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09 2024
:36;
103310
doi:
10.1016/j.jksus.2024.103310

Heavy metal toxicity induced by sewage water treatment in three different vegetables (lettuce, spinach and cabbage) was alleviated by brassinosteroid and silicon supplementation

Department of Horticulture, College of Agriculture, University of Sargodha, Sargodha 40100, Punjab, Pakistan
Department of Soil and Environmental Sciences, College of Agriculture, University of Sargodha, Sargodha 40100, Punjab, Pakistan
Institute of Soil and Environmental Sciences, University of Agriculture Faisalabad, Pakistan
Department of Zoology, College of Science, King Saud University, Riyadh-11451, Saudi Arabia
School of Bioengineering and Biosciences, Lovely Professional University, Phagwara, Punjab 144411, India

⁎Corresponding authors. rashad.mukhtar@uos.edu.pk (Rashad Mukhtar Balal), ayazleo46@yahoo.com (Syed Ayyaz Javed)

Disclaimer:
This article was originally published by Elsevier and was migrated to Scientific Scholar after the change of Publisher.

Abstract

Purpose: Heavy metal stress due to the application of sewage water is considered a leading factor for constrained plant growth. Therefore, Current study was performed in the field to investigate the interactive influence of two irrigation sources (canal and sewage) and exogenous application of brassinosteroid (BRs) and silicon (Si) at different rates on growth, photosynthetic and physiological attributes of three leafy vegetables (lettuce, cabbage, and spinach). Methods: Three treatments were applied such as control, BRs and Si with three replications under split plot factorial design. Results: The results indicated that all the growth parameters including fresh biomass of plants and roots, dry biomass of plant and root, leaf area (LA), photosynthetic traits, chlorophyll contents, water use efficiency (WUE), activity of antioxidant enzymes; superoxide dismutase (SOD), peroxidase (POD), Catalase (CAT), ascorbate peroxidase (APX) and uptake of silicon except Cd and Pb contents were improved significantly with the foliar spray of BRs and Si over control treatment under both types of irrigation sources. However maximum improvement in leafy vegetables was recorded when the foliar spray of BRs and Si were applied under canal water irrigation. Conclusions: The foliar application of BRs and Si was proved as an ameliorating strategy for improving tolerance mechanisms associated with heavy metal stress. The major restoring mechanism was the restricted translocation of Cd and Pb leading to better growth and physiology under sewage water. Thus the application of BRs and Si reduced the detrimental effect of Cd and Pb led to improve the growth and physiological traits of leafy vegetables under irrigation with sewage water.

Keywords

Antioxidant enzymes
Cadmium
Cabbage
Lead
Lettuce
Spinach
Silicon
Sewage water
1

1 Introduction

Heavy metal intake through food stuffs is considered a major threat to human health worldwide due to its non-biodegradable and tenacious nature. Heavy metals are toxic elements having density ≥ 4 gcm−3 and reduce plant growth by creating the environment vulnerable to the plant population. Intake of these metals by various means of food stuff beyond the normal range in the biological system prompts destabilization of human physiology and affects the functions of major organs related to human physiology such as kidney, liver, brain, liver and bones. Irrigation of sewage water to vegetables, cereals, and fruit crops isthe major cause of heavy metal stress in plant and living organisms (Tariq et al., 2023). Other than sewage water irrigation, species of plants, type of soil and the dynamic intensity of heavy metal stress are also the main factors contributing to the induce metal toxicity in soil and vegetables (Hardaway et al., 2016). Moreover, pesticide and organic and inorganic fertilizer applications also affect the absorbance of nutrients by the plant due to modification in soil properties which could lead to a favorable environment for heavy metal contamination (Rizwan et al., 2021). Among vegetables, leafy vegetables receive more concentrations of heavy metal elements than fruits, cereals, and grain crops (Najmi et al., 2023) which results in a high concentration of impurities in the edible plant parts and subsequently increases in the human body. Metal contaminants are mainly absorbed by plant roots form soil and translocated to other plant parts as dissolved ions (Feng et al., 2021). Most of the researchers reported that leafy vegetables including lettuce, spinach cabbage, etc. uptake metal contaminants in higher concentrations after tuber and fruit crops (Christou et al., 2019). Rehman et al. (2017) declared in his research that Cd and Pb were found maximum in green vegetables as compared to other tuber crops. Heavy metal stress encourages stunted plant growth owing to reduced photosynthetic activity, disrupted transpiration and respiration processes and ion homeostasis (Manzoor et al., 2018). Reduction in root: shoot ratio and plant biomass are also due to heavy metal stress. Similarly, deterioration of plant defense systems against stress is also found in plants under the contaminated region. Activation and inhibition of enzymes, membrane damage, and electron transport systems are associated with heavy metal toxicity (Awasthi et al., 2020). Thus the plants suffering stress induced by metal elements contribute to oxidative stress, and physical and biological damage which ultimately destroys plant quality and productivity (Noor et al., 2022). Additionally, protein, lipids, and thylakoid membranes are also retarded in plans due to heavy metal accumulation in plants beyond the limits (Kim et al., 2014). Hence heavy metal contamination is a threatning aspect for plants and animals as well as for human health which could be minimized by applying different techniques (Sadaf et al., 2024). Among various approaches to alleviate the adverse effect of metal contamination, silicon (Si) and brassinosteroid (BRs) could be applied through foliar application to vegetables and other fruit crops.

