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Author:
Sam Boarder & Muki
Shpigel
Institution:
Fremantle Maritime Centre,
Western Australia & National Centre for Mariculture, Israel, 1999
Title:
Comparative performances of juvenile
Haliotis roei fed
on enriched Ulva rigida and various artificial diets
SAM J. BOARDER 1 and MUKI SHPIGEL
2
1 Fremantle Maritime Centre: 1 Fleet Street FREMANTLE WESTERN
AUSTRALIA
2 Israel Oceanographic and Limnological Research; National
Centre for Mariculture: PO BOX
1212 EILAT ISRAEL
Abstract
Growth rates of juvenile Haliotis
roei fed inorganically enriched Ulva rigida were compared with growth
achieved on various artificial diets. Juvenile abalone (20-40mm S.L.) were
collected from reef platforms off the Perth (Western Australia) metropolitan
area and assigned to one of seven different dietary treatments. All diets were
fed ad libitum (3% b.w. day –1) every second day and growth
rates were quantified over a three month period. Specific growth rate (SGR) for
both shell length and whole body weight indicated that growth of abalone fed
enriched Ulva was not significantly different (p>0.05) to
growth achieved from the best performing artificial diets.
A 96-h salinity stress test was also conducted on all treatments to assess
the effects of diet on stress resistance. Diet significantly effected survival
at 20‰, with the Ulva fed animals exhibiting decreased tolerance to
hypo-osmotic conditions (p<0.05). This may have been caused by an
interference with the cell volume regulatory mechanisms normally utilised by Haliotis
spp.
Enrichment of wild U. rigida increased the algal protein content from
11.4±2% (dry weight) to 32.2±1.5%, perhaps partially explaining the difference
in performance between this and other abalone feed trials utilising Ulva.
Results indicate that enriched U. rigida is a suitable feed for H. roei, providing similar growth to that achieved from several commercially
available diets.
Key words: abalone,
Haliotis roei, Ulva rigida, nutrition, salinity tolerance
Introduction
The main
constituent of aquaculture effluent is ammonia and phosphate, with ammonia known
to be the main contributor to marine eutrophication when added to an
oligotrophic marine environment (Dosdat et al., 1995; Wu, 1995; Lemarie,
1998). Many shore-based aquaculture facilities utilise sedimentation ponds to
remove particulate matter but ignore dissolved inorganics such as ammonia (NH3/NH4+)
and phosphate (PO43-) due to the difficulty of their
removal from high volumes of water. Use of macroalgal biofilters has been shown
to remove a large proportion of the dissolved nitrogen from aquaculture effluent
when integrated into intensive fish culture systems (Neori et al., 1996; Shpigel
et al., 1996a). Species of sea lettuce (Ulva spp.), have been shown to
remove up to 90% of dissolved nitrogen from aquaculture effluent (Neori et al.
1989). Research in Israel has also shown that culture of Ulva spp. in
nutrient rich waters increases their protein content from 11-13% to over 35% of
the dry weight (Shpigel et al., 1999). This enriched Ulva has been shown
to provide good growth rates for Haliotis tuberculata (Neori et al.,
1998; Shpigel et al., 1999), and Haliotis discus hannai (Corazani and
Illanes, 1998; Shpigel et al., 1999). Aquaculturists may be enticed to adopt
effluent treatment procedures more readily if shown that enriched Ulva
can also be used as a feed for abalone species.
Stress tests
have previously been utilised as an assessment of general health or vigour in
several aquatic species (Dhert et al., 1990a; Dhert et al., 1990b; Briggs, 1992;
Boarder and Maguire, 1998; Samocha et al., 1998). Abalone are osmoconformers and
possess only limited osmoregulatory capabilities, thus the effects of salinity
fluctuations directly effect internal ionic composition (Brix, 1983; Somero and
Bowlus, 1983). It has been shown previously that dietary history can directly
effect resistance to low salinity in abalone (Boarder and Maguire, 1998).
This trial was
conducted to assess the suitability of enriched Ulva rigida
as a feed for Haliotis roei and to compare growth rates of this diet with
growth rates on various artificial diets.
