An Ecological and Economical Assessment of Integrated Amaranth ( Amaranthus hybridus ) and Nile Tilapia ( Oreochromis niloticus ) Farming in Dar es Salaam, Tanzania

: Organic wastes can be recycled in an ecologically sound way in ﬁshponds by applying integrated agriculture and aquaculture systems (IAA). This kind of waste recycling can help to protect the environment from pollution and improve ﬁshpond yields. Additionally, IAA provides an opportunity for diversiﬁcation of the output from two or more existing subsystems leading to higher overall farm economic returns. This study explored the potential application of amaranth wastes (AW) as a dietary ingredient for tilapia in a tilapia-amaranths integrated system (ITA). An experimental diet (AD) contained 10% (based on the control diet, CD) inclusion of AW collected from a nearby vegetable market. The experiments included triplicate treatments with; (i) ﬁsh fed on AD, where the pond water was used for irrigating the amaranth plants (IAA-ﬁsh), and (ii) ﬁsh fed on CD, where no pond water was used for irrigating the amaranth plants (non-IAA ﬁsh). 90 days after ﬁsh stocking, eighteen 4 m 2 amaranth plots were prepared and treated with (i) tap water without fertilization (control amaranths), (ii) water from IAA-ﬁsh pond and organically fertilized (IAA amaranths), and (iii) tap water and inorganically fertilized (non-IAA amaranths). The use of AW improved the ﬁsh feed conversion ratio. The overall net income from ITA was 3.2, 2.3, 2.6, and 1.8 higher than from non-IAA amaranths, IAA-amaranths, non-IAA ﬁsh, and IAA ﬁsh sub-systems respectively. ﬁnished, three quarters of the water volume in each tank were replaced once a month. Irrigation (5 liters per 1 m 2 ) was done once a day during the evening. Water from the three IAA ponds was blended and randomly irrigated to the IAA amaranth plots. Pond water for irrigation was compensated by adding tap water to maintain the pond water level for both treatments. Eighteen amaranths ( Amaranthus hybridus ) plots of 2 × 2 m were prepared nearby the IAA ponds. The experiment involved three treatments in six replicates.


Introduction
The urgent need for increasing protein production per unit area of farmed land is a priority worldwide [1]. Capture fisheries have been one of the major animal protein sources for many people in East Africa [2]. However, with the current declining wild fish yields and growing population, fish protein is increasingly becoming scarcer. Recent studies suggest that almost half of the African fish stocks are overexploited or fully exploited [3]. Hence, despite the dominance of capture fisheries in total fish production in the continent, the promise of aquaculture as the new frontier in fish production holds strong. About one-sixth of the total production of food fish in Africa in 2016 came from aquaculture [4]. The fish supply deficit in most African countries presents significant prospects for aquaculture development [5].
However, in order for aquaculture to fill this gap, a number of challenges, varying from one place to another, need to be addressed [4,6,7]. In Sub Saharan Africa (SSA) for example, insufficient availability DM stands for dry matter, CP for crude protein, CL for crude lipid and CF for crude fibre. Table 2. Composition of the fish control diet (CD) and the diet with AW inclusion (AD) and the total cost to produce 1 kg of each feed.

Fish Growth Performance, Survival, Feed Utilization and Yield
Fish growth was not affected by the inclusion of AW in the fish diet (Table 4). There were no significant differences (p > 0.05) in terms of final weight, daily weight gain, specific growth rate, yield, condition factor and survival rate. Overall, there were no statistically significant differences in the growth between fish given the control and amaranth diets, although there appeared to be slight growth variation in the first 90 days (Figure 1). The feed conversion ratio was significantly lower in fish fed AD than in fish fed CD (p < 0.05). A similar trend was observed in terms of protein efficiency ratio (PER), where a PER value of 2.07 exhibited by the fish fed AD was 13% higher than 1.84 for the fish fed CD (p < 0.05).

Effect of Integrating Amaranth with Tilapia Farming
IAA amaranth plots had about 46% higher yield than non-IAA amaranth plots for the first harvest (p < 0.05), and comparable (p > 0.05) yields for the second harvest and for the overall farming cycle ( Figure 2). The control group had significantly lower yields than the IAA and non-IAA groups. A similar trend was observed in terms of growth performance for the final harvest ( Figure 3).