Silicon (Si) as a beneficial nutrient plays a significant function in reducing negative impacts of abiotic stress (Liang et al., 2015; Deshmukh et al., 2017; Ahanger et al., 2020). Silicon application stimulate the metal detoxification process by altering cellular and biochemical mechanisms during plant growth (Shanmugaiah et al., 2023). The integrity of the positive effect of Si differs plant to plant specie and is more prominent in plants that regulate the maximum proportion of silicon in plant parts (Hosseini et al., 2019). Plant uptake Si by roots from soil solution as silicic acid in the range of 0.1 to 0.5 mmol L −1. Silicon can recover soil physicochemical characteristics by improving water and air transport in soil and subsequently increase nutrient availability by alleviating toxicity of metal ion (Zhu et al., 2019). Thus silicon application also regulates enzymes and gene expressions related to metal transporters (Etesami and Jeong, 2018). Previous researchers reported that plants showed improved growth under heavy metal stress when silicon was applied in optimum concentrations in various crops including, cotton, wheat, maize and penut (Rehman et al., 2021).

Similarly, Brassinosteroids (Brs), a steroid hormone, also influences cell elongation, cell expansion, male fertility and flowering, germination of seed, synthesis of stomata, and structure of plant (Sadaf et al., 2024). Various types of Brs are categorized with respect to the carbon numbers in their structure. Brassinosteroids (Brs) perform different functions in plants to protect against biotic and abiotic stressers (Wang et al., 2014).

By understanding how Brs and Si affect plant responses to WW irrigation, it may be possible to design strategies that maximize crop production while minimizing environmental contamination. This can lead to more efficient and responsible use of WW resources in agricultural settings. The current study's potential benefits include improved crop productivity, enhanced stress tolerance, regulated metal uptake, sustainable waste water (WW) management, and potential applications in various crops and environments. These outcomes have the potential to contribute to more efficient and environmentally conscious agricultural practices, ensuring food security and minimizing the risks associated with wastewater irrigation.

Therefore, this study was aimed to understand the interactive effect of metal stress and foliar spray of Brs and Si on growth and physiological components of plant and on antioxidant enzymatic activities of leafy vegetables (lettuce, spinach, and cabbage) under sewage water irrigation.

2

2 Material and Methods

2.1

2.1 Experiment site

The trial location was situated under semi-arid conditions, with mixed cultivation of orchards and field crops. The weather was characterized by extreme conditions i.e. hot summer and cold winter. Generally, temperatures begin to rise from mid-March and attain a maximum by May-June (mean maximum temperature is about 40 °C. The average rainfall in this area is about 96.2 mm, and the mean relative humidity is 61 %. The field trail was performed in the experimental zone of Horticulture Department, College of Agriculture, University of Sargodha in Punjab province of Pakistan.

2.2

2.2 Experiment

The field trial was conducted during October 2016–17. The seeds of 3 different vegetable species were collected from NARC, Islamabad, and sown on ridges. Seeds were dibbled manually by maintaining the proper distance. Three seeds of lettuce (Butter Head) and spinach (Local Sindhi) cabbage (Golden Acre) were sown per dibbled and thinned to a single plant after germination. All these vegetable varieties are mostly preferred in native region for home gardening. In addition, these varieties are high yielding capable to grow under stress conditions and have disease resistance.

