DISCUSSION
This experiment indicates that the C.
lentillifera under a light density of 20 μmol
photons m-2.s-1 had almost no Lyngbya sp.
present on their branches after 28 days. In
addition, new branches were emerging along
the stolons. On the opposite, the seaweeds
under a light density of 40 were covered by
Lyngbya sp. and about to die at the end of the
experiment. In fact, C. lentillifera from the
first group was longer, heavier, and had a
better SGR than the second group. In
particular, during the 4th week, we found an
SGR of 4.5%d-1. This result is consistent with
the study of Guo et al., [12] for the same
temperature. Their final length and weight
were greater than the initial ones. Those
seaweeds have overcome the presence of
Lyngbya sp. and will keep growing.
The Lyngbya sp. occurred during the time
between two measures, so we cannot say
whether it had a quantitative effect on the
growth of C. lentillifera before the beginning of
the treatment. Still, the thalli appeared to be
weak, some ramuli became white. However,
even if the measures were taken just before its
occurrence, we might not have been able to
observe significant results because C.
lentillifera is mainly weakened on the longterm aspect.
During the experiment, we observed an
increase in the pH, particularly under the light
density of 40 μmol photons m-2.s-1. This is
linked to the fact that C. lentillifera and
Lyngbya sp. are both oxygenic photosynthetic
organisms and will use the CO2 in the seawater
to synthesize carbon. The depletion of the
cyanobacteria might be explained by the fact
that Lyngbya sp. cannot fix N2 under the dark
condition as found by Jones [17].
We also observed different phases of
variation of the SGR and obviously the weight.
In particular, the SGR was negative at the end
of the second week for both groups because the
weight decreased. But those observations were
not the same for the length, which kept
increasing at that moment. One explanation
could be the loss of some white-dead branches
during the second week, while the stolons kept
growing. But this might be not enough to
explain this event because we observed an
outcome of cyanobacteria in the same period.
This phenomenon could not be explained with
the data collected.
Nonetheless, this study may be useful in the
project of creating a new way of producing
seafood with C. lentillifera in tanks. If those
tanks were to be invaded by Lyngbya sp.,
reducing the light density with some nets might
be enough to eliminate those algae without
losing the production of C. lentillifera.
However, it might take some time before
witnessing the results.
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Vietnam Journal of Marine Science and Technology; Vol. 20, No. 3; 2020: 317–324
DOI: https://doi.org/10.15625/1859-3097/20/3/14880
Utilization of the light density to reduce the development of Lyngbya sp.
and their growth on Caulerpa lentillifera J. Agardh in a recirculating
aquature system
Florian Quemper
1
, Tien Duc Dam
2
, Linh Manh Nguyen
2,3
, Anh Thi Mai Nguyen
2
,
Hoang Nguyen
4
, Hung Manh Vu
2,*
1
lnstitut National Sup4rieur des Sciences Agronomiques, de I’Alimentation et de l’Environrement
(AgroSup Dijon). No. 26 Bd Dr Petitjean - BP 87999 21079 Dijon Cedex, France
2
Institute of Marine Environment and Resources, VAST, Vietnam
3
Graduate University of Science and Technology, VAST, Vietnam
4
Vietnam Centre of Science and Technology for Sea Culture, Hanoi, Vietnam
*
Corresponding E-mail: hungvm@imer.vast.vn
Received: 10 March 2020; Accepted: 15 June 2020
©2020 Vietnam Academy of Science and Technology (VAST)
Abstract
The release of pollutants is endangering ecosystems, biodiversity and seafood. Therefore, it is of the
requirement to create innovative methods in seafood production. Caulerpa lentillifera J. Agardh is a well-
known seaweed for its properties and edible. We cultured C. lentillifera in a recirculating aquaculture system
under laboratory conditions. However, after 7 days the culture was invaded by epiphyte algae Lyngbya sp.
This experiment was designed to remove those algae by using light density as a treatment. Two irradiances
were tested including 20 μmol photons m-2.s-1 (low light density) and 40 μmol photons m-2.s-1 (initial light
density). Every week we measured the stolon length, thallus weight, and calculated the specific growth rate.
