Phycological Research 2008; 56: 33–38
Seasonal variation on size and chemical constituents of
Sargassum sinicola Setchell et Gardner from Bahía de La
Paz, Baja California Sur, Mexico
Yoloxochitl Elizabeth Rodríguez-Montesinos,* Dora Luz Arvizu-Higuera and Gustavo Hernández-Carmona
Interdisciplinary Center of Marine Science-IPN. PO Box 592, La Paz, Baja California Sur, 23000, México
SUMMARY
Investigation on seasonal variation in size and chemical
constituents of Sargassum sinicola Setchell et Gardner
from Bahía de La Paz, Baja California Sur, Mexico, was
carried out from a control bed and compared with an
experimental bed with artificial nutrients added. No
significant differences were found between the control
and experimental thalli for size or chemical composition, except for iodine and raw fiber. For control thalli
the results were: size 7.5–56.0 cm, alginate yield
7.2–13.7%, viscosity 58.7–191.7 millipascal seconds
(mPa s), mannitol 2.9–8.1%, raw fiber 5.5–7.5% and
iodine 0.020–0.141%; while in the experimental thalli
the size ranged from 7.5 to 80.3 cm and the alginate
yield was 7.8–10.4%, viscosity 41.4–163.4 mPa s,
mannitol 2.9–8.3%, raw fiber 5.9–10.7% and iodine
0.021–0.098%. These variations were related to its
natural growth cycle, and showed reductions during the
senescence period. Results suggest that S. sinicola is
not affected by relatively low nutrient concentrations,
and could be considered as raw material for alginate
production.
Key words: alginate, chemical constituents, iodine,
mannitol, raw fiber, Sargassum sinicola, size.
INTRODUCTION
Sargassum sinicola Setchell et Gardner is the most
common and abundant seaweed in the Gulf of California (Casas-Valdez et al. 1993; Nuñez-López & CasasValdez 1997, 1998; Pacheco-Ruíz et al. 1998).
Potential uses of Sargassum species are as animal food
complement, fertilizer, and as a source of antibacterial
substances and alginates (Chapman & Chapman 1980;
Ang 1987; Padmini-Sreenivasa-Rao et al. 1988; Marín
et al. 2003). Total biomass estimated for all the species
of the genus Sargassum from the western coast of the
Gulf of California is 154 000 wet tons (Pacheco-Ruíz
et al. 1998) and 18 900 wet tons in Bahía de La Paz
(Hernández-Carmona et al. 1990; Fajardo-León 1994).
However, in spite of its wide distribution and abundance, Sargassum species have not been harvested
commercially in the Gulf of California.
Some macroalgae (e.g. Macrocystis pyrifera
(Linnaeus) C. Agardh) are severely affected by high
water temperature and low nutrient concentrations as
occur during the El Niño Southern Oscillation (ENSO).
Experimental studies have demonstrated that adding
artificial nutrients helps to maintain M. pyrifera during
ENSO conditions. In contrast, other species such as
Eisenia arborea J.E. Areschoug is more resistant to low
nutrient concentrations (Hernández-Carmona et al.
2001). However, the effects of nutrients on the chemical constituents of S. sinicola are unknown. In addition,
studies on the natural variation of the main chemical
constituents of the alga could determine the potential
use of the algae. The goal of this study was to examine
the seasonal variation in the content of four of the main
chemical constituents (alginate, mannitol, raw fiber
and iodine) of S. sinicola under two conditions; without
artificial nutrients (control) and with artificial nutrients
added (experimental).
Study area
Bahia de La Paz, Baja California Sur, Mexico is a
coastal water body adjacent to the Gulf of California
with a length of 90 km and a width of 60 km. The
climate is very dry and warm. The average annual
rainfall in the area is 188 mm and the wettest
month (62 mm) is September (Jiménez-Illescas et al.
1997). The sea surface water temperature in winter
(December–February) ranges from 19 to 21°C, in spring
(March–May) from 21 to 24°C, in summer (June–
August) from 24 to 28°C and in autumn (September–
November) from 28 to 18°C (González-Navarro &
Saldierna-Martínez 1997). El Sauzoso, located to the
*To whom correspondence should be addressed.
Email: yrodriguez@ipn.mx
Communicating editor: D. Fujita.
