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Evaluation of growth and production performances of the white sea urchin, Salmacis sphaeroides (Linnaeus, 1758) in a captive aqua-rearing system

M. Aminur Rahman12*, Md. Habibur Rahman1, O. E. Asare2, F. O. Megwalu2, M. Habibur Rahman Molla2, M. Zahangir Alom1

1Department of Fisheries and Marine Bioscience, Faculty of Biological Science and Technology, Jashore University of Science and Technology, Jashore - 7408, Bangladesh, 2World Fisheries University Pilot Programme, Pukyong National University, 45 Yongso-ro, Nam-gu, Busan - 48513, Korea

Address for correspondence: M. Aminur Rahman, Department of Fisheries and Marine Bioscience, Faculty of Biological Science and Technology, Jashore University of Science and Technology, Jashore - 7408, Bangladesh. E-mail: aminur1963@gmail.com
Submitted: 05-03-2019, Accepted: 15-03-2019, Published: 29-03-2019

ABSTRACT

The white sea urchin, Salmacis sphaeroides, is one of the high-valued tropical species having significant biological, ecological, aquacultural, and conservational values. To domesticate as well as to develop appropriate culture techniques of this commercial species, a grow-out culture experiment was conducted in a controlled aqua-rearing condition. A 3-month-old healthy juveniles produced from captive spawning, larval rearing, and metamorphic induction were cultured in each of nine well-established and aerated aquaria (90 cm × 45 cm × 45 cm). Stocking density was maintained at 30 juveniles/aquarium. The juveniles provided with red macroalga (Amphiroa fragilissima) as food were regarded as Treatment-1 (T1), brown macroalga (Sargassum polysystum) as Treatment-2 (T2), and green seagrass (Enhalus acoroides) as Treatment-3 (T3), respectively. All juveniles during stocking were with the same age group and batch rearing, having a mean weight of 0.49 ± 0.11 g and length of 10.04 ± 0.70 cm. They were fed with different macroalga in excess and the seawater from each rearing aquaria was changed with regular intermissions. This grow-out trial was continued for 2 years within which all the sea urchins achieved sexual maturity and contained adequate amounts of gonads. Growth performances (such as final weight, final length, weight gain, length gain, specific growth rate, and daily growth rate) and survival of adult urchins were significantly higher (P < 0.05) in T1 than those in T2 and T3, respectively. Production of edible gonads in terms of wet gonad weight and gonad index was also followed the similar trends as growth parameters. Therefore, it can be concluded that red alga is the most suitable food for S. sphaeroides in captive culture condition. The findings emerged from the study would be helpful for the adoption of sea urchin culture in commercial scale.

Keywords: Growth, Macroalgae, Production, Salmacis sphaeroides, Survival


INTRODUCTION

Salmacis sphaeroides (Echinodermata: Echinoidea: Temnopleuridae), commonly referred to as ball-like white sea urchin, occurs in the tropical Indo-West Pacific ocean where it can be found from China down to Australia.[1-3] It can also be found in the warm temperate regions including Johor States, between Malaysia and Singapore.[4-6] This species can occur at the range of depth between 0 m and 90 m, but it is mostly found in shallow waters, especially muddy sublittoral habitats with soft sediments (below the intertidal area).[7] They are often associated with macroalgae (seaweeds) and seagrass meadows or washed ashore and in coral reef habitats.[2,4] Various studies confirmed that S. sphaeroides is a generalist, feeding on a variety of seagrasses[8] and macroalgae,[9] sea pens, jellyfish, and a rather random plethora of experimentally introduced food items such as banana skins and salami.[10] They have also been observed attacking and preying on members of their own species.[11] It has been reported that this species has significant biological, ecological, aquacultural, pharmaceutical, and nutritional values.[5,6]

