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Soft-Shell Production of the Invasive Atlantic Blue Crab Callinectes sapidus in the Lesina Lagoon (Se Italy):

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Abstract
The current invasion of the Mediterranean Sea by the Atlantic blue crab Callinectes sapidus entails the implementation of effective strategies of control and management. In native areas, the species is highly appreciated as a hard- and soft-shell seafood, and hard-shell fisheries are developing in a number of invaded countries. Here, to verify alternative approaches for enhancing the commercial value of the species, we carried out a pilot experiment to test a flow-through system for the production of soft-shell blue crabs. Fifty crabs were collected in the Lesina lagoon (Adriatic Sea, Italy) and inspected for the coloration of the line on the distal edge of the fifth pereiopod. Accordingly, they were grouped into three groups showing no, white, and red lines, symptomatic of the progression of the pre-molt phase, and maintained for 31 days in a flow-through pond system. The overall mortality rate determined during the trial was similar across the three groups and ranged between 10 and 20%, indicating that the flow-through system was effective for rearing the crabs. In addition, the molting rate was 10%, 65%, and 85% for individuals at an early, intermediate, and advanced pre-molt stage, confirming that the line coloration can be used as an effective indicator of the advancement of the molting process. Our study provides a first contribution towards the introduction in the Mediterranean fishery sector of novel procedures and practices for the production of soft-shell blue crabs, which may represent a cost-effective strategy to enhance the capture and commercialization of this invasive species as a high quality and valuable shellfish product.
Keywords: 
Subject: Biology and Life Sciences  -   Aquatic Science

1. Introduction

Marine bioinvasions are to date recognized as a global threat to the integrity of natural ecosystems and the activities of human populations; accordingly, they are acknowledged as one of the top conservation concerns worldwide [1]. Increasing efforts are devoted to horizon scanning exercises, allowing an early detection of potentially invasive species (IAS hereafter) and, in turn, the implementation of rapid eradication procedures [2,3,4,5]. Indeed, effective eradication of marine IAS has only been achieved when species were detected early, and management responded rapidly [6]. However, mitigating the effect of successful bioinvasions through complete eradication is problematic in marine habitats due to their high environmental connectivity [7]. In contrast, functional eradication i.e. the reduction of population densities below levels that impacts on the native ecosystem are considered acceptable, is to date acknowledged as an appropriate and effective control strategy to manage marine IAS and to mitigate the negative effects on the delivery of goods and services of invaded ecosystems [8,9]. This is particularly true when bioinvaders are species of economic interest, so that functional eradication can be combined with commercial exploitation [10,11,12].