Economic Analysis of the Farming Systems
The economic performances of fish and amaranth grown separately and integrated, are presented in Figures 4-6. IAA fish had significantly (p < 0.05) lower feed cost and total cost, and higher benefit cost ratio (BCR) with 1.28 times higher total net income than non-IAA fish. IAA amaranth had 1.12 and 1.34 times higher revenue and net profit, respectively, than the non-IAA amaranths with comparable BCR. The integration of fish and amaranths resulted in 4.4, 3.9, 1.27 and 1.30 times higher (p < 0.05) total revenue than non-IAA amaranths, IAA amaranths, non-IAA fish and IAA fish, respectively. Similarly, the net return for fish-amaranth integration was 3.2, 2.3, 2.6, and 1.8 times higher than (p < 0.05) non-IAA amaranths, IAA amaranths, non-IAA, and IAA fish, respectively.

Effects of IAA Farming on Water and Soil
Dissolved oxygen, water temperature and pH in the fishponds did not vary significantly between IAA and non-IAA fishponds ( Table 5). The two IAA and non-IAA treatments had similar concentration of nitrogen and phosphate in the water but had significantly (p < 0.05) higher nutrient levels in the soil than the areas irrigated with tap water (control treatment) ( Table 6). No NO 2 or NH 4 were detected in the tap water ( Table 6). The IAA and non-IAA fishpond water had about 3.5, 2.4, and 7.8 times higher TN, PO 4 , and TP concentrations, respectively, than the tap water (Table 6). Similarly, in the soil samples, IAA and non-IAA amaranth plots had statistically higher nutrient concentrations at the end of the experiment compared to concentrations at the beginning of the experiment and compared to the control soil samples, except for TN, which varied significantly among treatments (Table 6).