Trials were conducted in split-plot two factorial designs where irrigational treatments were assigned in the main plot while vegetables were grown in micro plots. Theplot size was 90 cm × 300 cm and treatments were replicated thrice. Foliar application of Brassinosteroid @ 3.5 µM and Silicon @ 2 mM in case of lettuce and cabbage while Brassinosteroid @ 3.5 µM and Silicon @ 3 mM in case of spinach were applied at 15 days after germination in all three crops. The field was irrigated as per requirement with canal and sewage water according to the treatment plan.

2.3

2.3 Collection of data regarding growth parameters

For agronomic attributes, each seedling and its root were harvested after 35 days of plant growth, washed to clean its surface dirt, dried with tissue paper, and weighed by digital electric balance to determine the fresh weight. Harvested seedlings and roots were dried at 70 °C in an oven (KorlKolb 112 SL, Germany) for 48 h to constant mass. The dried weight of the seedling and root was determined through analytical balance. Area of leaf was estimated by using a digital meter (Ll-3000C) known as leaf area (LA) meter. The average leaf area was calculated by the method of (Binkley et al., 2002). The root length was measured with the help of measuring tape.

2.4

2.4 Collection of data regarding physiology and antioxidant enzymatic activities

Transpiration rate, Photosynthesis rate and stomatal conductance were determined by an instrument IRGA, CI-340 CID Biosciences, USA. All the gas exchange attributes were measured on top third leaf which was full expandedduring day hours. Water use efficiency (WUE) was measured by using following formula WUE = A / E Where, A = Photosynthetic rate E = transpiration rate

Similarly SPAD meter (502 SPAD spectrum) was used to measure chlorophyll contents of leaf.

The Catalase (CAT) activity was examined by a procedure elaborated by Chance and Maehly (1955). While superoxide dismutase (SOD) was measured by the method of Giannopolitis and Ries (1977). Activity of Peroxidase (POD) enzyme from solution mixture was measured by spectrophotometer (Hitachi U-1800) at 470 nm wavelength. The activity of antioxidant enzymes was determined on the basis of protein contents. Activity of Ascorbate peroxidase (APX) enzyme was measured by theprocedure explicated by Mittler and Zilinskas (1991). It was based on the stoichiometric reduction of phosphor molybdenum by ascorbic acid.

2.5

2.5 Determination of silicon, cadmium, and lead concentration

Spectrophotometer was used to measure concentration of silicon in plant sample according to the method explained by Elliott and Snyder (1991). Whereas atomic absorption spectrophotometer (AAS) was used to determine the Cadmium (Cd) and lead (Pb) contents in plant samples.

2.6

2.6 Statistical analysis

A statistical analysis on collected datawas performed to compare treatment means by using LSD at a 5 % probability level. The software Origin 2023 (Origin Lab, Massachusetts, USA) was used to make graphs and find the Pearson correlation among various growth, physiological, and antioxidant enzymatic activities with silicon, lead, and cadmium concentrations.

3

3 Results

3.1

3.1 Effect on growth attributes of leafy vegetables

Data (Table 1) regarding growth traits of lettuce, spinach, and cabbage showed that sewerage water irrigation reduced fresh weight of shoot, dry weight of shoot and leaf area as compared to canal water, as canal water contains less heavy metals than sewerage water. Mean while spraying BRs and Si on lettuce, cabbage, and spinach improved these parameters under the canal as well as sewage water irrigation. However, all these growth attributes were significantly (p ≤ 0.05) improved when lettuce, cabbage, and spinach were irrigated with canal water and sprayed with BRs and Si.