The Atlantic blue crab Callinectes sapidus (Rathbum,1896) (Decapoda, Brachyura, Portunidae) is native to the western coasts of the Atlantic Ocean with a distribution ranging from Nova Scotia to northern Argentina [13,14,15]. The species was introduced in European waters during the first half of the XXth century [16] and, to date, it can be found almost ubiquitously in the Mediterranean and Black Sea, as well as along the European and African Atlantic coasts [15,17]. The invasive success of C. sapidus relates with its r-selected life history traits of high fecundity, dispersal capacity and fast growth, together with its broad environmental tolerance, large body size and aggressive behavior [16]. Noticeably, negative impacts on fishing activities have been repeatedly highlighted due to e.g., consumption of commercial fish caught in traps and damage of nets, especially where established population of C. sapidus are present [18,19]. Moreover, long-term impacts in invaded areas have been observed, related with declines in abundance of native species, and suggesting that enduring negative effects may occur also at relatively low blue crab densities [20].
In native areas, the blue crab is a valuable shellfish product, supporting important commercial and recreational fisheries [21,22]. Noticeably, since the beginning of the nineteenth century, in the eastern United States hard-shell blue crab production has been paralleled by aquaculture activities dedicated to soft-shell crabs [23]. The term soft-shell crab (SSC hereafter) refers to the state of any crab that has just completed the ecdysis, replacing the exoskeleton with a new decalcified and soft one. Hard-shelled crabs are characterized by a low meat yield (generally between 20 and 25%), while SCC can be consumed as a whole with an almost 100% meat yield, making them a much-appreciated and highly valued delicacy [23,24,25]. In the Mediterranean Sea, hard-shell commercial fisheries have also developed in Turkey [26] and northern Greece [27,28], increasing the economic interest towards this species across invaded Mediterranean countries. On the other hand, artisanal fisheries along the Adriatic coasts are currently struggling to find a solution to cope with the presence of established populations of the crab (https://www.catchupfish.it/prodotti-tecnici/).
A possible solution to increase the commercial interest in blue crabs from invaded areas and ensure their sustainable use is by generating higher added value and diversify the market demand by developing SSC production [29]. Here, we focused on the blue crab population in the Lesina Lagoon (Apulia Region, SE Italy), where the occurrence of the species was first recorded in 2007 and repeatedly confirmed in the following years [30,31]. To date, blue crabs represent a predominant component of the by-catch in the basin and the species is perceived as a nuisance by anglers, given its low market price and limited interest from local processing companies. Specifically, the main objectives of the present study were to:
i)
explore for the first time in Europe the suitability of a pond system to produce SSC; to this end, the flow-through or recirculating cultivation facilities in use in native areas to rear pre-molt individuals of C. sapidus (locally known as peelers), were taken as a model [24];
ii)
investigate the molting process in blue crabs from the Lesina Lagoon, and verify if the population is characterized by a predictable molting pattern similar to that observed in native areas.
Indeed, in recent years a number of investigations have focused on the biology and ecology of C. sapidus in Mediterranean waters, in terms of distribution [15,18,32] population structure and dynamics [33] and trophic habits ([34-37
]]. Noticeably, no efforts have been made to provide detailed information on this crucial phase of the biological cycle of the species in invaded areas.