Received 10 June 2006; accepted 21 May 2007.
doi: 10.1111/j.1440-1835.2008.00482.x
Y. E. Rodríguez-Montesinos et al.
34
Table 1. Average total length (cm) of experimental Sargassum sinicola thalli with and without (control) nutrients added, from Bahía de
La Paz, Baja California Sur, Mexico. Data are mean ⫾ standard error (n = 30)
Treatment
Experimental
Control
Season
Autumn
Winter
Spring
Summer
7.5 ⫾ 2.8
7.5 ⫾ 2.8
40.3 ⫾ 19.5
38.3 ⫾ 22.1
56.3 ⫾ 29.8
80.3 ⫾ 28.9
11.0 ⫾ 2.3
16.5 ⫾ 5.1
west of the bay at 24°18′ 26′-N and 110°38′ 17′-W, is
a semiprotected site having moderate surge, with a
shallow slope (Cruz-Ayala et al. 1998).
MATERIALS AND METHODS
This experiment is part of a broader study of S. sinicola
in El Sauzoso. We specifically examined the effect of
nutrient availability on a population recruited on three
quadrats of one square meter, where artificial nutrient
(Osmocote: N 14%, P 14%, K 14%) was dispensed
using PVC pipes attached to concrete blocks of
56 W ¥ 36 L ¥ 12 H cm (Hernández-Carmona et al.
2001). To avoid bias in sampling, quadrats were placed
at random along the coast line from where S. sinicola
thalli were sampled. We used another three quadrats for
sampling thalli in areas without nutrient enrichment
(control). Thirty thalli were tagged in each quadrat with
numbered plastic tags and the total length was measured each month to determine changes in thallus size.
S. sinicola was sampled from the control and experimental quadrats seasonally. Nitrate was determinate
from bottom seawater, near the quadrats (1 m2), using
the cadmium reduction technique (Strickland & Parson
1972).
In alginate extraction, the method described by
Arvizu-Higuera et al. (2002) was used. Twenty grams of
the dried and milled algal materials (30 mesh with a
sieve size of 0.5 mm) were hydrated overnight with
0.1% formaldehyde and then washed with HCl at pH 4.
The alginate was extracted with Na2CO3 at pH 10 in a
water bath at 80°C for 2 h. The paste was diluted and
filtered under vacuum and the clarified solution was
precipitated with ethanol at a proportion of 1:1. The
alginate fibers were then dried at 50°C for 12 h. Alginate yield was expressed as percentage/dry weight. The
apparent viscosity of the alginate was determined in 1%
(w/v) solution at 22°C with a viscometer (Brookfield
LVT, Middleboro, MA, USA), at 60 r.p.m. (6.28 rad·s-1)
using the appropriate spindle, adding 0.5% sodium
hexametaphosphate as calcium sequester.
Mannitol, iodine and raw fibers were determined
using the techniques described by Larsen (1978). Mannitol was determined by a fast oxidation of the polyol,
titrating with Na2S2O3.5H2O, with starch solution as an
indicator; iodine, by fusion in the presence of NaOH to
release it, adding Br and titrating with Na2S2O3.5H2O;
and raw fiber by extraction of the soluble material in
acid and alkali at high temperature, and determining
the organic part remaining by the weight lost.
Data were computed to obtain the average and standard error (⫾1 SE) with the significance level at 95%.
ANOVA was used to detect significant differences among
seasons and among treatments (P < 0.05), and Tukey
test to detect significant differences between means
(Zar 1999).
RESULTS
At the beginning of the experiment, the average seawater nitrate concentration was not significantly different
between the treatments with (0.62 mM) and without
nutrients (0.25 mM). During winter, the concentration
was significantly higher in quadrats with nutrients
(8.76 mM) than without (2.55 mM). During spring,
there was a trend for higher nitrate concentrations in
quadrats with nutrients (6.03 mM) than the controls
(2.57 mM), but this trend was not significantly different. Near the end of the experiment in summer,
nitrate concentrations were not significantly different,
although concentrations were still higher with nutrients
(6.83 mM) than without nutrients (4.34 mM).
The average initial size of S. sinicola thalli was
7.5 cm high (autumn) in both control and experimental
thalli. Maximum average sizes reached in spring were
80.3 cm in control thalli and 56 cm in experimental
thalli (Table 1). Size showed significant seasonal variation, but it was not significantly different between treatments (Table 2).
Sodium alginate yield (Fig. 1a) and viscosity
(Fig. 1b) were significantly different between seasons
but not significantly different between treatments
(Table 2). The highest yield was obtained in control
thalli during spring (13.7%), and the highest viscosity
(191.7 mllipascal seconds (mPa s)) in winter. Alginate
viscosity showed the same trend for control and experimental thalli. The minimum viscosity occurred in spring
with 58.7 mPa s in control thalli and 41.4 mPa s in
experimental thalli.
