Introduction
Fluoride contamination is a pressing environmental and public health challenge, particularly impacting arid and semi-arid regions by degrading water quality and posing significant health risks. Over the last decade, countries across Africa, Asia, and South America have reported fluoride levels surpassing the World Health Organization’s safety standard of 1.5 mg/L,¹ with Rajasthan in India² experiencing elevated concentrations due to both geological and anthropogenic factors. Globally, more than 200 million people are affected by fluoride contamination,³ notably in Africa, Asia, and parts of Europe. In countries like Iran, Pakistan, and Kenya, high fluoride levels in groundwater primarily result from natural weathering of fluorite-bearing minerals.³ However, industrial emissions, phosphate fertilizers, and brick manufacturing also contribute significantly to anthropogenic fluoride discharges.¹
India serves as a critical focus for studying fluoride pollution, affecting approximately 62 million people with conditions like dental and skeletal fluorosis, notably in regions like Rajasthan where fluoride levels range from 0.2 to 69.0 mg/L due to natural and human activities.² This widespread exposure underscores the urgent need for effective management strategies. Fluoride’s impact stretches across environmental facets, including soil, water, and biological systems. Chronic exposure results in dental and skeletal fluorosis, with children being particularly susceptible due to developmental consequences. The agricultural footprint involves disrupted crop yield and quality, impacting processes like photosynthesis and nutrient uptake, and the systemic uptake of fluoride through irrigation exacerbates its presence in the human food chain.⁴
Fluoride challenges agriculture by disrupting key physiological processes such as photosynthesis and respiration, causing stunted growth and reduced yields. While some plants like Camellia sinensis show tolerance, recent studies spotlight Plant Growth-Promoting Fungi (PGPF) as a natural means to enhance plant resilience to fluoride stress.⁵ These fungi engage symbiotically with plants, boosting nutrient uptake and activating defense mechanisms to counter fluoride-induced oxidative stress. Rhizosphere fungi like Trichoderma and Penicillium alleviate fluoride toxicity by bioaccumulation, chelation, and strengthening antioxidative defenses, enhancing plant growth under abiotic stress conditions.⁶ Additionally, these fungi detoxify fluoride by secreting organic acids that chelate fluoride ions, reducing their availability to plants.⁷
This research focuses on identifying and applying Plant Growth-Promoting Fungi (PGPF) as innovative solutions to mitigate the effects of fluoride contamination on soil and plant health. PGPF have demonstrated potential in enhancing plant growth and tolerance to various environmental stresses, including high fluoride levels, by optimizing nutrient absorption, activating plant defenses, and aiding in the detoxification of harmful ions through crucial biochemical pathways.⁸ The goal is to establish sustainable and eco-friendly strategies using fluoride-tolerant fungi to alleviate fluoride toxicity in agriculture, improve nutrient uptake, and enhance plant resilience. This approach aims to boost crop yields and quality while promoting food security in fluoride-affected regions, aligning with sustainable agricultural practices to address this pervasive environmental challenge.
Materials and Methods
In the present study, we evaluated selected fluoride-resistant fungi for Plant Growth-Promoting Abilities including Aspergillus niger, Aspergillus tamari, Trichoderma harzianum, Aspergillus flavus, Penicillium chrysogenum, and, Cladosporium cladosporioides, all of which were isolated from the rhizosphere of plants in fluoride-impacted areas of Bhopal District Madhya Pradesh and Sikar District Rajasthan. The isolated fungal colonies were identified based on their morphological characteristics and further confirmed through molecular techniques, such as DNA sequencing, in our previous study.
Evaluation of Plant Growth-Promoting Abilities
Indole-3-Acetic Acid (IAA) Production
The ability of the isolated fungi to produce IAA was assessed using the Salkowski method.⁹ Fungal cultures were grown in Luria-Bertani broth supplemented with 0.1% tryptophan. After 7 days of incubation at 28 ± 2°C, IAA was extracted using ethyl acetate and quantified at 530 nm using a spectrophotometer. Qualitatively analyzing IAA production, fungal cultures (e.g., Aspergillus niger, Trichoderma harzianum) were prepared with the same incubation and extraction procedures described. The Salkowski test was performed by mixing 1 ml of the ethyl acetate extract with 2 ml of Salkowski reagent and allowing it to stand for 30 minutes to develop color, indicating the presence of IAA.¹⁰ The intensity of the color was compared against a control (LB broth with tryptophan) to assess qualitative differences in IAA production. Results were documented by photographing each sample, clearly labeling the fungal species and corresponding IAA levels, and compiling these into a single figure for visual representation. This approach enables clear visualization of the metabolites produced and highlights the plant growth-promoting potential of the analyzed fungi.