Materials and
Methods
H. roei
were collected from limestone reef platforms in the Perth Metropolitan area in
March 1999. Abalone were gently removed from the reef-top and were immediately
placed into aerated seawater for transport. All animals were tagged (Hallprint
Pty Ltd; FPN shellfish tags) and then randomly distributed to 28 trial tanks
after being weighed to the nearest 0.01 g (whole wet body weight; WWBW) and
measured with manual calipers (0.1mm accuracy). The initial mean length and
weight of the abalone were 31.9 ± 4.3 mm and 6.17 ± 2.28 g (mean ± SE) (n =
560).
Trial System
Abalone
were kept in rectangular 27 L plastic aquaria with artificial grass strips above
the water line to prevent abalone from climbing out of the tanks. Twenty abalone
were allocated to each trial tank (4 replicates per diet) and all 28 tanks were
arranged randomly in relation to experimental diet. The system was flowthrough
and utilized a seawater bore as the water source. The flow rate to each tank was
maintained at 1 L min-1 and checked weekly. Water quality parameters
(D.O., pH and temperature) were randomly measured during each feed with
systematic analyses made in each tank weekly.
Diets used in
this trial are listed in Table 1. All artificial diets were commercially
available (with the exception of the FRDC2 control diet) and enriched Ulva
was grown in high nutrient water (5 g N m-2 day-1; 0.6 g P
m-2 day-1) on inorganic nutrients (NH4Cl and Na2HPO4)
in accordance with Shpigel et al., (1999). The abalone were fed 3% b.w./day,
which is in excess of requirements for greenlip abalone, H. laevigata
(Tom Coote, 1999 pers. comm.). Tanks were cleaned by siphon every second day.
Feed rates for Ulva were calculated on a dry weight basis. This was based
on enriched Ulva possessing a water content of 84%. The control diet,
known as the FRDC2 formulation, was made available by the Fisheries Research and
Development Council (FRDC). The dry ingredients included fishmeal, soyflour,
semolina, sodium alginate and CaCO3. The Deakin diet (Diet 6), and
Adam and Amos (Diet 2) diet were both commercially available within Australia.
Haliogro (Diet 5) was from New Zealand and AB-feed (Diet 4) from
South Africa. It must be noted that none of the diets used in this trial were
specifically formulated for H. roei.
Analysis of U.
rigida
Proximate
analysis of U. rigida was undertaken throughout the trial to quantify
moisture, ash, protein (nitrogen x 6.25), fat and carbohydrate levels. Moisture
content was determined by gravimetric weight loss on heating the samples to a
constant weight at 105oC (AOAC method number 950.46B). Ash was
determined by gravimetric weight loss on ashing the samples in a muffle furnace
at 550oC (AOAC method number 920.153). Analysis of nitrogen content
utilised the Kjeldahl method (AOAC method number 928.08) and fat/lipid levels
were determined via acid hydrolysis and solvent extraction (AOAC method number
950.54).
Consumption
analyses
Consumption was
assessed twice during the trial by manually siphoning uneaten feed from tanks.
Consumption was estimated by relating the dry weight of the uneaten food to the
known dry weight of the feed provided. Consumption data were corrected for dry
matter weight loss due to leaching by leaching all diets over a period of 48
hours and drying to a constant weight. Consumption estimates involved the
collection of all uneaten food prior to cleaning on the second day of the
feed/clean cycle, through manual siphon onto 100 µm mesh screen. Collected feed
was carefully washed onto a circular filter mesh for drying and weighing. Feed
was dried at 55-60oC for a period of two days prior to weighing. This
procedure was conducted on two occasions over the duration of the trial.
Salinity
Stress Test
A 96-hour stress
test for overall health was conducted to assess if diet had effected abalone
health. Salinities for the stress test were derived from a preliminary
assessment of salinity tolerance for H. roei and the limited literature
regarding salinity tolerances of abalone (Nakanishi, 1978; Mgaya and Mercer,
1994; Jarayabhand and Paphavasit, 1996; Boarder and Maguire, 1998). Abalone were
held in PVC cages (see Harris et al., 1997) and acclimatised in full strength
seawater for 4 days (Boarder and Maguire, 1998). Twelve abalone were randomly
assigned to each cage. Upon acclimation, one cage from each diet was suspended
vertically within an aerated 1000-L tank of a particular salinity. Salinities
used were 35‰, 25‰ and 20‰ and each salinity was replicated twice. Cages
were checked every 4 hours for 96 hours by lifting the cage clear of the water
and gently shaking. Abalone no longer attached to the cage and non-responsive to
touch on the mantle were classified as mortalities. Animals responsive to touch
and not attached to the cage were recorded as detachments and returned to the
cages.
