Научная статья на тему 'Arsenic Induced Oxidative Stress and Role of Scavenging Enzymes in Phytoremediation by Pteris vittata and Eichhornia crassipes'

Arsenic Induced Oxidative Stress and Role of Scavenging Enzymes in Phytoremediation by Pteris vittata and Eichhornia crassipes Текст научной статьи по специальности «Биологические науки»

CC BY
71
12
i Надоели баннеры? Вы всегда можете отключить рекламу.
Ключевые слова
Arsenic toxicity / oxidative stress / reactive oxygen species / plant antioxidant defense / stress amelioration

Аннотация научной статьи по биологическим наукам, автор научной работы — Supatra Sen

Arsenic pollution is a growing menace in major parts of West Bengal, India and Bangladesh. Arsenic phytoremediation abilities of two common plants Pteris vittata and Eichhornia crassipes growing abundantly under natural tropical conditions of India were biochemically analyzed. Reactive oxygen species, taking total peroxide and malondialdehyde contents as the parameters, indicate the extent of arsenic induced oxidative stress, while the activities of the scavenging enzymes catalase, peroxidase and superoxide dismutase indicate the comparative effectiveness of the two plants in arsenic detoxification. Total peroxide and MDA contents were significantly higher in all samples of Eichhornia as compared to Pteris throughout the experimental period while the three scavenging enzymes viz. catalase, peroxidase and superoxide dismutase exhibited higher activities in Pteris with increasing arsenic concentration while Eichhornia showed a reverse trend. The comparative study reveals that Pteris vittata is the more efficient plant in combating and tolerating arsenic stress, as revealed by the results obtained of biochemical constituents and enzymatic profile. Of the two selected plant species,Pteris is found to be more effective in arsenic removal can serve as a cheap and easily available green source for arsenic detoxification. Key words: Arsenic toxicity, oxidative stress, reactive oxygen specie

i Надоели баннеры? Вы всегда можете отключить рекламу.
iНе можете найти то, что вам нужно? Попробуйте сервис подбора литературы.
i Надоели баннеры? Вы всегда можете отключить рекламу.

Текст научной работы на тему «Arsenic Induced Oxidative Stress and Role of Scavenging Enzymes in Phytoremediation by Pteris vittata and Eichhornia crassipes»

Journal of Stress Physiology & Biochemistry, Vol. 19, No. 4, 2023, pp. 63-70 ISSN 1997-0838

Original Text Copyright © 2023 by Supatra Sen

ORIGINAL ARTICLE

Arsenic Induced Oxidative Stress and Role of Scavenging Enzymes in Phytoremediation by Pteris vittata and

Eichhornia crassipes

Supatra Sen

1 Department of Botany, Asutosh College, Kolkata, Pin 700026. INDIA

*E-Mail: supatra.sen@asutoshcollege.in

Received May 23, 2023

Arsenic pollution is a growing menace in major parts of West Bengal, India and Bangladesh. Arsenic phytoremediation abilities of two common plants Pteris vittata and Eichhornia crassipes growing abundantly under natural tropical conditions of India were biochemically analyzed. Reactive oxygen species, taking total peroxide and malondialdehyde contents as the parameters, indicate the extent of arsenic induced oxidative stress, while the activities of the scavenging enzymes catalase, peroxidase and superoxide dismutase indicate the comparative effectiveness of the two plants in arsenic detoxification. Total peroxide and MDA contents were significantly higher in all samples of Eichhornia as compared to Pteris throughout the experimental period while the three scavenging enzymes viz. catalase, peroxidase and superoxide dismutase exhibited higher activities in Pteris with increasing arsenic concentration while Eichhornia showed a reverse trend. The comparative study reveals that Pteris vittata is the more efficient plant in combating and tolerating arsenic stress, as revealed by the results obtained of biochemical constituents and enzymatic profile. Of the two selected plant species, Pteris is found to be more effective in arsenic removal can serve as a cheap and easily available green source for arsenic detoxification.