Ammonia Production
Ammonia production was determined using the Nessler’s reagent method as described by Cappuccino and Sherman.¹¹ Fungal cultures were grown in peptone water, and after incubation, the presence of ammonia was confirmed with Nessler’s reagent, allowing for colorimetric analysis. This method assists in evaluating the nitrogen availability provided by the fungi.¹²
Phosphate Solubilization
Phosphate solubilization capacity was evaluated on Pikovskaya’s agar following the methodology of Pikovskaya¹³ and Nautiyal.¹⁴ The fungal isolates were inoculated into the medium, and after incubation, the solubilization halo around the colonies was measured to assess phosphorous solubilization efficiency.
Hydrogen Cyanide (HCN) Production
HCN production was measured using the alkaline method as described by Bakker and Schippers.¹⁵ Fungal cultures were aseptically inoculated into a medium containing glycine, and after incubation, the production of HCN was assessed by the color change when reacting with NaOH and FeCl₃.
Siderophore Production
The production of siderophores was assessed using the Chrome Azurol S (CAS) assay, based on the method by Schwyn and Neilands¹⁶ and Alexander and Zuberer.¹⁷ Fungal isolates were grown in liquid medium containing CAS, and after incubation, the change in color indicated the presence of siderophores. Quantification was achieved by measuring the absorbance at 630 nm. For the assessment of siderophore production by fungal species through the observation of characteristic blue and orange zones, Potato Dextrose Agar (PDA) or Czapek’s Yeast Extract Agar was prepared, and the plates were inoculated with selected fungal isolates using sterile techniques. After incubating the inoculated plates at 28 ± 2°C for 5-7 days, the plates were examined for clear zones around the fungal colonies. The presence of orange or blue zones indicated the type of siderophores produced; orange zones typically suggest hydroxamate-type while blue zones indicate catecholate-type siderophores.
Control and Fluoride-Treated Conditions: Parallel experiments were conducted under control and fluoride-treated conditions (0.5%). Fluoride treatment involved adding specific concentrations of sodium fluoride to the growth media to simulate fluoride stress. The performance of fungal species under these conditions was compared to their respective controls to assess the impact of fluoride on their plant growth-promoting abilities.
Results
The study specifically examines IAA production, ammonia production, phosphate solubilization, and hydrogen cyanide (HCN) production in six key fungal species: Aspergillus niger, A. tamari, A. flavus, Trichoderma harzianum, Penicillium chrysogenum, and Cladosporium cladosporioides. Evaluating each species’ ability to produce these metabolites under both control and fluoride-treated conditions indicates their potential to act as PGPFs, which can be crucial for environmentally friendly practices worldwide, particularly in regions affected by fluoride.
IAA Production
The analysis of indole-3-acetic acid (IAA) production demonstrated significant variability among the tested fungal species.
Table 1: provides absorbance readings at 530 nm, indicating IAA levels under control and fluoride-exposed (0.5%) conditions.
S. No. | Species | Control IAA (μg/ml) Mean | IAA under Toxicant (μg/ml) Mean | Control IAA – IAA under Toxicant (μg/ml) Mean |
1 | Aspergillus niger | 27.71 | 24.88 | 2.83 |
2 | Trichoderma harzianum | 27.33 | 21.79 | 5.92 |
3 | Aspergillus flavus | 18.33 | 9.22 | 9.11 |
4 | Penicillium chrysogenum | 23.37 | 15.50 | 7.87 |
5 | Cladosporium cladosporioides | 14.26 | 8.51 | 5.75 |
6 | Aspergillus tamarii | 16.12 | 14.80 | 1.32 |
Data indicated that Aspergillus niger maintained the highest IAA production levels (27.71 µg/ml) despite a decrease to 24.88 µg/ml in the presence of fluoride, suggesting potential resilience to fluoride toxicity. In contrast, Trichoderma harzianum exhibited a decline from 27.33 µg/ml to 21.79 µg/ml, while Aspergillus flavus showed a substantial reduction from 18.33 µg/ml to 9.22 µg/ml, highlighting its sensitivity.