Sea urchins are found in oceans all over the world and greatly contribute to the food chains of marine environment by ingesting varieties of algae and invertebrates and also being consumed by mammals, fishes, crabs, sea stars and birds.[11] Gonads of sea urchin commonly known as “sea urchin roe” or “uni” are well accepted as a highly tasty food item in Asian, Mediterranean, and Western Hemisphere countries.[5,6,11-16] Either fresh or in the form of processed food, sea urchin gonad has long since been using as high delicacy and expensive food by the common Japanese peoples.[15-18] Despite S. sphaeroides has not yet been used as edible species in Malaysia, it has been found to serve as a delicacy food item in local seafood restaurants in Hong Kong.[19] Valuable bioactive compounds such as polyunsaturated fatty acids (PUPAs) and β-carotene are abundantly found in the gonads of sea urchin[20,21] and reported that the PUPAs, particularly eicosapentaenoic acid (EPA, C20:5) [n-3]) and docosahexaenoic acid (DHA C22:6) [n-3]), do have substantial protective effects on cardiac illnesses, arrhythmia, and cancer. Instead, the high amounts of arachidonic acid and EPA recently identified in S. sphaeroides[19] exhilarated the establishment of appropriate culture techniques of this high-valued sea urchin in captivity since PUPAs are essential for human nutrition.[22] Sea urchin gonad is also enriched with the first-class proteins and thus provide an excellent source of protein in human foods such as fish, meat, legumes, and beans.[11] However, in recent years, sea urchin fisheries have extended too largely that their population throughout the world have been depleted due to overfishing. These declining patterns clearly indicate the overexploitation of major fishery grounds and focus the necessity for proper conservation strategies, stock enhancement, fishery management, and aquaculture development to fill-up the gap between the supply and demand.[5,6,23-25]

The urchin research is quite new in Malaysia. However, a few studies on the population characteristics, distribution, feeding, breeding, and development of S. sphaeroides have recently been carried out,[1,5,6,26] no systematic studies have yet been conducted to optimize the juvenile and adult growth and production in rearing conditions. Hence, an effort has been carried out to establish a suitable aquaculture protocol of S. sphaeroides in a captive aqua-rearing condition.

MATERIALS AND METHODS

Broodstock Collection and Maintenance

Matured adults of the sea urchin, S. sphaeroides, weighing from 110 g to 180 g, were collected from Merambong shoal of Tanjung Kupang (01°34’ N; 103°60’ E), Johor, Malaysia, in July–October 2013, during which the urchins attain sexual maturity. Immediately after collection, the live sea urchins were transported to the Marine Biotechnology Laboratory, Institute of Bioscience, Universiti Putra Malaysia, where they were maintained in aerated aquaria before use for the experiments.

Induced Spawning and Fertilization

Gametes were collected from the sexually matured urchins by the intracoelomic injection with a 0.5 M concentration of potassium chloride solution. Spawned eggs were then shredded by placing the inverted female individuals on a transparent glass beaker filled with sterilized filtered seawater (FSW), while the concentrated sperms were pipetted off the genital pore from the male individuals. Fertilization of eggs was done using 10−5 diluted concentration of “dry” sperm.[27-29] Sperms were left for at least 10 min to ensure that all the eggs were encountered by spermatozoa during the fertilization process. Excess sperms and debris were then removed from the inseminated eggs by 3–4 consecutive washes with FSW.[5,30]

Larval Rearing

The incubation of fertilized eggs was followed in 500 ml glass beakers containing FSW at ambient temperature (25–26°C) until they formed into free-swimming blastula. They were then reared in 500-ml glass bottles containing SFSW on 10 rpm rotating rollers. Densities of larvae up to the four-armed pluteus stage were kept at 2–3 individuals/ml, using the protocols reported by Rahman et al.[27,29,31] When larvae attained four-armed pluteus stage, they were reared in 1000 ml glass bottles with a larval density of 1 individual/ml. The cultured unicellular diatom, Chaetoceros calcitrans, was supplemented as larval food at the rates of 5000, 10,000, and 15,000 cells/ml for four-, six-, and eight-armed pluteus stage, respectively, until attaining the metamorphic competence and settlement stage.[5,27]

Settlement Induction and Metamorphosis

After 30–34 days of larval rearing, when the matured larvae attained competent stage were then used for the settlement induction. Competence was judged by the evidence of large juvenile rudiments and a high metamorphosis rate.[30] Settlement induction and metamorphosis of competent larvae were done on coralline red algal extracts in plastic Petri dishes (9.0 cm × 3.0 cm) containing FSW. Density of larvae at this trail was maintained at one individual/2 ml FSW, following the method of Rahman et al.[30] and Rahman et al.[5] Transformation was proceeded by the absorption of larval arms and tissues, and the formation of complete juvenile structure with growing adult spines extended tube feet and well-developed pedicellaria, the entire event of which usually took place within 1-day post-settlement.[5]