Table 1 Foliar Effect of BRs and Si solutions on fresh weight, dry weight and leaf area of leafy vegetables irrigated with canal and sewage water.
Treatments Water Source Lettuce Spinach Cabbage
Fresh weight (g) Dry weight (g) Leaf area (cm2) Fresh weight (g) Dry weight (g) Leaf area (cm2) Fresh weight (g) Dry weight (g) Leaf area (cm2)
Control CW 42.31 ± 2.60b 4.37 ± 0.27b 43.11 ± 2.65b 66.81 ± 4.10b 6.74 ± 0.41bc 78.83 ± 4.84b 54.56 ± 3.35bc 5.08 ± 0.31b 52.85 ± 3.25bc
SW 22.90 ± 2.03c 2.86 ± 0.25c 13.15 ± 2.34d 36.19 ± 3.21c 4.41 ± 0.39d 26.30 ± 4.67d 29.56 ± 2.62d 3.33 ± 0.29c 16.12 ± 2.86d
3.5 µM BRs CW 59.24 ± 3.64a 5.64 ± 0.32a 57.71 ± 4.79a 86.50 ± 5.31a 7.96 ± 0.45ab 101.46 ± 8.42a 76.39 ± 4.69ab 6.55 ± 0.37a 70.74 ± 5.87a
SW 44.90 ± 2.59b 4.43 ± 0.27b 33.13 ± 2.48c 70.90 ± 4.09b 5.84 ± 0.36c 65.04 ± 4.86bc 57.90 ± 3.34c 5.15 ± 0.32b 40.61 ± 3.04c
2.0 mM Si CW 62.82 ± 3.54a 5.56 ± 0.31a 57.02 ± 3.21a 87.32 ± 4.92a 8.70 ± 0.49a 99.43 ± 5.60a 81.01 ± 4.56a 6.47 ± 0.36a 69.89 ± 3.93ab
SW 46.40 ± 2.68b 4.44 ± 0.27b 34.17 ± 2.10bc 66.21 ± 3.82b 6.72 ± 0.41bc 60.60 ± 3.72c 59.83 ± 3.45c 5.16 ± 0.32b 41.88 ± 2.57c

Data about the root components (Table 2) of leafy vegetables in terms of root fresh weight, root dry weight and root length had revealed the negative effects of sewage water irrigation on leafy vegetables owing to significant reduction in root attributes while roots of plants irrigated with canal water flourished vigorously. Foliar spray of BRs and Si under canal water irrigation showed promising (p ≤ 0.05) results by improving root fresh weight, root dry weight and root length while minimum values of root components were observed for plants irrigated with sewage water without BRs and Si application.

Table 2 Foliar Effect of BRs and Si solutions on Root length, Root fresh weight and Root dry weight of leafy vegetables irrigated with canal and sewage water.
Treatments Water Source Lettuce Spinach Cabbage
Root length(cm) Root Fresh weight (g) Root Dry weight (g) Root length (cm) Root Fresh weight (g) Root Dry weight (g) Root length(cm) Root Fresh weight (g) Root Dry weight (g)
Control CW 7.08 ± 0.43b 18.28 ± 1.12b 1.95 ± 0.12b 8.00 ± 0.49b 19.42 ± 1.19b 2.74 ± 0.17b 7.08 ± 0.43b 17.48 ± 1.07b 2.51 ± 0.15b
SW 3.44 ± 0.21d 6.90 ± 0.42d 1.05 ± 0.06d 3.88 ± 0.24d 7.33 ± 0.45d 1.48 ± 0.09d 3.44 ± 0.21c 6.60 ± 0.41c 1.35 ± 0.08c
3.5 µM BRs CW 9.55 ± 0.54a 25.19 ± 1.55a 2.67 ± 0.16a 10.38 ± 0.58a 24.23 ± 1.49a 3.58 ± 0.22a 9.55 ± 0.54a 24.08 ± 1.48a 3.43 ± 0.21a
SW 6.19 ± 0.34bc 15.13 ± 0.83bc 1.72 ± 0.09bc 7.24 ± 0.40bc 17.58 ± 0.97b 2.48 ± 0.14bc 6.19 ± 0.34b 14.47 ± 0.80b 2.21 ± 0.12b
2.0 mM Si CW 9.31 ± 0.52a 24.02 ± 1.35a 2.58 ± 0.15a 10.90 ± 0.61a 26.47 ± 1.49a 3.74 ± 0.21a 9.31 ± 0.52a 22.97 ± 1.29a 3.32 ± 0.19a
SW 5.60 ± 0.31c 14.44 ± 0.80c 1.56 ± 0.09c 6.50 ± 0.36c 13.99 ± 0.77c 2.23 ± 0.12c 5.60 ± 0.31b 13.81 ± 0.76b 2.00 ± 0.11bc

3.2

3.2 Effect on gas exchange parameters, water use efficiency and chlorophyll contents

The maximum and significant (p ≤ 0.05) increase in gas exchange attributes in terms of transpiration rate, stomatal conductance and photosynthetic rate (Table 3) and chlorophyll contents and water use efficiency (WUE) (Table 4) of leafy vegetables was observed under canal water irrigation along with leafy spray BRs and Si solutions. Whereas the lowest values were recorded when plants were irrigated with sewerage water without any treatment.

