Evaluation of Coffee Ground as a Feedstuff in Practical Diets for Olive Flounder Paralichthys olivaceus

  • cc icon

    A 10-week feeding trial was carried out to investigate the feasibility of using spent coffee ground (CG) as a potential feed ingredient for olive flounder. Growth, feed utilization, body composition and antioxidant enzyme activity were examined. A control diet was formulated and three other diets were prepared to contain 5, 10 or 15% CG (designated as Con, CG5, CG10 and CG15, respectively) by replacing for wheat flour. Two hundred forty fish (104 ± 0.7 g/fish) were allotted to 12 circular tanks of 400 L capacity at a density of 20 fish per tank and fed the experimental diets twice daily. At the end of the feeding trial, fish fed the CG5 diet exhibited significantly (P < 0.05) higher growth performance than those fed the control diet. Also, fish fed the CG10 diet had a comparable growth to that of the control group, but further increase of dietary CG inclusion level to 15% resulted in significant decrease of growth performance. Fish fed the CG15 diet showed significantly lower feed efficiency and protein efficiency ratio than other treatments. Significantly lower muscle protein content was observed in fish fed CG15 diet compared to the control. Significant reduction in plasma cholesterol concentration was found in fish fed CG15 diet compared to control. No significant changes were found in alkyle and superoxide radicals scavenging activities of plasma, muscle and liver among dietary treatments. Also, liver total protein, total antioxidant capacity, catalase and glutathione peroxidase activities were not significantly influenced by dietary inclusion of CG. According to these results, we concluded that CG can be included up to 10% in the diet for olive flounder without any adverse effects on growth, feed utilization and antioxidant enzyme activity.


    Olive flounder , Coffee ground , Growth performance , Feed utilization , Antioxidant enzyme activity

  • Introduction

    Aquaculture continues to be the fastest growing animal food-producing sector. As aquaculture production becomes increasingly intensive, fish feed will be an important factor in increasing the productivity and profitability of the sector (Jamu and Ayinla, 2003). Considering that feed is the single costliest item in aquaculture practice, accounting for > 50% of the production cost, feed management determines aquaculture viability (Shang, 1992; Craig and Helfrich, 2002; Jamu and Ayinla, 2003). In this regard, nutrition research that reduces the cost of fish feeds without reducing their efficacy will be crucial to the successful development of aquaculture.

    The use of crop and animal waste as animal feed is of considerable interest because it produces an environmental benefit besides reducing the cost of animal production (Samuels et al., 1991; Westendorf et al., 1998; Myer et al., 1999; Westendorf, 2000). In many tropical regions of Asia and Africa, waste from crops, agro-industry and animal production are commonly used in aquaculture. Such waste has been used as a feed ingredient, supplementary feed, or pond fertilizer (Ravishankar and Keshavanath, 1986; Wohlfarth and Hulata, 1987; Subosa, 1992; Tacon, 1993, 1994).

    Coffee production for human consumption gives rise to a number of byproducts that can be used as feedstuff. These include leaves, pulp from the bean, coffee residues, coffee meal, and spent coffee grounds (CG). The coffee bean can be used to make one of the most popular beverages in the world, and considerable amounts of coffee bean are processed daily, leading to large quantities of byproducts that could be used as dietary ingredients (Heuzé and Tran, 2011). Coffee byproducts are rich, low-cost sources of carbohydrates, proteins and bioactive compounds. Roasted coffee contains ~10% protein, 11–17% lipid, 38–42% carbohydrates, and 4.5–4.7% minerals (Esquivel and Jiménez, 2012). In addition, coffee beans comprise a complex array of components with the potential to influence metabolic processes. The most influential compounds are alkaloids (caffeine and trigonelline), phenolic compounds (chlorogenic acids), and diterpenes (Oestreich-Janzen, 2010). These coffee components are believed to have potential as antioxidants and free radical scavengers. CG are the residue of soluble coffee processing. Although the volume of coffee residues has decreased due to improvements in soluble coffee processing, their disposal remains a matter of great concern. Hence, the development of rational uses for roasted coffee residues is necessary. Many attempts have been made to use roasted coffee residues as a fertilizer, animal feed, or a substitute for industrial materials.

    There are several reports on the use of coffee pulp as a feed ingredient for fish (Rojas, 2002; Moreau et al., 2003); however, to the best of our knowledge, no study on the use of spent CG in fish feed has been reported. Therefore, the present study aimed to evaluate CG as a potential feedstuff for olive flounder in terms of growth performance, feed utilization, body composition, and antioxidant enzyme activity.

