Impact of Heavy Metal Pollution in the Environment on the Metabolic Profile of Medicinal Plants and Their Therapeutic Potential
Abstract
:1. Introduction
1.1. Importance of Medicinal Plants and Their Compounds
1.2. Medicinal Plants and Their Bioactive Compounds
2. Medicinal Plant Compounds with Antioxidant Activity
2.1. Key Medicinal Plant Compounds Known for Their Antioxidant Properties
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- Polyphenols: represent a group of naturally occurring compounds characterized by the presence of multiple phenol structural units. They are widely distributed in plants and have gained significant attention for their antioxidant properties [4]. Flavonoids, phenolic acids, lignans, and stilbenes are subcategories of polyphenols found in various medicinal plants. Quercetin, resveratrol, and catechins are well-known polyphenols with potent antioxidant activities [27,28].
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- Flavonoids: constitute a major subclass of polyphenols and are renowned for their antioxidant, anti-inflammatory, and anticancer properties. They are abundant in fruits, vegetables, and medicinal herbs. Quercetin (found in apples, onions), epicatechin (abundant in green tea, cocoa), and hesperidin (citrus fruits) are prominent flavonoids with notable antioxidant effects [29,30].
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- Alkaloids: e a diverse group of nitrogen-containing compounds with varying pharmacological activities. Many alkaloids derived from medicinal plants exhibit antioxidant potential, contributing to their therapeutic effects [2]. Berberine (found in Berberis species), caffeine (present in coffee beans), morphine (from Papaver somniferum) are examples of alkaloids known for their antioxidant properties [31,32].
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- Carotenoids: are pigments responsible for the red, orange, and yellow colors in various fruits and vegetables. They serve as antioxidants and are vital for human health, especially in protectting against oxidative stress. Beta-carotene (abundant in carrots, sweet potatoes), lutein (found in spinach, kale), and lycopene (present in tomatoes) are well-studied carotenoids with antioxidant benefits [33,34].
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- Terpenoids (terpenes): are a large and diverse class of compounds derived from the isoprene unit. They are found in essential oils and resinous exudates of medicinal plants, contributing to their antioxidant and anti-inflammatory activities [35]. Limonene (citrus fruits), menthol (mint), and curcumin (turmeric) are terpenoids known for their antioxidant and medicinal properties.
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- Phenolic acids: are a subgroup of polyphenols with a phenolic ring and an acidic moiety. They are abundant in fruits, vegetables, and whole grains, playing a crucial role in the antioxidant defense system [36,37]. Ferulic acid (present in whole grains), caffeic acid (found in coffee), and rosmarinic acid (in rosemary and sage) are phenolic acids with antioxidant potential.
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- Saponins: are glycosides with a hydrophobic aglycone, exhibiting diverse biological activities, including antioxidant effects. They are commonly found in various medicinal plants [38]. Examples of saponins with antioxidant properties are ginsenosides (from Panax ginseng), quillaja saponins (from Quillaja saponaria), and soyasaponins (from soybeans).
2.2. Significance of Antioxidant Activity in Sustaining Plant Health
2.3. Significance of Natural Antioxidant Activity in Maintaining Human Health
2.4. Factors Affecting the Content of Antioxidants in Medicinal Plants
2.4.1. Factors with Positive Influence on the Content of Antioxidants in Medicinal Plants
2.4.2. Factors with Negative Influence on the Content of Antioxidants in Medicinal Plants
3. Impact of Environmental Pollution on Antioxidant Content and Activity in Medicinal Plants
3.1. Air Pollution
3.2. Water Pollution
3.3. Soil Pollution
4. Heavy Metal Pollution of the Environment and Concerns for Medicinal Plants
4.1. Source of Environmental Pollution with Heavy Metals
4.2. Uptake and Accumulation of Heavy Metals in Medicinal Plants
4.2.1. Exploring How Medicinal Plants Absorb and Accumulate Heavy Metals
4.2.2. Factors Influencing the Heavy Metals Uptake Process by Herbs
4.3. Impact of Heavy Metals on Medicinal Plant Compounds
4.3.1. Heavy Metals Impact on the Synthesis and Concentration of Medicinal Plant Compounds
4.3.2. Variations in Responses among Different Medicinal Plant Species versus Heavy Metal Action
4.3.3. Soil Microbial Interactions and Interactive Soil-Metal-Plant Relationships