2. Materials and Methods

  • 3.1. Study Area
The Lesina Lagoon (41.88°N and 15.45°E; Figure 1) is a microtidal shallow (0.7-1.5 m) lagoon located along the south-western Adriatic coasts of Italy. It has a total water surface of 51.4 km2 separated from the Adriatic Sea by a sandy isthmus about 18 km and connected to it by two tidal channels: Acquarotta to the West, and Schiapparo to the East [31,38].
The lagoon's main hydrological features, temperature and salinity follow a seasonal trend, with minimum values in winter and maximum values in summer [39]. Anglers operate in the lagoon using mainly fixed nets, known locally as “paranze”. These are nylon seines with a 6-mm mesh placed perpendicularly to the shores, which convey the prey into fyke-nets with a 4 to 6 -mm mesh installed at regular intervals along them [40].
  • 3.2. Experimental Setup
The trial was performed in a pond located in a semi-enclosed facility located on the southern banks of the Lesina Lagoon close to the IRBIM-CNR Institute. The facility was constituted by a system of four interconnected artificial ponds (Figure 1) waterproofed by polyethylene sheets and an average area of 100 m2 and a depth of 1.5 m deep (Figure 1). The water circulation was open, and directly connected with the lagoon by means of a flow-through system connected to an underwater electric pump (Wilo-Emu FA). Taking as a reference published information on farms producing soft-shell portunid crabs in Americas and Asia [24] a floating boxes system was built up inside one of the ponds. These devices avoid cannibalism, since each crab was kept in small individual polyethylene cages (30 x 40 x 30 cm) immersed close to the water surface and supported by a floating system anchored to the side of the pond (Figure 2).
The trial took place in July 2020 as preliminary studies on blue crab’s population dynamics in the basin showed abundance peaks of catches during warmer months, as well as a higher abundance of individuals in the pre-molt phase (Cilenti, personal observation).
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Figure 2. Floating-boxes system anchored to the side of the pond (A) and detail (B) of the polyethylene cages deployed to keep the individuals of Callinectes sapidus.
Figure 2. Floating-boxes system anchored to the side of the pond (A) and detail (B) of the polyethylene cages deployed to keep the individuals of Callinectes sapidus.
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80 randomly-chosen specimens of C. sapidus captured using fyke-nets and gillnets by local anglers were transferred using aerated tanks to the laboratories of the IRBIM-CNR Institute of Lesina, where they were inspected. Only 50 specimens showed intact appendages; accordingly, they were selected and divided in three groups based on pre-molt signs. Although there are several macroscopic indicators of the pre-molt phase [41], specimens’ selection was carried out by inspecting the coloration of the line along the inside edge of the last flattened section of the pereiopods, where the new shell formation is more visible.
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Figure 3. Presence (A and B) and absence (C) of the macroscopic sign indicators of the pre-moult phase in the inside edge of the last flattened sections of the pereiopod. In figure A the arrow indicates the white line characteristic of an early pre-moult stage, while in figure B the arrow indicates the red line indicative of an advance pre-moult stage and the proximity of ecdysis.
Figure 3. Presence (A and B) and absence (C) of the macroscopic sign indicators of the pre-moult phase in the inside edge of the last flattened sections of the pereiopod. In figure A the arrow indicates the white line characteristic of an early pre-moult stage, while in figure B the arrow indicates the red line indicative of an advance pre-moult stage and the proximity of ecdysis.
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This is the most reliable and widely used method to identify the pre-molt stage [41]. A white line indicates that the specimen will molt in two weeks; as molting approaches, the color gradually turns to pink and then red, indicating that the crab will molt within one week and one-three days respectively [41,42] (Figure 3). Accordingly, three groups were identified: (1) 20 individuals showing the presence of a white line (W group hereafter), (2) 20 individuals showing the presence of a pink to red line (R group), and (3) 10 individuals showing no line along the edge of the flatten pereiopods (C group). The sex of all individuals was determined by examination of the apron shape; their carapace width (CW) and carapace length (CL) were measured using a caliper (to the nearest 0.1 cm), while their wet weight (WW) was measured using a digital balance (to the nearest 0.1 g). Subsequently, individual crabs were randomly introduced into the polyethylene cages.
The trial lasted 31 days. During the study, water circulation in and out the system was kept continuously active, ensuring an optimal water exchange between the lagoon and the pond. No food were provided, as crabs in the pre-molt stage do not feed [41]. Cages were inspected three times a day (07:00, 14:00 and 21:00) to record molting or mortality cases. Once molting was observed, crabs were removed from the cage. Pond’s water temperature (°C), salinity (PSU), dissolved oxygen (mg L-1) and percentage of oxygen saturation (%) were monitored weekly in triplicate using a multi-parametric probe (Hydrolab DS5).
  • 3.3. Data Analysis
Values in the text are expressed as mean ± 1 SD if not otherwise specified. Data were preliminarily checked for normality (Shapiro-Wilk test) and homoscedasticity (Cochran’s C-test); when necessary, they were square root- or log(x+1)-transformed to meet the required assumptions. Two-way ANOVAs with “sex” (two levels) and “treatment” (three levels) as orthogonal fixed factors were performed to test the differences in biometric parameters (CW, CL, and WW) among the three groups of crabs as affected by sex. Mortality and molting rates were compared using “N-1” χ-square tests as generally recommended [43,44]. Given the peculiar characteristics of the data (see Results), a Type III (partial sum of squares) one-way permutational multivariate analysis of variance (PERMANOVA; Anderson, 2005) with 9,999 unrestricted permutation of raw data was subsequently used to test for among-group differences in the number of days taken by specimens to molt.