Discussion
In this study, the effects of utilizing amaranth vegetable wastes in fish feed, and fishpond water for irrigating amaranth plots, on growth, yield and economic benefits were explored. The results demonstrate that the inclusion of AW in the fish feed does not compromise, but rather improves the feed utilization efficiency by the fish. Similar results were reported in Kenya when replacing fish meal with concentrates of amaranth in fish feeds for tilapia [35]. Feed conversion ratio (FCR) is an important proxy of the feed utilization efficiency [36]. The superior FCR for fish grown in IAA ponds compared with fish grown in non-IAA ponds in the present study, could be due to the fact that the inclusion of amaranth reduced the amount of rice brans (having high ash and fiber content) in the feed by 12%, thus improving the feed digestibility [37].
The crude protein level (47.4%) of freshwater shrimp in this study was lower than that (60%) reported by Litti et al. [38], but within the range (45-64%) reported by Munguti et al. [39]. The variation in crude protein levels could be related to prior handling processes by local suppliers, which involves recovery from the wild, drying, transportation and storage.
Despite a lower feed intake by the fish fed the AD diet, the overall growth was similar to the fish fed the control diet (CD). The lower feed intake corresponds to a relatively lower growth of fish in the first 100 days, when AD was fed to fish in the IAA regime. This is seen in the growth curve ( Figure 1), which indicates that, on the 90th day when the last measurement was taken before shifting from the AD to the CD diet, fish fed the CD diet had about 24% higher growth than fish fed the AD diet. The reduced feed intake in fish fed the AD diet could be related to the pungent smell from amaranth inclusion that might have affected the feed flavor, and also a slightly lower survival rate compared to the fish fed the CD diet. However, all these factors did not significantly affect the overall fish growth and pond yield at harvest.
The yields of 17,720 kg fish/ha and 16,914 kg fish/ha for non-IAA and IAA ponds, respectively, were similar to that reported by Toma et al. [40] in Bangladesh, but were about three times higher than the yield reported by Chenyambuga et al. [41] in Mbarali and Mvomero in Tanzania. This difference could be because the present study involved the use of improved mono-sex tilapia strains with higher stocking density (8 fish/m 2 ), as opposed to the use of mixed sex tilapia stocked at less than 4 fish/m 2 in the previous studies in Tanzania [13,42].
The positive effect of using pond water for amaranth irrigation was evident on the first amaranth harvest. IAA amaranth plots had 1.4 and 5.5 times higher yields than non-IAA and control plots respectively. This is due to the fact that pond water had higher nutrient concentration for promoting amaranth growth than the tap water. The increased yield for the non-IAA amaranths plots in the second harvest was probably due to the increase in the nitrogen supply from urea, which was provided as a booster fertilizer only in this treatment. Studies on higher plants, report an increased S:R ratio linked to an increased plant growth because of an increased nutrient supply, especially nitrogen [43,44]. This was also found in the present study, where IAA and non-IAA plots had significantly higher S:R ratio than the control plots. This may be attributed to a sufficient supply of nutrients for the IAA plots from the fish-pond water, and for the non-IAA plots from the chemical fertilizers.
The overall amaranth yields in this study were slightly higher than those reported from a study by Baitilwake et al. [45], who investigated the impact of different fertilization regimes on amaranth and spinach yield in Morogoro. The yields from the present study were also two times higher than those reported from a study by Mulandana et al. [46] in South Africa. The differences in amaranth yields observed between these studies could be related to differences in amaranth species used and also farming approaches between these studies. For example, in the present study, sowing was done by broadcasting, long cultivation cycle, and use of fishpond water for irrigation as opposed to transplant planting and non-integrated farming systems in previous studies.
Additionally, while it is recognized that the use of chemical fertilizers can significantly increase crop yield, these fertilizers could have adverse environmental effects, such as changing the soil pH and nutrient enrichment, which can disturb the ecosystem. In this regard, amaranth farming based on organic manure and nutrients from fishponds is more sustainable, from an environmental point of view, compared to farming systems which rely completely on chemical fertilizers [47].
In the IAA and non-IAA fishponds, no statistical differences were observed in the water temperature, DO, pH and nutrient concentrations, which were expected as the ponds were managed in the same way, except from a slightly different composition in the feed fed to the fish. Thus, the different FCR and PER were most likely related to the different feed compositions, while the slightly higher yield of the non-IAA fish was primarily related to a slightly higher survival rate. Although the nutrient concentration in the soil samples for IAA and non-IAA plots did not show any marked variation, there seemed to be a slightly higher accumulation of nutrients and especially nitrogen in the soil fertilized with fish-pond water. The slightly higher nutrient concentrations in the IAA plots could indicate that nutrients in the pond water sufficiently replaced the urea fertilizer. This could also be an explanation for the slightly higher amaranth yield in the IAA plots than in the non-IAA plots.
The significantly lower total cost and higher BCR obtained in the IAA fishponds show that the incorporation of AW in the tilapia feed improved the financial efficiency of the system. The incorporation of AW (considered to be of zero cost) as one of the ingredients in the fish feed lowered the feed cost from 0.51 to 0.45 US $/kg, which corresponds to a 12% decreased feed cost. Similar results were reported by Poot-López et al. [30], when tree spinach was used as a dietary ingredient for tilapia culture in an IAA system. Other examples of studies involving use of vegetables as fish feed, with similar results, include Mathia and Fotter [48] and Swain et al. [49]. The IAA and non-IAA plots had comparable revenues and net returns, despite that no chemical fertilizers were applied to the IAA plots. This implies that, the use of pond water (regarded as of zero cost) sufficiently covered for chemical fertilizer, which were applied in the non-IAA plots.
The integration of tilapia farming and amaranth cropping resulted in significantly higher net returns than when these subsystems were analyzed separately. Similar results were reported from previous studies by other researchers in Tanzania and some other parts of Africa. Limbu et al. [12], for example, reported a higher annual net cash flow from integrated tilapia-catfish-spinach farming, than when fish and vegetables were farmed separately. Similarly, a study by Dey et al. [18] in Malawi reported a 11% higher production from IAA farmers than non-IAA farmers. These findings are also corroborated by those by Shoko et al. [13], who reported that the highest economic returns could be attained from fish farming when integrated with agriculture. This may be explained by the fact that integrated agriculture and aquaculture systems build on an increased recycling of nutrients and matter, and provide room for diversification of the outputs from existing sub-systems leading to an overall higher farm yield and income [14,50].
In addition to increasing the overall farm yield and economic benefits, IAA technology could play an important role in improving household food security and providing diversified livelihoods in Tanzania. For a farmer applying an integrated tilapia-amaranth system, tilapia can become an important source of animal protein and high quality essential fatty acids, particularly long-chain polyunsaturated fatty acids (LCPUFA) and micronutrients, that are in higher quantities in fish than terrestrial based animal food sources [51]. Amaranth also contains essential metabolites such as minerals, vitamins (especially A and C), coloring, aromatic and thickening agents, that are essential for human growth and wellbeing. Hence, well designed integrated systems could provide diversified nutritional crops, which could help in the fight against "hidden hunger," a term that describes people who do not get enough vitamins, proteins, minerals, zinc, and iron [52].
The growing human population and accelerating urbanization has led to an increased food demand but also increased amounts of agricultural wastes [53]. These wastes are usually seen as a problem impacting on both human health and the environment, but could also, if properly processed, be used as feed input in animal and fish production, and thus improve food security among small scale farmers [54]. Systems that rely on recycled agricultural by-products and simple technology have been able to double production of small farms, and although this has been done from a very low base, it has had substantial impact on rural food security [10]. Water storage in fishponds can also play a critical role for farmers who are exposed to increased frequency of droughts following from climate change [13]. It is believed that the results from this study shows that a diversified production through integrated agriculture-aquaculture can improve the ecological sustainability and economic durability of farming in Tanzania.