Table 3 Foliar Effect of BRs and Si solutions on photosynthetic rate, transpiration rate and stomatal condtuctance of leafy vegetables irrigated with canal and sewage water.
Treatments Water Source Lettuce Spinach Cabbage
Photosynthetic
rate
(µmol m−2 s−1)
transpiration rate
(mmol m-2s−1)
Stomatal conductance (mmol−2 s−1) Photosynthetic
rate
(µmol m−2 s−1)
transpiration rate
(mmol m-2s−1)
Stomatal conductance (mmol−2 s−1) Photosynthetic
rate
(µmol m−2 s−1)
transpiration rate
(mmol m-2s−1)
Stomatal conductance (mmol−2 s−1)
Control CW 28.51 ± 1.76a 16.08 ± 0.99b 1.17 ± 0.06b 22.65 ± 1.39bc 10.33 ± 0.63b 1.04 ± 0.06b 27.42 ± 1.68a 16.14 ± 0.99bc 1.17 ± 0.06bc
SW 17.16 ± 1.05b 6.93 ± 0.43d 0.50 ± 0.03d 13.59 ± 0.83d 4.45 ± 0.27d 0.45 ± 0.03d 16.45 ± 1.01b 6.95 ± 0.43d 0.50 ± 0.03e
3.5 µM BRs CW 32.04 ± 1.97a 20.18 ± 1.24a 1.46 ± 0.09a 28.50 ± 1.75ab 12.59 ± 0.77a 1.33 ± 0.08a 30.71 ± 1.89a 20.26 ± 1.24ab 1.46 ± 0.09ab
SW 31.00 ± 1.71a 12.51 ± 0.69c 0.85 ± 0.05c 23.43 ± 1.29c 9.18 ± 0.51bc 0.92 ± 0.05bc 29.70 ± 1.64a 12.56 ± 0.69c 0.85 ± 0.05d
2.0 mM Si CW 32.96 ± 1.86a 20.99 ± 1.18a 1.52 ± 0.09a 29.78 ± 1.68a 12.61 ± 0.71a 1.39 ± 0.08a 31.59 ± 1.78a 21.08 ± 1.19a 1.52 ± 0.09a
SW 31.19 ± 1.72a 12.71 ± 0.73c 0.90 ± 0.06c 24.26 ± 1.34c 8.32 ± 0.48c 0.76 ± 0.05c 29.89 ± 1.65a 12.76 ± 0.74c 0.90 ± 0.06 cd
Table 4 Foliar Effect of BRs and Si solutions on WUE and chlorophyll contents of leafy vegetables irrigated with canal and sewage water.
Treatments Water Source Lettuce Spinach Cabbage
Water use efficiency (WUE) chlorophyll contents Water use efficiency (WUE) chlorophyll contents Water use efficiency (WUE) chlorophyll contents
Control CW 2.67 ± 0.15c 51.70 ± 2.85b 4.65 ± 0.26c 26.40 ± 1.46b 2.47 ± 0.15d 56.10 ± 3.09ab
SW 3.95 ± 0.24b 23.63 ± 2.09c 6.27 ± 0.39c 12.06 ± 1.07c 3.95 ± 0.24bc 25.64 ± 2.27c
3.5 µM BRs CW 2.97 ± 0.17ab 63.76 ± 3.59a 4.98 ± 0.30bc 32.56 ± 1.83a 2.92 ± 0.17 cd 69.19 ± 3.89ab
SW 4.88 ± 0.27b 50.57 ± 3.06b 7.10 ± 0.40a 26.05 ± 1.58b 4.48 ± 0.27ab 54.87 ± 3.33ab
2.0 mM Si CW 3.10 ± 0.17a 64.78 ± 3.65a 5.40 ± 0.30ab 33.08 ± 1.86a 3.22 ± 0.17b 70.30 ± 3.96a
SW 5.26 ± 0.32a 49.37 ± 2.85b 7.65 ± 0.47a 25.44 ± 1.47b 5.26 ± 0.32a
53.57 ± 3.09b

3.3

3.3 Effect on enzymatic activity

Data related to the activity of antioxidant enzymes such as SOD, POD, CAT and APX in lettuce, cabbage and spinach plants revealed (Figs. 1 and 2) that enzymatic activity was significantly (p ≤ 0.05) influenced byBRs and Si under both types of irrigation sources. BRs and Si mitigated the negative effects of metal stress and aggaravated the activity of antioxidant enzymes. The minimum enzymatic activity was recorded when plants were irrigated with sewerage water without BRs and Si whereas plants irrigated with canal water or sewerage water showed higher activity under the foliar spray of BRs and Si solutions.