The findings presented in quantitative and qualitative tests (Table 1) highlight the variable resilience of different fungal species to fluoride stress, suggesting that species like Aspergillus niger could play an essential role in promoting plant growth in contaminated soils.1,²
Ammonia Production
Ammonia production serves as a crucial indicator of nitrogen availability for plants. Aspergillus niger displayed the highest ammonia production (178.94 μg/ml), though it decreased to 135.41 μg/ml under fluoride conditions, indicating strong but impaired ammonia production under stress (Table 2). Trichoderma harzianum maintained a reasonable level of ammonia production despite a modest decline. In contrast, Penicillium chrysogenum, Cladosporium cladosporioides, and Aspergillus tamarii showed almost complete inhibition under fluoride conditions, highlighting their vulnerability to fluoride toxicity. The findings suggest that while some species exhibit notable resilience, others are significantly affected by fluoride, potentially limiting their effectiveness as PGPFs.¹⁸,⁴
Table 2: summarizes the mean ammonia concentrations produced by the PGPF species both under control conditions and in the presence of fluoride.
S. No. | Species | Control Ammonia (μg/ml) Mean | Ammonia Under Toxicant (μg/ml) Mean |
1 | Aspergillus niger | 178.94 | 135.41 |
2 | Trichoderma harzianum | 103.06 | 96.00 |
3 | Penicillium chrysogenum | 23.65 | 0.12 |
4 | Aspergillus flavus | 91.29 | 58.94 |
5 | Cladosporium cladosporioides | 10.71 | ND |
6 | Aspergillus tamarii | 8.35 | ND |
Phosphate Solubilization
Phosphate solubilization by fungi is crucial for enhancing soil fertility, particularly in environments characterized by nutrient limitations and chemical contaminants. The results for phosphate solubilization are summarized in Table 3.
Table 3: showcasing the effectiveness of these fungal species under control and fluoride-treated conditions.
S. No. | Species | Control Phosphate Solubilization (µg/ml) Mean | Phosphate Solubilization Under Toxicant (µg/ml) Mean |
1 | Penicillium chrysogenum | 125.68 | 116.59 |
2 | Trichoderma harzianum | 137.05 | 105.23 |
3 | Aspergillus niger | 137.05 | 116.59 |
4 | Aspergillus flavus | 175.68 | 137.05 |
5 | Cladosporium cladosporioides | 50.68 | 46.14 |
6 | Aspergillus tamarii | 143.86 | 130.23 |
Aspergillus flavus exhibited the highest phosphate solubilization under control conditions at 175.68 µg/ml, but its ability decreased to 137.05 µg/ml when exposed to fluoride. This indicates a significant reduction yet suggests a capacity for maintaining functional solubilization. Similarly, Trichoderma harzianum showed a decline from 137.05 µg/ml to 105.23 µg/ml, reflecting a reduction due to fluoride stress.
In contrast, Penicillium chrysogenum, while initially effective, faced considerable reductions in their phosphate solubilization capabilities under fluoride conditions. The declines emphasize the importance of these functions in agricultural settings, where nutrient uptake is critical for plant health.⁷,¹⁹
The ability of these fungi to solubilize phosphate under fluoride stress is vital for improving soil nutrient profiles. The findings suggest that species such as Aspergillus niger and Trichoderma harzianum, despite some decline, can still play important roles in enhancing phosphorus availability in contaminated soils.
Hydrogen Cyanide Production
The production of hydrogen cyanide (HCN) by beneficial fungi serves as an important mechanism of biocontrol, as HCN can inhibit the growth of pathogens.
Table 4: The HCN production data from the selected fungal species under different experimental conditions.