Study Design
Briefly, our study involved three stages as follows: (1) A fish feed experiment, where the fish were fed either the control diet (CD) through-out the experiment (183 days) or the amaranth diet (AD) for the first 100 days and then the control diet (CD) for the remaining 83 days; (2) An amaranth fertilization experiment (90 days after fish stocking), where amaranth plots were irrigated with either tap water or pond water from fish fed the amaranth diet, and treated with various fertilizers; (3) Analysis of growth performance, yield and economic benefits of pond and amaranth farming when practiced as an integrated system or as separate activities (Figure 7).

Fish and Facilities
The study was conducted at the Tanzania Fisheries Research Institute (TAFIRI) Dar es Salaam center using six (7 m 2 with mean depth of 1 m) round concrete ponds for 183 days. The geographical location of the site is 6 • 39 51.57" S and 39 • 12 45.32" E, at an elevation of 10 m above sea level. The experiment was intentionally designed to reflect small scale fish famers in Dar es Salaam, who usually combine two or more ingredients as feed for the fish. Nile tilapia (Oreochromis niloticus) mono-sex fingerlings were obtained from a commercial local hatchery and stocked at 8 fish per m 2 .

Fish Feed Experiment
Amaranth wastes (AW), including both unsold and unused amaranth leaves, were collected from Tegeta vegetable market (about 3 km from the study site). AW was washed with tap water to remove sediments and then soaked in boiling water for 10 min to reduce the potential high contents of anti-nutritional factors, such as phytates, saponins and tannis [55]. AW was solar dried (under a shade) to a constant weight, powdered using a kitchen blender, and then stored in a refrigerator until use. The AW powder was used as an ingredient in fish diet at 10% inclusion for the experimental diet [31,56]. Other ingredients (shrimp meal, soybean, and rice bran) were grounded separately, using a hammer mill at a milling factory in Dar es Salaam. The resulting mash was weighed and mixed accordingly. The resulting composition was blended using warm water to form a dough and subsequently extruded into pellets using a meat mincer. The extruded pellets were solar dried under a shade until complete dryness for about three days, and then stored in a cold dry room until it was used. The pelleted sinking diets were hand-fed to fish by dispensing it at the surface of each pond.
The compositions of the control (CD) and experimental (AD) diets are shown in Tables 1 and 2. The two diets were formulated targeting a 30% protein inclusion. Fish were fed at 5% of their body weight divided in two portions per day, one given in the morning (around 9.00 am) and one given in the evening (around 4.00 pm). The feeding rate was reduced to 3% when the average weight of the fish reached over 120 g. Two treatments in triplicates were applied as follows; (i) fish fed control feed (CD) without inclusion of the AW, hereafter referred to as non-integrated fish ponds (non-IAA fish) and (ii) fish fed AD diet, hereafter referred to as integrated fish ponds (IAA fish), as the pond water was also used to irrigate the amaranth plots. Fish in the IAA ponds were fed with experimental diet for the first 100 days and then shifted to the control feed (CD) for the remaining 83 days until the end of the experiment. This is because AW is only readily available during the dry season (July-October), which is the peak for amaranth production in Dar es Salaam.