4.3.4. Hormonal Regulation
4.3.5. Epigenetic Modifications and Regulation
4.3.6. Interactive Effects with Environmental Factors
5. Mechanisms of Heavy Metal-Induced Changes in Antioxidant Activity
5.1. Molecular and Biochemical Insights into the Impact of Heavy Metals on Antioxidant Activity in Medicinal Plants
5.1.1. Heavy Metal Uptake and Translocation
5.1.2. Oxidative Stress Initiation
5.1.3. Antioxidant Defense Mechanisms
5.1.4. Metal-Chelating Compounds and Detoxification
5.1.5. Bioactive Compound Synthesis
5.1.6. Species-Specific Responses
5.1.7. Interactive Effects of Co-Contaminants
5.1.8. Long-Term Consequences
5.1.9. Interactions among Secondary Metabolites
5.1.10. Cellular Compartmentalization
5.2. Other Potential Pathways and Interactions Involved in the Impact of Heavy Metals on Medicinal Plants’ Antioxidant Activity
5.2.1. Cellular Signaling Networks
5.2.2. Metabolic Reprogramming
5.2.3. Redox-Sensitive Transcription Factors
5.2.4. Interactive Root-Shoot Signaling
5.2.5. Post-Transcriptional Regulation
5.2.6. Synthetic Biology Approaches
5.2.7. Ecosystem-Level Dynamics
6. Implications of Heavy Metal-Induced Alterations on Bioactive Compounds and Therapeutic Potential of Medicinal Plants
6.1. Effects of Heavy Metals Stress on Bioactive Compounds Changes and Their Therapeutic Capacity
6.2. Potential Risks for Human Consumption of Medicinal Plants Contaminated with Heavy Metals
7. Methodology
7.1. Information Sources
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- Databases: Major databases such as ScienceDirect, Springer, Wiley, PubMed, Scopus, and Web of Science were searched to retrieve relevant studies. These databases cover the period from 2010 to 2024.
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- Date last searched: The databases were last searched in 2015 to ensure that the most up-to-date studies were included in the review.
7.2. Electronic Search Strategy
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- Search terms: antioxidant defense mechanisms; bioactive compound synthesis; environmental factors; health risks; epigenetic modifications; oxidative stress; redox equilibrium; regulatory challenges; root-shoot signaling
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- Limits: publication date: 2010–2024, language: English
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- Boolean operators: the use of AND, OR, NOT operators
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- Search syntax: e.g., Web of Science: TS = (“medicinal plants” AND “antioxidants” AND “heavy metal”) AND PY = 2010–2024; e.g., Scopus: TITLE-ABS-KEY(“medicinal plants” AND “antioxidants” AND “heavy metal”) AND PUBYEAR > 2010 AND PUBYEAR < 2024; ScienceDirect: e.g., TITLE-ABS-KEY(“medicinal plants” AND “antioxidants” AND “heavy metal”) AND PUBYEAR > 2010 AND PUBYEAR < 2024
7.3. Study Selection Process
7.4. Methodologies to Minimize Bias
7.4.1. Comprehensive Search
7.4.2. Inclusion Criteria
7.4.3. Risk of Bias Analysis
7.5. Data Extraction
7.6. Additional Analyses
8. Conclusions
9. Recommendations for Future Research
Author Contributions
Funding
Data Availability Statement
Conflicts of Interest
References
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Characteristics | Factors | Description | References |
---|---|---|---|
Soil characteristics | pH levels | The pH of the soil plays an essential role in metal availability to plants. Generally, metals like lead and cadmium are more available in acidic soils, while alkaline conditions may enhance the mobility of metals like nickel and zinc. Soil pH affects metal speciation, influencing their solubility and uptake | [82,95,96] |
Soil texture | The texture of the soil, whether it’s sandy, loamy, or clayey, affects water retention and drainage. Sandy soils, for example, generally have lower cation exchange capacity (CEC) and may allow metals to leach more easily. Clay soils, with higher CEC, can retain metals, influencing their availability. | [54,89,97,98] | |
Organic matter content | Soil organic matter can bind with metals, affecting their mobility and bioavailability. High organic matter content tends to reduce metal uptake by forming complexes, while low organic matter may enhance metal mobility. | [23,99,100,101] | |
Metal characteristics | Chemical form | The chemical form or speciation of metals in the soil determines their availability to plants. Metals may exist in various forms, such as free ions, complexes, or bound to soil particles. Plants tend to take up metal ions more readily than complexed or precipitated forms. | [102,103] |
Redox potential | The redox potential of the soil, indicating its oxidative or reducing conditions, affects metal speciation. For instance, in reduced conditions, metals like iron and manganese become more soluble, influencing their availability for plant uptake | [104,105] | |
