Method Article
The Lemna Toxicity Test: Guideline of a New Test System Based on Root Re-Growth
Taejun Han
Taejun Han, Incheon National University
Corresponding Author
Abstract
A new phytotoxicity test method based on Lemna root elongation has been developed. Tests with aquatic plants have, typically, favored measurements on fronds (e.g. frond number, area, biomass) rather than on roots, due, in part, to issues associated with handling fragile roots and the time-consuming procedures of selecting roots with identical root lengths. The new test method differs from the traditional procedures by removing all roots from fronds prior to exposure to toxicants with subsequent measurements on newly developed roots. The root re-growth bioassay also differs from three internationally standardized methods (ISO, OCED and US EPA) in that it is completed within a shorter time period (72 h), the required volume of test solutions is only 3.0 mL and non-axenic plants are used. Our results show that the Lemna root method is a simple, rapid, cost-effective, sensitive and precise bioassay to assess the toxic risks of environmental contaminants.
Keywords
Aquatic plants, Lemna spp., Root, Toxicity
Figures
Figure 1
Figure 2
Figure 3
Figure 4
Introduction
Aquatic vascular plants belonging to the genus Lemna have gained broad acceptance as bioassays in ecotoxicological research. Lemna spp. are C3 monocots and have many advantages as test organisms, including their simple structure and small size, allowing for small volumes of sample toxicants to be used (Li and Xiong, 2004 and Kumar and Han, 2010), rapid rates of growth (a doubling time of 2–4 d), ease of culture and handling, high degree of homogeneity such that most clones are morphologically similar (Lahive et al., 2011), and sensitivity to a wide range of pollutants (Hillman, 1961, Wang and Williams, 1990 and Christen and Theuer, 1996). Moreover, Lemna plants are appealing test organisms because they play key roles in primary production, nutrient cycling and structuring aquatic ecosystems by supplying food, habitats and nursery grounds for organisms of higher trophic levels as well as their wide geographical occurrence (Drost et al., 2007). Among Lemna spp., L. gibba and L minor have been most extensively used in phytotoxicity testing and there are several standard methods which have been adopted by major international standardization agencies e.g. U.S. Environmental Protection Agency (USEPA, 1996), Organization for Economic Cooperation and Development (OECD, 2002), and International Standardization Organization (ISO, 2005).
To ensure thorough evaluation of the risks posed by pollutants for environmental and human health, the test methods employed should be sensitive, rapid, simple and of ecological relevance. Therefore, a technique that can assess toxicity more rapidly but without loss of sensitivity would be a valuable asset. In the case of Lemna, bioassays using traditional endpoints such as number of fronds, wet or dry biomass and growth rates of fronds require standard exposure durations of at least 7 d to detect toxicity. Tests based on root elongation are some of the most widely used phytotoxicity methodologies for terrestrial angiosperms (Wang, 1991) because of their simplicity and rapidity (Munzuroglu and Geckil, 2002). However, despite reports that roots of L. minor are highly sensitive to environmental stressors (Panda and Upadhyay, 2003) and that they play important ecological roles by providing stability and facilitate dispersal there have been few studies incorporating root elongation as a test endpoint (Davis, 1981). This may be due, in part, to the fragility of the roots, which makes handling of roots for measurements of length difficult (Davis, 1981). It can also be impractical to obtain sufficient numbers of individual plants with identical root lengths for initiating tests.
Recently, a new root elongation test method has been developed using three Lemna species (L. gibba, L. minor, and L. paucicostata) and the sensitivity and consistency of the method were evaluated upon exposure to 5 different essential and non-essential metals (Ag, Cd, Cr, Cu and Hg) (Park et al., 2013). The new test method differs from the traditional procedures by removing all roots from fronds prior to exposure to toxicants with subsequent measurements on newly developed roots.The root re-growth bioassay also differs from three internationally standardized methods (ISO, OCED and US EPA) in that it is completed in 72 h, the required volume of test solutions is only 3.0 mL and non-axenic plants are used. The new Lemna root method is a simple, rapid, cost-effective, sensitive and precise bioassay to assess the toxic risks of environmental pollutants. The use of this methodology may be extended for estimating the toxicity of various substances or mixtures contained in fresh water, waste water and environmental water samples including treated municipal wastewater and industrial effluents.
