4. CONCLUSIONS
The objective of this study was investigated the diversity of diatom composition in the Red
River that flows through Son Tay town, Hanoi. So far, studies on the diversity of phytoplankton
in general and diatom in particular of the Red River system are still limited. The results of the
study were conducted in the dry season of 2014 showing that the diatom is quite abundant with
79 species and sub-species of the 8 classes that have been identified. 5 species and sub-species
predominate in the silica community including: Navicularecens, Nitzschiapalea, Synodra
fasciculate, Luticola minor, Gomphonemaparvulum. Diatom that prefer clean water and less
polluted water accounted for a small proportion (4 and 20 % of total community) and the types
of diatom that exist in high polluted water and polluted water accounted for an average of 13 and
51 % of the total community respectively
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Vietnam Journal of Science and Technology 55 (4C) (2017) 90-96
DIATOM COMPOSITION IN THE RED RIVER
NEAR SON TAY, HA NOI
Hoang Thi Thu Hang
1, 2
, Le Thi Phuong Quynh
3
, Duong Thi Thuy
1, *
1
Institute of Environmental Technology, VAST, 18 Hoang Quoc Viet, Ha Noi
2
Graduate University of Science and Technology, VAST, 18 Hoang Quoc Viet, Ha Noi
3
Institute of Natural Product Chemistry, VAST, 18 Hoang Quoc Viet, Ha Noi
*Email: duongthuy0712@yahoo.com
Received: 1 August 2017; Accepted for publication: 18 October 2017
ABSTRACT
This study represents data on diatom composition in water samples collected in the Red
River near Son Tay town, Hanoi. Diatom samples were selected from marcophyte and stone
surfaces during dry season of 2014. 79 diatom species belonging to 8 families were identified.
The most species rich genera are Nitzchia (16 species), Navicula (14 species), Gomphonema
(5 species). There are five diatom species which are dominant in Red River diatom community
including Navicularecens (30 % of the total community), Nitzschiapalea (9.3 %), Synedra
fasciculate (8.1 %), Luticola minor (5 %) and Gomphonemaparvulum (2.8 %). The
Oligosaprobous and α -m esosaprobous diatom taxa make up only around 3% and to 20 % of the
total community. However, polysaprobous and ß- mesosaprobous taxa dominate in the Red
River accounted 13 to 51 % total community.
Keywords: diatom, community, red river.
1. INTRODUCTION
Diatoms are photosynthetic organisms, single-celled or monovalent organisms, and have
size from 10 μm to 100 μm. Diatom has a silica (SiO2) skeleton [1, 2]. Diatoms are widely
distributed throughout the various habitats on Earth. Because of the large biomass and species
diversity, diatom provides about 20 – 25 % of total organic carbon and is a primary source of
energy in aquatic ecosystems. Furthermore, it can be used as a food of many organisms and
microorganisms [3]. Therefore, diatoms play an important role in the food chain and
biogeochemical cycle, and they are influenced by many environmental factors such as light, pH,
temperature, hydrology and nutrients, etc. [4]. Diatoms have short growing cycles (several hours
to several days), sensitive and responsive to the environmental changes. With these advantages,
silica algae are often used to assess water pollution as well as ecological, chemical and physical
changes, providing early warning of pollution and recovery results of water ecosystem [5].
Research on the classification of diatom in water bodies of Vietnam is not much, including
the projects by Dang Thi Sy [6] and Luong Quang Doc et al. [7]. Untill now, publications
fordiatom distribution and diversity are focused mainly in estuarine and coastal ecosystems.
Diatom composition in the Red river near Son Tay, Ha Noi
91
Some studies use diatom as indicator organisms for organic pollution in river systems of new
urban that have been mentioned in recent years [5, 8].