Amaranth Irrigation and Fertilization Experiment
Amaranth farming was done during the dry season, three months after stocking of the fish, to allow nutrients to accumulate in the pond water and also to avoid the influence from rainfall on the amaranth growth. During this period, no water was exchanged in the fishponds, and water was only added to compensate for the loss of water through evaporation. After the amaranth culturing had finished, three quarters of the water volume in each tank were replaced once a month. Irrigation (5 liters per 1 m 2 ) was done once a day during the evening. Water from the three IAA ponds was blended and randomly irrigated to the IAA amaranth plots. Pond water for irrigation was compensated by adding tap water to maintain the pond water level for both treatments. Eighteen amaranths (Amaranthus hybridus) plots of 2 × 2 m were prepared nearby the IAA ponds. The experiment involved three treatments in six replicates.
Treatments were applied as follows: (i) amaranth plots irrigated with tap water without fertilization, hereafter referred to as control amaranths, (ii) amaranth plots irrigated with water from the IAA fish ponds above, and with only organic fertilizer applied, hereafter referred to as integrated amaranth (IAA amaranth) and (iii) amaranth plots irrigated with tap water, and fertilized with a combination of organic and chemical fertilizers (a practice commonly used by farmers in Dar es Salaam), hereafter referred to as non-integrated amaranth (non-IAA amaranth).
Before sowing, both IAA and non-IAA amaranth plots were fertilized with broiler manure at a rate of 10 Kg per m 2 . Manure applications were done a week before to allow for proper mineralization [57]. Sowing was done by mixing 10 g of amaranth seeds with 1 kg of sand to obtain uniform stands, and then broadcasted at a rate of 1 g of seeds per m 2 [45,58]. The first harvest was done 21 days after sowing, to remove mature leaves for sale and give space for young plants to grow to maturity. After the first harvest, urea (a booster fertilizer) was applied at a rate 1 g per m 2 on the non-IAA amaranth plants. No additional chemical fertilizer was applied on the IAA amaranth plants, which only were irrigated with the water from the IAA fishpond until the final harvest, which was done after 33 days.

Chemical Analysis
The proximate analyses of the experimental feeds were done to determine the content of moisture, ash, crude protein, crude lipid, and crude fiber. Moisture content was obtained by oven drying of the fresh samples at 60 • C overnight [59]. The crude protein (N X625) was determined using a semi-micro Kjeldahl digestion followed by indophenol-blue colorimetric method [59,60]. The crude lipid was determined according to the procedures described by Bligh and Dyer [61]. The crude fiber was analyzed gravimetrically by acid hydrolysis followed by an alkali extraction method [59,62]. Briefly, 1 g of sample was weighed in in a Pyrex beaker and added in boiling sulfuric acid (1.25% v/v). The mixture was rinsed with boiling water to eliminate the acid and then added to 1.25% sodium hydroxide for extraction. The solution was separated from the fiber using a suction pump. The fiber was washed with hot water followed by oven drying at 105 • C for 3 h. The weight of fiber in the sample was then determined gravimetrically. The ash content was determined by incinerating the fresh samples in a muffle furnace at 550 • C for 2 h.
The concentrations of calcium and iron minerals in the AW were determined by the acid oxidation method according to Emteryd [60] and Girmshaw et al. [63]. This was done by dissolving 1 g of AW sample in a mixture of 1 mL perchloric acid (HClO 4 ) and 5 mL of nitric acid (HNO 3 ) in the ratio of 1:5. The mixture was digested at 120 • C until it became colorless and the volume was reduced to 1 mL. The concentrations of the individual minerals were determined using an atomic absorption spectrophotometer (AA240 Varian, USA).
The contents of Vitamins A and C in AW samples were determined according to the procedures described by Rutkowski and Grzegorczyk [64]. The concentrations were determined from a calibration curve prepared using a standard solution: hydrophilic complex of retinol acetate with cyclodextrane for vitamin A and L-ascorbic acid for Vitamin C. For the fish samples, the concentration of vitamins (B1, B2, B3 and B6) were determined by the procedures described by Rajput et al. [65]. In brief, the working solution for the standard vitamins and fish samples were prepared by dissolving a known weight of the standard vitamin in a known volume of diluent in a volumetric flask. Riboflavin, nicotinamide, pyridoxine hydrochloride, and cyanocobalamin were used as stock solutions. The absorbance of the stock solution, feed samples and the blank were then read at 430 nm for vitamin B1, 444 nm for vitamin B2, 450 nm for vitamin B3, and 650 nm for vitamin B6 using a UV-visible spectrophotometer (Jenway 6305).
Water samples from the fishponds and tap water were collected bimonthly. Soil samples were collected at the start and end of the experiment. Three soil samples in each plot were randomly collected to a depth of 20 cm. The three soil samples were then mixed to obtain homogenous samples, and stored in sealed plastic bags and sent to the laboratory. The samples were analysed for the concentration of total nitrogen (TN), total phosphorus (TP), nitrite (NO 2 ), nitrate (NO 3 ) and ammonia (NH 3 ) using standard methods [66,67]. Water quality parameters (pH, dissolved oxygen (DO) and temperature) was measured twice a day in the morning and evening around 9.00 am and 4.00 pm respectively. Water pH was measured using a pH meter (model Combo H198129), dissolved oxygen (DO) and temperature measurements were taken using a multiprobe kit (model Ecosense DO 200A China).