This protocol provides the detailed information on how to set up and conduct the root re-growth test with Lemna as well as how to analyse the toxicity data. This protocol is intended for use with L. minor but it can also be applied to Spirodela species with some modifications.
Reagents
1. Test organisms
: The standard test organisms of this test are duckweeds, Lemna spp., which are freshwater-floating plants.
2. Growth medium and nutritional ingredients.
: Prepare stock solution by adding the weighed chemicals according to Table 1 to the desired volume of distilled water for the growth medium and test compound solutions. DW should be used for the dilution of liquid media and test substances.
: pH of liquid media should be adjusted to 6.9 ± 0.1 after adding DW to each stock solution.
: Liquid media can be stored for up to one month at room temperature in the dark.
Equipment
The test requires usual laboratory equipment and the following.
1. Temperature-controlled cabinet or room, with a white fluorescent light, providing uniform illumination in accordance with the requirements specified in Table 2.
2. Light-meter, to be used to measure photon irradiance expressed in micromoles per square meter per second.
3. pH meter, for the adjustment of pH during the preparation of cultures and test solutions and to measure pH at the beginning and end of a test.
4. Tweezers, for handling fronds
5. Stainless scissors, for excising roots
6. Glass wares, for the preparation of different concentration series and nutrient medium.
6.1 Beakers, 250 mL
6.2 Graduated cylinders, capacities of 50 mL and 100 mL
6.3 Pipettes, 1 mL and 5 mL
7. Conical tubes, capacities of 50 mL
8. Plastic tank, 10 L
9. Exposure dishes, for example 24 well cell plates with 3.0 mL per well (a diameter of 15.6 mm may be suitable). Cell plates shall be sealed with sealing tape for prevention of evaporation of medium and test solution. In the case of volatile organic compounds, separate cell plates should be used in order that transfer of volatile compounds between the lined wells may affect the test.
10. Sealing tape, to seal around the exposure dishes.
11. Chemical balance, stirrer, magnetic bar, spatula
These are useful tools for measuring and melting chemicals during preparations for culture solutions.
12. Microscope slide glasses, for putting fronds on for taking measurements of root length.
13. Image analysis system, with a magnification of 4 times to 6 times, for measurements of the root length.
Procedure
1. Preparation of medium
1.1 To prepare 1 L of Steinberg medium, the necessary reagents and respective quantities are outlined in Table 1. Stock solutions are added to 938 mL of distilled water.
1.2 Chemicals must be reagent-grade. The medium is stirred until all the contents are dissolved. CAUTION The pH of liquid media should be adjusted to 6.9 ± 0.1with either HCl or NaOH at strengths ≤ 1 M after adding distilled water to each stock solution.
2. Preparation of toxicant solution and test dilutions
2.1 Test dilutions
Test dilutions can be prepared in volumetric flasks and then distributed to the replicate test vessels. Test vessels are left at room temperature for 1 hour to allow equilibrium of the medium and toxicant.
2.2 Selection of test concentrations
Set the concentration of the test substances using half dilution of the medium and the toxicity test solution. In cases of uncertainty about sample toxicity, it is beneficial to run a range-finding test for choosing concentrations of definitive test. A wide range of concentrations (e.g., ≥ an order of magnitude) should assist in selection of the concentrations for the definitive test.
In case the test solution is an effluent or liquid material, set the concentration to 0, 6.25, 12.5, 25.0, 50.0, and 100%. The concentration should be selected so that different levels (4-5 sections) of growth can occur in the range of less than 10% to over 90%. It is best to choose the range of concentrations through preliminary experiments, which includes broad range of concentrations.
2.3 Control
All experiments require a negative control with the identical culture medium, test conditions and procedures, but exclude the test substance.
3. Transfer of test organisms
Sort out fronds of duckweed that are dark green and consist of two or three identical leaves attached; The roots of selected fronds are excised using stainless steel scissors (Fig. 1a,b); Place individual rootless plants in each cell of a 24-well plates by using tweezers (Fig. 1c,d)
4. Culture
As a standard condition, the test organism is cultured at 25℃ with continuous white light of 90-100 μmol·m-2·s-1. The duration of the _Lemna* root growth inhibition test is 72 hours.