Culturing of Juveniles and Adults

The newly metamorphosed juvenile urchins were cultured in small glass aquaria provided with continuous aerated FSW and the coralline red algae on the calcareous stones were supplied as diet.[27,29] The rearing seawater in aquaria was changed bimonthly with new FSW. This procedure was followed for a period of 3 months, during which time the juveniles reached to 9.0–10.0 mm in length. The 3-month-old juveniles with an average weight and length of 0.39 ± 0.05 g and 9.63 ± 0.31 mm, respectively, were then cultured in nine replicate glass aquaria (90 cm × 45 cm × 45 cm) and provided with aerated seawater in the grow-out culture unit of the Institute of Bioscience, Universiti Putra Malaysia. The stocking density was maintained at 30 juveniles per aquarium. The juveniles provided with red macroalga (Amphiroa fragilissima) as food were regarded as Treatment-1 (T1), brown macroalga (Sargassum polysystum) as Treatment-2 (T2), and green seagrass (Enhalus acoroides) as Treatment-3 (T3), respectively. They were fed ad libitum and the uneaten feed and feces were removed on regular basis. Seawater in each culturing aquaria was changed completely at every 2–3 months until the end of the grow-out experiments.

The physicochemical parameters of culturing waters were measured fortnightly at 09.00–09.30 h. Water temperature, salinity (ppt), dissolved oxygen (DO) (mg/l), and pH were measured instantly using a water quality analyzer (YSI Model 58, Yellow Springs Instruments, Ohio, USA) and ammonia nitrogen, nitrate nitrogen, nitrite nitrogen, and phosphate phosphorous by a standard HACH water analysis kit. Total alkalinity was determined using the established procedure.[32,33]

Growth performances in respects of length, weight, and health condition of the rearing urchins were monitored regularly. 10 individuals from each aquarium were measured at each 3 months of interval until they attained the adult stage. The culture was continued for 2 years and terminated on September 2015, within which the sea urchins achieved sexual maturity and also have sufficient mature gametes. Growth in terms of final length and weight, length and weight gain, specific growth rate (SGR), and daily growth rate (DGR), and survival was estimated the following standard methods. The SGR and DGR values were estimated the following Brown[34] and De Silva and Anderson,[35] respectively. Production of edible gonad was estimated the following Rahman et al.[5] while the gonad index (GI) was computed according to the formula[36,37,38] as given below:

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Data Analyses

All percent data were arcsine transformed before used for statistical analyses. This transformation assisted to normalize the data and also reduced the heterogeneity in variances. A Bartlett’s test was used to analyze the homogeneity of variances.[39] When the variances were not significantly heterogeneous and did not have any major departures from normality, a one-way analysis of variance (ANOVA) was done followed by Tukey’s multiple comparison test, and the significance level was set at 0.05.

RESULTS

Physicochemical Parameters

The mean and range values of water quality parameters in the rearing aquaria over the 2-year culture period of S. sphaeroides are summarized in Table 1. The mean values of temperature (oC), salinity (ppt), DO (mg/l), total alkalinity (mg/l), ammonia nitrogen (mg/l), nitrate nitrogen (mg/l), nitrite nitrogen (mg/l), and phosphate phosphorus (mg/l) did not show any significant differences (Tukey’s test, P > 0.05) among the treatments evaluated [Table 1].

Table 1: Mean±SD and range values of physicochemical parameters of seawater for the 2-year rearing period of S. sphaeroides in captive aqua-rearing condition

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Growth and Production Performances

Detailed growth performances (such as final weight, final length, weight gain, length gain, SGR, DGR, gonad weight, and GI) and percent survival of S. sphaeroides at the termination of the 2-year culture period in the experimental treatments are presented in Table 2, while the growth trends in length and weight at each 3 months interval are depicted in Figures 1 and 2. The length and weight increment were the highest in T1 followed by that in T2 and the lowest in T3. The final mean length and weight of S. sphaeroides were significantly higher (Tukey’s test, P < 0.05) in T1 than the values obtained in T2 and T3. Similar trends were also found in weight and length gains. Percent weight gain and length gain were significantly highest in T1 and the lowest in T3 [Table 2]. Significantly higher (Tukey’s test, P < 0.05) SGR and DGR values were also obtained in T1 than those in T2 and T3 in this order.