Results
Growth
As measured by
either whole weight (P<0.05) or by shell length (P<0.01), specific growth
rate (SGR) was significantly affected by diet. Growth rates for H. roei
fed inorganically enriched U. rigida (D3) were not significantly
different (Tukey test, P>0.05) to growth achieved from the best performing
artificial diets. The abalone grew best on the Adam and Amos (D2) diet for both
length and weight (SGR-L = 0.161 ± 0.004; SGR-W = 0.495 ± 0.2). However,
growth was not significantly higher than on the FRDC2 (SGR-L = 0.139 ± 0.006;
SGR-W = 0.371 ± 0.035), Ulva (SGR-L = 0.142 ± 0.010; SGR-W = 0.379 ±
0.040) or AB-feed (SGR-L = 0.131 ± 0.006; SGR-W = 0.4113 ± 0.014) diets. This
is shown in Figures 1 and 2, respectively.
Consumption
analyses
Consumption rate
was significantly affected (P<0.01) by diet for both consumption assessments.
The two consumption analyses were also significantly different from each other
(p<0.01), as shown in Figure 3. Diets 2, 5, 6 and 7 were all observed to be
less water stable than Diets 1, 3 and 4 after two days within the treatment
tanks.
Salinity Stress
Test
Abalone held in
full strength seawater and 25‰ salinity exhibited 100% survival at the
conclusion of the 96 hour trial, with the exception of abalone fed on Diet 3
which exhibited 92% survival over the same period in 25‰. Detachment rates for
both salinities were negligible for all diets at the higher salinities.
Diet
significantly affected survival at 20‰ (P<0.05). No abalone fed Diet 3
(enriched Ulva) survived in 20‰ after 96-h (Figure 4). Survival was
significantly the same for all other diets (Tukey test; P>0.05), with an
average survival of 40.28 ± 4.33%. Diet 3 was not included in the ANOVA due to
zero variance caused by 0% survival. Mortality on Diet 3 was also observed
earlier than all other diets (Table 2). Fifty percent of all animals fed
enriched Ulva died after 68 hours, compared with an average of 9.73 ±
2.06% for abalone fed other diets over the same time period. Most other diets
reached 50% mortality after approximately 85 hours, almost 20 hours later than
the Ulva fed abalone (Table 2). Abalone fed Diet 3 were also observed to
detach earlier than other diets.
Discussion
Growth rates of H.
roei fed enriched U. rigida were not significantly different from
growth rates achieved on the three best performing artificial diets (p>0.05).
Previous growth trials with Ulva sp. as a feed for abalone species have
utilised "wild" Ulva or Ulva that has not been enriched
(Mai et al., 1994; Mai et al., 1996; Simpson and Cook, 1998). These growth
trials have shown the effectiveness of Ulva as a feed to be totally
dependent on the abalone species to which it is being fed. Mai et al. (1996)
found that, although wild U. lactuca was a "moderately good
diet" for H. tuberculata, it was the worst of five diets for H.
discus hannai. Corazani and Illanes (1998) showed that H. discus hannai
grew significantly faster on Ulva rigida than on other macroalgal diets
and the authors recommend juvenile abalone of this species be fed a diet of Ulva
sp. in combination with an artificial diet. They felt that the artificial
component of the diet was a supplement to the Ulva sp. and should be fed
at levels no higher than 1% of total body weight day-1.
Simpson and Cook
(1998) investigated the growth of H. midae grown on various natural algal
diets. They found that after 4 months on trial diets, abalone fed on a diet of
wild Ulva spp. were significantly shorter in shell length than
abalone fed on most other macroalgal diets. Ulva fed animals were also
found to have the lowest wet weight to shell length ratios. However, when the
animals were fed Ulva as a proportion of a mixed diet they exhibited
excellent growth rates suggesting that Ulva provided essential nutrients
not found in the other algae fed.
