Organic pollution, nutrient increase and eutrophication of aquatic environment are common
problems in the world in general and Vietnam in particular. Phytoremediation is one of the most
priority means to improve the surface water quality because of the friendly environment, low cost
and high efficiency. In this study, we evaluated the nitrate uptake capacity of duckweed (Lemna
minor L.) from Vietnam upon the laboratory conditions. The results showed that after 9 days of
incubation, the duckweed could uptake from 10 - 23% of the nitrate concentration. Based on the
biomass, the nitrate uptake capacity of the duckweed was around 24.87 mg nitrate/ g wet weight of
the plant. The high nitrate uptake capacity of the duckweed suggests further researches at higher
scales (e.g. pilot) before application
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Kỷ yếu Hội nghị: Nghiên cứu cơ bản trong “Khoa học Trái đất và Môi trường”
DOI: 10.15625/vap.2019.000198
534
NITRATE UPTAKE CAPACITY OF DUCKWEED LEMNA MINOR L. UPON
THE LABORATORY CONDITIONS
Nguyen Quy Hao
1
, Tran Ngo Hoang Dung
1
, Bui Thi Nhu Phuong
2
,
Phan The Huy
2
, Dao Thanh Son
1*
, Bui Xuan Thanh
1
1
Faculty of Environment and Natural Resources, Ho Chi Minh City University of Technology,
VNU-HCM, Vietnam. 268 Ly Thuong Kiet street, district 10, Ho Chi Minh City, Vietnam.
2
Institute for Environmental and Resources, VNU - HCM
*Corresponding author’s email: dao.son@hcmut.edu.vn
ABSTRACT
Organic pollution, nutrient increase and eutrophication of aquatic environment are common
problems in the world in general and Vietnam in particular. Phytoremediation is one of the most
priority means to improve the surface water quality because of the friendly environment, low cost
and high efficiency. In this study, we evaluated the nitrate uptake capacity of duckweed (Lemna
minor L.) from Vietnam upon the laboratory conditions. The results showed that after 9 days of
incubation, the duckweed could uptake from 10 - 23% of the nitrate concentration. Based on the
biomass, the nitrate uptake capacity of the duckweed was around 24.87 mg nitrate/ g wet weight of
the plant. The high nitrate uptake capacity of the duckweed suggests further researches at higher
scales (e.g. pilot) before application.
Keywords: Duckweed, nitrate, phytoremediation.
1. INTRODUCTION
Duckweed (Lemna minor L.) is a water plant, which is widely distributed throughout the
world, especially in tropical and subtropical regions. They are often found in lakes or swamps.
Duckweed is also found in places with high nutrient content (nitrogen, phosphorus) such as
domestic and agricultural wastewater, septic tanks [1]. Duckweed is an important food source for
some aquatic organisms such as waterfowl, fish and poultry [2], [3]. Duckweed plays an important
role in overcoming the excess of mineral nutrients in ponds by biological methods because they
grow quickly and absorb most of these substances, namely nitrogen and phosphorus [4]. Using
duckweed to evaluate environmental quality has also achieved many scientific and practical
achievements [5].
Research on duckweed in our country is still modest and sporadic with a few published
works. Besides, duckweed shows great potential in cleaning the aquatic environment [3]. Organic
pollution is a common problem in fresh water bodies in Vietnam. The water environment in
Vietnam, in general, has been and is polluted organically. The objective of this study was to
evaluate nitrogen uptake capacity of Vietnamese duckweed in laboratory conditions.
2. MATERIAL AND METHODS
2.1. Material
Duckweed is collected from a polyculture pond with fish culture in District 12, Ho Chi Minh
City. Duckweed (Lemna minor L.) is being maintained at the Ecological Toxicology Module,
Department of Environment and Resources, Ho Chi Minh City University of Technology.
Duckweed is reared in a modified nutrient solution Z8 [6] under laboratory conditions with a
temperature of 27 ± 2 ° C, pH = 7, light intensity of about 3,000 Lux at the water surface and a light
and dark cycle. 12 am: 12 pm [2].
2.2. Methods
In the study, the experiment was designed to include the Z8 medium with duckweed. Two
flasks were prepared and carried out in parallel, the first containing 250mL of Z8 medium and 125
Hồ Chí Minh, tháng 11 năm 2019
535
duckweed. Water samples used to measure nitrate (50 mL) for the experiment were collected 3
times, which are on the first day, on the 5th day and the last day of the experiment (day 9). The
number of duckweeds in the experimental vessels at day 5 and day 9 of the experiment was also
recorded. The average weight of a duckweed was also determined by randomly weighing 30
duckweeds (2-leaf plants each) from the experimental batches.
The second flask of the experiment contains 300 ml of Z8 medium and 150 duckweeds. The
third one only has 300 ml of Z8 medium with no duckweeds added in parallel to verify the change
of nitrate (in Z8) in the absence of duckweed.
The experiment lasted for 9 days and by the last day, there was enough duckweed to cover the
surface area of the flasks.
2.3. Analytical methods
Using analytical methods for nitrate according to TCVN 6180:1996.