Table 2: Comparison of growth and production parameters of S. sphaeroides fed with different algal feeds at the termination of a 2-year culture experiment. For each treatment, a total of 30 live urchins were measured for each parameter with 10 randomly selected individuals per replicate. All values indicate mean±SE and ranges in parentheses

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Figure 1: Growth in respects of length increment in Salmacis sphaeroides fed with different macroalgae during the culture for 2 years

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Figure 2: Growth in respects of live weight increment in Salmacis sphaeroides fed with different macroalgae during the culture for 2 years

Production of edible gonad was significantly higher (Tukey’s test, P < 0.05) in T1 than those produced in T2 and T3 [Table 2]. Similarly, the GI (percentage gonad weight in regard to the drained body weight) was significantly highest (Tukey’s test, P < 0.05) in T1 followed by T2 and the lowest in T3. However, the productions of edible gonad and GI in sea urchins fed with red alga (T1) showed an increment of 158.52% and 22.98% over seagrass (T2) and 69.07% and 11.03% over brown alga (T3) fed urchins, while it showed an increase of 52.97% and 10.76% over seagrass, respectively, when the urchins were fed with brown alga. Percentage values of mean survival in T1 (88.89%) did significantly higher (Tukey’s test, P < 0.05) than the survivals in T2 (73.33%) and T3 (56.67%), respectively [Table 2].

DISCUSSION

Coral reefs are considered as important habitats for most of the marine vertebrate and invertebrate organisms. Survival, reproduction, and development of marine organisms highly depend on the environmental factors such as water temperature, salinity, pH, and minerals.[40-44] Range values of water temperature (27.65–29.50°C) and salinity (29.40–32.00 ppt) in the experimental aquaria were within the appropriate level for sea urchin culture, which are in closer agreements with to the findings of Rahman et al.[27-29,45] The DO concentrations (6.22–7.52 mg/l) in our study were higher than that of Asia,[45] who recorded the DO levels ranged from 4.57 to 5.98 mg/l, while rearing collector sea urchin (Tripneustes gratilla) in glass aquaria and are within the suitable levels for grow-out culture in captivity. The pH values ranged from 7.52 to 8.32, agree well with the findings of Asia[45] and are in the good water quality levels for culturing of sea urchin under aquarium system. Besides these, the influences of other water quality parameters, namely total alkalinity, ammonia nitrogen, nitrate nitrogen, nitrate nitrogen, and phosphate phosphorous on body growth of sea urchins, have yet not been thoroughly examined. Nevertheless, we investigated these parameters for the 1st time in our present sea urchin culture trials and observed that all of them were within the suitable levels for sea urchins, as similar to those reported in various fish culture ponds.[46-53]

The growth parameters, survival rate, and edible gonad production of 2-year-old adults S. sphaeroides fed with red alga (A. fragilissima) were significantly higher (Tukey’s test, P < 0.05) in T1 than that fed with brown alga (S. polysystum) (T2) and green seagrass (E. acoroides) (T3). This may be because red alga was the preferred food in hastening the growth performances of S. sphaeroides than other algal foods. Likewise, coralline red algae were reported as one of the best algal diets in enhancing the growth performances, survival, and production of the adults of conspecific parents and the reciprocal hybrids among the different species of Echinometra spp. in Okinawa, Japan.[5,46,47] The results from our study are more or similar to the findings of Steinberg.[54,55] This contrasts with the observation of Sonnenholzner et al.[56] who found that the sea urchin (Strongylocentrotus purpuratus) fed on coralline red alga (Bossiella orbigniana) and the eelgrass (Phyllospadix scouleri) reduced their size and weight severely, and actually, these did not accelerate the growth of gonadal tissues for the rearing juvenile urchins as expected. Nevertheless, they also observed that a mixed diet comprising the aforementioned three algal species did perform well for the subadult of S. purpuratus than a single diet consisting of coralline algae (B. orbigniana) or eelgrass (P. scoulei) only.

