Cameroon is drained by four watersheds namely the Sanaga, Congo, Niger and Chad. The Nile Tilapia is naturally widespread in the watersheds of the Benue (Niger) and Lake Chad 9. Today it is present in all the Cameroonian water where it breeds naturally 10. In terms of importance, when collecting fish in the wild by producers and logistics, fish were collected in the basins of Niger (precisely at the Lagdo dam) and the Sanaga (at the Mape dam). In addition, the domestic population of the pilot IRAD station of Foumban formerly imported from RCA 11 was used.

The study took place from 20 March to 05 May 2019 at the IRAD’s farm of Foumban, more precisely at the fish station of Koupa-Matapit (LN: 5º 21' to 5 ° 58 'and LE: 10º 17' to 11º 02 '). The average altitude is 1145 m. The climate is Sudano-Guinean and includes one rainy season (March - October) and one dry season (November - February). The annual average temperature and rainfall are 22ºC and 1800mm respectively.

Eighty-one (81) spawners including 54 females (average weight 124 ± 6g) and 27 males (average weight 144 ± 5g) have been used. Thus 18 females and 9 males of each Hydrogeographic origin were randomly distributed in three concrete tanks (length 1.5 m, width 0.7 m, height 0.8 m)equipped with a system to bring and overflow and fully drainable by gravity. The completely randomized design with 3 treatments ("Sanaga" = fish population of Sanaga, "Niger" = population of Niger, and "Koupa" = population of IRAD station of Foumban) and 3 repetitions was used. Thus, 54 females and 27 males were divided into triplicate randomly into 3 lots and within 9 tanks.

The implementation of the trial began 07 May 2019 by cleaning the tanks and putting them in Assec (let dry on the sun) for seven days. After this period, the impoundment (put in water) has been made in order to obtain a water depth of 60 cm. Three days later, the fish were randomly distributed at a density of 9 individuals / m² and a sex ratio of 1 male for 2 females. When putting the fishes into tanks, a sample of 10% of the total fishes was weighed and measured individually, using respectively an electronic balance (reference: BF-400, accuracy 0.1g) and an ichtyometer (1 mm accuracy).

During the test, all treatments received 20% protein feed twice per day, consisting in fishmeal, soybean meal, yellow corn meal, blood meal, palm oil and vitamin premix prepared at the IRAD station as described by 12. The ratio of 5% of the biomass as was applied during the experiment for feeding as in 13.The physico-chemical parameters of water such as dissolved oxygen, pH and temperature were measured directly "in situ" weekly. The females were monitored daily to identify those carrying eggs in their oral cavities (enlargement of the oral cavity, aggressiveness, continuous circular movement). Six females per population were collected throughout the trial in post-laying phase. After collecting the eggs, the females were carefully returned to the water and all the eggs present in the oral cavity were counted to determine the absolute fertility.

Forty-five days after the implementation of the test, the tanks were drained, adults and juveniles collected and counted. In order to evaluate the gonado-somatic and the gonado-metric parameters at the end of reproduction, all spawners were weighed and eviscerated. The gonads were removed and weighed, as well as the eviscerated fishes.

At the end of this test some characteristics were determined or calculated. The total or absolute productivity is the average number of offspring (fry, alevins and eggs) produced per female. The relative productivity is the number of offspring produced per g of females stored. The productivity of the system is the average daily production of offspring per m² of the operated area. Absolute fecundity is determined by counting the total number of newly recovered egg of the oral cavity of the female. Gonado-Somatic Ratio (GSR) and gonado-Somatic Index (GSI) correspond respectively to the gonad weight (GW) in percentage of the body weight (BW) (GSR = GW / BW * 100) and the eviscerated fish weight (EW) (GSI = GW / EW * 100). The formula used to calculate the Gonado-metric Ratio (GMR) and gonado-metric Index (GMI) was respectively GMR = GW / TL * 100 and GMI = GW / SL * 100. Where GW = gonad weight (g); BW = body weight; EW = eviscerated fish weight (g); TL = fish's total length (cm) and SL = fish's standard length (cm).

The data were submitted to the one-way analysis of variance (ANOVA 1). When the effect of the waterway of origin was significant, the Duncan test was used to separate the means clustering at 5% threshold. The F test was used to determine the significance of the effect of sex and means clustering were compared pairwise using the t test of Student. All analyzes were performed using the SPSS software version 21. 0.

The gonado-somatic ratio, the gonado-somatic index, the gonado-metric ratio and the gonado-metric index of the fish population of the Koupa research station are significantly lower (P ≤ 0.05) than those of the Niger and Sanaga watersheds and whose values were comparable (P ≥ 0.05) between these two populations. Considering the sex and regardless of the characteristic considered, the males presented the lowest significant values (P ≤ 0.05). (Table 1)

From Table 2, we can see that, regardless of the considered characteristic, the highest significant values (P ≤ 0.05) ​​were obtained in the population of the fish hatchery IRAD of Koupa and the lowest in the population of the Sanaga watershed.