Foliar effect of BRs and Si on superoxide dismutase (SOD) and catalase activity (CAT) of leafy vegetables irrigated with canal and sewage water. Means sharing same letter (s) do not differ significantly at p ≤ 0.05.
Fig. 1
Foliar effect of BRs and Si on superoxide dismutase (SOD) and catalase activity (CAT) of leafy vegetables irrigated with canal and sewage water. Means sharing same letter (s) do not differ significantly at p ≤ 0.05.
Foliar effect of BRs and Si on peroxidase dismutase (POD) and ascorbate peroxidase (APX) activity of leafy vegetables irrigated with canal and sewage water. Means sharing same letter (s) do not differ significantly at p ≤ 0.05.
Fig. 2
Foliar effect of BRs and Si on peroxidase dismutase (POD) and ascorbate peroxidase (APX) activity of leafy vegetables irrigated with canal and sewage water. Means sharing same letter (s) do not differ significantly at p ≤ 0.05.

3.4

3.4 Effect on silicon, cadmium, and lead uptake

Data about concentration of Cd and Pb in vegetable plants showed (Fig. 3) increased content of Cd and Pb in plants were observed when sewerage water was applied as an irrigation source while minimum heavy metal (Cd and Pb) concentration was observed when irrigated with canal water. However, minimum Cd concentration was recorded in plants when irrigated with canal water along with a foliar spray of BRs and Si while plants irrigated with sewerage water and no foliar spray of BRs and Si showed maximum uptake of Cd and Pb concentration.

Foliar effect of BRs and Si on Si, Pb and Cd concentration of leafy vegetables irrigated with canal and sewage water. Means sharing same letter (s) do not differ significantly at p ≤ 0.05.
Fig. 3
Foliar effect of BRs and Si on Si, Pb and Cd concentration of leafy vegetables irrigated with canal and sewage water. Means sharing same letter (s) do not differ significantly at p ≤ 0.05.

The results regarding silicon contents in leafy vegetables showed (Fig. 4) that foliar spray of Si improved the Si contents significantly (p ≤ 0.05) and followed by BRs. The increase in Si concentration decreased the detrimental effects of Cd and Pb found in sewerage water. Minimum Si concentration was measured in plants when irrigated with sewerage water without foliar spray of Si. On the other hand, plants irrigated with canal water and foliar spray of silicon (Si) significantly improved Si contents.

Correlation between antioxidant enzymatic activities, growth parameters and metal concentration in lettuce. Superoxide dismutase (SOD), catalase (CAT) peroxidase (POD), Ascorbate peroxidase (APX), Si (silicon), Pb (lead), Cd (cadmium), SFW (shoot fresh weight), SDW (shoot dry weight), RL (root length) and Chl (chlorophyll contents).
Fig. 4
Correlation between antioxidant enzymatic activities, growth parameters and metal concentration in lettuce. Superoxide dismutase (SOD), catalase (CAT) peroxidase (POD), Ascorbate peroxidase (APX), Si (silicon), Pb (lead), Cd (cadmium), SFW (shoot fresh weight), SDW (shoot dry weight), RL (root length) and Chl (chlorophyll contents).

3.5

3.5 Pearson association between growth and physiological parameters, metal concentration, and antioxidant enzymatic activities

The data revealed that the shoot fresh and dry weight, chlorophyll content, and root length were significantly positively associated with POD, SOD, CAT, and APX in all the tested leafy vegetables (Figs. 4, 5, and 6). However, the Pb and Cd concentration was negatively related to the growth parameters and antioxidant enzymatic activities in spinach, cabbage, and lettuce. Silicon concentration was not significantly associated with shoot fresh and dry weight, root length, and chlorophyll contents but it was negatively associated with the concentration of Pd and Cd.