In regard to the point of nutritional assessment, nitrogen has been considered as an essential part for the reproduction and growth of herbivores.[57] However, nitrogen (henceforth referred to as protein) is usually lower in all kinds of marine plants and appears to be the nutritional constituents, which best repeatedly impacts on the diet selections of herbivores.[56,58] For instance, the eelgrass and kelp contain similar amounts of proteins, lipids, and carbohydrates of 0.8–1.5%) and 40–45% (“dry” weight basis), respectively. Conversely, the coralline red alga, B. orbigniana, covers lesser amounts of proteins, fats, and carbohydrates of <3%, 0.5%, and 8–10%, respectively. Despite the fact that the eelgrass, P. scouleri was considered as a good source of protein similar to the brown kelp (E. menziesii), the highest growth rate was obtained in S. purpuratus when they were fed with kelp.[56] Even though we have not been able to estimate the proximate compositions of the algal plants used in this present study, it might not be overlooked that these plants can exhibit significant discrepancies in the contents of majority of its nutritional constituents that deserve more investigations.

In general, algae release extracellular organic matter, which may increase with stress.[28,59,60] It has also been reported that brown and green algae release higher amounts of polyphenols than do red algae[28] which was most probably accounted for the relatively much lower percent of metamorphosis and survival of juvenile urchins in treatments with these algae than did red algae.[28] Similarly, other studies have determined that the brown algae and green seagrass can seasonally produce several detergents such as condensed tannins and phenolic compounds, and thus, upsurge toxicity or decrease tastiness for herbivores, indicating the decline in nutritive value[61-63] and therefore, was perhaps the central key factors for restricting the ingestion of S. polysystum and E. acoroides by the juveniles and adults of S. sphaeroides in our experiments.

It is evident that the highest growth, gonad production and survival of S. sphaeroides were achieved from the sea urchins fed with red alga (T1) than those with brown alga (T2) and green seagrass (T3) in this order. This is the first successful approach to culture the high-valued tropical sea urchin, S. sphaeroides for 2 years in a captive aquaria-rearing condition. Due to the severe environmental perturbations and man-induced hazards in marine habitats, breeding, feeding, and living ground have been drastically degraded for this valuable sea urchin fishery in Malaysia. In these circumstances, the production of adequate quantities of sexually matured adult sea urchins using our current findings might be helpful toward the development of sustainable aquaculture and biodiversity conservation of S. sphaeroides. More researches are also acclaimed to search out more accurate seed production techniques, stocking densities, feeding regimes, and culture protocols of this high-valued sea urchin fishery to a greater extent.

ACKNOWLEDGMENTS

Our most sincere gratitude and appreciations are due to the Ministry of Science, Technology and Innovation, Malaysia for allocating funds through Research Management Center of Universiti Putra Malaysia (UPM) with the “ScienceFund” Project 04-01-04-SF2227 for successfully carryout this work. We would also like to extend our earnest thanks to the head, science officers, researchers and students of the Marine Biotechnology Laboratory, Institute of Bioscience, UPM for their many helps and cooperation during the entire experiment.

REFERENCES

1.  Lane DJ, Marsh LM, Vandenspiegel D, Rowe FW. Echinoderm fauna of the South China Sea:An inventory and analysis of distribution patterns. Raffles Bull Zool Suppl 2000;8:459-93.

2.  Schoppe S. AGuide to Common Shallow Water Sea Stars, Sea Urchins, Sea Cucumbers and Feather Stars (Echinoderms) of the Philippines. Singapore:Times Publishing Group;2000.

3.  Miskelly, A. Sea Urchins of Australia and the Indo-Pacific. Sydney, Australia:Capricornica Publications;2002.

4.  Tan LW, Ng PK. AGuide to Seashore Life. Singapore:The Singapore Science Centre;1988.

5.  Rahman MA, Yusoff FM, Arshad A, Shamsudin MN, Amin SM. Embryonic, larval, and early juvenile development of the tropical sea urchin, Salmacis sphaeroides (Echinodermata:Echinoidea). Sci World J 2012:1-9.