S. No. | Species | Control Hydrogen Cyanide (HCN) (Absorbance at 625 nm) Mean | HCN Under Toxicant (Absorbance at 625 nm) Mean |
1 | Aspergillus niger | 0.090 | 0.018 |
2 | Aspergillus flavus | 0.098 | 0.092 |
3 | Penicillium chrysogenum | 0.072 | 0.069 |
4 | Trichoderma harzianum | 0.0123 | 0.0115 |
5 | Aspergillus tamarii | 0.059 | 0.051 |
6 | Cladosporium cladosporioides | 0.0104 | 0.0080 |
In the present study (Table 4 ) Aspergillus niger showcased the highest HCN production under control conditions but experienced a drastic reduction in levels when exposed to fluoride, indicating high sensitivity and potential metabolic disruption. The ability to produce HCN, despite fluoride toxicity, points to its implications for biocontrol mechanisms. While the analyzed fungal species showed varying degrees of resilience to fluoride, those like Aspergillus niger and Trichoderma harzianum exhibit significant PGP potential through IAA, ammonia, and phosphate production, whereas their ability to synthesize HCN reveals their potential as biocontrol agents. The modest reductions in HCN levels suggest that such species may still be employed effectively in agricultural practices, even under fluoride-stressed conditions.
Siderophore Production
Siderophores are essential for iron acquisition in fungal species, particularly in environments where iron availability is restricted by various stressors. By quantifying the production of siderophores in the examined fungal species, we can gain important insights into their capacity to enhance plant growth through improved nutrient uptake. This study specifically investigates the siderophore production potential of four plant growth-promoting fungi: Aspergillus niger, Trichoderma harzianum, Aspergillus flavus, and Penicillium chrysogenum, all of which demonstrated strong plant growth-promoting potential in other assays conducted during this research
Table 5: outlines the siderophore production levels measured under control and fluoride conditions.
S. No. | Species | Control Siderophore % (Mean ± SD) | Siderophore % Under Toxicant (Mean ± SD) |
1 | Aspergillus niger | 82.28 ± 0.67 | 79.65 ± 0.74 |
2 | Trichoderma harzianum | 56.25 ± 0.84 | 54.87 ± 0.68 |
3 | Aspergillus flavus | 36.38 ± 0.83 | 31.21 ± 0.69 |
4 | Penicillium chrysogenum | 63.69 ± 0.65 | 58.00 ± 0.78 |
In the present study (Table 5) Aspergillus niger maintained the highest siderophore production levels, with only a slight decrease when exposed to fluoride. This resilience indicates its potential effectiveness in mobilizing iron, which is essential for plant growth, particularly in iron-deficient soils. Similarly, Trichoderma harzianum showed a minor reduction in its siderophore production, suggesting that it can also maintain iron acquisition capabilities under stress. Conversely, other species such as Aspergillus flavus and Penicillium chrysogenum displayed significant declines in siderophore production upon exposure to fluoride, indicating their sensitivity to environmental stressors. The reduction in iron-mobilizing abilities due to fluoride exposure could limit these fungi’s effectiveness as PGPFs, particularly in contaminated environments.
Discussion
This study underscores the multifaceted roles and mechanisms by which select fungi function as plant growth-promoting agents in fluoride-contaminated agricultural systems. Notably, species like Aspergillus niger and Trichoderma harzianum significantly enhance plant health through the production of indole-3-acetic acid (IAA), ammonia, phosphate solubilization, and siderophore production.20 Although fluoride exposure impairs metabolic functions, it also presents opportunities for utilizing these fungi in bioremediation to restore soil health.21
Maintaining essential nutrient cycling under fluoride stress is critical, highlighting the importance of these resilient fungi in enhancing soil fertility and plant growth in contaminated areas. This can play a vital role in supporting food security and ecosystem health. The observed sensitivity and resilience variations among fungal species facilitate the strategic selection of the most appropriate strains for specific environmental contexts, with adaptive species serving as effective bioamendments in fluoride-affected soils to boost agricultural productivity and soil vitality.22
The findings reveal significant variability in the resilience and efficacy of the examined fungi. Aspergillus niger exhibited robust IAA production despite fluoride exposure, indicating its resilience, while Aspergillus flavus showed reduced production, reflecting its sensitivity. Concerning ammonia production, Aspergillus niger maintained relatively high levels under fluoride stress, whereas Penicillium chrysogenum faced near-total inhibition, indicating its vulnerability. Although phosphate solubilization generally decreased due to fluoride, Aspergillus flavus retained some functionality, demonstrating adaptability in nutrient-poor environments. While Aspergillus niger showed elevated hydrogen cyanide (HCN) production under control conditions, its drastic reduction under fluoride suggests metabolic challenges, though it retains its biocontrol potential. Siderophore production by Aspergillus niger and Trichoderma harzianum remained stable, which is crucial for facilitating plant growth in iron-deficient soils, while other species displayed significant declines.23,24 Overall, fungi like Aspergillus niger and Trichoderma harzianum emerge as promising candidates for promoting plant growth, particularly in fluoride-impacted regions. Their adaptability variability highlights the necessity of developing sustainable agricultural practices that are specifically tailored to address unique environmental challenges.