Correlation between antioxidant enzymatic activities, growth parameters and metal concentration in spinach. Superoxide dismutase (SOD), catalase (CAT) peroxidase (POD), Ascorbate peroxidase (APX), Si (silicon), Pb (lead), Cd (cadmium), SFW (shoot fresh weight), SDW (shoot dry weight), RL (root length) and Chl (chlorophyll contents).
Fig. 5
Correlation between antioxidant enzymatic activities, growth parameters and metal concentration in spinach. Superoxide dismutase (SOD), catalase (CAT) peroxidase (POD), Ascorbate peroxidase (APX), Si (silicon), Pb (lead), Cd (cadmium), SFW (shoot fresh weight), SDW (shoot dry weight), RL (root length) and Chl (chlorophyll contents).
Correlation between antioxidant enzymatic activities, growth parameters and metal concentration in cabbage. Superoxide dismutase (SOD), catalase (CAT) peroxidase (POD), Ascorbate peroxidase (APX), Si (silicon), Pb (lead), Cd (cadmium), SFW (shoot fresh weight), SDW (shoot dry weight), RL (root length) and Chl (chlorophyll contents).
Fig. 6
Correlation between antioxidant enzymatic activities, growth parameters and metal concentration in cabbage. Superoxide dismutase (SOD), catalase (CAT) peroxidase (POD), Ascorbate peroxidase (APX), Si (silicon), Pb (lead), Cd (cadmium), SFW (shoot fresh weight), SDW (shoot dry weight), RL (root length) and Chl (chlorophyll contents).

4

4 Discussion

4.1

4.1 Growth attributes of vegetables

The stunted growth of all leafy vegetables was owing to the upregulation of heavy metals, particularly Cd and Pb under sewage water irrigation. The improvement in growth attributes in terms of fresh weight of shoot and roots and dry weight of shoot and roots, root length, and leaf area were attributed to the foliar spray of BRs and silicon. Foliar application of BRs accelerated cell division and cell elongation controlling the growth of plants under a heavy metal stress (Shafi et al., 2023). Likewise, Si foliar application also improved photosynthetic apparatus and nutrient absorption by confining the translocation of Cd an Pb which subsequently were associated with improved growth in plants (Hussain et al., 2019). Si spray also contributed to the intermodal elongation of shoots of leafy vegetables under metal contamination stress (Kabir et al., 2016).

4.2

4.2 Gas exchange parameters of vegetables and chlorophyll contents

Transpiration rate, Photosynthetic rate, stomatal conductance and chlorophyll contents were downregulated under sewage water irrigation due to the absorption of metal ions (Cd and Pb) in high concentration rather than other essential nutrients. Uptake of Cd and Pb in high concentration inhibited the exchange of CO2 and O2 in plant parts by increased chlorophyllase activity leading to disrupted stomatal conductance and transpiration rate which were imperative for the process of photosynthesis (Paunov et al., 2018; Hajihashemi et al., 2020). The upregulation in these gas exchange attributes was observed under BRs and Si application and they improved photosynthetic pigment by adjusting ion homeostasis and CO2 fixation by reducing Cd and Pb ions and activity of chlorophyllase enzymes in plant tissues leading to encourage exchange parameters and chlorophyll contents in plant leaves (Adrees et al., 2015; Sonjaroon et al., 2018). BRs and Si foliar application to leafy vegetables prevented the accumulation of toxic elements and increased availability of essential ions in plants to improve photosynthetic rate by replacing central atom (Mg2+) of photosynthetic apparatus which is directly associated with increased stomatal conductance, transpiration rate and chlorophyll pigment (Agami, 2013; Shu et al., 2013).

4.3

4.3 Water use efficiency of vegetables

A decline in water use efficiency (WUE) by leafy vegetables was recorded under sewage water irrigation which is attributed to low relative water contents due to the toxic concentration of metal elements. Accumulation of Cd and Pb caused damage to plant plasma membrane due to the induction of reactive oxygen species (ROS) leading to a decrease in water transporters and subsequently low water use efficiency (Kaur et al., 2018). Foliar spray of BRs and Si reversed the loss of relative water contents by improving the membrane stability index owing to the limited supply of heavy metal ions. These also contributed to reducing oxidative damage to the plasma membrane by lowering toxic elements and upregulation of essential elements to increase membrane stability and relative water contents (Jan et al., 2018). Under stress environment foliar spray of BRs also increased osmolytes, particularly proline and Glycinebetain (GB) which improved water potential in plant tissues (Ahmad et al., 2015). All these processes are associated with improved WUE in leafy vegetables under both canal water and sewage water irrigation.