6.  Rahman MA, Yusoff FM, Arshad A, Amin SM, Shamsudin MN. Population characteristics and fecundity estimates of short-spined white sea urchin, Salmacis sphaeroides (Linnaeus, 1758) from the coastal waters of Johor, Malaysia. Asian J Anim Vet Adv 2013a;8:301-8.

7.  Tan LW, Ng PK.AGuide to Seashore Life. Revised Edition. Singapore:Singapore Science Centre;1992. p. 160.

8.  Klummp DW, Salita-Espinosa JT, Fortes MD. Feeding ecology and trophic role of sea urchins in a tropical seagrass community. Aquat Bot 1993;45:205-29.

9.  Ng CS, Toh TC, Toh KB, Guest J, Chou LM. Dietary habits of grazers influence their suitability as biological controls of fouling macroalgae in ex situ mariculture. Aquac Res 2014;45:1852-60.

10.  Tsuchiya M, Nishihira M, Poung S, Choohabandit S. Feeding behavior of the urchin-eating urchin Salmacis sphaeroides. Galaxea J Coral Reef Stud 2009;11:149-53.

11.  Parvez MS, Rahman MA, Yusoff FM, Arshad A. Status, prospects and potentials of the commercially important species of sea urchin, Tripneustes gratilla (Linnaeus 1758) in Malaysia. Int J Biol Ecol Environ Sci 2016;5:50-4.

12.  Lawrence JM, Olave S, Otaiza R, Lawrence AL, Bustos E. Enhancement of gonad production in the sea urchin Loxechinus albus in chile fed extruded feeds.JWorld Aquac Soc 1997;28:91-6.

13.  Rahman MA, Yusoff FM. Sea urchins in Malaysian coastal waters. Oceanographer 2010;4:20-1.

14.  Rahman MA, Uehara T, Arshad A, Yusoff FM, Shamsudin MN. Absence of postzygotic isolating mechanisms:Evidence from experimental hybridization between two species of tropical sea urchins.JZhejiang Univ Sci B 2012b;13:797-810.

15.  Rahman MA, Arshad A, Yusoff FM. Captive breeding, seed production, grow-out culture and biomedicinal properties of the commercially important sea urchins (Echinodermata:Echinoidea). Int J Adv Chem Eng Biol Sci 2014a;1:187-92.

16.  Rahman MA, Yusoff FM, Arshad A. Potential and prospect for sea urchin resource development in Malaysia. Fishmail 2014b;21:16-8.

17.  Hagen NT. Echinoculture:From fishery enhancement to closed-cycle cultivation. World Aquac 1996;27:6-19.

18.  Shimabukuro S. Tripneustes gratilla (Sea Urchin). In:Shokita S, Kakazu K, Tomomi A, Toma T, Yamaguchi M, editors. Aquaculture in Tropical Areas. Tokyo, Japan:Midori Shobo Co. Ltd.;1991. p. 313-28.

19.  Chen GQ, Xian WZ, Lau CC, Peng J, Qiu JW, Chen F, Jiang Y.Acomparative analysis of lipid and carotenoid composition of the gonads of Anthocidaris crassispina, Diadema setosum and Salmacis sphaeroides. Food Chem 2010;120:973-7.

20.  Dincer T, Cakli S. Chemical composition and biometrical measurements of the Turkish sea urchin (Paracentrotus lividus, Lamarck, 1816). Crit Rev Food Sci Nutr 2007;47:21-6.

21.  Pulz O, Gross W. Valuable products from biotechnology of microalgae. Appl Microbiol Biotechnol 2004;65:635-48.

22.  Lawrence JM. Edible Sea Urchins:Biology and Ecology. Boston, USAL:Elsevier;2007.

23.  Andrew NL, Agatsuma Y, Ballesteros E, Bazhin AG, Creaser EP, Barnes DK, et al. Xiaoqi status and management of world sea urchin fisheries. Oceanogr Mar Biol Ann Rev 2002;40:343-425.

24.  Andrew NL, Agatsuma Y, Dewees CM, Stotz WB. State of sea-urchin fisheries 2003. In:Lawrence JM, Guzma´n O, editors. Sea Urchin Fisheries and Ecology. Lancaster, PA, USA:DE Stech Publications;2004. p. 96-8.