3. Results

3.1. Crabs Sex Ratio and Biometry at the Start of the Trial

The overall female-to-male sex ratio of the 50 crab specimens involved in the trial was 0.68:0.32. The sex ratio for the control group was 0.7:03, while for the R and W group was respectively 0.55:0.45 and 0.8:0.2 (Table 1), yet no significant differences across the three treatments were determined (max χ2 = 2.76, P = 0.11, 1 d.f. estimated for the comparison Group W vs. Group R).
The overall mean (± 1SD) individual carapace width, length, and wet weight of the specimens from the three treatments were 107.6 ± 13.3 mm, 53.1 ± 5.4 mm, and 100.3 ± 34.3 g. The crabs in the C group had a mean CW, CL, and WW of 110.1 ± 13.8 mm (88 - 126 mm min-max range), 53.3 ± 4.5 mm (46 - 60 mm min-max range), and 110.2 ± 38.9 g (58.1 - 168.1 g min-max range), respectively. In the W group, specimens had a mean CW, CL, and WW of 111.15 ± 15.5 mm (90 - 127 mm min-max range), 54.7 ± 4.9 mm (45 - 63 mm min-max range), and 105.4 ± 29.3 g (60.9 - 152.1 g min-max range), respectively.
Table 1. Mean individual carapace width (CW), carapace length (CL), and wet weight (WW) the crab specimens included in the different treatments at the start of the trial. Standard deviations are reported in round brackets, while the number of specimens for each combination treatment/sex are in square brackets.
Table 1. Mean individual carapace width (CW), carapace length (CL), and wet weight (WW) the crab specimens included in the different treatments at the start of the trial. Standard deviations are reported in round brackets, while the number of specimens for each combination treatment/sex are in square brackets.
Treatment Sex CW (mm) CL (mm) WW (g)
C group F [7] 108.29 (12.13) 53.86 (4.85) 100.54 (27.83)
M [3] 114.33 (19.35) 52.01 (4.01) 132.71 (58.39)
W group F [16] 113.44 (11.87) 55.06 (4.99) 108.64 (28.05)
M [4] 102.01 (12.08) 53.01 (4.76) 92.39 (34.97)
R group F [11] 102.45 (11.94) 50.18 (4.85) 84.51 (23.59)
M [9] 103.22 (14.78) 52.89 (7.15) 97.36 (47.08)
Finally, the CW of crabs in group R ranged between 84 - 128 mm and averaged 102.8 ± 12.9 mm, with a CL ranging between 45 and 66 mm (51.4 ± 6 mm, mean ± 1SD), and a WW comprised between 50.6 and 187.4 g (90.3 ± 35.6 g, mean ± 1SD). In addition, sex-related differences in the body size of crabs in each treatment were observed (Table 1), yet in general, no significant effects were observed for either the factor “treatment” or “sex” on the variation in body size of the crabs (Table 2).

3.2. Pond Water Parameters

During the trial, the temperature of the water in the pond increased from 25.8 to 27.7°C (Figure A1 in Appendix A), paralleled by a decrease in the concentration of the dissolved oxygen concentration from 7.7 to 5.8. Salinity decreased in the first week of the trail from an initial value of 28.5 PSU to 27.9, and then increased up to 28.9 PSU. Despite the observed variations, all water parameters remained in the ranges suggested for optimal maintenance conditions of peelers (Table 3).

3.3. Crabs Mortality and Molting during the Trial

In total, seven specimens died during the trial (Table 4), with an overall mortality rate of 14%. No significant differences in mortality rates were observed across treatments (max χ2 = 0.04, P = 0.84, 1 d.f. for the comparison Group W vs. Group R). Noticeably, the majority of the mortality events (5) occurred during the first 24 h, and one crab from the R group died during the process of molting after 48 h.
The lowest frequency of molting events occurred in the C group, where only one crab molted after 17 days from the beginning of the trial. Conversely, the highest frequencies occurred in crabs belonging to groups W and R, with a molt rate of 65.0% and 85%, respectively (Table 4).
Table 4. Mortality and molting rates of the individuals held in the floating-boxes system.
Table 4. Mortality and molting rates of the individuals held in the floating-boxes system.
Treatment Dead Molting Non-molting Days to molting
C group 2 (20%) 1 (10%) 7 (70%) 17
W group 2 (10%) 13 (65%) 5 (25%) 13.07 ± 6.91
R group 3 (15%) 17 (85%) 0 4 ± 1.27
Negligible differences were observed between them (χ2 = 2.08, P = 0.14, 1 d.f.), yet both treatments showed frequencies significantly higher than that observed in the control group (W group vs. C group: χ2 = 7.83, P = 0.005; R group vs. C group: χ2 = 15.09, P = 0.0001; 1 d.f. for both tests). In addition, the number of days taken by specimens to molt varied significantly across treatments (one-way PERMANOVA, pseudo-F2,30 = 25.07, Pperm = 0.0001). On average, crabs in the R group molted after 4 days, significantly earlier than what observed for both the C and W groups (Table 4; post-hoc bivariate comparisons: minimum t = 4.46, P = 0.032 for the comparison group R vs. group C). In contrast, no significant differences were observed between group C and W (t = 0.71, P = 0.78).