4.4

4.4 Activity of antioxidant enzymes in vegetables

The activity of antioxidants such as SOD, POD, CAT and APX in leafy vegetables decreased under sewage water irrigation while increased under canal water irrigation. Generally, the antioxidants activity increased under stress environment but our results are contradictory with the findings of other researchers such as (Fulekar et al., 2012) and (Garcia-Caparros et al., 2021). This might be due to the fact that in some situations protein misfolding happens under heavy metal stress that can decrease the activities of the enzymes. Moreover, for the activation of antioxidant enzymes, plants must be genetically capable of producing and activating antioxidant enzymes. Thus in some conditions, the plants are unable to activate the antioxidant system due to the lack of genetic capabilities (Tamás et al., 2014). Thus foliar application of BRs and Si is attributed to improve antioxidant enzymatic activities under both types of irrigation sources; canal water and sewage water. Under heavy metal stress, BRs and Si augmented their activity by lowering translocation of Cd metal through chelating agents (phytochelatins, phenols) and activating metal regulation through metal transporter within plants (Jan et al., 2018). The increase in activity of antioxidants caused a reduction in ROS species including hydrogen peroxide (H2O2) and singlet oxygen (O2) and subsequently upregulated plant metabolic functions (Rahman et al., 2017).

4.5

4.5 Silicon, cadmium, and lead contents in vegetables

Increased concentration of silicon under stressed conditions is attributed to the adjustment of ion homeostasis by foliar application of Si and BRs in leafy vegetables (Wani et al., 2017). Furthermore, silicon application prompted to formation of silicates in cytoplasm leading to restricting the mobility of Cd and Pb in plants. Foliar application of Si also increased silicon contents by inducing silicon-containing compounds such as cysteine, glutathione, and methionine (Ji et al., 2017). Whereas transportation of Cd and Pb diminished due to increased absorption of other essential elements including P, K, Mg, Ca and Si, within plant tissues (Ahmad et al., 2018) through the antagonistic effect of nutrient ions. Thus depressing effect of Br and Si on Cd and Pb concentrations was mediated by ion homeostasis and the antagonistic effect of nutrient ions with each other (Waisi et al., 2017). Moreover, the induction of chelating agents like phenols and phytocelatins (PC) by BRs and Si provided favorable conditions for osmotic adjustment to vegetable plants under heavy metal stress (Cao et al., 2017).

5

5 Conclusion

All the measured attributes regarding growth, physiological, biochemical and yield of leafy vegetables had decreased significantly when irrigated with sewage water as compared to canal water. However, foliar application of BRs and Si solution in recommended doses under both irrigation sources had delivered a substantial contribution in minimizing the overwhelming affects of Cd and Pb stress due to sewage water irrigation. Foliar application of BRs and Si was proved as an ameliorating strategy for heavy metal stress by improving tolerance mechanisms associated with heavy metal stress. The major ameliorating mechanism in this strategy was restricted translocation of Cd and Pb leading to improved growth and silicon contents. Our study was limited to only two heavy metals Cd and Pb due to their dominance in sewage water. This strategyfurther could be applied under different ecological zones of Pakistan in the future.

6

6 Compliance with ethical standards

Not applicable.

7

7 Declaration of funding

This research did not receive any specific grant from funding agencies in the public, commercial, or not-for-profit sectors.

Author contributions

All authors contributed in research conception. RMB and SAJ drafted the experimental design and MTJ did the experimental work. AS, BAP and AA analyzed the data and helped the writing of this paper. RS, RMB, SAJ and AS revised the manuscript.

CRediT authorship contribution statement

Rashad Mukhtar Balal: Writing – review & editing, Methodology, Conceptualization. Syed Ayyaz Javed: Writing – review & editing, Methodology, Conceptualization. Muhammad Tauseef Jaffar: Investigation, Conceptualization. Anam Sadaf: Writing – original draft, Formal analysis, Data curation, Conceptualization. Bilal Ahamad Paray: Writing – original draft, Formal analysis, Data curation, Conceptualization. Rattandeep Singh: Writing – review & editing, Conceptualization.

Acknowledgements

The authors would like to extend their sincere appreciation to the Researchers Supporting Project Number (RSP2024R144) King Saud University, Riyadh, Saudi Arabia.

Declaration of competing interest

The authors declare that they have no known competing financial interests or personal relationships that could have appeared to influence the work reported in this paper.

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Appendix A

Supplementary data

Supplementary data to this article can be found online at https://doi.org/10.1016/j.jksus.2024.103310.

Appendix A

Supplementary data

The following are the Supplementary data to this article:

Supplementary Data 1

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