Conclusion
This research elucidates the role of soil as a medium in sustaining plant growth while displacing soil detrimental antibiotic activity or severe fluorine impact. Soils affected by fluorine were found to contain fungi that promote plant growth such as Aspergillus niger and Trichoderma harzianum, that performed well on axes like IAA production, ammonia synthesis, phosphate solubilization, and siderophore production. Due to their high level of tolerance with regard to fluoride, they could be utilized to promote plant growth and rehabilitate soil in polluted areas. It is important to point out that Aspergillus species are capable of enhancing the growth of plants, but depending on the condition, they can also be toxic. This dual nature emphasizes the need for careful consideration of their application in agricultural practices, particularly in fluoride-stressed environments.
Acknowledgement
The authors express their gratitude to the Department of Bioscience at Mody University of Science & Technology, Lakshmangarh, Sikar (Rajasthan), and CMBR Biotech Pvt Ltd, Bhopal, MP, for providing their laboratory facilities.
Funding Sources
The author(s) received no financial support for the research, authorship, and/or publication of this article.
Conflict of Interest
The authors do not have any conflict of interest.
Data Availability Statement
This statement does not apply to this article.
Ethical Statement
This research did not involve human participants, animal subjects, or any material that requires ethical approval.
Author Contributions
Ritu Kanthiy: Data collection, Performing the experiments, and manuscript writing.
Rakesh Kumar Verma: Conceptualization, Supervision and critical revision of the manuscript.
Deepak Bharti: statistical analysis and help in manuscript writing.
Saloni Kanthiya: Literature review and editing assistance.
References
- Shaji E, Sarath K, Santosh M, et al. Fluoride contamination in groundwater: A global review of the status, processes, challenges, and remedial measures. Geosci Front. 2023; 15(2):101734. https://doi.org/10.1016/j.gsf.2023.101734
CrossRef - Ahmad S, Singh R, Arfin T, Neeti K. Fluoride contamination, consequences, and removal techniques in water: A review. Environ Sci Adv. 2022; 1(5):620-661. https://doi.org/10.1039/d1va00039j
CrossRef - Rasool A, Farooqi A, Xiao T, et al. A review of global outlook on fluoride contamination in groundwater with prominence on the Pakistan current situation. Environ Geochem Health. 2017;40(4):1265-1281. https://doi.org/10.1007/s10653-017-0054-z
CrossRef - Adimalla Kumari, S., Dhankhar, H., Abrol, V., & Yadav, A. K. (2024). Bioaccumulation of Fluoride Toxicity in Plants and Its Effects on Plants and Techniques for Its Removal. Advanced Treatment Technologies for Fluoride Removal in Water: Water Purification, 271-290.
CrossRef - Emmanuel OC, Babalola OO. Productivity and quality of horticultural crops through co-inoculation of arbuscular mycorrhizal fungi and plant growth-promoting bacteria. Microbiol Res. 2020; 239:126569. https://doi.org/10.1016/j.micres.2020.126569
CrossRef - Murali M, Naziya B, Ansari MA, et al. Bioprospecting of rhizosphere-resident fungi: Their role and importance in sustainable agriculture. J Fungi. 2021; 7(4):314. https://doi.org/10.3390/jof7040314
CrossRef - Berbasova Yang, J., Liu, C., Li, J., Zhang, Y., Zhu, C., Gu, D., & Zeng, L. (2024). Critical review of fluoride in tea plants (Camellia sinensis): absorption, transportation, tolerance mechanisms, and defluorination measures. Beverage Plant Research, 4(1). Add page nos.