Minimum mannitol value was 2.9% in autumn in
both treatments and increased to a maximum value in
winter with 8.1% in control thalli and 8.3% in the
experimental thalli. Mannitol decreased in spring and
Constituents of Sargassum sinicola
35
Table 2. ANOVA for significant differences between seasons and treatments in size, viscosity and chemical composition from Sargassum
sinicola
Size
Yield
Viscosity
Mannitol
Raw fiber
Iodine
Effects
d.f.
effect
MS
effect
F
P
Season
Nutrients
S vs N
Season
Nutrients
S vs N
Season
Nutrients
S vs N
Season
Nutrients
S vs N
Season
Nutrients
S vs N
Season
Nutrients
S vs N
3
1
3
3
1
3
3
1
3
3
1
3
3
1
3
3
1
3
4 613.9800
283.5900
210.5900
24.2287
32.9720
12.7741
57 767.1731
133.9582
4 620.1986
58.3993
0.7151
7.0916
12.8379
19.1330
15.1331
0.0257
0.0103
0.0057
17.92
1.10
0.82
2.96
4.03
1.56
70.47
0.16
5.64
39.66
0.49
4.82
29.04
43.28
34.23
36.03
14.51
8.06
0.000*
0.309
0.502
0.042*
0.051
0.212
0.000*
0.688
0.002*
0.000*
0.489
0.005*
0.000*
0.000*
0.000*
0.000*
0.000*
0.000*
*P < 0.05. d.f., degrees of freedom; MS, mean square.
summer in both treatments (Fig. 1c). Differences were
significant between seasons, but not between treatments (Table 2).
In raw fiber, minimum values occurred in summer
(5.5 and 5.9%) in both treatments. In contrast, the
maximum values were in spring for the control thalli
(7.5%) and autumn (10.7%) for experimental thalli
(Fig. 1d). Significant differences were obtained
between seasons and treatments (Table 2).
Iodine in control plants were lower from autumn to
winter and increased significantly in spring and peaked
in summer (0.141%). Experimental thalli had similar
iodine values as control thalli from autumn to spring
and decreasing significantly in summer (0.027%)
(Fig. 1e). Significant differences between seasons and
treatments were obtained (Table 2).
DISCUSSION
Although nutrient concentration was higher in the
experimental quadrats during winter, thalli were not
significantly different in size. The thalli length from
autumn represents the average size of all populations at
the beginning of the experiment. During spring, in
which thalli reached their maximum size of 56 cm with
nutrients and 80 cm without nutrients, it was possible
that high nitrate levels during spring (15 mM) (PaúlChávez pers. comm. 2005) in experimental quadrats
might have lowered its basic metabolic process (Lobban
& Harrison 1994), resulting in lower growth rates and
smaller thalli. In summer, all thalli deteriorated due
to natural senescence. The large variation of thallus
length during winter and spring was due to the mix of
old thalli, that lost part of the fronds, with new thalli
that regenerated or germinated from zygotes.
Seasonal variation in alginate yield from S. sinicola
may be related with changes in light, wave exposure,
currents, temperature (Espinoza-Avalos & RodríguezGarza 1986; Espinoza & Rodríguez 1987) or others.
However our results suggest that nutrient concentration
could not be the main factor affecting the size and
chemical constituents and that the variation could be
related to thallus growth. In control quadrats, the thalli
collected from autumn to winter were juveniles with low
content of alginate (11.7%). As they matured in the
spring, the cell wall and intercellular matrix increased
with alginate and reached a maximum of 13.7%. In
summer, senescent thalli with residual fronds had lower
levels of alginate (7.2%). Similar results were obtained
by Aponte de Ataola et al. (1983) for Sargassum
species from Puerto Rico with yields of 7–12% in
January (winter) and 17.5–20% in May (spring) for
Sargassum vulgare C. Agardh and Sargassum polyceratium Montagne, respectively. Also Sargassum swartzii
C. Agardh and Sargassum tenerrium J. Agardh from
India had alginate yields of 19.7 and 11%, respectively
(Chauhan 1970). Hernández-Carmona (1985) found
values of 16.5% in winter and 27% in spring for
S. sinicola from La Paz, Baja California Sur, Mexico;
Pérez-Reyes (1997) reported Sargassum spp. values of
6.6% in January (winter) and 11.8% in May (spring)
from the same location as the present study. The experimental thalli exposed to nutrients followed a similar
trend to control thalli.