5. Methods of measurements
After 72 h of culture, harvest all plants and place them on glass slides and measure the length of the longest roots using an image analyzer (Fig. 2). An individual plant generally has 2-3 fronds each with one root.
Timing
Preparation of stock solution and culture media takes 1 h. Frond selection and root cutting takes 1 h (in case of n = 72). Transferring the sample plants into the new or test media requires 15 min. Running multiple tests in tandem will increase the time required to complete the test. An incubation period for test is 72 h. Once a test is completed, processing times for harvesting the sample plants, then measurements of root elongation require 30 min. Allocate 30 min for statistical tests although there will be some variations in time required depending on the expertise.
Troubleshooting
CRITICAL The fronds are cultured at 25℃, given 24 h continuous white light at an intensity of 30-40 μmol·m-2·s-1. The medium is replaced at an interval of 7 days and the storage culture can be kept continually unless uncontrolled contamination occurs. Cloudy medium in a Lemna stock culture indicates bacterial contamination, whereas contamination with mould may not be clearly evident until large colonies appear in the medium or a slime layer develops on the vessel. Contaminated Lemna cultures must be discarded.
CRITICAL Care must be taken to ensure that the plants do not adhere to the side of the well; The transfer of Lemna to test solutions must be done in random order across the replicates within a concentration; Cover the plate and seal with sealing tape to avoid evaporation of medium or test solution.
CRITICAL The test is a static type so that the test solutions are not changed for the duration of the test. In carrying out the experimental procedures, a fully randomized design is used to account for any variability in environmental conditions within the culture cabinet.
References
Christen, O. and Theuer, C. Sensitivity of Lemna Bioassay interacts with stock-culture period. J. Chem. Ecol. 22, 1177-1186 (1996).
Davis, J.A. Comparison of Static-replacement and Flow-through Bioassays Using Duckweed 'Lemna Gibba' G-3. EPA 560/6-81-003. United States Environmental Protection Agency, Washington, D.C (1981).
Drost, W. et al. Heavy metal toxicity to Lemna minor: studies on the time dependence of growth inhibition and the recovery after exposure. Chemosphere 67, 36-43 (2007).
Hillman, W.S. The Lemnaceae or duckweed: a review of the descriptive and experimental literature. Bot. Rev. 27, 221-287 (1961).
ISO. Water Quality – Determination of the Toxic effect of Water Constituents and Waste to Duckweed (Lemna minor) – Duckweed Growth Inhibition Test. International Organization for Standardization, Geneva, Switzerland (2005).
Kumar, K.S. and Han, T. Physiological response of Lemna species to herbicides and its probable use in toxicity testing. Toxicol. Environ. Sci. Health. 2, 39-49 (2010).
Lahive, E. et al. Differential sensitivity of four Lemnaceae species to zinc sulphate. Environ. Exp. Bot. 71, 25-33 (2011).
Li, T. and Xiong, Z. Cadmium-induced colony disintegration of duckweed (Lemna paucicostata Hegelm.) and as biomarker of phytotoxicity. Ecotoxicol. Environ. Saf. 59, 174-179 (2004).
OECD. Guidelines for the Testing of Chemicals. Lemna sp. Growth Inhibition Test, Draft Guideline 221 (2002).
Munzuroglu, O. and Geckil, H. Effects of metals on seed germination, root elongation, and coleoptile and hypocotyl growth in Triticum aestivum and Cucumis sativus. Arch. Environ. Contam. Toxicol. 43, 203-213 (2002).
Panda, S.K. and Upadhyay, R.K. Salt stress injury induces oxidative alterations and antioxidative defence in the roots of Lemna minor. Biol. Plant. 48, 249-253 (2003).
Park, A. et al. A novel bioassay using root re-growth in Lemna. Aquat. Toxicicol. 140-141, 415-424 (2013).
USEPA. Aquatic Plants Toxicity Test Using Lemna spp. United States Environmental Protection Agency, EPA 712-C-96-156 (1996).
Wang, W. Literature review on higher plants for toxicity testing. Water Air Soil Pollut. 59, 381-400 (1991).
Wang, W. and Williams, J.M. The use of phytotoxicity tests (common duckweed, cabbage, and millet) for determining effluent toxicity. Environ. Monit. Assess. 14, 45-58 (1990).