Red River system with a basin
area of 156,451 square kilometers is
one of the two largest river systems in
Vietnam. Red River is a typical
example of Southeast Asian rivers
which are severely impacted by
human and the climate. Recent studies
show that socio-economic
development, population growth,
deforestation, land-use change, etc.
have had a negative impact on water
quality of Red River. Up to now,
studies on the Red River have focused
only on water quality, suspended
solids, hydrological regime, etc. [9,
10]. Research on phytoplankton
diversity, especially diatom is still limited. This paper represents the diverse composition of
diatom in Red River, which flows through Son Tay town. (Figure 1).
2. MATERIALS AND METHODS
Diatom samples (n = 9) were collected from macrophyte and stone surfaces during dry season
(Jannuary to March) of 2014 at Son Tay hydrological station, Red River. After collection, the
samples were fixed with formol 4 %. Removal of organic matter on the shell surface and
endosmosis of diatom by burning in H2O2 solution (30 %) and HCl (37 %). Diatom after being
cleaned, was glued on blue glass slides in the high refraction environment (Naphrax, Brunel
Microscopes Ltd, UK; RI = 1.74). Diatom valves were identified under Olympus BX microscope
at 1,000× magnification. On each slide, 400 diatom valves were identified following European
standards and the Süßwasserflora nomenclature [11 - 14]
3. RESULTS AND DISCUSSION
The analycal results of silica algae samples collected from macrophyte and stone surfaces
at the Son Tay hydrological station, Red River are presented in Table 1. The results have
identified 80 species and subspecies of 8 different families. The eight families encountered
during the investigation included Araphideae, Brachyraphideae; Centrophycideae,
Monoraphideae, Naviculaceae, Nitzchiaceae, Surirellaceae and Epithemiaceae. The genera of
large species includeNitzchia (16 species), Navicula (14 species), Gomphonema (5 species), etc.
Most species found in this study are widely distributed [15].
Among of the 80 species and sub-species of silica algae was found at Son Tay sampling
sites, there are five diatom species which are dominant in Red River diatom community
including Navicula recens (30 % of total community), Nitzschia palea (9.3 %) Synodra
fasciculate (8.1 %), Luticola minor (5 %), Gomphonema parvulum (2.8 %). The composition of
the silica algae recorded in this study is typical algae of the continuous flow river systems in the
world as well as the Red River that presented in previous studies [8, 5]. Navicula recens are
Figure 1. Sampling station in the Red River at Son Tay.
Hoang Thi Thu Hang, Le Thi Phuong Quynh, Duong Thi Thuy
92
predominant species in silica algae community. This is adaptive and fast grows species under
conditions of high total phosphorus content [16]
In addition to the Navicula recenssilica algae as described above, N. lanceolata, Luticola
goeppertiana adapted to the conditions of high total phosphorus were found in this study with
relative abundance ranging from 0.4 % to 1.17 % of the total community. Gomphonema
parvulum and Nitzschia palea, the same predominance in the silica community in this study has
also been recorded in high nutrient water bodies (nitrate and phosphate) in many countries
around the world, such as the United States, Japan, Poland and Germany [17] According to
Duong et al. (2012) [5], silica algae community on the To Lich river are featured by
Gomphonema parvulum and Nitzschia palea that adapted to high organic pollution and heavy
metal tolerance [5,18]. Besides, these species are also commonly found in some nutrient-rich
water bodies and low levels of dissolved oxygen [8].
To describe the ecological
demands of silica algae at study sites,
the Van Dam (1994) classification was
used, with two criteria: determining the
demands of silica algae with dissolved
oxygen and saprobic
nutritionalstatus.The distribution of
silica algae according to oxygen
demand is shown in Figure 2.
The results showed that, xygen-
preferred silica algae species account
for a low proportion (7,5 -11 % of the
total community). This may explain the
presence of Achnanthidium
minutissimum. According to many
studies, this species is very sensitive to
organic pollution and suitable for high
dissolved oxygen [19]. Meanwhile, less
oxygenated and oxygenated species are
predominate (37 % and 44 % of the total
species of the community).