36
Y. E. Rodríguez-Montesinos et al.
Yield (%)
(a)
Viscosity (mPa s)
(b)
18
16
14
12
10
8
6
4
2
California Sur, Mexico. 䊐, experimental thalli; 䊏, control thalli.
Vertical bars indicate the standard error.
䉳
Autumn
Winter
2000
Spring
Summer
2001
Autumn
Winter
2000
Spring
Summer
2001
Autumn
Winter
2000
Spring
Summer
2001
Autumn
Winter
2000
Spring
Summer
2001
Autumn
Winter
2000
Spring
Summer
2001
250
200
150
100
50
0
(c)
Fig. 1. Seasonal variation in average yield (a) and viscosity of 1%
sodium alginate solution (b), mannitol (c), raw fiber (d) and iodine
(e) of Sargassum sinicola collected from Bahía de La Paz, Baja
10
Mannitol (%)
8
6
4
2
0
(d)
12
Raw fiber (%)
10
8
6
4
2
0
(e)
0.20
Iodine (%)
0.16
0.12
0.08
0.04
0.00
Alginate viscosity was highly variable during the year.
The lower values in the control thalli from spring to
summer are correlated with senescence of thallus
(Shah et al. 1970). The highest alginate viscosity of
191.7 mPa s in a 1% solution falls into the low viscosity type. This value was higher than that reported by
Alankararao et al. (1988) for S. vulgare in India with
60 mPa s and lower than in S. polycystum C. Agardh
with 70.8 mPa s in a 0.5% alginate solution (Saraswathi et al. 2003). The alginates extracted from Sargassum species contain a higher amount of guluronic
acid blocks that produce stronger gels, as compared
with alginates from Macrocystis (Shyamali et al. 1984;
McHugh 1987; Saraswathi et al. 2003); therefore this
type of alginate could be used in applications requiring
the formation of strong gels.
Mannitol is a monomeric compound used by algae as
a reserve and is remobilized from mature or old tissue
to provide energy and carbon skeletons for growth in the
meristems, and is influenced by osmotic potential
(Lobban & Harrison 1994). Mannitol showed significant
seasonal variation in thallus growth and reproductive
condition. However, it was not significantly different
between control and nourished thalli. Mannitol content
in control thalli (2.9–8.1%) was, however, higher than
those reported for Sargassum ilicifolium (Turner) C.
Agardh 2–5% and Sargassum myriocystum J. Agardh
(1.3–5.0%) in India (Chennubhotla et al. 1982).
The fiber method determines the amount of nonextractable organic material in the sample (Larsen
1978). In this study, the fiber content was significantly
higher in experimental (5.9–10.7%) than control thalli
(5.5–7.5%). These values, however, were lower than
those reported by Pérez-Reyes (1997) for Mexican Sargassum spp. with 10.3–11.3% and by Huerta-Múzquiz
et al. (1998) for S. polyceratium with 12% fiber
content.
Iodine is located mainly in the stipe tissue (Kolb
et al. 2004). Iodine content in S. sinicola ranged from
0.021 to 0.141%, and was higher in mature than in
juvenile thalli. The iodine content for S. sinicola
was higher than those obtained by Qing-xiang and
Xiao (1998) for different species of Sargassum from
China, including Sargassum vachellianum Greville
(4.5 ¥ 10-3%), Sargassum hemiphyllum (Turner) C.
Agardh (4.7 ¥ 10-3%), and Sargassum assimile Harvey
(5.6 ¥ 10-3%). This suggests that S. sinicola has a
higher capacity to store iodine than other Sargassum
species.
Constituents of Sargassum sinicola
In the present study it has been shown that there is
an inverse relationship between the mannitol and
iodine content (mannitol increasing – iodine decreasing) in all seasons and this relationship changed only in
summer in experimental thalli.
Variations of the main chemical constituents may be
related to the plant growth cycle and not strongly influenced by seawater nitrate concentrations. S. sinicola
showed significant reductions during the senescence
period. The results suggest that S. sinicola could be
considered to be an important raw material for alginate
production. Thus, Sargassum spp. should be harvested
in spring, a period of maximum biomass and high yield.
Although viscosity is lower in spring, gel strength could
be high.