Key words: Arsenic toxicity, oxidative stress, reactive oxygen species, plant antioxidant defense, stress amelioration

OPEN

9

ACCESS

Arsenic (As) pollution is on the rise globally and is a looming environmental threat. Arsenic is found chiefly as arsenate (AsV) and arsenite (AsIII) showing a broad range of solubility controlled by the ionic environment and pH. Arsenate behaves as a phosphate chemical analog, taking

ATP synthesis causing toxicity. Arsenite toxicity is mainly due to its affinity to react with thiol (-SH) groups of

Phytoremediation, an important eco-friendly technology, uses different techniques, such as uptake, transport, translocation, and detoxification, to remediate such harmful metals and metalloids. Hyperaccumulator plants take up metals and metalloids from soils, translocate and store them in their above ground biomass (Reeves, 2006). Similarly, arsenic hyperaccumulator plants have also developed different approaches to accumulate and withstand high concentrations of As. Arsenic toxicity induces oxidative stress due to abundant production of reactive oxygen species (ROS). The hyperaccumulator plants by their

The objective of this work was to compare the arsenic phytoremediation abilities of two common plants Pteris vittata and Eichhornia crassipes both growing abundantly under natural tropical conditions of India. Arsenic pollution is a growing menace in major parts of West Bengal, India and Bangladesh. The two selected plant species, if found effective in arsenic removal could serve as cheap and easily available green sources for detoxification. An analyses of their reactive oxygen species, taking total peroxide and malondialdehyde contents as the parameters, could indicate the extent of arsenic induced oxidative stress, while the activities of the scavenging enzymes catalase, peroxidase and superoxide dismutase could indicate the comparative effectiveness of the two plants in arsenic detoxification.

MATERIALS AND METHODS

Pteris vittata and Eichhornia crassipes used for the experimental work were ensured to be of identical age. Pteris plants were germinated from spores and 4 month old plants were acclimatized in a hydroponic system to promote root growth. After acclimatization in 0.2 strength Hoagland nutrient solution for 2 weeks, the plants were transferred into 0.2-strength Hoagland nutrient solution containing different concentrations of arsenic as As (V), as sodium arsenate (Na2HAsO4.7H2O). The finally selected concentrations of arsenic are 0, 130-133 and 267-270 |M. The plants were harvested at three intervals - 1, 5 and 10 days post arsenic treatment. Eichhornia was collected from local ponds and thereby grown, acclimatized and allowed to reproduce under laboratory conditions. The daughter plants obtained were of the same age and were taken as test materials. Eichhornia was also subjected to the same treatment with arsenic in the form of sodium arsenate. The treated plants were collected at three intervals, i.e. 1, 5 and 10 days post arsenic treatment. Control sets were maintained throughout for comparison.

The test materials were subjected to biochemical and enzymatic analyses using standard methods and tests. Estimation of total peroxide was done by ferrithiocyanate method of Thurman et al. (1972) and Malondialdehyde (MDA) was estimated by the method of Heath and Packer (1968). Catalase enzyme activity was assayed by the method of Gasper and Lacoppe (1968), peroxidase enzyme activity was assayed spectrophotometrically according to Chance and Maehly (1955) and superoxide dismutase (SOD) was assayed by the method of Marshall and Worsfold (1978). All the experiments were carried out in triplicates and then subjected to statistical analyses using analysis of variance (ANOVA) table.

RESULTS

The results showed that total peroxide content (Fig.1) and MDA content (Fig.2) was significantly higher in all samples of Eichhornia as compared to Pteris throughout the experimental period. The results of the enzymatic analyses revealed an identical trend in all the three assayed enzymes viz. catalase (Fig.3), peroxidase (Fig.4) and SOD (Fig.5). The three scavenging enzymes

the help of phosphate transporters to enter the plant system, resulting in disparity of phosphate supply (Finnegan and Chen, 2012). Within the cell, arsenate disrupts the phosphate-controlled metabolism including

enzymes and proteins with cysteine residues, disturbing their structure and function (Hasanuzzaman et al., 2015).

strong antioxidative defenses could constitute an important arsenic detoxification strategy.

exhibited higher activities in Pteris with increasing arsenic concentration while Eichhornia showed a reverse trend.

S 40

III

0 130

1 Day

Figure. 1. Total Peroxide Content P - Pteris, E - Eichhornia S.E.= 0.74 C.D. =0.78 (5%)

5 Day

Arsenic Concentration jiM

5 Day

Arsenic Concentration jiM

0 13D 270

10 Day

Figure 2. Malondialdehyde Content P - Pteris, E - Eichhornia S.E.= 0.73 C.D. =0.75 (5%)

o

w.

o.