CrossRef - Adedayo AA, Babalola OO. Fungi that promote plant growth in the rhizosphere boost crop growth. J Fungi. 2023;9(2):239. https://doi.org/10.3390/jof9020239
CrossRef - Gordon SA, Weber RP. Colorimetric estimation of indoleacetic acid. Plant Physiol. 1951;26(1):192-195. https://doi.org/10.1104/pp.26.1.192
CrossRef - Patten CL, Glick BR. Role of Pseudomonas putida indoleacetic acid in the development of the host plant root system. Appl Environ Microbiol. 2002; 68(8):3795-3801. https://doi.org/10.1128/AEM.68.8.3795-3801.2002
CrossRef - Cappuccino JG, Sherman N. Microbiology: A laboratory manual. 4th ed. Benjamin/Cummings Publishing Company; 1992.
- Santoyo G, Moreno-Hagelsieb G, Orozco-Mosqueda MDC, Glick BR. Plant growth-promoting bacterial endophytes. Microbiol Res. 2016; 183:92-99. https://doi.org/10.1016/j.micres.2015.11.008
CrossRef - Pikovskaya RI. Mobilization of phosphorus in soil in connection with the vital activity of some microbial species. Mikrobiologiya. 1948; 17:362-370.
- Nautiyal CS. An efficient microbiological growth medium for screening phosphate solubilizing microorganisms. FEMS Microbiol Lett. 1999; 170(1):265-270.
CrossRef - Bakker AW, Schippers B. Microbial cyanide production in the rhizosphere in relation to potato yield reduction and Pseudomonas spp.-mediated plant growth stimulation. Soil Biol Biochem. 1987;19(4):451-457. https://doi.org/10.1016/0038-0717(87)90037-X
CrossRef - Schwyn B, Neilands JB. Universal chemical assay for the detection and determination of siderophores. Anal Biochem. 1987; 160(1):47-56. https://doi.org/10.1016/0003-2697(87)906
CrossRef - Alexander DB, Zuberer DA. Use of chrome azurol S reagent to evaluate siderophore production by rhizosphere bacteria. Biol Fertil Soils. 1991; 12(1):39-45. https://doi.org/10.1007/BF00369386
CrossRef - Miller WP, Shuman DM. The mechanism of fluoride inhibition of photosynthesis in higher plants. Photosynth Res. 1986; 10(1):151-160. https://doi.org/10.1007/BF00019035
CrossRef - Krishnan V, Asaithambi M. Hydro-meteorological aspects of soil fluorides in semi-arid soils using microwave remote sensing. Environ Monit Assess. 2024; 196(7):669. https://doi.org/10.1007/s10661-024-11669-3
CrossRef - Adedayo, A. A., & Babalola, O. O. (2023). Fungi that promote plant growth in the rhizosphere boost crop growth. Journal of Fungi, 9(2), 239.
CrossRef - Satyakala K, Alladi A, Thakur KD. Effect of physiological parameters on growth of Aspergillus niger and Trichoderma harzianum. Int J Pure Appl Biosci. 2017; 5(4):1808-1812. doi:10.18782/2320-7051.5731
CrossRef - Sinha, B., Behera, P. R., & Saha, B. (2024). Fluoride Contamination in Ecosystem and Mitigation Strategy. In Environmental Contaminants(pp. 141-166). Apple Academic Press.
CrossRef - Shamla AK, Chitra AV. Assessing the impact of Terminalia arjuna plant extracts on the growth and sporulation of Trichoderma harzianum, Aspergillus niger, and Penicillium chrysogenum. J Pure Appl Microbiol Res. 2024; 18(4):32. doi:10.22207/JPAM.18.4.32
CrossRef - Zayed O, Hewedy OA, Abdelmoteleb A, et al. Nitrogen journey in plants: From uptake to metabolism, stress response, and microbe interaction. Biomolecules. 2023; 13(10):1443. https://doi.org/10.3390/biom13101443
CrossRef