    Materials and Methods

      >  Experimental diets

    Proximate and essential amino acid compositions of the major dietary ingredients used in this study are shown in Table 1. A basal diet was formulated and used as a control and three other test diets were prepared to contain 5, 10 or 15% CG (designated as Con, CG5, CG10, and CG15, respectively) (Table 2). Roasted Arabica coffee residue was used as the source of CG in this study. Coffee beans were roasted at 180–210°C for 15 min, and the drip water temperature was set to 90°C. Fish meal was used as the primary protein source and fish oil was used as the lipid source. All ingredients were thoroughly mixed with 30% distilled water and pellets were prepared using a laboratory moist-pelleting machine. The pellets were dried at room temperature for 48 h, crushed into the desired particle size and stored at -30°C until use.

      >  Fish and feeding trial

    Flounder were transported from a local hatchery (Namhae, Korea) to the Gangneung-Wonju National University, Korea. The fish were acclimated to laboratory conditions and fed a commercial diet twice daily for 2 weeks prior to starting the feeding trial. Two hundred forty fish (104 ± 0.7 g/fish) were randomly distributed into twelve 400 L polyvinyl circular tanks at a density of 20 fish per tank. Each experimental diet was fed to triplicate groups of fish to apparent satiation twice daily (09:00 and 17:00) for 10 weeks. A flow-through system was used, and each tank was supplied with filtered seawater at a flow rate of 4 L min-1 and aeration to maintain sufficient dissolved oxygen. The water temperature during the experiment was maintained at 21.5 ± 3.59°C and the photoperiod was maintained on a 12:12 h light:dark schedule.

      >  Sample collection and analyses

    At the end of the feeding trial, all fish in each tank were counted and collectively weighed to calculate growth parameters and survival. Five fish per tank (15 fish per dietary treatment) were randomly captured and anesthetized with tricainmethanesulfonate (MS222, Sigma, St. Louis, MO, USA) (100 mg L-1). Blood samples were then collected from the caudal vein using heparinized syringes. Plasma was then separated by centrifugation at 7,500 rpm at 4°C for 10 min and stored at -70°C to determine alkyl radical and superoxide radical-scavenging activities and blood biochemical parameters. After collecting blood, dorsal muscle and liver were sampled to determine the radical-scavenging activities, liver total protein (TP), catalase activity (CAT), total antioxidant capacity (TAC), and glutathione peroxidase activity (GPx), as mentioned above. In addition, another set of five fish per tank was sampled and stored at -25°C for muscle and liver proximate composition analyses.

      >  Proximate composition analysis

    Proximate composition of the diet, and dorsal muscle and liver samples were analyzed according to standard methods (AOAC 1995). Crude protein content was determined by the Kjeldahl method using the Kjeldahl System (Buchi, Flawil, Switzerland). Crude lipid content was analyzed by ether extraction in a Soxhlet extractor (SER 148, VELP Scientifica, Milano, Italy). Moisture was determined by oven-drying at 105°C for 6 h, and ash content was determined after combustion at 550°C for 4 h in a muffle furnace. The amino acid composition of the major ingredients and experimental diets was determined using an automated amino acid analyzer (Hitachi, Tokyo, Japan) following acid hydrolysis with 6 N HCl (reflux for 23 h at 110°C).

      >  Blood biochemical parameters

    Plasma total protein, glucose, glutamate oxaloacetate transaminase (GOT), glutamate pyruvate transaminase (GPT), and total cholesterol concentrations were determined using a commercial clinical investigation kit (Asan Pharmaceutical Co., Seoul, Korea).

      >  Antioxidant enzyme activities

    Liver CAT and TAC activities were analyzed using commercially available kits (Bioassay Systems Hayward, CA, USA) following the manufacturer’s instructions.

    GPx activity was assayed using a commercial kit (Bioassay Systems Hayward, CA, USA). In this assay, cumenehydroperoxide was used as a peroxide substrate (ROOH), and glutathione reductase (GSSG-R) and NADPH (β-nicotinamide adenine dinucleotide phosphate, reduced) were included in the reaction mixture. The change in absorbance at 340 nm due to NADPH oxidation was monitored to assess GPx activity. Briefly, 50 μL of plasma were added to 40 μL of the reaction mixture and incubated for 15 min; 10 μL of cumenehydroperoxide were then added and the OD1 was read at 340 nm. After 5 min of incubation, the OD2 at 340 nm was read using an enzyme-linked immunosorbent assay (ELISA) reader (Mannedorf, Zurich, Switzerland). GPx activity was calculated as U/L.