25.  Molla HR, Islam MS, Rahman MA, Lee SG, Jahan B, Iqbal J. An assessment of geo-morphology and hydro-biological factors of major wetlands of Bangladesh. Water Sci Technol 2018;78:578-87.

26.  Yulin L. The echinoderm fauna of Hainan Island. In:Morton B, editor. Proceedings of the Third International Conference on the Marine Biology of the South China Sea. Hong Kong:Hong Kong University Press;1998. p. 75-82.

27.  Rahman MA, Uehara T, Aslan LM. Comparative viability and growth of hybrids between two sympatric species of sea urchins (genus Echinometra) in Okinawa. Aquaculture 2000;183:45-56.

28.  Rahman MA, Uehara T. Induction of metamorphosis and substratum preference in four sympatric and closely related species of sea urchins (Genus Echinometra) in Okinawa. Zool Stud 2001;40:29-43.

29.  Rahman MA, Uehara T, Lawrence LM. Growth and heterosis of hybrids of two closely related species of Pacific sea urchins (Genus Echinometra) in Okinawa. Aquaculture 2005;245:121-33.

30.  Rahman MA, Uehara T, Pearse JS. Experimental hybridization between two recently diverged species of tropical sea urchins, Echinometra mathaei and Echinometra oblonga. Invertebr Reprod Dev 2004;45:1-14.

31.  Rahman MA, Uehara T, Pearse JS. Hybrids of two closely related tropical sea urchins (genus Echinometra):Evidence against postzygotic isolating mechanisms. Biol Bull 2001;200:97-106.

32.  Stirling HP. Chemical and biological methods of water analysis for aquaculturists. Inst Aquac Univ Stirling 1985;p 119.

33.  APHA. Standard Methods for the Examination of Water and Wastewater. Washington DC:American Public Health Association;1992.

34.  Brown ME. Experimental studies on growth. In:Brown ME, editor. The Physiology of Fishes, Vol. 1. New York, USA:Academic Press;1957. p. 361-400.

35.  De Silva SS, Anderson TA. Fish Nutrition in Aquaculture. London:Chapman and Hall Aquaculture Series;1995.

36.  Lamare MD, Stewart BG. Mass spawning by the sea urchin Evechinus chloroticus (Echinodermata:Echinoidea) in a New Zealand fiord. Mar Biol 1998;132:135-40.

37.  Meidel SK, Scheibling RE. Annual reproductive cycle of the green sea urchin, Strongylocentrotus droebachiensis, in differing habitats in Nova Scotia, Canada. Mar Biol 1998;131:461-78.

38.  Walker CW, Lesser MP. Manipulation of food and photoperiod promotes out-of-season gametogenesis in the green sea urchin, Strongylocentrotus droebachiensis:implications for aquaculture. Mar Biol 1998;132:663-76.

39.  Bartlett MS. Some examples of statistical methods of research in agriculture and applied biology.JRoyal Stat Soc Suppl 1937;4:137-70.

40.  Grosjean PH, Spirlet CH, Jangoux M. Experimental study of growth in the echinoid Paracentrotus lividus (Lamarck 1816) (Echinodermata).JExp Mar Biol Ecol 1996;201:173-84.

41.  Alsaffar AH, Lone KP. Reproductive cycle of Diadema setosum and Echinometra mathaei (Echinoidea:Echinodermata) from Kuwait (Northern Arabian Gulf). Bull Mar Sci 2000;67:845-56.

42.  Chen W, Zhao Y, Wang J, Tong S. Mineral element and protein levels of the sea urchin Strongylocentrotus intermedius and its diets.JDalian Fish Coll 2000;15:41-4.

43.  Kennedy EJ, Shawn MC, Robinson G, Parsons J, Castell JD. Effect of dietary minerals and pigment on somatic growth of juvenile green sea urchins, Strongylocentrotus droebachiensis.JWorld Aquac Soc 2007;38:36-48.

44.  Sarifudin M, Rahman MA, Yu SH, Yusoff FM, Arshad A. Salinity effects on the embryonic and larval development of the tropical species of Indo-Pacific sea urchin, Salmacis sphaeroides (Linnaeus, 1758). In:Rahman MA, Muzenda E, editors. Proceedings of the International Conference on Agriculture, Food and Environmental Engineering. Kuala Lumpur, Malaysia:Planetary Scientific Research Centre;2014. p. 96-8.

