Variation in the different water quality parameters are presented in Fig 1 and 2. The water temperature varied in a range of 23.3-33.1°C. The two treatments T-1 and T-2 with photoperiod variation showed lower pH and DO, higher CO
2 and higher levels TAN, NO
2 and NO
3 and the variation of these parameters were more pronounced with reduced photoperiod from control to T-2. In contrast, the other two treatments T-3 and T-4 stocked with higher densities did not show any marked variation of these above parameters with those of control only except the higher CO
2 and phosphorous contents. Whereas, the total alkalinity and hardness of water gradually increased with progress of rearing period in all the groups, but did not show marked variations among themselves (Fig 1).
The growth curves as depicted in Fig 3 revealed both darkness and crowding to affect adversely on the length and weight gain process in the fingerlings and the stunting effect was more pronounced with reduced photoperiod than crowding. Further, in both the cases, the stunting effect increased with reduced photoperiod from control to T-2 as well as increased density from T-3 to T-4.
With regard to photoperiod effect, there were significant reduction in the survival, harvested body weight, total length, specific growth rate as well as biomass yield per tank in the treatments T-1 and T-2 compared to the control (P<0.05) (Table 1). Further, the survival, harvested body weight and total length between T-1 and T-2 were statistically similar (P>0.05), though the values were relatively higher in T-1. Similarly T-1 showed significantly higher SGR and biomass yield than T-2.
Survival in T-3 and T-4 were similar despite their varied density, but both were significantly lower than the control (P<0.05) (Table 1). The average body weight (ABW) at the end of the study significantly reduced with increased density from T-3 to T-4. Similarly, the total length and SGR in control were statistically similar to those in T-3 groups, while T-4 recorded significantly lower values of these two attributes. Average biomass yield per tank in T-3 group was the highest among the treatments (P<0.05), but did not vary between control and T-4.
Incident light plays the crucial role in aquatic system through the photosynthetic activity by the planktons to generate the much wanted oxygen required for organism respiration and to fuel the decomposition process for nutrient recycling. Reduced incidence or absence of light obviously affects these processes. Reduction in DO from the control to T-2 in the present study was obviously attributed to the reduced photosynthesis as there was reducing light incidence in these tanks. Fish respiration further added CO2 in these tanks with obvious consequence of lowering of the water pH. As a result, the lower DO and pH would have affected the organic (faeces and waste feed) decomposition process leading to prevalence of proportionately higher nitrogen species as observed in these treatments (
Ghosh and Mohanty, 1981;
Boyd, 1990;
Das et al., 2005; Hargreaves and Tucker, 2004). In contrast to the tanks meant for photoperiod study, T-3 and T-4 did not show much variation in the water parameters compared to the control. Although at some points of sampling, the DO and pH in these two treatments were relatively lower, those were attributed to the fish respiration. But the decomposition process was not affected as revealed from the similar nutrient levels in these tanks as that of control.
Varied photoperiod in the treatments markedly influenced the growth and survival of catla fingerlings. Prevalence of poor water quality in terms of lower DO and pH and higher level of nitrogen species as observed in the study would have affected the fish growth and survival (
Barton and Iwama, 1991;
Wedemeyer, 1997;
Parker, 1988;
Vijayan and Leatherland, 1988). In fact, the survival reduced in the fingerlings with reduced photoperiod in the present study. Such direct relationship of survival and photoperiod has been reported earlier in many other fishes
(Bani et al., 2009; Liu et al., 2015; Falahatkar et al., 2017; Aragon-Flores et al., 2017). Observation of the reduced growth (both harvested body weight and total length) in fingerling in the present study with decreased photoperiod is in concurrence with earlier reports of
Kashyap et al., (2015) in
Catla catla,
Yagci and Yigit (2009) in
Cyprinus carpio),
Biswas and Takeuchi (2002) in
Oreochromis niloticus and Turker (2005) in Sea turbot,
Psetta maeotica. Such growth reduction in the fingerlings may be attributed to a slower fish activity for foraging and feed intake under short photoperiod exposure (
Ali and El-Feky, 2013), reduced appetite due to hormonal effect
(Karlsen et al., 1999) and poor feed conversion efficiency (
Yagci and Yigit, 2009;
Bani et al., 2009, Woiwode and Adelman, 1991). Indian major carps are basically planktivorous in nature. Though they are grown at higher density with supplementary feed in pond system, the natural food through plankton intake forms an important constituent in the diet, particularly in catla. The greater growth depression in the fingerlings with reduced photoperiod in the present study probably is attributed to such phenomenon as it would have restricted the plankton growth in the tanks limiting their availability for the fish. In fact, water in tanks of T-2 was remaining visibly clear during the study suggesting neglible plankton population. The pronounced growth suppression with squeezing of photoperiod indicated increasingly adverse effect of darkness on fingerling growth and can be used as a tool for seed stunting.
Observation of reduced survival with increased rearing density in the second part of this study was obvious as reported earlier in carps
(Jena et al., 1998; Chakraborty and Mirza, 2007;
Rahman and Marimuthu, 2010;
Mane et al., 2019 and
Fatima et al., 2018). Papoutsoglou et al., (1979) and
Leatherland (1993) attributed the reason for such lower survival to decreased average food consumption by individual fish with increased density while
Narejo et al., (2005) attributed it to availability of less living space in addition to food. Reduction of fingerling growth, their SGRs and biomass yields with increased density from the Control through T-3 and T-4 in the present study could also be attributed to the above reasons, as higher densities causes increased competition for food and space (
Hepher and Prugnin, 1981;
Haque et al., 1994; Jena et al., 1998; Gomes et al., 2000; Chakraborty and Mirza, 2007). Never the less, the study revealed increased stocking density to cause growth suppression and can be used as a tool for seed stunting in catla.\