      >  Radical-scavenging activity

    Dorsal muscle and liver samples were homogenized (Wiggenhauser, Berlin, Germany) with extract buffer in 5 mM Tris-HCl and 35 mM glycine (pH 8.4) followed by centrifugation at 13,000 g for 10 min at 4°C. The supernatant was then used to determine radical-scavenging activity.

    Alkyl radicals were determined by the 2,2-azobiz-(2-amidinopropane)-hydrochloride (AAPH) method. The phosphate-buffered saline (pH 7.4) reaction mixtures included 10 mmol/L AAPH, 10 mmol/L 4-POBN, and known concentrations of sample (100 μg/mL), which were incubated at 37°C in a water bath for 30 min (Hiramoto et al., 1993) and then transferred to a capillary tube. The spin adduct was recorded using a spectrometer (JEOL LTD., Tokyo, Japan). The measurement conditions were as follows: modulation frequency, 100 kHz; microwave power, 10 mW; microwave frequency, 9,441 MHz; magnetic field, 336.5 ± 5 mT; sweep time, 30 s. Alkyl radical-scavenging activity (RSA) was calculated using the following equation:

    RSA (%) = [(Acontrol– Asample) / Acontrol] × 100,

    where Asample is the relative peak height of radical sample signals and Acontrol is the relative peak height of radical control signals.

    Superoxide radicals were generated using an ultraviolet (UV)-irradiated riboflavin/EDTA system (Guo et al., 1999). The reaction mixture containing 0.3 mM riboflavin, 1.6 mM EDTA, 800 mM DMPO, and the indicated sample concentration was irradiated for 1 min under a UV lamp at 365 nm. The reaction mixture was then transferred to a 100 μL quartz capillary tube for measurement by ESR spectrometry. The experimental conditions were: magnetic field, 336.5 ± 5 mT; power, 10 mW; modulation frequency, 9.41 GHz; amplitude, 1 × 1,000; sweep time, 1 min. The superoxide radical-scavenging ability of each sample was calculated as follows:

    Superoxide radical scavenging activity (%) = (1-A/A0) × 100,

    where A and A0 are the relative peak heights of radical signals with and without sample, respectively.

      >  Statistical analysis

    Data were subjected to one-way analysis of variance (ANOVA) and if significant (P < 0.05) differences were found, Duncan’s multiple range test (Duncan, 1955) was used to rank the groups. All statistical analyses were carried out using SPSS version 19 (SPSS, Michigan Avenue, Chicago, Illinois, USA). Data are presented as the means ± standard deviation (SD). Percentage data were arcsine-transformed prior to statistical analysis.


    Growth performance and feed utilization of olive flounder fed the experimental diets are shown in Table 3. The results showed significant (P < 0.05) improvement of growth performance in fish fed CG5 diet compared to those fed the control diet. Also, the fish given CG10 diet exhibited a comparable growth to that of control group but further increase of dietary inclusion level of CG to 15% resulted in significant decrease of weight gain and specific growth rate. No significant differences were found in feed efficiency and protein efficiency ratio among groups fed Con, CG5 and CG10 diets but the fish fed CG15 diet had significantly lower feed utilization than other treatments. Fish survival rate varied from 98 to 100% and no significant changes were found among dietary treatments.

    Dorsal muscle and liver compositions were significantly influenced by dietary CG (Table 4). Significantly lower muscle protein content was found in fish fed CG15 diet compared the other dietary treatments. However, muscle lipid, moisture and ash contents did not significantly differ among treatments. Also, the results showed significant increase of liver moisture content in all CG fed fish compared to the control.

    Results of biochemical analysis of blood showed the significant decrease of plasma total cholesterol concentration in fish fed CG15 diet in comparison to control group (Table 5). However, plasma total protein, glucose, GOT and GPT concentrations were not significantly influenced by dietary CG.

    Radical scavenging activity of plasma, dorsal muscle and liver is provided in Table 6. The results showed that inclusion of CG in diets for olive flounder has no significant effects on alkyl and superoxide radicals scavenging activity. Also, no significant changes were found in liver total protein content, TAC or CAT and GPx activities among dietary treatments (Table 7).