4. Discussion

Our study indicated that for Callinectes sapidus from the Lesina Lagoon the color of the propodus and dactylus of the fifth pereiopod can be successfully used as an indicator of the progress of the molting process. A visual inspection allowed the identification of peelers, and accordingly, to separate individuals in the pre-molt stage from those in the intermolt stage as previously described [42]. These results are comparable to those observed in a study on molting success conducted in Maryland in a floating system, where the time to molt of peelers showing white and red line on their paddles took respectively 3-10 days and 1-3 days [42]. The macroscopic sign observed during the initial selection of individuals, as well as the progressive change of the line’s color from white to red, were similar to those previously reported by studies on the determination pre-molt phase of C. sapidus [42] as well as of C. arcuatus and C. ornatus [46,47]. Furthermore, significant differences between the days to molt allowed the differentiation of individuals in the very early phase of the pre-molt stage to those in the advanced phase.
Information on Asian and American soft-shell crab enterprises are rare and data on peelers mortality rates are difficult to obtain [24,48]. Nevertheless, the overall mortality rate recorded in this study was lower to that reported by Spitznagel et al. [49] for eight different culture facilities in the Chesapeake Bay region, where the mean mortality was 21.7 ± 2.8%. Interestingly, our results were closer to that reported for recirculating systems (16.4 ± 3.1%) than for flow-through facilities (32.9 ± 4.3%). Experiments conducted in continuous flow system similar to that used in the present study on C. danae and C. exasperatus [50], reported mortality rates ranging from 37.5 to 60%. A study on the North Carolina (U.S.A.) soft-shell crab industry [51] estimated that approximately 23% of the crabs placed in shedding systems die within 5 days, highlighting that the stress caused by capture and transport is one of the causes of peelers mortality. Therefore, it is likely that the high death rate observed here within the first 24h might have been determined by the stress induced by capture, handling, and transport from the Lesina Lagoon. The common practice of anglers to keep crabs in waterless containers increases the probability of injuries and physiological stress and may result in immediate or delayed effects on the captured blue crabs, including mortality [52]. However, excessive stress and consequent mortality can be avoided by keeping the crabs cool and moisten during transport, as highlighted elsewhere [51].
Noticeably, we showed that only the advanced pre-molt stage testified by the reddening of the line on the paddles can be used as an effective indicator, since crabs characterized by a white line (W group), did not show significant differences in terms of days taken to molt with the control group. This lack of differentiation is likely to have been determined by the relatively low number of specimens involved in the trial, and by the duration of the trial itself. The experiment had to be terminated after one month given the fully summer conditions and the variations observed in the chemical-physical characteristics of the pond water, where temperatures reached values no longer suitable for optimal crabs rearing (Table 3). The high survival and molting success of our experiment, together with the water parameters in line with those suggested by Malone and Burden [45], indicated that the semi-closed system equipped with floating boxes can represent a viable semi-culture technology to keep individuals of C. sapidus under controlled conditions and let them complete the molting process. However, future experimental designs performed in larger ponds, with a higher number of specimens, and with a longer duration, may allow crabs showing no pre-molt signs in control groups to conclude the molting process and have the appropriate statistical power to validate the results of the present study. Yet, we are confident that our investigation provided a preliminary yet robust confirmation that the procedures generally in use to identify and rear Callinectes sapidus for the production of soft-shell crabs in native areas can be successfully used also in the Mediterranean context.
Our study clearly suggests that the commercial interest in the blue crab in invaded areas may be increased promoting the development of a product similar to the soft-shell crabs provided in the American and Asian markets, where the price of soft-shell crabs can exceed that of a hard-shelled ones by 300% to 400% [29]. To our knowledge, the only example of soft-shell crabs production in the Mediterranean Sea is represented by the “moleche” industry in Venice Lagoon, where males of the Mediterranean crab Carcinus aestuarii are seasonally harvested and held in submerged wooden or plastic containers (vieri) until molting [53,54]. Moleche represent an important source of income for the fishermen, given that their market price may exceed 80 €/kg [55]. Taking as a model these already-established circumstances, the introduction in the Mediterranean fishery sector of novel technical procedures and practices for the production of soft-shell blue crabs may represent a cost-effective strategy to encourage the capture and marketing of this invasive species as a high quality and valuable shellfish product, while minimizing control costs and impacts.

