurus electricus (Gmelin 1789) (Malapteruridae). Tropical Zoology 14: 1-6. Fagbenro O.A., Adedire C.O., Owoseeni E.A. & Ayotunde E.O. 1993. Studies on the biology and aquaculture potential of feral catfish Heterobranchus bidorsalis Geoffroy St. Hilaire (1809) (Clariidae). Tropical Zoology 6: 67-79. Fawole O.O. 2002. Morphometry and diet of Mormyrus rume in the Lekki Lagoon, Nigeria. Reviews in Tropical Biology 50 (2): 689-694. 88 D.O. Odedeyi and O.A. Fagbenro Ipinjolu J.K, Malami Z.G., Hassan W.A & Abubakar U. 2005. Food habits of elephant snout (Morumyrus rume Cuvier & Valenciennes) in River Rima and Goronyo Dam in northwestern Nigeria. Bulletin of the Science Association of Nigeria 26: 173-185. Kouamelan P.E., Teugels G.G., Gourene G., Ollevier F. & Thys Vanden Audenaerde D.F.E. 1999. The effect of a man-made lake on the diet of the African electric fish Mormyrus rume Valenciennes, 1846 (Osteoglossiformes; Mormyridae). Hydrobiologia 380: 141-151. Kuz’mina V.V., Golovanova I.L. & Kovalenko E. 2002. Separate and combined effects of cadmium, temperature and pH on digestive enzymes in three freshwater teleosts. Bulletin of Environmental Contamination and Toxicology 69 (2): 302-308. Lagler K.F., Bardach J.E. & MilleR R.R. 1977. Ichthyology: the study of fishes. New York: USA: John Wiley & Sons Inc., 544 pp. Lee P.G., Smith L.L. & Lawrence A.L. 1984. Digestive proteases of Penaeus vannamei Boone: relationship between enzyme activity, size, and diet. Aquaculture 42: 225-239. Le François N.R, Lemieux H., Blier, P., Falt-petersen I.B., Hendry C.I. & Mc Laddery S.E. 2000. Effects of three different feeding regimes on growth, metabolism and digestive enzymes activities in early life of Atlantic wolfish (Anartichas lupus). Proceedings of the 17th Annual Meeting of the Aquaculture Association of Canada. Special Publication of the Aquaculture Association of Canada 4: 53-56. Lindsay G.J.H. 1984. Distribution and function of digestive tract chitinolytic enzymes in fish. Journal of Fish Biology 24: 529-536. Maar A., Mortimer M.A.E. & Van Der Lingen I. 1983. Fish culture in Central East Africa. Rome: FAO, 158 pp. Oda D.K. & Parrish J.D. 1981. Ecology of commercial snappers and groupers introduced to Hawaiian reefs. Proceedings of the Fourth International Coral Reef Symposium 1: 59-67. Ogunbiyi O.A. & OkoN E.E. 1976. Studies on the digestive enzymes of the African fruit bat, Eilodon helvum (Kerr.). Comparative Biochemistry and Physiology 55: 359-361. Olatunde A.A. & Ogunbiyi O.A. 1977. Digestive enzymes in the alimentary tracts in three tropical catfishes. Hydrobiologia 56: 21-24. Olatunde A.A., Ukoha A.I. & Oguntayo B.F. 1988. Digestive enzymes in the alimentary tract of Clarias lazera (Cuvier & Valenciennes) Family Clariidae (Osteichthyes: Siluriformes). Archiv für Hydrobiologie 112: 107-113. Omotosho J.S. 1993. Analysis of fish species composition of Oyun mini-dam, University of Ilorin, Nigeria. Journal of West African Science Association 36: 37-48. Paugy D. 2002. Reproductive strategies of fishes in a tropical temporary stream of the upper Senegal basin: Baoule River in Mali. Aquatic Living Resources 15: 25-35. Plummer D.T. 1978. An introduction to practical biochemistry, 2nd ed. London, UK: McGraw Hill Book Company, 347 pp. Rinderknecht H., Geokas M.C., Silverman P. & Haverback B.J. 1968. A new ultrasensitive method for the determination of proteolytic activity. Clinica Chimica Acta 21: 197-203. Smith L.S. 1980. Digestion in teleost fishes, pp. 3-18. In: Chow K.W., Edit. Fish feeds technology. FAO/UNDP Aquaculture Development and Coordination Programme. ADCP/REP/SO/11. Rome: FAO/UNDP, 295 pp. Swarup C. & Goel K.A. 1975. Histochemical study of the activity of lipase in the digestive system of some teleost fishes. Acta Histochemica 54: 10-15. Feeding habits and digestive enzymes in Mormyrus rume 89 Tengjaroenkul B., Smith B.J., Caceci T. & Smith S.A. 2000. Distribution of intestinal enzyme activities along the intestinal tract of cultured Nile tilapia, Oreochromis niloticus L. Aquaculture 182: 317-327. Tramati C., Savona B. & Mazzola A. 2005. A study of the pattern of digestive enzymes in Diplodus puntazzo (Cetti 1777) (Osteichthyes, Sparidae): evidence for the definition of nutritional protocols. Aquaculture International 13: 89-95. Ugwumba A. & Ugwumba A.A.A. 2007. Food and feeding ecology of fishes in Nigeria. Ajah, Lagos: Crystal Publishers, 91 pp. Ugwumba A., Ugwumba A.A.A. & Mbu-Oben P. 1990. Food, feeding ecology of the mormyrids of Lekki Lagoon, Nigeria. Nigerian Journal of Natural Sciences 5 (1-2): 38-46. Ugwumba A.A.A. 1993. Carbohydrate in the digestive tract of the African bony-tongue Heterotis niloticus (Pisces: Osteoglossidae). Hydrobiologia 257 (2): 95-100. Uys W. & Hecht T. 1987. Assays on the digestive enzymes of sharp tooth catfish Clarias gariepinus (Pisces: Clariidae). Aquaculture 63: 301-313.
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