The increase in
protein content of U. rigida observed within this trial is supported by previous
research in which Ulva spp. have been utilised as macroalgal biofilters (Tenore,
1976; Neori, 1996; Shpigel et al., 1996a; Shpigel et al., 1996b). In the current
trial, wild U. rigida was found to have a protein content of 13% (% dry
weight), compared with 32.2±1.5% (% dry weight) for Ulva which had been
enriched on inorganic nutrients. The high protein content of the Ulva
throughout the trial could explain the differences observed between the growth
achieved on wild Ulva spp. in other research and the growth achieved
within this trial. Fleming (1995) found that the intake of digestible nitrogen
directly influences the growth rates of H. rubra. This suggests that
nitrogen may be a limiting factor for growth in Haliotis spp. Britz and
Hecht (1997) support this view by stating that maximum growth can only be
achieved when sufficient protein, in the correct proportions of amino acids, is
supplied in the feed. Shpigel et al. (1996a; 1999) state that the good growth of
H. tuberculata and H. fulgens when fed enriched U. lactuca was due to consistent supply of high protein diet.
The consumption
results in this study do not adequately reflect the trends observed within the
tanks. Some diets were observed to be more water stable than others and thus
were easier to fragment upon siphoning for collection. Diets 1 and 4 (FRDC2 and
AB-feed) were both extremely water stable within the tank and thus held together
well through the siphoning collection process. Diets 2, 5 and 6 (Adam &
Amos, Haliogro and Deakin) were less water stable, but were still firm after two
days. These diets fragmented when they were siphoned, as did Diet 7, which was
very soft after 2 days within the tanks. The data was potentially biased against
diets 1, 3 and 4 because of the fragmentation of other diets causing some loss
of material during analysis. This would have reduced the amount of feed actually
collected thus increasing the apparent consumption. Differences in the various
diets water stability may be due to the diets being formulated for colder water
species.
Stress
determination for aquatic animals usually involves a quantitative evaluation of
a variable that is directly affected by the stressor. The application of an
environmental stress allows an assessment of general health or vigour for
animals from different treatments. Salinity stress tests have been used
previously to determine the quality of prawn post-larvae (Briggs, 1992; Samocha
et al., 1998), fish larvae (Dhert et al., 1990a; Dhert et al., 1990b) and the
effects of diet on abalone robustness (Boarder and Maguire, 1998). Boarder and
Maguire (1998) found that dietary vitamin levels directly determined the
survival of H. laevigata at 23‰ salinity. Animals fed on twice the
normal dietary inclusion level of vitamin mix exhibited over 90% survival after
96 hours, compared with approximately 50% survival for animals fed the normal
dietary vitamin level.
The poor
survival at 20‰ for abalone fed U. rigida within this trial may be due
to the osmoregulatory mechanisms utilised by Haliotis spp. rather than a
general lack of health. Abalone species are known ionic conformers and thus
blood osmolality and ionic concentration closely resembles that of the external
environment (Somero and Bowlus, 1983). The ability to regulate cell volume is
also an important ability in soft-bodied osmoconforming marine animals (Tarr,
1976; Burton, 1983) as this prevents cells rupturing upon exposure to low
salinities. Cell volume regulation within some osmoconforming molluscs is
controlled by organic solutes, such as amino acids (Burton, 1983; Mai et al.,
1994). At low salinities, amino acids are excreted from the cell along with
osmotically obligated water thus restoring cell volume (Pierce and Amende,
1981). Pierce and Amende (1981) state that there is a possibility that the
physiological response of osmoconforming molluscs to low salinity may be
directly related to the ability to maintain and control a large intracellular
free amino acid pool.
The most
important free amino acids for cell volume regulation (dependant on abalone
species) are taurine, glycine, alanine and proline with an emphasis on taurine
(Burton, 1983). Biosynthesis of the amino acid taurine from methionine is known
to occur in gastropod molluscs (Mai et al., 1994). Mai et al. (1994) found that
the levels of taurine in the viscera of H. discus hannai were
significantly lower in abalone fed wild U. lactuca than abalone fed on
all other diets. The authors also found that the viscera methionine levels
within the abalone fed U. lactuca were extremely high, indicating
some physiological inhibition in the biosynthesis of taurine from methionine.
Toxic substances contained within U. lactuca, as detailed by Borowsky and
Borowsky (1990), were thought to cause this inhibition. Johnson and Welsh (1985)
found that an exudate excreted from U. lactuca killed 100% of estuarine
crab larvae within 24 hours. The authors also report that the bactericidal and
fungicidal properties of Ulva spp. exudate have been known for some time.