M £

3

O X

1

II

III. III.

130 270

1 Day

Figure 3. Catalase enzyme activity P - Pteris, E - Eichhornia S.E.= 0.26 C.D. =0.27 (5%)

0 130 270 5 Day

Arsenic Concentration (iM

1

i

0 130 270 10 Day

<u 0 1

u

0 130 270 1 Day

Figure 4. Peroxidase enzyme activity P - Pteris, E - Eichhornia S.E.= 0.07 C.D. =0.07 (5%)

130 270

5 Day

Arsenic Concentration |iM

0 130 270 10 Day

5 -

4

3

2

1

I

130 270

1 Day

L

[

I

0 130 270 5 Day

Arsenic Concentration (iM

Figure 5. Superoxide dismutase (SOD) enzyme activity P - Pteris, E - Eichhornia S.E.= 0.07 C.D. =0.07 (5%)

I

130 270

10 Day

DISCUSSION

In my earlier work in 2014 most of the arsenic concentration was reported in the fronds (Pteris) or leaves (Eichhornia) (Sen, 2014a,b). Further biochemical and enzymatic analyses was carried out with frond and leaf samples. The results obtained indicated Pteris vittata to be more efficient in arsenic uptake than Eichhornia. Arsenic concentration was high in 10 day old samples of P. vittata as compared to Eichhornia exhibiting lower uptake (Sen, 2014a,b). While Eichhornia showed significantly reduced concentrations of biochemical constituents viz. chlorophyll, carotenoids, protein, amino acid, nitrogen, total carbohydrates and total phenols even in low doses of arsenic, Pteris appeared to be relatively less affected. The significantly higher starch content in Eichhornia under arsenic toxicity is possibly an adaptation for survival under stress.

The Brake fern, Pteris vittata, has the remarkable ability to hyperaccumulate arsenic in its shoots, with shoot concentrations reaching levels ~100-fold higher than soil concentrations (Ma et al. 2001). Pteris takes up arsenate, arsenite and MMA, the maximum amount nearly 93%

concentrated in the fronds (Ma et al. 2001). Detailed work has been carried out in Pteris vittata to study arsenic phytoextraction ( Fayiga and Saha, 2016) as an in situ alternative to alleviate arsenic toxicity of soils through phytoremediation (Tack and Meers, 2010; Wan et al., 2016). Pteris is used in phyto-extraction of arsenic under a wide array of soil physico-chemical conditions (Ciurli et al., 2014; da Silva et al, 2018; Sen 2014c). Tu and Ma (2002) after a greenhouse study reported that P. vittata could phytoextract up to 38 mg As/plant after 20 weeks of plant growth which meant nearly a 25% reduction in soil arsenic content.

Arsenic is known to induce oxidative stress in plants by generating various ROS (Sen 2016a) resulting in a range of responses in plants, including readjustment of transport and metabolic processes and growth inhibition (Hartley-Whitaker et al. 2001). In this work total, peroxide (Fig. 1) and MDA content (Fig. 2) were found to be higher in all treated Eichhornia samples as compared to Pteris. Several reactive oxygen species (superoxide anion, hydroxyl radicals, hydrogen peroxide and lipid peroxide) are generated in the cell wall and within the cell, which affect membrane permeability, enzyme activity,

photosynthetic activity, plant biomass (Karabel et al. 2003; Nguyen et al. 2003).

In my work, all the three scavenging enzymes viz. catalase (Fig.3), peroxidase (Fig.4) and SOD (Fig.5) showed higher activities in all samples of Pteris as compared to Eichhornia. This could be well correlated with low content of peroxide and MDA in all samples of Pteris. The scavenging enzymes of Pteris effectively remove the harmful peroxides and MDA thus making Pteris more effective than Eichhornia in combating arsenic stress. Like all other abiotic stresses, exposure of plants to arsenic stress increases ROS accumulation due to the disruption of electron transport chains (ETC) in mitochondria and chloroplasts, glycolate oxidase activation, antioxidant and scavenging enzymes inactivation, and GSH depletion

2013; Fayiga and Saha, 2016. Karimi and Souri, 2016 reported a positive correlation between greater antioxidant content and As tolerance in hyperaccumulator plants. According to Singh et al. (2006) the large GSH pool helps to combat As-induced oxidative stress and improves As tolerance in Pteris. Moreover, ROS, particularly H2O2, play an important role as signaling molecules which participate in the complex network regulating cell responses to As

2015).

In my earlier work while Eichhornia showed significantly diminished concentrations of chlorophyll, carotenoids, protein, nitrogen, amino acid, total phenols and carbohydrates even in low concentrations of arsenic, Pteris appeared to be comparatively unaffected (Sen 2016b, 2019). According to Tu and Ma (2003) arsenic stress creates conditions where the energy level exceeds the quantity that can be dispelled by chloroplast metabolism in the thylakoids. As a result, the electron transport processes in the thylakoid membranes are hampered and lethal symptoms appear.