Results showed that after 30 days C. lentillifera under low light density regained their healthy green color
and Lyngbya sp. was no longer present. Meanwhile, in the initial light density (40 μmol photons m-2.s-1)
Lyngbya sp. covered almost all thalli of C. lentillifera, and half of them were dead. The measured results of
specific growth rate (%d
-1
) and weight (g) of C. lentillifera in low light density conditions were better than
those of C. lentillifera in the initial condition. The light density, therefore, might be used as a treatment to
remove Lyngbya sp. from Caulerpa lentillifera in aquaculture.
Keywords: Caulerpa lentillifera, Lyngbya sp., light density, recirculating aquaculture system, seaweed culture.
Citation: Florian Quemper, Tien Duc Dam, Linh Manh Nguyen, Anh Thi Mai Nguyen, Hoang Nguyen, Hung Manh Vu,
2020. Utilization of the light density to reduce the development of Lyngbya sp. and their growth on Caulerpa lentillifera
J. Agardh in a recirculating aquaculture system. Vietnam Journal of Marine Science and Technology, 20(3), 317–324.
Florian Quemper et al.
318
INTRODUCTION
The current global warming, caused by
greenhouse gas emission, results in the rise of
ocean temperature and CO2 contribution to
ocean acidification. Besides, heavy metals are
absorbed by the seafood [1] and directly
involved consumers [2, 3]. Otherwise,
sustainable fisheries production is a major
challenge for the aquaculture industry. In
particular, there is the intensive use of
commercial feeds which, in turn, contributes to
an important issue in the open water system,
water pollution [4].
It is of necessity to develop novel methods
in seafood production to mitigate the negative
effects of effluents. Integrated systems might
be an approach to tackle these issues [4]. By
associating fish production, whose nutrients are
used to grow seaweeds cleaning the water and
producing biomass. Hence, wastes are
transformed into resources in those integrated
systems [5].
Caulerpa lentillifera J. Agardh could be
used in such a method. This seaweed, also
known as “sea grape”, is edible and commonly
consumed in a salad of vegetables. C. lentillifera
contains high amounts of minerals, proteins and
balanced amino acid (ref). It is also notably rich
in iodine phosphorus, calcium, magnesium,
copper; thereby highlighting its role as an
ingredient with high nutritional values and as a
healthy food for human diets [6]. Other studies
showed that the seaweed might even be used in
medicine as an anti-diabetic agent [7] and dye
industries [8, 9]. Besides those properties, C.
lentillifera has shown the potential ability to
remove nutrients from aquaculture effluent [10–
13] and heavy metals from wastewater [9, 14].
However, it has been documented that their
culture in ponds might become a problem
because they absorb heavy metals [3] and for
this reason, it might be interesting to culture
them in a controlled system.
To determine the best environmental
conditions for culturing this seaweed, the
growth of C. lentillifera was observed under
laboratory conditions. We tested a condition
(photoperiod of 10 h:14 h (light:dark) with 40
μmol photons m-2.s-1 at 27.5oC), described as
optimal for the asexual propagation of C.
lentillifera J. Agarhd by Guo [12]. In the first
days, the seaweed adapted quickly and was
healthy. Almost every thallus had a new branch
and rhizoids, their stolon became longer.
However, despite the controlled conditions,
Lyngbya sp. appeared, developed on it, and
quickly grew in a few days. Their development
had reduced the growth of C. lentillifera. In
nature, the problem caused by algae seriously
affects the yield of seaweed. It is a constraint of
seaweed farming, for example, the epiphytism
(Lyngbya sp.) had completely covered the raft
of Kappaphycus alvarezii farming in Tamil
Nadu, India [15]. The Lyngbya sp. is a benthic
cyanobacterium that is common and prevalent
in the shallow water of tropical and subtropical
marine areas including atolls, salt marshes and
estuary water [16].
Thus, the aquatic industrial and seaweed
farmer usually face benthic cyanobacterial
blooms. They lack information about the
treatment to limit the development and to
remove the Lyngbya sp. Jones (1990) showed
that Lyngbya sp. is incapable of nitrogen fixation
under dark conditions [17], while C. lentillifera
is able to develop under low light density [12].