ACKNOWLEDGMENTS
We thank the Instituto Politécnico Nacional (CICIMARIPN) for financial support, the ‘Comisión para el
Fomento de Actividades Académicas (COFAA-IPN)’ and
the program ‘Estímulo al Desempeño de la Investigación (EDI-IPN)’ for the scholarship received. Also we
thank Matthew Forrest and Kim Siewers for English
language editing.
REFERENCES
Alankararao, G. S. J. G., Rajendra Prasad, Y. and Rama Rao,
K. 1988. Alginic acid from Sargassum vulgare Børgesen.
Phykos 27: 174–6.
Ang, P. O. Jr. 1987. Use of projection matrix models in the
assessment of harvesting strategies for Sargassum. Hydrobiologia 151/152: 335–9.
Aponte de Ataola, N. E., Diaz-Piferrer, M. and Graham, H. D.
1983. Seasonal variations and anatomical distribution of
alginic acid in Sargassum spp. found along the coasts of
Puerto Rico. J. Agric. Univ. P.R. 67: 464–8.
Arvizu-Higuera, D. L., Hernández-Carmona, G. and RodríguezMontesinos, Y. E. 2002. Parameters affecting the conversion of alginic acid to sodium alginate. Cienc. Mar. 28:
27–36.
Casas-Valdez, M., Sánchez-Rodríguez, I. and HernándezCarmona, G. 1993. Evaluación de Sargassum spp en la
costa oeste de Bahía Concepción, B.C.S., México. Inv.
Mar. CICIMAR 8: 61–9.
Chapman, V. J. and Chapman, D. J. 1980. Seaweed and Their
Uses. Chapman & Hall, London.
Chauhan, V. D. 1970. Variation in alginic acid content with
growth stages in two species of Sargassum. Bot. Mar. 13:
57–8.
Chennubhotla, V. S. K., Kaliaperunal, N., Kalimuthu, S.,
Selvaraj, M. J., Ramalingam, R. and Najmuddin, M. 1982.
Seasonal changes in growth and alginic acid and mannitol
contents in Sargassum ilicifolium (Tunner) J. Agardh and
S. myriocystum J. Agardh. Ind. J. Mar. Sci. 11: 195–6.
37
Cruz-Ayala, M. B., Casas-Valdez, M. M. and Ortega-García, S.
1998. Temporal and spatial variation of frondose benthic
seaweeds in La Paz Bay, B.C.S., Mexico. Bot. Mar. 41:
191–8.
Espinoza, J. and Rodríguez, H. 1987. Seasonal phenology and
reciprocal transplantation of Sargassum sinicola Setchell
et Gardner in the Southern Gulf of California. J. Exp. Mar.
Biol. Ecol. 110: 183–95.
Espinoza-Avalos, J. and Rodríguez-Garza, H. 1986. Variaciones de Sargassum muticum (Yendo) Fensholt en la
exposición al oleaje. Inv. Mar. CICIMAR 3: 119–26.
Fajardo-León, M. C. 1994. Evaluación de biomasa y determinación de especies de los mantos del género. Sargassum
spp. Agardh, 1821 (Fucales; Phaeophyta) en la Bahía de
La Paz, B.C.S., México, en primavera de 1988. MCs
thesis, CICIMAR-IPN, La Paz, B.C.S., México.
González-Navarro, E. and Saldierna-Martínez, R. 1997. Zooplancton de la Bahía de la Paz, B.C.S. (1990-1991).
InUrbán-Ramírez, J. and Ramírez-Rodríguez, M. (Eds) La
Bahía de La Paz. Investigación y conservación. Universidad Autónoma de Baja California Sur, La Paz, Baja
California Sur, México, pp. 43–57.
Hernández-Carmona, G. 1985. Variación estacional del contenido de alginatos en tres especies de feofitas de Baja
California Sur, México. Inv. Mar. CICIMAR 2: 29–45.
Hernández-Carmona, G., Casas-Valdez, M. M., Fajardo-León,
C., Sánchez-Rodríguez, I. and Rodríguez-Montesinos, Y. E.
1990. Evaluación de Sargassum spp. en la Bahía de La
Paz, B.C.S., México. Inv. Mar. CICIMAR 5: 11–18.
Hernández-Carmona, G., Robledo, D. and Serviere-Zaragoza,
E. 2001. Effect of nutrient availability on Macrocystis
pyrifera recruitment survival near its southern limit of Baja
California. Bot. Mar. 44: 221–9.