Plants usually contain trace concentrations of several contaminants which at higher concentrations cause harm. At low levels, plants can usually metabolize or dispose of these compounds without any significant injury. Generally, at high contaminant concentrations in soil or water, plants often suffer (like Eichhornia, in the earlier study, Sen 2014a,b) and/or die because of their inability to metabolize these harmful elements. In the same study by Sen (2014a,

b) Pteris was found to survive and thrive even after considerable arsenic accumulation. However, some plants can, (like Pteris, in the present study) survive and/or thrive even when they accumulate high concentrations of toxic elements (Sen 2016a, b; 2019).

From the results obtained, Pteris vittata appears to be more suitable than Eichhornia crassipes for its possible use in phytoextraction of arsenic-contaminated soils. The comparative study reveals that Pteris vittata is the more efficient plant in combating and tolerating arsenic stress, as revealed by the biochemical constituents (Fig.1 and 2) and enzymatic profile (Fig.3,4 and 5). The physiological status of Eichhornia reveals the inefficiency of the plant to deal with arsenic stress and Arsenic-induced oxidative stress. The activities of the scavenging enzymes viz. catalase, peroxidase and SOD are significantly diminished under oxidative stress and are thus largely responsible for the prevailing stressful conditions (Sen 2016a,c). Since Pteris is a better accumulator of arsenic and is physiologically more adapted to cope with arsenic stress (as evidenced by obtained results), it is more suitable for phytoremediation (phytoextraction) in cases of arsenic pollution or contamination as compared to Eichhornia.

ACKNOWLEDGEM ENT

University Grants Commission (New Delhi, India) is gratefully acknowledged for financial assistance.

CONFLICT OF INTERESTS

The author declare that he has no potential conflicts of interest.

REFERENCES

Chance B. and Maehly A.C. (1955) Assay of catalases and peroxidases. In : Methods in Enzymology, (Ed. Colowick, S.P. and Kaplan, N.O.), Academic Press, New York. 2, 764-775. Ciurli, L. L., Alpi A. and Pardossi A. (2014) Arsenic uptake and translocation by plants in pot and field experiments. Int J. Phytoremediat., 16, 804-823. da Silva, E.B., Lessl J.T., Wilkie A.C., Liu X., Liu Y., Ma L.Q. (2018) Arsenic removal by As-hyperaccumulator Pteris vittata from two contaminated soils: A 5-year study. Chemosphere, 206, 736-741

according to the studies of Gupta et al.,

iНе можете найти то, что вам нужно? Попробуйте сервис подбора литературы.

(Sharma 2012, Thao et al.,

Fayiga, Abioye and Saha, U. (2016) Arsenic hyperaccumulating fern: Implications for remediation of arsenic contaminated soils. Geoderma. 284, 132143. 10.1016/j.geoderma.2016.09.003.

Finnegan Patrick and Weihua C. (2012) Arsenic Toxicity: The Effects on Plant Metabolism. Frontiers in Physiology. 3 D0I=10.3389/fphys.2012.00182 https://www.frontiersin.org/articles/10.3389/fphys.201 2.00182

Gasper T. and Lacoppe J. (1968) The effect of CCC and AMO-1618 on growth, catalase, peroxidase, 1M -oxidase activity of young barley seedlings. Physiol. Plant., 2, 1104-1109.

of phytochelatins in heavy metal stress and detoxification mechanisms in plants in Gupta D.K., Corpas F.J. and Palma J.M. (eds.) Heavy Metal Stress in Plants. Berlin: Springer, pp. 73-94. doi: 10.1007/978-3-642-38469-1_4

Hartley-Whitaker J., Ainsworth G. and Meharg A.A. (2001) Copper- and arsenate induced oxidative stress in Holcus lanatus L. clones with differential sensitivity. Plant Cell Environ., 24, 713.

Hasanuzzaman M., Nahar K., Rehman K., Hakeem, Munir Ozturk, Masayuki Fujita,Chapter 16 - Arsenic Toxicity in Plants and Possible Remediation,Editor(s): Khalid Rehman Hakeem, Muhammad Sabir, Munir Ozturk, Ahmet Ruhi Mermut, Soil Remediation and Plants,Academic Press,2015, Pages 433-501, ISBN 9780127999371,https://doi.org/10.1016/B978-0-12-799937-1.00016-4.(https://www.sciencedirect.com/ science/article/pii/B9780127999371000164)

Heath R.L. and Packer L. (1968) Photoperoxidation in isolated chloroplasts. I. Kinetics and stoichiometry of fatty acid peroxidation. Arch. Biochem. Biophys., 125, 189- 198

Karabal E., Yucel M. and Oktem H.V. (2003) Antioxidant responses of tolerant and sensitive barley cultivars to boron toxicity. Plant Sci., 164, 925.