Thus, we hypothesized that the Lyngbya sp. can
be treated under low irradiance. This study aims
to test our hypothesis by using the low light
density to treat and remove the Lyngbya sp.
from the seaweed culture in laboratory
conditions. To test this hypothesis, we set up
two conditions in different light densities: The
initial irradiance (40 μmol photons m-2.s-1) as a
control experiment and 20 μmol photons m-2.s-1
as a treatment condition. Our experiment expects
to find a solution to the problem caused by
benthic cyanobacteria without losing the
production of C. lentillifera.
MATERIAL AND METHODS
Material
Fresh Caulerpa lentillifera J. Agardh
(Chlorophytes) were sampled at a seaweed
pond culture in Ninh Hoa dist., Khanh Hoa
prov. in the Central Vietnam. The seaweeds
were transported by airplane (5 hours), stored
in an insulated container under the temperature
range from 23–25oC in a cool box. The
seaweed samples were kept in an aquarium
Utilization of the light density
319
tank (running water cycle) for 2 days to adapt
to the laboratory condition. The seawater (30.0
± 1.0‰ sanity) was filtered by the
phytoplankton net before use.
Methods
Green healthy seaweeds with a frond of 4
cm were selected and cut with 2 cm of stolon
(fig. 1) (N = 40).
Figure 1. Diagram of C. lentillifera and the initial dimension of the thalli chosen for the
experiment. F = fruit; Rh = root; S = stolon; Ra = branch
They were disposed in a bottle with 4 liters
of seawater under a photon flux density of 40
μmol photons.m-2.s-1 and a photoperiod of 10
h:14 h (light:dark) at 27–27.5oC. There were 5
samples per bottle. Seawater was changed once
a week. Measures were done daily. Irradiance
was measured with a waterproof light density
recorder HOBO data logger Pendant UA
Temp/Light; pH was measured daily with a
probe–pH (Okaton pH 11 series, Singapore).
After 10 days of development, Lyngbya sp.
was present on each thallus, mainly on the
branches of C. Lentillifera (fig. 2). Some thalli
of C. lentillifera became weak.
Figure 2. C. lentillifera was attacked by Lyngbya sp., (a) a branch of C. lentillifera after 10 days of
the experiment; (b) structure of Lyngbya sp. under a microscope
Florian Quemper et al.
320
We randomly distributed all the samples (N
= 40) under an irradiance of 20 μmol photons
m
-2
.s
-1
(low light density) for a treatment
condition and 40 μmol photons m-2.s-1 (initial
light density) with 5 samples per bottle.
We measured every 7 days the length of the
stolons, the weight of each sample and
calculated the specific growth rate (SGR) with
the following formula:
2
1
100
ln
W
SGR
W t
(1)
Where: W2: The weight measured; W1: The
previous weight measured; t: The difference of
time between the two measures (= t2 –t1).
Note: Before every measure of weight, the
water attached on the seaweed surface was
removed with absorbent paper.
The percentage of Lyngbya sp. attached on
Caulerpa lentillifera was calculated by the
ratio between the number of branch and root
of C. lentillifera, which were attached by
Lyngbya sp. and the total of branch and root of
each sample.
Statistical analysis
The data were tested with an unpaired two-
sided t-test. For each test, we compared the
mean of the samples under the two light density
conditions. At the end of the experiment, the
data were tested with a paired two-sided t-test
in order to compare the initial and final
measures of each group. If the assumption of
normality of the sample mean in both groups
could not have been made, we have used the
non-parametric equivalent of the two-sample t-
test: The Wilcoxon rank-sum test.
Differences obtained at a level of P < 0.05
indicated that it is significant. Analyses were
done using the software R (3.6.0).
RESULTS
SGR and weight
From the 21
st
day of culture until the end,
there was a significant difference among the
SGR of the group at light densities of 20–40 (W
= 212, P < 0.05 and W = 124, P < 0.05) and this
showed that the SGR of C. lentillifera was
better under a light density of 20 μmol photons
m
-2
.s
-1
. The same results were observed with
the weight, and the weight of C. lentillifera
under a light density of 20 μmol photons m-2.s-1
is greater (t = 2.8158, P < 0.05 and t = 5.0571,
P < 0.05). We also observed a difference
between the initial and final weights for both
groups and it showed that the C. lentillifera
under a light density of 20 μmol photons m-2.s-1
is heavier (W = 78, P < 0.05) while the other
group is lighter (t = 5.5196, P = 0.05).