    In the present study significant enhancement in growth performance of olive flounder was observed by dietary inclusion of 5% CG. It has been reported that dietary supplementation of polyphenol-rich plant products improves growth performance by influencing the gut microbiota (Fiesel et al., 2014). Dueñas et al. (2015) suggested that dietary polyphenols exert prebiotic-like effects by stimulating the growth of beneficial bacteria (i.e., lactobacilli and bifidobacteria) and inhibiting the pathogenic bacteria. The findings of this study indicate that up to 10% CG can be included in the diet of olive flounder without adverse effects on growth performance and feed utilization. To the best of our knowledge, no study on the utilization of CG in fish feed has been reported. However, several studies have examined other coffee byproducts (e.g., coffee pulp) as feedstuff for cultured fish. Rojas and Verreth (2003) evaluated the effects of graded levels of coffee pulp as a dietary ingredient on the growth performance of Oreochromis aureus and their results showed that up to 13% coffee pulp can be included in the diet without negative effects on growth performance. Also, Moreau et al. (2003) tested fresh and ensiled coffee pulp as dietary protein and energy sources in the diet of Nile tilapia Oreochromis niloticus. However, these two forms of coffee pulp exerted detrimental effects on growth performance and pointed out that these byproducts cannot be considered suitable feedstuffs for Nile tilapia. Few studies on the use of CG as a feed component in terrestrial animals have been conducted (Claude, 1979; Givens and Barber, 1986). Bartley et al. (1978) included 5 and 10% CG in rations for Holstein cows and their results showed that 5% CG had no detrimental effects on growth performance, while higher CG levels resulted in reduced growth. In the present study, a further increase in CG inclusion from 10 to 15% resulted in a significant decrease in growth performance. This is in agreement with previous reports of retarded growth due to the addition of coffee byproducts at greater-than-threshold levels (Rojas, 2002; Rojas and Verreth, 2003). Impaired growth performance in fish fed the CG15 diet was due mainly to inferior diet utilization, as FE and PER were significantly lower compared to the control group. Similarly decreased growth performance, feed and protein utilization resulted from inclusion of coffee pulp in the diet of tilapia, which were attributed to the high levels of dietary fiber and anti-nutritional factors in coffee pulp (Rojas, 2002; Rojas and Verreth, 2003; Workagegn et al., 2014). It has been reported that the utility of coffee byproducts as animal feed is limited by the presence of antiphysiological and antinutritional factors such as caffeine, tannins and fiber (Didana, 2014). The antinutritional effects of tannins are associated with their ability to combine with dietary protein, cellulose, hemicellulose, pectin, and minerals, retarding their digestion and utilization (McSeweeney et al., 2001). Moreover, it has been suggested that the high lignin content (~25%) of CG limits their utilization in animal feed (Cruz, 1983).

    In the present study, whole-body protein content was significantly reduced in fish fed the CG15 diet. This is in correspondence with the results obtained for PER. Indeed, the use of coffee byproducts in animal feed has been reported to interfere with nutrient availability and absorption in the gastrointestinal tract (Cabezas et al., 1987; Aregheore, 1998; Rathinavelu and Graziosi, 2005). As mentioned above, coffee byproducts contain high levels of tannins, which affect feed digestibility and nitrogen utilization in animals (Marcel et al., 2011). Tannins have been reported to reduce protein digestibility and assimilation either through interaction with dietary protein or through inhibition of digestive proteases (Reed, 1995; Bravo, 1998). Furthermore, evidence suggests that nitrogen availability can be affected by the formation of protein complexes by tannins.

    In this study dietary inclusion of CG resulted in a reduction in plasma cholesterol concentration and a significant difference was observed between groups fed the control and CG15 diets. It has been shown that some dietary polyphenols, such as coffee polyphenols exert hypocholesterolemic effects. Meguro et al. (2013) reported that the addition of coffee polyphenols to a high-cholesterol diet for zebrafish Danio rerio significantly suppressed the increase in plasma and liver cholesterol levels. The authors suggested that downregulation of cholesterol and lipoprotein synthesis and upregulation of bile acid synthesis in the liver may be the fundamental underlying mechanisms by which coffee polyphenols exert their hypocholesterolemic effects.