Distribution of saprobic nutritional
demand of algae in the silica algae is
presented in Figure 3.
Theresults showed that, silica algae
that prefer clean water and less polluted
water (oligosaprobic và β –
mesosaprobic) account for a small proportion (4 and 20 % of total community). Meanwhile, the
types of algae that exist in hight polluted water and polluted water (Polysaprobic và α -
mesosaprobic) accounted for an average of 13 and 51 % of the total community respectively.
11.4%
7.5%
36.9%
44.2%
Continuously (100%sat) Fairly high (75% sat.)
Modrate %) Low (>30% sat.)
Figure 2. Oxygen demand distribution of algae in the diatom
community of the Red River near Son Tay, Ha Noi.
3.8%
20.1 %
56%
12.5%
12.7%
oligosaprobous ß- mesosaprobous
alpha-mesosaprobous alpha -meso/polysabrobous
polysaprobous
Figure 3. Distribution of saprobic nutritional demand of algae in
the diatom community of the Red River near Son Tay, Ha Noi.
Diatom composition in the Red river near Son Tay, Ha Noi
93
Table 1. List of species and sub-species of diatom recorded in the Red River of Son Tay, Ha Noi.
No. Name of taxon Relative abundance(%)
1. Achnanthes curtissima Carter 2
2. Achnanthidium catenatum (Bily & Marvan) Lange-Bertalot 2
3. Achnanthidium minutissimum (Kütz.) Czarnecki 4
4. Achnanthidium saprophila (Kobayasi et Mayama) 4
5. Amphora montana Krasske 2
6. Aulacoseira alpigena (Grunow) Krammer 2
7. Aulacoseira granulata (Ehr.) Simonsen 25
8. Bacillaria paxillifera (O.F. Müller) Hendey var.paxillifer 6
9. Caloneis molaris (Grunow) Krammer 4
10. Cocconeis placentula Ehrenberg var. placentula 12
11. Cocconeis placentula Ehrenberg var.lineata(Ehr.)Van Heurck 2
12. Craticula perrotettii Grunow 4
13. Cyclotella stelligera Cleve et Grun (in Van Heurck) 4
14. Cymbella tumida (Brebisson)Van Heurck 17
15. Cymbella turgidula var.bengalensis Krammer 4
16. Diadesmis confervacea Kützing 2
17. Encyonema mesianum (Cholnoky) D.G. Mann 2
18. Encyonema minutum (Hilse in Rabh.) D.G. Mann 6
19. Encyonema perpusillum (A. Cleve) D.G. Mann 2
20. Entomoneis alata Ehrenberg 2
21. Eolimna minima (Grunow) Lange-Bertalot 2
22. Eolimna subminuscula (Manguin) Moser Lange-Bertalot 2
23. Eunotia bilunaris (Ehr.) Mills var. bilunaris 2
24. Geissleria decussis(Ostrup) Lange-Bertalot & Metzeltin 2
25. Gomphonema lagenula Kützing 6
26. Gomphonema minutum (Ag.)Agardh f. minutum 21
27. Gomphonema parvulum (Kützing) Kützing var. parvulum 27
28. Gomphonema pumilum (Grunow) Reichardt & Lange-Bertalot 2
29. Gyrosigma acuminatum (Kutzing) Rabenhorst 2
30. Gyrosigma scalproides (Rabenhorst) Cleve 4
31. Gyrosigma spencerii (Quekett) Griffith et Henfrey 2
32. Hantzschia abundans Lange-Bertalot 2
33. Hippodonta hungarica (Grunow) Lange-Bertalot Metzeltin 2
34. Luticola goeppertiana (Bleisch in Rabenhorst) D.G. Mann 17
35. Luticola minor (R.M.Patrick) Mayama 50
36. Luticola peguana (Grunow in Cl. & Moeller) D.G. Mann 25
37. Mayamaea atomus var. permitis (Hustedt) Lange-Bertalot 2
38. Melosira varians Agardh 4
39. Navicula amphiceropsis Lange-Bertalot & Rumrich 2
Hoang Thi Thu Hang, Le Thi Phuong Quynh, Duong Thi Thuy
94
40. Navicula capitatoradiata Germain 4