Plant-related factors | Plant species | Different plant species exhibit varying affinities for specific metals. Some species are hyperaccumulators, capable of accumulating high concentrations of certain metals without significant toxicity. Understanding the metal uptake characteristics of specific plant species is critical for phytoremediation and sustainable land management. | [61,106,107] |
Root characteristics | The morphology and structure of plant roots influence metal uptake. Plants with extensive root systems can explore larger soil volumes and access metals more effectively. The presence of root filaments and mycorrhizal symbiosis can also enhance metal uptake. | [65,79,108,109,110] | |
Physiological responses | Plants respond to metal stress by activating various physiological mechanisms. Metallothioneins, phytochelatins, and glutathione are examples of compounds synthesized by plants to chelate and detoxify metals, mitigating their potential harmful effects. | [83,111] | |
Environmental conditions | Temperature and moisture | Environmental conditions such as temperature and moisture influence microbial activity and the chemical reactions in the soil. These conditions, in turn, affect metal availability and uptake. Warmer temperatures may enhance microbial activity, influencing metal transformations. | [47,69,112] |
Aeration | Adequate soil aeration is essential for root respiration and microbial activity. Poor aeration, often associated with waterlogged conditions, may create reducing conditions that influence the mobility and uptake of certain metals. | [109,110] | |
Competing ions | The presence of other ions in the soil solution can compete with metal ions for uptake by plant roots. High concentrations of essential nutrients or other ions may influence the bioavailability and uptake of heavy metals. | [23,73,107] |
Key Aspect | Response | Description | References |
---|---|---|---|
Metal tolerance and accumulation | Differential tolerance | Plant species vary in their tolerance to specific heavy metals. Some species demonstrate a higher tolerance to elevated metal concentrations in the soil, allowing them to thrive in metal-contaminated environments. Others may be more sensitive and susceptible to metal toxicity. | [77,87,124,125] |
Accumulation capacities | Certain plant species are adept at accumulating and sequestering heavy metals in their tissues without suffering severe toxicity. These metal-accumulating plants, known as hyperaccumulators, can store high concentrations of metals in their tissues, often as a defense mechanism against herbivores or pathogens. | [61,81,107] | |
Morphological and physiological adaptations | Root morphology | Variations in root morphology contribute to differential metal uptake among plant species. Some species may develop specialized root structures, such as root hairs or mycorrhizal associations, to enhance metal absorption and tolerance. | [79,87,126,127] |
Metal transport mechanisms | Different plant species employ distinct mechanisms for transporting heavy metals within their tissues. These mechanisms, including metal transporters and chelation processes, contribute to the variations observed in metal accumulation and distribution. | [60,66,121] | |
Biochemical responses | Metal chelation | Plants utilize various biochemical strategies to cope with metal stress. Chelation involves the binding of metals to organic molecules, reducing their toxicity. Some species may exhibit a higher capacity for metal chelation, leading to lower levels of free, toxic metal ions in plant tissues. | [50,77,111,121] |
Synthesis of metal-binding proteins | Differences in the synthesis of metal-binding proteins, such as metallothioneins and phytochelatins, contribute to species-specific responses. These proteins play critical roles in detoxifying metals and regulating metal homeostasis. | [83,111,128,129] | |
Genetic variation | Genetic diversity | Genetic factors significantly influence the responses of plant species to heavy metals. Variations in gene expression, genetic traits related to metal tolerance, and the presence of specific alleles contribute to the observed diversity in responses among different species. | [49,125,127] |
Adaptation and evolution | Over time, plant species may evolve specific adaptations to metal-contaminated environments. Natural selection favors individuals with genetic traits that confer advantages in metal-rich soils, leading to the development of metal-tolerant populations. | [81,130,131] | |