5. Conclusions

Invasive alien species are undesired organisms for which eradication and/or prevention of expansion is considered as the main management objective. However, eradication can be costly or unfeasible, depriving local communities of economic benefits, and even produce counterintuitive effects on the integrity of ecosystems [56]. For instance, the proposed management of the pacific oyster Crassostrea gigas recommended the sustainable use of this non-native species if individuals are kept in confined cages, while suggested eradication from local invaded marine ecosystems of wild populations [57]. A comparable scenario is that of the Atlantic blue crab Callinectes sapidus, representing a highly invasive alien species impacting biodiversity and ecosystem services and threatening the socio-economic sector of fishing of invaded regions, even though in native areas is a commercially important species [10,18]. Established blue crab populations in the Mediterranean regions need to be controlled to satisfy the principles of sustainable development that guarantees environmental protection and conservation while ensuring the economic growth of local communities. The present study provided a clear indication that the capture of C. sapidus specimens in the pre-molt phase together with the development of techniques and practices for their rearing could represent an additional seasonal activity allowing professional anglers to improve their profit while contributing to mitigate the impact on invaded ecosystems.

Author Contributions

Conceptualization, L.C., N.L. and G.M.; investigation, L.C., N.L., A.O.L., D. Li V., and T.S.; methodology, L.C. and N.L.; formal analysis, L.C. and G.M.; data curation, L.C., N.L., and G.M., writing - original draft preparation, L.C. and N.L.; writing – review and editing, G.M.; funding acquisition, L.C. All authors have read and agreed to the published version of the manuscript.

Funding

This research was funded by funding from the Apulia Region through Po-FEAMP Misura 1.44 (Art. 44, par. 1 lett. cdel Reg. UE n. 508/2014) “CatchUpFish - Sviluppo di metodologie innovative per lo sfruttamento sostenibile delle risorse biologiche nella Laguna di Lesina”.

Institutional Review Board Statement

No ethical issues related with the use of animals in the performed analyses were involved.

Informed Consent Statement

Not applicable.

Data Availability Statement

data used in this study are available upon request from the corresponding author. The data are not publicly available due to ongoing comparative analyses.

Acknowledgments

The authors wish to thank for their help during field operations the associations of anglers operating in the Lesina Lagoon.

Conflicts of Interest

The authors declare no conflict of interest. The funders had no role in the design of this study; in the collection, analyses, or interpretation of data; in the writing of the manuscript; or in the decision to publish the results.

Appendix A

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Figure A1. Variation in mean temperature, salinity, and dissolved oxygen concentration of the pond water during the trial. The standard deviation of the estimations is not included for the sake of clarity.
Figure A1. Variation in mean temperature, salinity, and dissolved oxygen concentration of the pond water during the trial. The standard deviation of the estimations is not included for the sake of clarity.
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Figure 1. The Lesina Lagoon, and location of the semi-enclosed facility where the study was performed (indicated by the red cross). An aerial image of the experimental system where crabs were reared is included, and the pond used in the trial identified by a red arrow.
Figure 1. The Lesina Lagoon, and location of the semi-enclosed facility where the study was performed (indicated by the red cross). An aerial image of the experimental system where crabs were reared is included, and the pond used in the trial identified by a red arrow.
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Table 2. Summary of two-way factorial ANOVAs testing for the effect of treatment and sex on the mean carapace width (CW), carapace length (CL), and wet weight (WW) of crab specimens at the start of trial. F values are reported, with the corresponding P values in brackets.
Table 2. Summary of two-way factorial ANOVAs testing for the effect of treatment and sex on the mean carapace width (CW), carapace length (CL), and wet weight (WW) of crab specimens at the start of trial. F values are reported, with the corresponding P values in brackets.
Factor Degree of freedom* FCW FCL FWW
Sex [1] 1 0.13 (0.72) 0.05 (0.82) 0.73 (0.39)
Treatment [2] 2 1.41 (0.25) 0.87 (0.43) 1.72 (0.19)
1 × 2 2 1.37 (0.26) 0.98 (0.38) 1.41 (0.25)
* Error: n = 44
Table 3. Mean temperature, salinity, and dissolved oxygen concentration (mean ± standard deviation) measured in the experimental pond during the trial. Water parameters suggested in the literature [45] for optimal maintenance conditions are included.
Table 3. Mean temperature, salinity, and dissolved oxygen concentration (mean ± standard deviation) measured in the experimental pond during the trial. Water parameters suggested in the literature [45] for optimal maintenance conditions are included.
Parameter Pond Optimal conditions
Temperature (°C) 26.9 ± 0.9 21.1 – 26.7
Salinity (PSU) 28.4 ± 0.4 ± 5 PSU of harvesting water
Dissolved Oxygen (mg/L) 6.5 ± 0.8 > 5
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