Figure 3. Evolution of (a) specific growth rate (%d
-1
) and (b) weight (g) of C. lentillifera
cultivated in different irradiance (20 and 40 μmol photons.m-2.s-1) conditions for 28 days.
Error bars represent 95 % confidence intervals. N = 40 at (Day 10) and N = 20
for each condition at the beginning of the experiment (Day 0)
Utilization of the light density
321
We can distinguish 2 phases during their
growth: After one week of culture, both groups
studied still had a positive SGR around 4.5%d
-1
,
and then a negative SGR after the second week
(–4,5%d-1). Some branches from both groups
turned white and the growth of Lyngbya sp.
was more important. From this point the groups
of C. lentillifera had 2 different behaviors: the
weight of the group under a light density of 20
μmol photons m-2.s-1 increased, and obviously,
the SGR also increased and had
approximatively the same values as initially.
Meanwhile, the weight of the group of
seaweeds under the light density of 40 μmol
photons m
-2
.s
-1
has continued to decrease and
the SGR stayed negative around -5%d
-1
. After
21 days, new green and healthy branches were
emerging from the seaweeds of the first group.
No Lyngbya sp. was observed developing on it.
For the second group, most of the algae were
covered with Lyngbya sp., except the stolons.
After 28 days, C. lentillifera growing under a
light density of 20 μmol photons m-2.s-1 was
free of Lyngbya sp. For the second group, half
of the seaweeds were dead, and the remnant
branches were white.
Length
After 4 weeks, the C. lentillifera stolon
length under the two light density is
significantly different (t = 5.1181, P < 0.05)
and it showed that the C. lentillifera stolons
are longer under a light density of 20 μmol
photons m
-2
.s
-1
.
The final stolon length is more important
than the initial length
in both groups (P < 0.05).
During 28 days, the length of C. lentillifera
under a light density of 20 μmol photons m-2.s-1
increased until reaching a mean of 35.4 ±
7.38 cm (fig. 3), which is nearly 4 times longer
than the initial length. On the contrary, the
length of the seaweeds under the light density
of 40 μmol photons m-2.s-1 increased until the
21
st
day and then decreased and reached a mean
length of 16.0 ± 3.62 cm.
Figure 4. Evolution of length (cm) of C. lentillifera cultivated in different photon flux density
(20 and 40 μmol photons m-2.s-1) conditions for 28 days. Error bars represent 95%
confidence intervals. N = 40 at (Day 10) and N = 20 for each condition
at the beginning of the experiment (Day 0)
Lyngbya sp. Coverage
Table 1 showed the variation of Lyngbya
sp. covering C. lentillifera during the
experiment. The average percentage of
Lyngbya sp. coverage showed the different
tendencies between light densities. The
Lyngbya sp. coverage increased very fast
under 40 μmol photons m-2.s-1 condition from
Florian Quemper et al.
322
8.3% and 10.8% (day 0) to 90.3% and 99.8%
(day 28) on branch and root, respectively.
Meanwhile, under lower light condition
(20 μmol photons m-2.s-1) the Lyngbya sp.
coverage increased from day 0 to day 14 in
both branch and root of C. lentillifera. The
coverage showed decrease after 21 days under
low light conditions. Then the coverage
decreased to 12.3% and 15.7% in the branch
and root, respectively.
Table 1. Variation of Lyngbya sp. coverage on C. lentillifera (SD means standard deviation
with N = 4 for each condition of each period)
Light density (μmol
photons m-2.s-1)
Part of C. lentillifera
The average percentage of Lyngbya sp. coverage (±SD)
Day 0 Day 7 Day 14 Day 21 Day 28
20
Branch 8.3 ± 2.5 12.5 ± 5.4 18.3 ± 4.2 15.5 ± 3.8 12.3 ± 2.5
Root 10.8 ± 4.3 18.6 ± 3.8 20.8 ± 4.3 20.2 ± 6.3 15.7 ± 6.2
40 (initial condition)
Branch 8.0 ± 3.2 15.4 ± 4.6 38.3 ± 3.8 64.3 ± 2.5 90.3 ± 4.7
Root 10.5 ± 3.6 20.6 ± 4.3 40.8 ± 4.3 80.8 ± 4.3 99.8 ± 4.3
pH
After 7 days, the pH is more important
under a light density of 40 μmol photons m-2.s-1
than in the bottles under a light density of 20
μmol photons m-2.s-1 and this showed that the
light density affects the pH (t = -4.737, P <
0.05). The water was then changed, and the
same pH evolution was observed in the next
weeks. Initial pH was not significantly different
(t = 0.25265, P > 0.05).