    Antioxidant enzymes include superoxide dismutase (SOD), CAT and GPx, and constitute the first line of antioxidant enzymatic defense. SOD catalyzes the dismutation of superoxide radicals to hydrogen peroxide and oxygen, and CAT catalyzes the breakdown of hydrogen peroxide to water and molecular oxygen. GPX, a selenium-dependent enzyme, decomposes peroxides using the peptide glutathione as a co-substrate (Halliwell, 2006). Caffeine, chlorogenic acid (CGA), cafestol, trigonelline, and kahweol, all found in coffee, are believed to have significant potential as antioxidants and free radical scavengers. The roasting process influences the antioxidant properties of coffee as total antioxidant activity decreases with increased roasting temperature and duration (del Castillo et al., 2005). Polyphenol levels are reduced by 10% and those of CGA from 15% to 5% in dark versus lighter roasts (Cammerer and Kroh, 2006). Two low-molecular-mass products, CGA and caffeine, remain in dark roasts and have a protective effect (Daglia et al., 2000). Many researchers believe that Maillard reaction products, which are also strong antioxidants, are formed during the roasting process (Nicoli et al., 1997; Del Castillo et al., 2002; Nebesny and Budryn, 2003). Yen et al. (2005) evaluated the antioxidant properties of roasted coffee residues and found them to have excellent potential for use as a natural antioxidant source. Accordingly, in the present study, the changes in antioxidant enzyme activities following CG administration were evaluated. However, we found no significant change in TAC, CAT, GPx activity, or radical-scavenging activity among the diets. Del Castillo et al. (2002) reported that the degree of roasting affects the decrease in the antioxidant activity of coffee, which is associated mainly with the degradation of CGA. The antioxidant activity of roasted coffee is dependent on the roasting temperature and duration as well as the roasting method used (Nebesny and Budryn, 2003). In addition, the concentrations of coffee constituent compounds, such as CGA and polyphenols, which contribute to its antioxidant activity, vary geographically (Mullen et al., 2013). Therefore, further studies are required to examine the antioxidant activity of CG in other fishes.

    In conclusion, the findings of this study indicate that CG can be used as a feedstuff to enhance the growth of olive flounder. However, CG at > 10% of the diet dry weight should not be used, as inclusion of higher levels resulted in negative effects on growth performance and feed utilization.