Huerta-Múzquiz, L., Mendoza-González, A. C., Mateo-Cid, L.
E. et al. 1998. Algas marinas bentónicas de la Península
de Yucatán y su uso potencial de especies selectas.
Informe final del proyecto M039. CONABIO.
Jiménez-Illescas, A. R., Obeso-Nieblas, M. and Salas de León,
D. A. 1997. Oceanografía Física de la Bahía de la Paz,
B.C.S. In Urbán-Ramírez, J. and Ramírez-Rodríguez, M.
(Eds) La Bahía de La Paz. Investigación y conservación.
Universidad Autónoma de Baja California Sur, La Paz, Baja
California Sur, México, pp. 31–41.
Kolb, N., Vallorani, L., Milanovic, N. and Stocchi, V. 2004.
Evaluation of marine algae Wakame (Undaria pinnatifida)
and Kombu (Laminaria digitata japonica) as food supplements. Food Technol. Biotechnol. 42: 57–61.
Larsen, B. 1978. Brown seaweeds: analysis of ash, fiber,
iodine and mannitol. In Hellebust, J. A. and Craigie, J. S.
(Eds) Handbook of Phycological Methods. Cambridge University Press, Cambridge, pp. 181–8.
Lobban, C. S. and Harrison, P. J. 1994. Seaweed Ecology and
Physiology. Cambridge University Press, Cambridge.
Marín, A., Casas, M., Carrillo, S., Hernández, H. and Monroy,
A. 2003. Performance of sheep fed rations with Sargassum
spp. sea algae. Cuban J. Agric. Sci. 37: 119–23.
38
McHugh, D. J. 1987. Production, properties and uses of
alginates. In McHugh, D. J. (Eds) Production and utilization of products from commercial seaweeds. FAO Fisheries
Technical Paper (288). Publication division of the Food
and Agriculture Organization of the United Nations. Rome,
Italy, pp. 58–115.
Nuñez-López, R. A. and Casas-Valdez, M. M. 1997. Variación
estacional de la biomasa y talla de Sargassum spp. (Sargassaceae, Phaeophyta) en Bahía Concepción, B.C.S.,
México. Hidrobiológica 7: 19–25.
Nuñez-López, R. A. and Casas-Valdez, M. M. 1998. Seasonal
variation of seaweed biomass in San Ignacio Lagoon, Baja
California Sur, Mexico. Bot. Mar. 41: 421–6.
Pacheco-Ruíz, I., Zertuche-González, J. A., Chee-Barragán, A.
and Blanco-Betancourt, R. 1998. Distribution and quantification of Sargassum beds along the west coast of the
Gulf of California, Mexico. Bot. Mar. 41: 203–8.
Padmini-Sreenivasa-Rao, P., Sreenivasa-Rao, P. and Karmarkar, S. M. 1988. Antibacterial activity from Indian
species of Sargassum. Bot. Mar. 31: 295–8.
Pérez-Reyes, C. 1997. Composición química de Sargassum
spp. colectado en la Bahía de La Paz, B.C.S. y la factibilidad de su aprovechamiento en forma directa o como
Y. E. Rodríguez-Montesinos et al.
fuente de alginato. MSc thesis, CICIMAR-IPN. La Paz,
B.C.S., México.
Qing-xiang, L. and Xiao, F. 1998. Iodine content of Sargassum. Southern China. Chin. J. Oceanol. Limnol. 16: 286–
90.
Saraswathi, S. J., Babu, B. and Rengasamy, R. 2003. Seasonal studies on the alginate and its biochemical composition I: Sargassum polycystum (Fucales), Phaeophyceae.
Phycol. Res. 51: 240–3.
Shah, H. N., Mody, J. C. and Rao, A. V. 1970. Seasonal
variation of viscosity of sodium alginate from Sargassum
spp. & the preparation of high viscosity alginates. Bot. Mar.
XIII: 57–8.
Shyamali, S., De Silva, M. and Savitri Kumar, N. 1984.
Carbohydrate constituents of the marine algae of Sri
Lanka. 2. Composition and sequence of urinate residues in
alginates from some brown seaweeds. J. Nat. Sci. Counc.
Sri Lanka 12: 161–6.
Strickland, J. D. and Parson, T. R. 1972. A practical handbook of sewater analysis. Fish. Res. Bd. Can. Bull. 167:
310.
Zar, J. H. 1999. Biostatistical Analysis. Prentice Hall, Upper
Saddle River, NJ.