41. Navicula caterva Hohn & Hellerman 4
42. Navicula cryptocephala Kutzing 12
43. Navicula cryptotenella Lange-Bertalot 10
44. Navicula cryptotenelloides Lange-Bertalot 12
45. Navicula lanceolata (Agardh) Ehrenberg 4
46. Navicula recens (Lange-Bertalot) Lange-Bertalot 295
47. Navicula schroeteri Meister var. schroeteri 4
48. Navicula symmetrica Patrick 4
49. Navicula tenelloides Hustedt 2
50. Navicula trivialis Lange-Bertalot var. trivialis 15
51. Navicula veneta Kutzing 4
52. Navicula viridula (Kutz.) Ehr. var.rostellata (Kutz.) Cleve 15
53. Neidium alpinum Hustedt 2
54. Nitzschia amphibia Grunow f.amphibia 2
55. Nitzschia bulnheimiana (Rabenhorst) H.L.Smith 2
56. Nitzschia dissipata(Kutzing)Grunow var.dissipata 4
57. Nitzschia filiformis (W.M.Smith) Van Heurck var. filiformis 4
58. Nitzschia filiformis var.conferta (Richter) Lange-Bertalot 8
59. Nitzschia frustulum (Kutzing) Grunow var.frustulum 4
60. Nitzschia gracilis Hantzsch 2
61. Nitzschia intermedia Hantzsch ex Cleve & Grunow 12
62. Nitzschia kurzii Rabenhorst 4
63. Nitzschia linearis (Agardh) W.M.Smith 2
64. Nitzschia palea (Kutzing) W.Smith 91
65. Nitzschia paleacea (Grunow) Grunow in van Heurck 4
66. Nitzschia rosenstockii Lange-Bertalot 12
67. Nitzschia sinuata (Thwaites) Grunow var.sinuata 2
68. Nitzschia subacicularis Hustedt in A.Schmidt et al. 2
69. Nitzschia supralitorea Lange-Bertalot 2
70. Planothidium frequentissimum Lange-Bertalot) 17
71. Sellaphora species 2
72. Sellaphora pupula (Kutzing) Mereschkowksy 4
73. Seminavis strigosa (Hustedt) Danieledis & Economou-Amilli 6
74. Stauroneis phoenicenteron (Nitzsch) Ehrenberg 2
75. Surirella brebissonii Krammer & Lange-Bertalot 2
76. Surirella linearis W.M.Smith 6
77. Surirella suecica Grunow 2
78. Synedra fasciculata Kützing 81
79. Synedra tabulata (Agardh) Kutzing var. tabulata 29
Diatom composition in the Red river near Son Tay, Ha Noi
95
4. CONCLUSIONS
The objective of this study was investigated the diversity of diatom composition in the Red
River that flows through Son Tay town, Hanoi. So far, studies on the diversity of phytoplankton
in general and diatom in particular of the Red River system are still limited. The results of the
study were conducted in the dry season of 2014 showing that the diatom is quite abundant with
79 species and sub-species of the 8 classes that have been identified. 5 species and sub-species
predominate in the silica community including: Navicularecens, Nitzschiapalea, Synodra
fasciculate, Luticola minor, Gomphonemaparvulum. Diatom that prefer clean water and less
polluted water accounted for a small proportion (4 and 20 % of total community) and the types
of diatom that exist in high polluted water and polluted water accounted for an average of 13 and
51 % of the total community respectively.
Acknowledgments. This work was conducted within the framwork of the project NAFOSTED 106NN.99-
2014.20, IFS W/4674-2. The authors are grateful to the National for Science and Technology
Development (NAFOSTED) and the International and the Foundation for Science (IFS) for their financial
support.
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