Impact on growth and reproduction | Growth inhibition | The impact of heavy metals on plant growth varies among species. Some plants may exhibit minimal growth inhibition, while others experience stunted growth, chlorosis, and other morphological abnormalities in the presence of elevated metal concentrations. | [48,59,73] |
Reproductive consequences | Heavy metal exposure can affect reproductive processes differently across plant species. Some may maintain reproductive success, while others may experience reduced seed production, impaired germination, or altered reproductive structures | [46,49,122,132] | |
Soil-metal interactions | Rhizospheric influences | The rhizosphere, the soil region influenced by root activity, plays a decisive role in mediating plant-metal interactions. Variations in root exudates and microbial communities within the rhizosphere contribute to species-specific responses to heavy metal exposure. | [69,81,133,134] |
Soil pH and composition | Soil properties, including pH and composition, interact with metal availability. Plant species may exhibit differential responses based on their preferences for specific soil conditions, influencing metal bioavailability and uptake. | [59,92,112] |
Heavy Metal-Induced Changes | Implications | Effect |
---|---|---|
Alterations in bioactive compound profiles | Heavy metal stress can lead to changes in the biosynthesis of bioactive compounds, including polyphenols, alkaloids, and flavonoids, which contribute to the medicinal properties of plants | The altered profiles may result in variations in the concentration and diversity of bioactive compounds, influencing the plant’s overall pharmacological efficacy. |
Reduction in antioxidant capacity | Heavy metals induce oxidative stress, diverting resources toward antioxidant defenses. This may lead to a reduction in the antioxidant capacity of medicinal plants. | The diminished antioxidant activity may compromise the plant’s ability to neutralize free radicals, potentially reducing its effectiveness in combating oxidative stress-related health issues. |
Changes in secondary metabolite pathways | Heavy metal-induced disruptions in metabolic pathways can affect the synthesis of secondary metabolites, such as terpenoids and phenolics | Variations in these pathways may result in the loss or alteration of specific secondary metabolites, impacting the plant’s holistic therapeutic properties. |
Risk of contaminant accumulation | Medicinal plants may accumulate heavy metals, especially in the roots, leading to the risk of contamination | The presence of contaminants in medicinal plant tissues may pose health risks to consumers, as the plants intended for therapeutic use may inadvertently introduce heavy metals into herbal preparations. |
Influence on medicinal plant adaptations | Some medicinal plants may adapt to heavy metal stress by altering their physiological and biochemical responses. | While adaptations may enhance the plant’s survival in contaminated environments, they can also result in variations in the composition of bioactive compounds, affecting the plant’s traditional uses and applications. |
Compromised reproductive success | Heavy metal stress can affect reproductive processes, leading to compromised seed production and germination. | Reduced reproductive success may impact the availability and sustainability of medicinal plant populations, affecting the long-term supply of plant material for traditional medicine and herbal industries. |
Long-term effects on plant health | Prolonged exposure to heavy metals may exert cumulative effects on the overall health and vitality of medicinal plants | Chronically stressed plants may exhibit weakened immune responses, stunted growth, and increased susceptibility to pests and diseases, further compromising their quality and efficacy. |
Genetic and phenotypic variability | Genetic diversity among medicinal plant populations influences their responses to heavy metals | Variability in genetic and phenotypic traits can lead to differences in the susceptibility of plant populations to heavy metal stress, resulting in variable impacts on the quality and efficacy of medicinal plants. |
Environmental considerations | Medicinal plants grown in polluted environments may serve as phytoremediators, but their efficacy as therapeutic agents may be compromised. | The dual role of medicinal plants in environmental cleanup and traditional medicine raises ethical considerations, as the plants may accumulate contaminants while providing medicinal benefits. |
Consumer health risks | Contaminated medicinal plants pose potential health risks to consumers due to the presence of heavy metals. | Ingesting herbal preparations containing elevated levels of heavy metals may lead to adverse health effects, counteracting the intended therapeutic benefits and undermining the safety of traditional medicine. |