  • 1. 1995 Official Methods Analysis google
  • 2. Aregheore EM 1998 A review of implications of antiquality and toxic components in unconventional feedstuffs advocated for use in intensive animal production in Nigeria [Vet Hum Toxicol] Vol.40 P.35-39 google
  • 3. Bartley EE, Ibbetson RW, Chyba LJ, Dayton AD 1978 Coffee Grounds. II. Effects of Coffee Grounds on Performance of Milking Dairy Cows and Feedlot Cattle, and on Rumen Fermentation and Dry Matter Removal Rate [J Anim Sci] Vol.47 P.791-799 google
  • 4. Bravo L 1998 Polyphenols: chemistry, dietary sources, metabolism, and nutritional significance [Nutr Rev] Vol.56 P.317-333 google
  • 5. Cabezas MT, Flores A, Egana JI, Brahan JE, Bressani R 1987 Use of coffee pulp in ruminant feeding P.25-38 google
  • 6. Cammerer B, Kroh LW 2006 Antioxidant activity of coffee brews [Eur Food Res Technol] Vol.223 P.469-474 google doi
  • 7. Claude B 1979 Etude bibliographique: utilisation des sous-produits du cafe [Cafe Cacao The] Vol.23 P.146-152 google
  • 8. Craig S, Helfrich LA 2002 Understanding Fish Nutrition, Feeds and Feeding. Cooperative Extension Service, publication P.420-256 google
  • 9. Cruz GM 1983 Residuos de cultura e industria [Informe Agropecuario] Vol.9 P.32-37 google
  • 10. Daglia M, Papetti A, Gregotti C, Berte F, Gazzani G 2000 In vitro antioxidant and in vivo protective activities of green and roasted coffee [J Agric Food Chem] Vol.48 P.1449-1454 google doi
  • 11. del Castillo MD, Ames JM, Gordon MH 2002 Effect of roasting on the antioxidant activity of coffee brews [J Agric Food Chem] Vol.50 P.3698-3703 google doi
  • 12. del Castillo MD, Gordon MH, Ames JM 2005 Peroxyl radicalscavenging activity of coffee brews [Eur Food Res Technol] Vol.221 P.471-477 google doi
  • 13. Didanna HL 2014 A critical review on feed value of coffee waste for livestock feeding [World J Biol Biol Sci] Vol.2 P.72-86 google
  • 14. Duenas M, Munoz-Gonzalez I, Cueva C, Jimenez-Giron A, SanchezPatan F, Santos-Buelga C, Moreno-Arribas MV, Bartolome B 2015 Studies on Modulation of Gut Microbiota by Wine Polyphenols: From Isolated Cultures to Omic Approaches [Antioxidants] Vol.4 P.1-21 google doi
  • 15. Esquivel P, Jimenez VM 2012 Functional properties of coffee and coffee by-products [Food Res Int] Vol.46 P.488-495 google doi
  • 16. Fiesel A, Gessner DK, Most E, Eder K 2014 Effects of dietary polyphenol-rich plant products from grape or hop on pro-inflammatory gene expression in the intestine, nutrient digestibility and faecal microbiota of weaned pigs [BMC Vet Res] Vol.10 P.196 google doi
  • 17. Givens DI, Barber WP 1986 In vivo evaluation of spent coffee grounds as a ruminant feed [Agr Wastes] Vol.18 P.69-72 google doi
  • 18. Guo Q, Zhao B, Shen S, Hou J, Hu J, Xin W 1999 ESR study on the structure-antioxidant activity relationship of tea catechins and their epimers [Biochim Biophys Acta] Vol.1427 P.13-23 google doi
  • 19. Halliwell B 2006 Reactive Species and Antioxidants. Redox Biology Is a Fundamental Theme of Aerobic Life [Plant Physiol] Vol.141 P.312-322 google doi
  • 20. Heuze V, Tran G 2011 Coffee hulls, fruit pulp and byproducts. Feedipedia.org. A programme by INRA, CIRAD, AFZ and FAO google
  • 21. Hiramoto K, Johkoh H, Sako KI, Kikugawa K 1993 DNA breaking activity of the carbon-centered radical generated from 2,2′-azobis (2-amidinopropane) hydrochloride (AAPH) [Free Radic Res Commun] Vol.19 P.323-332 google doi
  • 22. Jamu DM, Ayinla OA 2003 Potential for the development of aquaculture in Africa [Worldfish Center Quarterly] Vol.26 P.9-13 google
  • 23. Marcel BKG, Andre KB, Viviane ZT, Seraphin KC 2011 Potential food waste and by-products of coffee in animal feed [Electron J Biol] Vol.7 P.74-80 google
  • 24. McSweeney CS, Palmer B, McNeill DM, Krause DO 2001 Microbial interaction with tannin: nutritional consequences for ruminants [Anim Feed Sci Tech] Vol.91 P.83-93 google doi
  • 25. Meguro S, Hasumura T, Hase T 2013 Coffee polyphenols exert hypocholesterolemic effects in zebrafish fed a high-cholesterol diet [Nutr Metabolism] Vol.10 P.61 google doi
  • 26. Moreau Y, Arredondo JL, Perraud-Gaime I, Roussos S 2003 Dietary utilisation of protein and energy from fresh and ensiled coffee pulp by the Nile tilapia, Oreochromis niloticus [Braz Arc Biol Technol] Vol.46 P.223-231 google
  • 27. Mullen W, Nemzer B, Stalmach A, Ali S, Combet E 2013 Polyphenolic and hydroxycinnamate contents of whole coffee fruits from China, India, and Mexico [J Agric Food Chem] Vol.61 P.5298-5309 google doi
  • 28. Myer RO, Brendemuhl JH, Johnson DD 1999 Evaluation of dehydrated restaurant food waste products as feedstuffs for finishing pigs [J Anim Sci] Vol.77 P.685-692 google