It appears in Table 3 that no negative correlation coefficient has been significant. Moreover, values ​​of the affected coefficients vary from strong (p ≤ 0.05, r = 0.832) to very strong (p ˂ 0.01, r = 0.999), correlation coefficients higher significant were obtained between productivity per g of female and system productivity (p ˂ 0.01, r = 0.998) between the productivity per g of total production and female (p ˂ 0.01, r = 0.999) and between the system productivity and total production (p ˂ 0.01, r = 0.998).

The gonado-somatic and gonado-metric characteristics are generally higher in females than in males. This corroborates the results obtained by 14. These features may vary depending on the species, age, type of food, sex and origin of populations. 15 observed that the GSR and GSI end of females and males (2.57% to 3.22% against 64% to 0.81%) were unaffected by the type of food. However, 16 comparing three natural populations of Oreochromis niloticus in southern Benin indicated that only gonadosomatic index of females varied depending on the origin of population and for all those gonad index parameters, the higher values were obtained in female corroborating our findings that our values ​​were lower than those obtained by the author. This could be explained by the low temperature of our study area (22°C).

In our experience the absolute fecundity and relative fecundity varied significantly between different populations. This is contrary to the results obtained by 1718 that studied reproductive performances strains of Oreochromis niloticusfrom Egypt, Ghana and Ivory Coast and found no significant difference in the relative fecundity, egg size, hatching rate and length of larvae, 24 hours after hatching. On the other hand, great variability in fertility in female Oreochromis niloticussame size, was reported by 1920 as is the case in Tilapia zillii2122. This is attributed to a genetic difference 2322 and a possible complex interaction of fertility, egg size and timing of egg laying 22.

Our values ​​for the absolute fertility (452 ​​± 39.90 to 43.43 ± 604 eggs per female) are low compared to those reported by 2324 and 19, which are 728-1774 respectively, from 600 to 1600 and from 724 to 1669 for the same size range. Our results are in the range (309-1158 eggs per female) reported by 20 and (241-1358 eggs per female) obtained by 25 although the highest number of eggs is far superior to that of our experiment. Our low values ​​can be explained by the large size of our begetters because according to 26 fertility of small females (58g) is bigger than that of large ones (185g).

Comparison of reproductive performances of Oreochromis niloticus populations are poorly documented in contrast to studies on systems of production or breeding techniques 16. However 27 evaluated the reproduction and growth characteristics of a domestic stock of Oreochromis niloticus (from the Ivory Coast), two non-domestic stocks (from Egypt and Sagana) and wild individuals (from Lake Victoria). The combined effects on the relative fertility, the percentage of female spawning and the success of incubation were evaluated, and it is clear from this study that the strain of the Ivory Coast has a larvae yield per gram of female eight times higher than that of Lake Victoria. This study corroborates the results we obtained since the various productivities (the total productivity, relative, system and productivity per female) Oreochromis niloticus varied depending on the origin of population. On the other hand, this is inconsistent with the observations of 1718 that by studying the reproductive performances of Oreochromis niloticus stem from Egypt, Ghana and Ivory Coast have found no significant difference between the performances considered. The values ​​of the relative productivity (larvae per g female) obtained in this experiment are greater than 1.4 ± 0.3 larvae per g female obtained by 25 with large females (25 cm total length). Low productivity could be explained by the large size of fish used in this test since according to this author, the relative productivity accuses significantly decreasing values ​​depending on the size of females. Hence the values ​​of 9.3 ± 0.7 and 6.8 ± 0.3 1.4 ± 0,2b obtained by the author with females respectively of 15.34 ± 0.25 cm and 20 54 ± 0.32 cm in total length. Moreover, this low productivity is also due to the low participation of large females in the reproductive process. Our results confirm those of 2825 who found that older breeding tilapia produce more larvae per clutch but less per unit weight than smaller ones. This is rooted in the social dominance effect because within the same population, the hierarchy is quickly established and dominant females reproduce more frequently than others 2930. In addition 15, reports that the Tilapia males are aggressive by nature and those dominants control the majority of egg-layings and therefore several females do not reproduce.

The productivity of the system is 22.33 larvae / m² / day is less than 32 larvae / m^² / d obtained by 25 in a study using the same slice of fish size. Similarly, the absolute productivity observed in our study are much lower than the 451 and 1,598 larvae obtained by 25 for respective female weight 113.4 and 183g. In addition, our values ​​remain low compared to results obtained by 31 (600 larvae / female) and 32 (510 larvae / female). Overall, the low values ​​observed can be explained by the high density used (8 spawners / m^²) because tests by various researchers 33343536 indicate that the best results are obtained with densities of 2.5 to 5.0 progenitors / m^². 37 also observed similar results, indicating that a density of 8 begetters / m^², equivalent to a weight of yearly females 526 g / m^², leading to significant reductions in the production of larvae. 38 also recommend a density of 5 begetters / m^². 39, who tested three broodstock stocking densities (4, 7 and 10 ind / m^²), report that the best fry productions are obtained with a density of 4 breeders / m^². In addition, the single collection would also be responsible for these low values. 40 propose a reproductive management in line with the reproductive cycle of tilapia in ponds. Thus, 36 report daily harvests, with a dip net. Also, 38 experiences showed that the optimal interval between harvests is 10 to 14 days to obtain a maximum offspring.