Synergistic interactions with co-contaminants | Medicinal plants often face co-contamination with multiple pollutants, including heavy metals and other environmental contaminants. | The synergistic or antagonistic interactions between co-contaminants may amplify or mitigate the impacts on the plant’s physiology, altering its biochemical composition and potentially affecting therapeutic efficacy. |
Impact on traditional knowledge and uses | Heavy metal contamination may challenge traditional knowledge regarding the selection and use of medicinal plants. | Traditional uses based on generations of empirical knowledge may need to be re-evaluated, considering the potential variations in bioactive compound profiles and the safety of using contaminated plants for therapeutic purposes. |
Phytoremediation potential vs. medicinal quality | Some medicinal plants are known for their phytoremediation potential, contributing to environmental cleanup | The trade-off between using plants for phytoremediation and maintaining their medicinal quality requires careful consideration. Strategies need to be developed to balance environmental benefits with the preservation of therapeutic efficacy. |
Influence on herbal industry and trade | Heavy metal contamination can impact the herbal industry and international trade of medicinal plants. | Stringent quality control measures may be necessary to ensure that herbal products meet safety standards. The reputation of medicinal plants from specific regions may be affected if contamination issues arise. |
Pharmacological variability within plant populations | Genetic and environmental factors contribute to pharmacological variability within medicinal plant populations. | Variability may extend to the concentration of bioactive compounds, making standardized formulations challenging. Identifying and selecting plant sources with minimal contamination becomes critical for ensuring consistent therapeutic effects. |
Regulatory considerations and quality standards | Regulatory bodies need to adapt to evolving challenges related to heavy metal contamination in medicinal plants. | Establishing and enforcing stringent quality standards, including maximum allowable limits for heavy metals, becomes crucial to safeguarding consumer health and maintaining the integrity of herbal products in the market. |
Community health and environmental justice | Communities relying on traditional medicine may be disproportionately affected by heavy metal contamination in medicinal plants. | Environmental justice considerations come into play, highlighting the need for sustainable land management practices, community awareness, and collaborative efforts to address both environmental and health concerns. |
Emerging technologies for monitoring and remediation | Advancements in technology offer new tools for monitoring heavy metal contamination and remediating polluted environments. | Integrating these technologies into herbal cultivation practices can enhance the safety and quality of medicinal plants. Nanotechnology, for example, shows promise in developing efficient and eco-friendly remediation strategies. |
Community-based conservation initiatives | Local communities are often the stewards of medicinal plant knowledge and resources. | Implementing community-based conservation initiatives that focus on sustainable cultivation practices, soil health improvement, and education can contribute to preserving the medicinal quality of plants while addressing environmental concerns. |
Global collaboration and research priorities | Heavy metal contamination is a global issue with far-reaching implications | Prioritizing collaborative research efforts, sharing knowledge, and implementing standardized methods for assessing heavy metal levels in medicinal plants can contribute to a global understanding and management of this complex challenge. |
Plant Name | Metal Concentration | Effect on Germination | Effect on Vegetative Growth | Effect on Reproductive Growth |
---|---|---|---|---|
Adhatoda vasica L. | 0, 100, 200, 300, 400, 500, 600 ppm | na | Increasing Cd conc. had inhibitory effect on elongation, fresh and dry weight of root and shoot RRG value, leaf number, fresh weight, and area | Number, dry weight, fresh weight of inflorescence, flower bud, fruit reduced |
Alternanthera tanella Colla | 0, 50, 100, 150 mM | na | The shoots and roots reduced with increasing concentration | na |
Amaranthus spinosus L. | 5–50 ppm for 60 days | na | Significant reduction in root and shoot length and fresh weight in dose dependent manner | na |