  • 29. Nebesny E, Budryn G 2003 Antioxidative activity of green and roasted coffee beans as influenced by convection and microwave roasting methods and content of certain compounds [Eur Food Res Technol] Vol.217 P.157-163 google doi
  • 30. Nicoli MC, Anese M, Manzocco L, Lerici CR 1997 Antioxidant properties of coffee brews in relation to the roasting degree [LWT-Food Sci Technol] Vol.30 P.292-297 google doi
  • 31. Oestreich-Janzen S, Mander L 2010 Chemistry of coffee. In: Comprehensive natural products II P.1085-1113 google
  • 32. Rathinavelu R, Graziosi G 2005 Potential alternative use of coffee wastes and by-products P.1-2 google
  • 33. Ravishankar A, Keshavanath P 1986 Growth response of Macrobrachium rosenbergii (de Man) fed on four pelleted feeds [Indian J Anim Sci] Vol.56 P.110-115 google
  • 34. Reed JD 1995 Nutritional toxicology of tannins and related polyphenols in forage legumes [J Anim Sci] Vol.73 P.1516-1528 google
  • 35. Rojas JBU 2002 Use of coffee pulp as feed ingredient for tilapia culture, Thesis P.133 google
  • 36. Rojas JBU, Verreth JAJ 2003 Growth of Oreochromis aureus fed with diets containing graded levels of coffee pulp and reared in two culture systems [Aquaculture] Vol.217 P.275-283 google doi
  • 37. Samuels WA, Fontenot JP, Allen VG, Abazinge MD 1991 Seafood processing wastes ensiled with straw: utilization and intake by sheep [J Anim Sci] Vol.69 P.4983-4992 google
  • 38. Shang YC 1992 The Role of Aquaculture in the World Fisheries [the World Fisheries Congress] P.30 google
  • 39. Subosa P 1992 Chicken manure, rice hulls, and sugar-mill wastes as potential organic fertilizers in shrimp (Penaeus monodom Fabricius) ponds [Aquaculture] Vol.102 P.95-103 google doi
  • 40. Tacon A 1993 Feed ingredients for warmwater fish: fish meal and other processed feedstuffs google
  • 41. Tacon A 1994 Feed ingredients for carnivorous fish species: alternatives to fish meal and other fishery resources google
  • 42. Westendorf ML, Dong ZC, Schoknecht PA 1998 Recycled cafeteria food waste as a feed for swine: nutrient content digestibility, growth, and meat quality [J Anim Sci] Vol.76 P.2976-2983 google
  • 43. Westendorf ML, Westendorf ML 2000 Food waste as animal feed: an introduction P.3-16, 69-90 google
  • 44. Wohlfarth G, Hulata G, Moriarty D, Pullin R 1987 Detritus and Microbiological Ecology in Aquaculture [ICLARM Conference Proceeding] Vol.14 P.353-367 google
  • 45. Workagegn KB, Ababboa ED, Yimer GT, Amare TA 2014 Growth Performance of the Nile Tilapia (Oreochromis niloticus L.) Fed Different Types of Diets Formulated from Varieties of Feed Ingredients google
  • 46. Yen WJ, Wang BS, Chang LW, Duh PD 2005 Antioxidant Properties of Roasted Coffee Residues [J Agric Food Chem] Vol.53 P.2658-2663 google doi
  • [Table 1.] Proximate composition and essential amino acid profile of the major dietary ingredients
    Proximate composition and essential amino acid profile of the major dietary ingredients
  • [Table 2.] Formulation, proximate composition and essential amino acid profile of the experimental diets
    Formulation, proximate composition and essential amino acid profile of the experimental diets
  • [Table 3.] Growth performance and feed utilization of olive flounder Paralichthys olivaceus (104 ± 0.7 g/fish) fed the experimental diets for 10 weeks
    Growth performance and feed utilization of olive flounder Paralichthys olivaceus (104 ± 0.7 g/fish) fed the experimental diets for 10 weeks
  • [Table 4.] Proximate composition of dorsal muscle and liver of olive flounder Paralichthys olivaceus fed the experimental diets for 10 weeks
    Proximate composition of dorsal muscle and liver of olive flounder Paralichthys olivaceus fed the experimental diets for 10 weeks
  • [Table 5.] Plasma biochemical parameters of olive flounder Paralichthys olivaceus fed the experimental diets for 10 weeks
    Plasma biochemical parameters of olive flounder Paralichthys olivaceus fed the experimental diets for 10 weeks
  • [Table 6.] Radical scavenging activity (%) of the muscle, plasma and liver in olive flounder Paralichthys olivaceus fed the experimental diets for 10 weeks
    Radical scavenging activity (%) of the muscle, plasma and liver in olive flounder Paralichthys olivaceus fed the experimental diets for 10 weeks
  • [Table 7.] Liver total protein (TP), catalase activity (CAT), total antioxidant capacity (TAC) and glutathione peroxidase activity (GPx) of olive flounder Paralichthys olivaceus fed the experimental diets for 10 weeks
    Liver total protein (TP), catalase activity (CAT), total antioxidant capacity (TAC) and glutathione peroxidase activity (GPx) of olive flounder Paralichthys olivaceus fed the experimental diets for 10 weeks