Table 2. pH and salinity of the seawater after 7 days of culture of C. lentillifera in different photon
flux densities (20 and 40 μmol photons m-2.s-1). Different letters above bars indicate significant
differences. Mean ± 95% confidence intervals. N = 4 for each condition of each period
Light density (μmol photons m-2.s-1) Day pH
20
0 7.62 ± 0.03a
7 7.81 ± 0.08b
40 (initial condition)
0 7.61 ± 0.02a
7 8.06 ± 0.14c
Notes: The letter a, b, c indicates the difference in the statistic. Difference letters mean significant differences.
DISCUSSION
This experiment indicates that the C.
lentillifera under a light density of 20 μmol
photons m
-2
.s
-1
had almost no Lyngbya sp.
present on their branches after 28 days. In
addition, new branches were emerging along
the stolons. On the opposite, the seaweeds
under a light density of 40 were covered by
Lyngbya sp. and about to die at the end of the
experiment. In fact, C. lentillifera from the
first group was longer, heavier, and had a
better SGR than the second group. In
particular, during the 4
th
week, we found an
SGR of 4.5%d
-1
. This result is consistent with
the study of Guo et al., [12] for the same
temperature. Their final length and weight
were greater than the initial ones. Those
seaweeds have overcome the presence of
Lyngbya sp. and will keep growing.
The Lyngbya sp. occurred during the time
between two measures, so we cannot say
whether it had a quantitative effect on the
growth of C. lentillifera before the beginning of
the treatment. Still, the thalli appeared to be
weak, some ramuli became white. However,
even if the measures were taken just before its
occurrence, we might not have been able to
observe significant results because C.
lentillifera is mainly weakened on the long-
term aspect.
During the experiment, we observed an
increase in the pH, particularly under the light
density of 40 μmol photons m-2.s-1. This is
linked to the fact that C. lentillifera and
Lyngbya sp. are both oxygenic photosynthetic
organisms and will use the CO2 in the seawater
to synthesize carbon. The depletion of the
cyanobacteria might be explained by the fact
Utilization of the light density
323
that Lyngbya sp. cannot fix N2 under the dark
condition as found by Jones [17].
We also observed different phases of
variation of the SGR and obviously the weight.
In particular, the SGR was negative at the end
of the second week for both groups because the
weight decreased. But those observations were
not the same for the length, which kept
increasing at that moment. One explanation
could be the loss of some white-dead branches
during the second week, while the stolons kept
growing. But this might be not enough to
explain this event because we observed an
outcome of cyanobacteria in the same period.
This phenomenon could not be explained with
the data collected.
Nonetheless, this study may be useful in the
project of creating a new way of producing
seafood with C. lentillifera in tanks. If those
tanks were to be invaded by Lyngbya sp.,
reducing the light density with some nets might
be enough to eliminate those algae without
losing the production of C. lentillifera.
However, it might take some time before
witnessing the results.
CONCLUSION
This experiment indicates that the length,
weight, and SGR is greater in the case of C.
lentillifera growing under a light density of 20
μmol photons m-2.s-1 after 28 days of
experimentation. In addition, qualitative
observation showed that after one month
Lyngbya sp. is no longer present in those
seaweeds while the seaweeds growing under 40
μmol photons m-2.s-1 are almost dead. For these
reasons, we can argue the light density as a
treatment to reduce and eliminate the presence
of Lyngbya sp. However, those results take
time and might not be the most suitable.
However, in the future, if such a development
happens in a tank, reducing the light density
might be enough to kill the cyanobacteria. This
study also contributes to finding a solution to
reduce the acidification issue by using seaweed
culture to absorb CO2 in the seawater. The
artificial culture of seaweed is the most
important model for the offshore island to
provide a fresh vegetable food source which
contributes to the sustainable development in
the offshore islands.
Acknowledgments: We thank the projects No.
VAST 07.03/18–19 and No. KC09.29/16–20
for supporting our experiment, thank the
scientists from the Institute of Marine
Environment and Resources for their help
during our experiment.
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