Andrographis paniculata (Burm.f.) Nees | 10, 50, 100, 150 and 200 ppm | na | Root and stem elongation, RRG values, leaf number, dry and fresh weight of root, stem, and leaf was gradually lowered and percent phytotoxicity values increased with increasing in metal concentration | Inflorescence branch number pollen tube growth and pollen germination, flower, flower bud and fruit number n fresh weight of inflorescence and flower bud decreased |
Anethum graveolens L. | 0, 100 and 200 mM | na | Root length, leaf area, shoot and root dry weight decreased | na |
Bacopa monnieri L. | 5, 10, 50, 100 mM | na | Browning and stunting of roots with decreased biomass were observed with increasing Cd concentration | na |
Bidens pilosa L. | 2.57, 7.94, 17.33, 37.17 ppm for 40 days | na | Root and shoot biomasses gradually decreased with increasing concentration | na |
Brassica juncea L. | 200 and 300 mg L−1 | na | Plant height, root length and biomass reduced | na |
Cannabis sativa L. | 25 mg kg−1 Cd for 45 days | na | Shoot and root biomass decreased with increasing concentration | na |
Catharanthus roseus var. rosea L. | (0, 10, 50, 100, 200, 500 and 1000 µM | 0% germination at 1000 µM concentration | The root length was inhibited | na |
Cajanus cajan L. | 1, 5, 10, 20, 50 mg L−1 | 60% reduction in seed germination with a decrease in the fresh and dry weight reduction in growth, stunting of seedlings | Reduction in fresh and dry weight and stunting of seedlings | na |
Centella asiatica L. | 50–100 ppm for 30 days | na | The root length remained the same except at 100 ppm while the shoot length increased significantly with metal concentration | na |
Cichorium pumilum Jacq. | 50, 100, 200, 400, 800, and 1600 µM | na | Hypocotyl and root length decreased with increasing Cd concentration | na |
Coriandrum sativum L. | 0, 25, 50, and 100 mg kg−1 | Germination % (least at 50 mg−1 kgCd) | Root length, shoot length decreased with an elevation of Cd conc. with least at 100 mg kg−1 Cd | na |
Cuminum cyminum L. | 0, 300, 450, 600, 750 and 1050 µM | 30% and 23% inhibition in seed germination of Isfahan and Khorasan ecotypes respectively. | 43.6% and 48.7% of root growth inhibition of Isfahan and Khorasan ecotypes respectively. | na |
Drimia elata Jacq. ex Willd. | 2, 5, 10 mg L−1 | na | The shoot and bulb dry weight reduced significantly with higher concentrations | na |
Melissa officinalis L. | 0, 10, 20 and 40 mM | na | Fresh weight increased up to 20 mM | na |
Merwilla plumbea (Lindl.) Speta | 1.5 ppm | na | The fresh weight of leaves, bulbs and roots significantly reduced | na |
Moringa oleifera Lam. | 1–5 mM for 30 days | na | The root and shoot length significantly reduced | na |
Ocimum basilicum L. | 5, 10, 15, 20, 25 ppm | na | The fresh and dry weight declined with increasing Cd concentration | na |
Ocimum basilicum L. | 0–16 mg L−1 | 4% reduction in germination at 16 mg L−1 Cd | na | na |
Ocimum canum Sims. | 50, 100, 150, 200, 250 mg kg−1 | na | The root elongation and stem height inhibited | Flower number and its fresh weight and dry weight, inflorescence, fruit number. dry weight |
Phyllanthus amarus Schumach. and Thonn. | 10–100 mg kg−1 | na | The root and shoot growth of plant remained unaffected up to 50 ppm and further decreased with the increasing concentration. | na |
Silybum marianum L. Gaertn. | 0, 100, 200, 400 and 600 mg L−1 | 14% seed germination at 600 mg L−1 | na | na |
Trigonellafoenum-graecum L. | 0.1, 0.5, 1 and 10 mM | 33% decrease in germination and no radicle growth at 10 mM | na | na |
Trigonella foenum-graecum L. | 0, 5, 15, 30, 50 mg g−1 | na | Magnitude of increase of number of leaves, leaf area and number of branches per plant, along with shoot and root length was lowered | na |
Typha latifolia L. | 0.2–0.8 mg g−1 | na | Leaf, shoot and root elongation and the dry weight reduced | na |
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Asiminicesei, D.-M.; Fertu, D.I.; Gavrilescu, M. Impact of Heavy Metal Pollution in the Environment on the Metabolic Profile of Medicinal Plants and Their Therapeutic Potential. Plants 2024, 13, 913. https://doi.org/10.3390/plants13060913
Asiminicesei D-M, Fertu DI, Gavrilescu M. Impact of Heavy Metal Pollution in the Environment on the Metabolic Profile of Medicinal Plants and Their Therapeutic Potential. Plants. 2024; 13(6):913. https://doi.org/10.3390/plants13060913
Chicago/Turabian StyleAsiminicesei, Dana-Mihaela, Daniela Ionela Fertu, and Maria Gavrilescu. 2024. "Impact of Heavy Metal Pollution in the Environment on the Metabolic Profile of Medicinal Plants and Their Therapeutic Potential" Plants 13, no. 6: 913. https://doi.org/10.3390/plants13060913
APA StyleAsiminicesei, D. -M., Fertu, D. I., & Gavrilescu, M. (2024). Impact of Heavy Metal Pollution in the Environment on the Metabolic Profile of Medicinal Plants and Their Therapeutic Potential. Plants, 13(6), 913. https://doi.org/10.3390/plants13060913