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A novel bioassay using root re-growth in Lemna
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Method Article
The Lemna Toxicity Test: Guideline of a New Test System Based on Root Re-Growth
Taejun Han
Taejun Han, Incheon National University
Corresponding Author
Article
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Abstract
A new phytotoxicity test method based on Lemna root elongation has been developed. Tests with aquatic plants have, typically, favored measurements on fronds (e.g. frond number, area, biomass) rather than on roots, due, in part, to issues associated with handling fragile roots and the time-consuming procedures of selecting roots with identical root lengths. The new test method differs from the traditional procedures by removing all roots from fronds prior to exposure to toxicants with subsequent measurements on newly developed roots. The root re-growth bioassay also differs from three internationally standardized methods (ISO, OCED and US EPA) in that it is completed within a shorter time period (72 h), the required volume of test solutions is only 3.0 mL and non-axenic plants are used. Our results show that the Lemna root method is a simple, rapid, cost-effective, sensitive and precise bioassay to assess the toxic risks of environmental contaminants.
Figures
Figure 1
Figure 2
Figure 3
Figure 4
Introduction
Aquatic vascular plants belonging to the genus Lemna have gained broad acceptance as bioassays in ecotoxicological research. Lemna spp. are C3 monocots and have many advantages as test organisms, including their simple structure and small size, allowing for small volumes of sample toxicants to be used (Li and Xiong, 2004 and Kumar and Han, 2010), rapid rates of growth (a doubling time of 2–4 d), ease of culture and handling, high degree of homogeneity such that most clones are morphologically similar (Lahive et al., 2011), and sensitivity to a wide range of pollutants (Hillman, 1961, Wang and Williams, 1990 and Christen and Theuer, 1996). Moreover, Lemna plants are appealing test organisms because they play key roles in primary production, nutrient cycling and structuring aquatic ecosystems by supplying food, habitats and nursery grounds for organisms of higher trophic levels as well as their wide geographical occurrence (Drost et al., 2007). Among Lemna spp., L. gibba and L minor have been most extensively used in phytotoxicity testing and there are several standard methods which have been adopted by major international standardization agencies e.g. U.S. Environmental Protection Agency (USEPA, 1996), Organization for Economic Cooperation and Development (OECD, 2002), and International Standardization Organization (ISO, 2005).
To ensure thorough evaluation of the risks posed by pollutants for environmental and human health, the test methods employed should be sensitive, rapid, simple and of ecological relevance. Therefore, a technique that can assess toxicity more rapidly but without loss of sensitivity would be a valuable asset. In the case of Lemna, bioassays using traditional endpoints such as number of fronds, wet or dry biomass and growth rates of fronds require standard exposure durations of at least 7 d to detect toxicity. Tests based on root elongation are some of the most widely used phytotoxicity methodologies for terrestrial angiosperms (Wang, 1991) because of their simplicity and rapidity (Munzuroglu and Geckil, 2002). However, despite reports that roots of L. minor are highly sensitive to environmental stressors (Panda and Upadhyay, 2003) and that they play important ecological roles by providing stability and facilitate dispersal there have been few studies incorporating root elongation as a test endpoint (Davis, 1981). This may be due, in part, to the fragility of the roots, which makes handling of roots for measurements of length difficult (Davis, 1981). It can also be impractical to obtain sufficient numbers of individual plants with identical root lengths for initiating tests.
Recently, a new root elongation test method has been developed using three Lemna species (L. gibba, L. minor, and L. paucicostata) and the sensitivity and consistency of the method were evaluated upon exposure to 5 different essential and non-essential metals (Ag, Cd, Cr, Cu and Hg) (Park et al., 2013). The new test method differs from the traditional procedures by removing all roots from fronds prior to exposure to toxicants with subsequent measurements on newly developed roots.The root re-growth bioassay also differs from three internationally standardized methods (ISO, OCED and US EPA) in that it is completed in 72 h, the required volume of test solutions is only 3.0 mL and non-axenic plants are used. The new Lemna root method is a simple, rapid, cost-effective, sensitive and precise bioassay to assess the toxic risks of environmental pollutants. The use of this methodology may be extended for estimating the toxicity of various substances or mixtures contained in fresh water, waste water and environmental water samples including treated municipal wastewater and industrial effluents.