Calculation of Fish Growth Performance and Yield
For the fish, data was collected at a monthly interval until the end of experiment when the ponds were drained completely to assess the fish growth performance, yield and economic returns. Fish growth performance was calculated using the following formula: Average daily weight gain (g/fish) (ADG) where W1 = mean initial weight (g), W2 = mean final weight (g), and T = experimental period (days) Specific growth rate (SGR): where Ln = natural Logarithm, W1 = mean initial weight (g), and W2 = mean final weight (g) FCR = Dry feed intake (g) Live weight gain (g) where FCR = feed conversion ratio. PER = Live weight gain (g) Protein intake (g) where PER = protein efficiency ratio.
where: SR = survival rate, NH = number of fish harvested, NS = number of fish stocked.
where CF = condition factor, W = body weight, and L = total length.
where TW = total weight of the fish harvested, A = pond area.

Estimation of Amaranth Growth and Yield
For the amaranths, sampling was done 21 and 33 days after sowing (when marketable size had been achieved). In both cases sampling was carried out between 6 and 8 am in the morning. Sampling was done by harvesting an area of 30 × 30 cm in three different locations of a 4 m 2 plot in each of the three different treatments. The above ground biomass of each sample was cleaned using a wet towel before weighing to obtain the yield. Twenty individual amaranth plants from each treatment were randomly sampled to assess growth performance in terms of shoot-root relationship.

Economic Return
A partial enterprises budget was used to assess the financial performance of the different farming systems when farmed as standalone activities and when farmed in integration. The input costs included pond construction (based on estimates by AMISODAGO, a fish pond construction consultancy), fish fingerlings, fish feeds, amaranth seed, manure, equipment, labour, transport (based on prevailing market price in Dar es Salaam), and water (according to DAWASA, Dar es Salaam Water and Sewerage Authority).
Except for amaranth waste (AW), that was obtained free of charge from the vegetable market, other dry ingredients were purchased from local suppliers at a cost of (USD/Kg): 1.09, 0.43, 0.13 and 0.22 for shrimp meal (Cardina nilotica), soya bean, rice bran and binder (cassava flour) respectively. The value of the fish and amaranth harvests were estimated from the prevailing market prices at Kunduchi in Dar es Salaam (Table 7). A US dollar exchange rate (at 2300 Tsh, December 2018), was used for the budget analysis.
Net farm income was calculated as follows: where NR = net return, TR = total revenue, TC = total cost, BCR = benefit cost ratio, p = unit price of output, and Q = total quantity of output.

Statistical Analysis
Data was tested for normal distribution and homogeneity of variance using Shapiro-Wilk and Levene's tests respectively. When homogeneity of variances was confirmed, t test was used to test the differences between experimental and control diets. Analysis of variance (ANOVA) was used to test for significant differences in growth performance, yield, and economic returns between IAA and non-IAA farming systems. When significant differences were detected, the Tukey post-hoc test was used to determine specific significant differences among farming systems. Statistical analysis was performed using excel 2016 and SPSS version 20.

Conclusions
In conclusion, the results of the present study suggest that amaranth wastes, which are in surplus during the dry season in Dar es salaam, can be used as a tilapia feed ingredient without comprising the fish growth. Compared to other ingredients, amaranths contain high quantities of protein, lipid, mineral, and vitamin with higher nutrient values than found in for example rice bran. These properties may have improved the feed utilization and the nutritional value of the cultured fish. Further, our study demonstrates that fish farmers can replace chemical fertilizer with nutrient rich pond water without affecting amaranth growth and yield. Our results also show that the integration of amaranth with tilapia is significantly more beneficial than when these subsystems are operated separately. With these findings, we suggest further studies using fresh vegetables as feed in fish farming, a practice commonly done by a number of rural fish farmers, but lacking scientific studies showing its implication on fish farming in Tanzania. We encourage farmers in Dar es Salaam to integrate fish and vegetable farming as a way to improve their farm productivity, household nutrition and income.