Karimi N. and Souri Z. (2016) Antioxidant enzymes and compounds complement each other during arsenic detoxification in shoots of Isatis cappadocica Desv. Chemistry and Ecology, 32, 1-15.

10.1080/02757540.2016.1236087.

Ma L.Q., Komar, K.M., Tu C., Zhang W., Cai Y. and Kennelley E.D. (2001) A fern that hyperaccumulates arsenic. Nature, 409, 579.

Marshall M.J. and Worsfold M. (1978) Superoxide dismutase: a direct, continuous linear assay using the oxygen electrode. Anal. Biochem., 86, 561-573.

Nguyen T.N., Mohapatra P.K. and Fujita K. (2003) Leaf necrosis is a visual symptom of the shift from growth stimulation to inhibition effect of Al in Eucalyptus camaldulensis. Plant Sci., 165, 147.

Reeves R. (2006) Hyperaccumulation of trace elements by plants. In: Morel, JL., Echevarria, G., Goncharova, N. (eds) Phytoremediation of Metal-Contaminated Soils. NATO Science Series, vol 68. Springer, Dordrecht. https://doi.org/10.1007/1-4020-4688-X_2

Sen S. (2014a) Changes in Biochemical Constituents in response to Arsenic-induced Stress in Pteris vittata and Eichhornia crassipes to determine Stress Tolerance - A Review. Beats of Natural Sciences, 2, 1-5.

Sen S. (2014b) A comparative study on Arsenic-induced biochemical changes in Eichhornia crassipes (Mart.) Solms (Water Hyacinth) and Pteris vittata L. (Brake Fern). Seminar Proceedings of Impact of Pollution: Assessment and Awareness Dept. of Zoology, Hooghly Women's College, pp.185-192. ISBN 97881-921083-8-4

Sen S. (2014c) Restoring the Environment: Microbes in Phytoremediation in Sen, S. (ed.) Good Earth: Exploring Possibilities, pp. 31-36. ISBN 978-81922305-9-7

Sen S. (2016a) Phytoremediation of Arsenic by Pteris vittata (Brake Fern) and Eichhornia crassipes (Water Hyacinth): A Comparative Study. Centurion, 1(1), 161-166.

Sen S. (2016b) One Environment, Myriad dimensions: Exploring the Indian Perspective. Lambert Academic Publishing ISBN 978-3-659-87031-6

Sen S. (2016c) Eco-Physiology of two Indian Crop Plants: Impact of Seasonal Stress. Lambert Academic Publishing ISBN 978-3-659-91778-3

Sen S. (2019) Blueprint for Sustainability: Reviewing the

Gupta, D. K., Vandenhove H., and Inouhe M. (2013) Role

Indian Scenario. Lambert Academic Publishing ISBN 978-620-0-23781-1

plants. Biología, 67(3), 447-

453. https://doi.org/10.2478/s11756-012-0024-y

(2006) Metabolic adaptation to arsenic-induced oxidative stress in Pteris vittata L. and Pteris ensiformis L. Plant Sci., 170, 274-282.

Tack F. and Meers E. (2010) Assisted phytoextraction: helping plants to help us. Elements, 6(6), 383-388. https://doi.org/10.2113/gselements.6.6.383

Thao NP, Khan MIR, Binh N, Thu A, Lan X, Hoang T et al. (2015) Role of ethylene and its cross talk with other signaling molecules in plant responses to heavy metal stress. Plant Cell Environ., 169, 7384. https://doi.org/10.1104/pp.15.00663

Thurman R.G., Ley H.G. and Scholz R. (1972) Hepatic microsomal ethanol oxidation, hydrogen peroxide

formation and the role of catalase. Eur. J. Biochem., 25, 420-430.

Tu C. and Ma L.Q. (2002) Effects of arsenic concentrations and forms on arsenic uptake by the hyperaccumulator ladder brake. J. Environ. Qual., 31, 641.

Tu S. and Ma L.Q. (2003) Interactive effects of pH, arsenic and phosphorus on uptake of As and P and growth of the arsenic hyperaccumulator Pteris vittata L. under hydroponic conditions. Environ. Exp. Bot., 50, 243.

Wan X., Lei M., Chen T. (2016) Cost-benefit calculation of phytoremediation technology for heavy-metal-contaminated soil. Science of The Total Environment, 563-564, 796-802. ISSN 0048-9697 https://doi.org/10.1016/j.scitotenv.2015.12.080. (https://www.sciencedirect.com/science/article/pii/S00 48969715312377)

Sharma I. (2012) Arsenic induced oxidative stress in

Singh N., Ma L.Q, Shrivastava M. and Rathinasapathi B.

i Надоели баннеры? Вы всегда можете отключить рекламу.