This protocol provides the detailed information on how to set up and conduct the root re-growth test with Lemna as well as how to analyse the toxicity data. This protocol is intended for use with L. minor but it can also be applied to Spirodela species with some modifications.
Reagents
1. Test organisms
: The standard test organisms of this test are duckweeds, Lemna spp., which are freshwater-floating plants.
2. Growth medium and nutritional ingredients.
: Prepare stock solution by adding the weighed chemicals according to Table 1 to the desired volume of distilled water for the growth medium and test compound solutions. DW should be used for the dilution of liquid media and test substances.
: pH of liquid media should be adjusted to 6.9 ± 0.1 after adding DW to each stock solution.
: Liquid media can be stored for up to one month at room temperature in the dark.
Equipment
The test requires usual laboratory equipment and the following.
1. Temperature-controlled cabinet or room, with a white fluorescent light, providing uniform illumination in accordance with the requirements specified in Table 2.
2. Light-meter, to be used to measure photon irradiance expressed in micromoles per square meter per second.
3. pH meter, for the adjustment of pH during the preparation of cultures and test solutions and to measure pH at the beginning and end of a test.
4. Tweezers, for handling fronds
5. Stainless scissors, for excising roots
6. Glass wares, for the preparation of different concentration series and nutrient medium.
6.1 Beakers, 250 mL
6.2 Graduated cylinders, capacities of 50 mL and 100 mL
6.3 Pipettes, 1 mL and 5 mL
7. Conical tubes, capacities of 50 mL
8. Plastic tank, 10 L
9. Exposure dishes, for example 24 well cell plates with 3.0 mL per well (a diameter of 15.6 mm may be suitable). Cell plates shall be sealed with sealing tape for prevention of evaporation of medium and test solution. In the case of volatile organic compounds, separate cell plates should be used in order that transfer of volatile compounds between the lined wells may affect the test.
10. Sealing tape, to seal around the exposure dishes.
11. Chemical balance, stirrer, magnetic bar, spatula
These are useful tools for measuring and melting chemicals during preparations for culture solutions.
12. Microscope slide glasses, for putting fronds on for taking measurements of root length.
13. Image analysis system, with a magnification of 4 times to 6 times, for measurements of the root length.
Procedure
1. Preparation of medium
1.1 To prepare 1 L of Steinberg medium, the necessary reagents and respective quantities are outlined in Table 1. Stock solutions are added to 938 mL of distilled water.
1.2 Chemicals must be reagent-grade. The medium is stirred until all the contents are dissolved. CAUTION The pH of liquid media should be adjusted to 6.9 ± 0.1with either HCl or NaOH at strengths ≤ 1 M after adding distilled water to each stock solution.
2. Preparation of toxicant solution and test dilutions
2.1 Test dilutions
Test dilutions can be prepared in volumetric flasks and then distributed to the replicate test vessels. Test vessels are left at room temperature for 1 hour to allow equilibrium of the medium and toxicant.
2.2 Selection of test concentrations
Set the concentration of the test substances using half dilution of the medium and the toxicity test solution. In cases of uncertainty about sample toxicity, it is beneficial to run a range-finding test for choosing concentrations of definitive test. A wide range of concentrations (e.g., ≥ an order of magnitude) should assist in selection of the concentrations for the definitive test.
In case the test solution is an effluent or liquid material, set the concentration to 0, 6.25, 12.5, 25.0, 50.0, and 100%. The concentration should be selected so that different levels (4-5 sections) of growth can occur in the range of less than 10% to over 90%. It is best to choose the range of concentrations through preliminary experiments, which includes broad range of concentrations.
2.3 Control
All experiments require a negative control with the identical culture medium, test conditions and procedures, but exclude the test substance.
3. Transfer of test organisms
Sort out fronds of duckweed that are dark green and consist of two or three identical leaves attached; The roots of selected fronds are excised using stainless steel scissors (Fig. 1a,b); Place individual rootless plants in each cell of a 24-well plates by using tweezers (Fig. 1c,d)
4. Culture
As a standard condition, the test organism is cultured at 25℃ with continuous white light of 90-100 μmol·m-2·s-1. The duration of the _Lemna* root growth inhibition test is 72 hours.