3. RESULTS AND CONCLUSIONS
3.1. The growth of duckweed and the change of nitrate concentration in the experiment
As shown in 3.2. Nitrate uptake capacity of duckweed
The results of fresh weight and average calculation (n = 30) showed that the average fresh
weight of 1 duckweed was 0.827 ± 0.1102 mg. Thus, considering the nitrate uptake capacity of
duckweed based on the number of duckweed and changes in nitrate concentration in Table 2, the
nitrate uptake capacity of duckweed in the current study is about 24.87mg nitrate/g fresh weight
duckweed.
Goopy and Murray (2003) reported that N uptake capacity of the aquatic plants (Lemnaceae)
can be up to 6,110 kg N/ha/year. However, the information on N uptake capacity of duckweed
(Lemna minor) per unit of fresh weight of duckweed, as far as we understand, is not available.
Therefore, it is necessary to study and calculate the absorption capacity of each individual aquatic
plant species to evaluate the effectiveness of nutrient treatment before putting them into application
under specific conditions. The results of this study show that nitrate uptake rate is very positive,
making it a basis for conducting research at a higher level (such as pilot) before putting into
practical application.
Table 1, the number of duckweeds increases steadily. It is possible that the number of
duckweeds and the surface area affect the production rate of duckweeds under laboratory
conditions. This needs to be studied further to determine the quantitative impact if any.
Considering the changes in nitrate concentration in the experiment, the rate of nitrate uptake
ranged from 10-23%, which is not high. This rate is still very low compared to the total nitrogen
treatment rate of water hyacinth (Eichhornia crassipes) in the pilot with hog farm wastewater,
which went up to 65% [7]. The major differences between this experiment and the ones carried out
by Nguyet et al., (2015) are (1) differences in plant objects (duckweed and water hyacinth) for
nutrient treatment; (2) research scale (laboratories and pilots); and (3) the nature of nutrient-
containing solution (artificial Z8 medium and pig waste after decomposition by microorganisms).
3.2. Nitrate uptake capacity of duckweed
The results of fresh weight and average calculation (n = 30) showed that the average fresh
weight of 1 duckweed was 0.827 ± 0.1102 mg. Thus, considering the nitrate uptake capacity of
duckweed based on the number of duckweed and changes in nitrate concentration in Table 2, the
nitrate uptake capacity of duckweed in the current study is about 24.87mg nitrate/g fresh weight
duckweed.
Goopy and Murray (2003) reported that N uptake capacity of the aquatic plants (Lemnaceae)
can be up to 6,110 kg N/ha/year. However, the information on N uptake capacity of duckweed
(Lemna minor) per unit of fresh weight of duckweed, as far as we understand, is not available.
Kỷ yếu Hội nghị: Nghiên cứu cơ bản trong “Khoa học Trái đất và Môi trường”
536
Therefore, it is necessary to study and calculate the absorption capacity of each individual aquatic
plant species to evaluate the effectiveness of nutrient treatment before putting them into application
under specific conditions. The results of this study show that nitrate uptake rate is very positive,
making it a basis for conducting research at a higher level (such as pilot) before putting into
practical application.
Table 1. Changes in number of duckweeds and nitrate content in the experiment
Z8 medium
(mL)
Day of the experiment
Number of
duckweeds
Nitrate
concentration (N-
NO3
-
mg/L)
1 150 47
300 mL 5 245 45
9 402 36
1 125 47
250 mL 5 285 46
9 363 42
Table 2. Nitrate uptake capacity of duckweed in laboratory conditions
Z8 medium (mL)
Nitrate uptake capacity of duckweed (mg nitrate/g
duckweed)
5 days of experiment 9 days of experiment
300mL 9,87 33,08
250 mL 4.24 16,65
Average 7.05 24,87
REFERENCES
[1]. C. A. Lembi, (2014). The Biology and Management of Algae, in BIOLOGY AND CONTROL OF
AQUATIC PLANTS - A Best Management Practices Handbook, West Lafayette: Aquatic Ecosystem
Restoration Foundation, pp. 97-104.
[2]. APHA (2012). Standard methods for the examination of water and wastewater, 22nd edition. Edited by
E. W. Rice, R. B. Baird, A. D.Eaton and L. S. Clesceri.
[3]. R. A. Leng, (1999). Duckweed: A tiny aquatic plant with enormous potential for agriculture and
environment. FAO.
[4]. J. P. Goopy and P. J. Murray, (2003). A review on the role of duckweed in nutrient reclamation and as a
source of animal feed,” Asian-Australasian J. Anim. Sci., 16(2), pp. 297-305.
[5]. T. Le Huu and H. Le Huy, (2016). Determination of some heavy metals in Eichhornia crassipes,
Ceratophyllum demersum and Myriophyllum spicatum in three water sources of Thai Nguyen city, J.
Sci. Technol., 59(11), pp. 28-31.
[6]. J. Kotai, (1972). Instructions for preparation of modified nutrient solution Z8 for algae, Nor. Inst. Water
Res. Oslo, 11(69), p. 5, 1972.
[7]. V. T. Nguyet, T. Van Tua, N. T. Kien, and D. D. Kim, (2015). The use of Eichhornia crassipes in a
surface flow wetland system for removing nitrogen and phosphorus of pig wastewater after anaerobic
treatment (biogas) process. Academica Vietnam Journal of Biology, 37(1), pp. 53-59.