45.  Asia BF. Optimizing prepared feed ration for somatic growth and gonad production of the sea urchin Tripneustes gratilla (Linnaeus, 1758). Asian Fish Sci 2009;22:71-84.

46.  Islam MS. Evaluation of supplementary feeds for semi-intensive pond culture of mahseer, Tor putitora (Hamilton). Aquaculture 2002;212:263-76.

47.  Kohinoor AH, Begum M, Hussain MG. Culture potentials of gulsha (Mystus cavasius) in monoculture management under different stocking densities. Bangladesh J Fish Res 2004;8:95-100.

48.  Rahman MA, Zaher M, Azimuddin KM. Evaluation of growth, survival, and production of an endangered fish, Labeo gonius (Hamilton) fingerlings in earthen nursery ponds.JAppl Aquac 2008a;20:62-78.

49.  Rahman MA, Yeasmine S, Khan MM. Growth, survival and production of a threatened silurid catfish, Ompok pabda (Hamilton) fingerlings in nursery ponds. Malays Appl Biol 2008b;37:47-56.

50.  Rahman MA, Arshad A, Amin SM. Evaluation of growth and production of the threatened giant river catfish, Sperata seenghala (Sykes) in polyculture with indigenous major carps. Afr J Biotech 2011a;10:2999-3008.

51.  Rahman MA, Azimuddin KM, Yeasmine S. Polyculture of a critically endangered olive barb, Puntius sarana (Ham), with indigenous major carps in earthen ponds.JWorld Aquac Soc 2011b;42:778-88.

52.  Rahman MA, Zaher M, Azimuddin KM, Yeasmine S, Khan MM, Arshad A. Stocking density effects on growth and production of the threatened silurid catfish, Mystus cavasius (Hamilton) fingerlings in nursery ponds. Aquac Res 2013b;44:1132-9.

53.  Rahman MA, Arshad A, Yusoff FM, Amin SM, Marimuthu K, Ara R. Development of captive breeding and seed production techniques for giant river catfish Sperata seenghala.NAm J Aquac 2014c;76(2):97-103.

54.  Steinberg PD. The effects of quantitative and qualitative variation in phenolic compounds on feeding in three species of marine invertebrate herbivores.JExp Mar Biol Ecol 1988;120:221-37.

55.  Kenner MC. Population dynamics of the sea urchin Strongylocentrotus purpuratus in a central California kelp forest:Recruitment, mortality, growth, and diet. Mar Biol 1992;112:107-18.

56.  Sonnenholzner JI, Montaño-Moctezuma G, Searcy-Bernal R, Salas-Garza A. Effect of macrophyte diet and initial size on the survival and somatic growth of sub-adult Strongylocentrotus purpuratus:Alaboratory experimental approach.JAppl Phycol 2011;23:505-13.

57.  Mattson WJ Jr. Herbivory in relation to plant nitrogen content. Annu Rev Ecol Evol Syst 1980;11:119-61.

58.  Neighbors MA, Horn MH. Nutritional quality of macrophytes eaten and not eaten by two temperate-zone herbivorous fishes:Amultivariate comparison. Mar Biol 1991;108:471-6.

59.  Sieburth JM. Studies on algal substances in the sea. III. The production of extracellular organic matter by littoral marine algae.JExp Mar Biol Ecol 1969;3:290-309.

60.  Kroes HW. Excretion of mucilage and yellow-brown substances by some brown algae from the intertidal zone. Bot Mar 1970;13:107-110.

61.  Zapata O, McMillan C. Phenolic acids in seagrasses. Aquat Bot 1979;7:307-17.

62.  Goecker ME, Heck Kl Jr., Valentine JF. Effects of nitrogen concentrations in turtle grass Thalassia testudinum on consumption by the bucktooth parrotfish Sparisoma radians. Mar Ecol Prog Ser 2005;286:239-48.

63.  Iken K, Dubois A. Kelp-Grazer Interactions in Kachemak Bay, Alaska:Grazing Activity and Chemical Defenses and Resource Allocation in Selected Kelp Species. Anchorage, AK:Northern Pacific Research Board Final Report;2006. p. 90.