5. Methods of measurements
After 72 h of culture, harvest all plants and place them on glass slides and measure the length of the longest roots using an image analyzer (Fig. 2). An individual plant generally has 2-3 fronds each with one root.
Timing
Preparation of stock solution and culture media takes 1 h. Frond selection and root cutting takes 1 h (in case of n = 72). Transferring the sample plants into the new or test media requires 15 min. Running multiple tests in tandem will increase the time required to complete the test. An incubation period for test is 72 h. Once a test is completed, processing times for harvesting the sample plants, then measurements of root elongation require 30 min. Allocate 30 min for statistical tests although there will be some variations in time required depending on the expertise.
Troubleshooting
CRITICAL The fronds are cultured at 25℃, given 24 h continuous white light at an intensity of 30-40 μmol·m-2·s-1. The medium is replaced at an interval of 7 days and the storage culture can be kept continually unless uncontrolled contamination occurs. Cloudy medium in a Lemna stock culture indicates bacterial contamination, whereas contamination with mould may not be clearly evident until large colonies appear in the medium or a slime layer develops on the vessel. Contaminated Lemna cultures must be discarded.
CRITICAL Care must be taken to ensure that the plants do not adhere to the side of the well; The transfer of Lemna to test solutions must be done in random order across the replicates within a concentration; Cover the plate and seal with sealing tape to avoid evaporation of medium or test solution.
CRITICAL The test is a static type so that the test solutions are not changed for the duration of the test. In carrying out the experimental procedures, a fully randomized design is used to account for any variability in environmental conditions within the culture cabinet.
References
Christen, O. and Theuer, C. Sensitivity of Lemna Bioassay interacts with stock-culture period. J. Chem. Ecol. 22, 1177-1186 (1996).
Davis, J.A. Comparison of Static-replacement and Flow-through Bioassays Using Duckweed 'Lemna Gibba' G-3. EPA 560/6-81-003. United States Environmental Protection Agency, Washington, D.C (1981).
Drost, W. et al. Heavy metal toxicity to Lemna minor: studies on the time dependence of growth inhibition and the recovery after exposure. Chemosphere 67, 36-43 (2007).
Hillman, W.S. The Lemnaceae or duckweed: a review of the descriptive and experimental literature. Bot. Rev. 27, 221-287 (1961).
ISO. Water Quality – Determination of the Toxic effect of Water Constituents and Waste to Duckweed (Lemna minor) – Duckweed Growth Inhibition Test. International Organization for Standardization, Geneva, Switzerland (2005).
Kumar, K.S. and Han, T. Physiological response of Lemna species to herbicides and its probable use in toxicity testing. Toxicol. Environ. Sci. Health. 2, 39-49 (2010).
Lahive, E. et al. Differential sensitivity of four Lemnaceae species to zinc sulphate. Environ. Exp. Bot. 71, 25-33 (2011).
Li, T. and Xiong, Z. Cadmium-induced colony disintegration of duckweed (Lemna paucicostata Hegelm.) and as biomarker of phytotoxicity. Ecotoxicol. Environ. Saf. 59, 174-179 (2004).
OECD. Guidelines for the Testing of Chemicals. Lemna sp. Growth Inhibition Test, Draft Guideline 221 (2002).
Munzuroglu, O. and Geckil, H. Effects of metals on seed germination, root elongation, and coleoptile and hypocotyl growth in Triticum aestivum and Cucumis sativus. Arch. Environ. Contam. Toxicol. 43, 203-213 (2002).
Panda, S.K. and Upadhyay, R.K. Salt stress injury induces oxidative alterations and antioxidative defence in the roots of Lemna minor. Biol. Plant. 48, 249-253 (2003).
Park, A. et al. A novel bioassay using root re-growth in Lemna. Aquat. Toxicicol. 140-141, 415-424 (2013).
USEPA. Aquatic Plants Toxicity Test Using Lemna spp. United States Environmental Protection Agency, EPA 712-C-96-156 (1996).
Wang, W. Literature review on higher plants for toxicity testing. Water Air Soil Pollut. 59, 381-400 (1991).
Wang, W. and Williams, J.M. The use of phytotoxicity tests (common duckweed, cabbage, and millet) for determining effluent toxicity. Environ. Monit. Assess. 14, 45-58 (1990).
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