As taurine is
one of the most important amino acids for cell volume regulation, inhibition of
taurine production from methionine could significantly effect the cell volume
regulation ability of abalone fed solely on Ulva spp. The comparatively
good growth observed in H. roei fed U. rigida within this trial
indicates that there was no feeding inhibition caused by anti-nutritional
compounds or toxic substances contained within the seaweed. Fleming (1995) found
that anti-nutritional compounds within some algal species did not prevent
preferences for algae containing high levels of digestible nitrogen. This
suggests that although the abalone fed on enriched U. rigida were capable
of good growth, they were not capable of adequate cell volume regulation when
exposed to hypo-osmotic conditions because of a lack of taurine within their
free amino acid pool. It is important to note that all other health parameters
(including growth) were excellent for abalone fed solely on enriched U.
rigida.
The results of
this trial indicate the salinity tolerance of H. roei to be between 25
and 20 ‰. This correlates closely with the limited literature on Haliotid
salinity tolerances, which indicate short-term survival is possible at
salinities around 20 ‰ (Singharaiwan et al., 1992; Jarayabhand and Phapavisit,
1996; pers. comm. T. McCormick, 1997; Boarder and Maguire, 1998). The 96-h LS50,
the salinity at which 50% of the test animals survive after 96-h, is relatively
close to 20 ‰ for H. roei. Most diets displayed 50% survival at just
under 96-h within this trial. This compares with only 10% survival after 96-h
for H. diversicolor supertexta juveniles transferred from 35 ‰ to 20
‰ at similar temperature (Chen and Chen, 2000).
In conclusion,
enriched U. rigida is a suitable feed for H. roei, producing
comparable growth rates to several commercially available manufactured feeds.
Diet directly effects survival of abalone under hypo-osmotic stress and U.
rigida may impair the ability to cope with this stress by effecting cell
volume regulatory mechanisms.
ACKNOWLEDGEMENTS
We thank the
Natural Heritage Trust – Coasts and Clean Seas, South Metropolitan College of
TAFE, Fisheries WA and the Aquaculture Development Fund for funding this
project. We also thank Mr. Arron Strawbridge for technical assistance and Mr.
Gavin Partridge for reviewing the manuscript.
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Table 1.
|
Treatment |
Diet |
Protein content
(% dry weight) |
|
1 |
FRDC 2 - Authors |
35 |
|
2 |
AAFDG - Adam and Amos |
27 |
|
3 |
Enriched Ulva rigida |
32.2 |
|
4 |
Abfeed – Sea Plant
Products |
34.6 |
|
5 |
Haliogro – E.N.
Hutchinson |
30.0 |
|
6 |
Deakin Diet – Marine
Feeds |
- |
|
7 |
Diet 7 - confidential |
- |
Note: feed manufacturers are listed in italics.
Table 2.
Effects of diet on time (hours ±
S.E.) taken to reach 50% mortality for juvenile H. roei held at 20‰
salinity (n = 2; 12 abalone per replicate). Note: Diets sharing the same
letters are not significantly different (P>0.05).
|
Diet |
1 |
2 |
3 |
4 |
5 |
6 |
7 |
|
L50Time @ 20 ‰ |
84±4ab |
86±2a |
68±4b |
82±2ab |
88±4a |
86±2a |
>96 |
Figures
1 - 4
Click
on figure for enlargement

Figure 1. Effect of diet on specific
growth rate for length (mm) for juvenile Haliotis roei (n=4).
Note:
Diets sharing the same letters are not significantly different (Tukey test,
P>0.05).

Figure 2. Effect of diet on specific growth rate
for weight (g) for juvenile Haliotis roei (n=4).
Note:
Diets sharing the same letters are not significantly different (Tukey test,
P>0.05).

Figure 3. Effect of diet on consumption rate
(grams dry feed consumed/gram tank biomass) for juvenile Haliotis roei
at two separate sampling times (n=4).
Note:
Diets sharing the same letters are not significantly different (Tukey test,
P>0.05). 
Figure 4. Effect of diet on survival after 96
hours at 20 ‰ salinity for juvenile H. roei (n=2; 12 abalone per
replicate). Note:
Diets sharing the same letters are not significantly different (Tukey test,
P>0.05).
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