1. Introduction
Fluoride is the thirteenth most common element found in earth’s crust. Most common sources of fluoride exposure to living organism are mainly through contaminated drinking water with geogenic origin [
1]. Fluorine has high electronegativity and therefore exists in aqueous systems as fluoride anion and readily forms strong ionic bonds with cationic species, such as calcium and magnesium [
2]. Fluoride is a beneficial mineral for the strengthening of both dental and skeletal tissues, however excessive exposure for pro-longed periods of time have serious health implication including disrupted metabolic processes and impaired mineralized in tissues [
3,
4]. The World Health Organization has established a maximum allowable limit of fluoride in drinking water at 1.5 mg/L [
5]. However, it is estimated that over 200 million people in more than 25 countries, including India, take fluoride above 1.5 mg/L [
6]. In India, some of the states that are most severely impacted include Rajasthan, Telangana, Bihar and Gujarat, where untreated ground water is the primary source of potable water [
7]. Bihar situated in the middle Indo-Gangetic plain (MIGP) is designated as a Category III Fluoride Endemic State by Ministry of Jal Shakti. Fluoride contamination is reported across 11 districts as per the Bihar Economic Survey 2021-22 [
8,
9,
10] with levels ranging from 1.16 mg/L to 2.32 mg/L and Sheikhpura district (Kumar et al. 2022). The effects of fluoride on animals have not received as much attention compared studies on human fluorosis. No study on animals is available from MIGP. Chronic exposure of livestock to fluoride causes mottling of dentin and osteosclerosis, resulting in joint stiffening, and irregularities in the blood or internal organs [
11,
12,
13]. Systemically, Fluoride will create a broad spectrum of toxicological effects on multiple organ systems in addition to disrupting the normal functioning of the liver, kidneys, neurological system and thyroid gland [
14]. Therefore, monitoring the effects of fluoride exposure in livestock and suitable adoptable remedial measures is needed for attracting planner attentions and awareness among farmers about its possible adverse effect on health and production. The problem may leveraged by focus on stall fed management, integration of livestock component with other enterprises and limited access to water quality monitoring and mitigation strategies for livestock.
While numerous public health efforts have been made to reduce fluoride exposure in human populations via community-level water treatment technologies, interventions for livestock remain largely absent [
15,
16]. This oversight is particularly concerning, as animals consume the same contaminated groundwater and fodder cultivated therein, yet remain unmonitored and untreated in most endemic zones. In recent years, nutraceuticals have emerged as a promising class of adjunct therapies for managing chronic toxicity.
Spirulina platensis (SP) is a filamentous cyanobacterial member of the Oscillatoriaceae, family. It is a promising therapeutic agent due to its extensive bioactive and nutrient profile and protection against oxidative damage [
17]. It also enhances the urinary excretion of fluoride and promotes its binding through trace elements [
18]. The ameliorative potentials of supplementing @ 500 mg/Kg body weight/day in lambs of Morocco has been reported to prevent dental fluorosis [
19]
Against this backdrop, we investigated the potential ameliorative effects of SP powder supplementation in naturally fluoride exposed cattle calves under field conditions. The study analyzed the pre- and post-supplementation changes in systemic fluoride burden, fluoride excretion dynamics, and associated hematological and biochemical indices, to evaluate its efficacy of the SP powder in mitigating fluoride induce adverse effects.
2. Materials and Methods
Study Area. The present study was conducted in the fluoride-endemic district of Sheikhpura, located in southern Bihar, India, with groundwater F
- concentration exceeding the maximum permissible limits of 1.5 mg/L at several locations. The region spans a geographical area of 609.51 km
2 and lies between 24°45′2″ to 25°45′2″ N latitude and 85°45′2″ to 86°45′2″ E longitude. The district comprises six administrative blocks and 360 villages. The study focused on three representative villages (Chorbar, Chordargah and Koinda) selected based on known groundwater F
- levels and reported cases of endemic fluorosis [
20].
Animals and study design. This study was carried out in 25 crossbred calves 5-8 months old of either sex. It included 20 clinically diagnosed fluorotic calves from the selected villages and five as baseline healthy controls from Patna district. The selection was based on visual assessment under daylight, focusing on characteristic signs of dental fluorosis, such as enamel mottling or discoloration of lower incisors. The severity of clinical fluorosis was evaluated based on dental deformities observed and scored from 0 to 4 using the standardized Dean’s Index grading system, corresponding with increasing severity [
21]. Additional inclusion criteria included physical symptoms like joint stiffness, lameness, and palpable exostoses in the metacarpal, metatarsal, frontal, and costal bones. Based on their clinical fluorosis scores and locations (
Figure 1), groups formed for the study are:
| Group I |
Baseline healthy control calves |
ICAR RCER, Patna Farm |
Dean’s score>0.5 |
| Group II |
Disease control calves without any interventions |
Sheikhpura farmers field |
Dean’s score<0.5 |
| Group III |
Test Group calves + SP @350 mg per kg body weight |
Sheikhpura farmers field |
Dean’s score<0.5 |
| Group IV |
Test Group calves + SP @650 mg per kg body weight |
Sheikhpura farmers field |
Dean’s score<0.5 |
| Group V |
Reference control calves + dicalcium phosphate (DCP) @ 30g per day per calf [22] |
Sheikhpura farmers field |
Dean’s score<0.5 |
All calves were stall-fed and provided a uniform basal diet comprising concentrate feed mixture and maize leaves twice daily, along with ad libitum access to groundwater sourced from their respective locations. To ensure optimal palatability and intake, SPP and DCP were homogenized with 5% molasses before administration [
23]. The animal study was approved by the Institutional Animal Ethics Committee (IAEC) at ICAR-RCER under the approval number IAEC/ICAR-RCER/20/08-Status of Fluorosis dated 08/01/2025.
Sample collection. Random groundwater samples (10 mL) were collected from hand pumps near to livestock sheds for fluoride estimation. Consent for participation was taken from all the livestock owner included in the study. Approximately 10 mL of blood was collected aseptically from the jugular vein using sterile clot activator vacutainers on day 0 and then on 15, 30, 45, and 60 of the experiment. Serum was collected and stored at –20 °C until analysis. Midstream urine (10mL) was collected in sterile polypropylene containers by the manual stimulation method and refrigerated at 4 °C before fluoride analysis.
Fluoride estimation. Fluoride concentration in serum and urine was quantified using an ion-selective electrode (ISE) method [
24]. The system employed an Orion 96-09 fluoride-selective electrode and mV meter (Thermo Fisher Scientific, USA). To ensure consistent ionic strength and pH, all standards and samples were mixed with Total Ionic Strength Adjustment Buffer (TISAB) in a 1:1 ratio. A calibration curve was generated using sodium fluoride standards (0.1–20 µg/mL), and sample readings were taken after 1–2 min of stabilization.
Hematological analysis. Hematological indices were measured using an automated hematology analyzer (Nihon Kohden, Europe) outsourced to Bihar Veterinary College, Patna.
Liver function test. Serum total protein (TP) was determined by the biuret method [
25] and albumin levels using the bromocresol green (BCG) assay [
26]. Globulin was calculated by subtracting albumin from total protein. Aspartate transaminase
(AST) and alanine transaminase (ALT) activities were determined as per the IFCC method [
27], based on NADH oxidation. Serum alkaline phosphatase (ALP) activity was estimated using p-nitrophenyl phosphate (PNPP) substrate [
28].
Kidney function test. Blood urea nitrogen (BUN) was calculated from serum urea levels estimated using the diacetyl monoxime method [
29] and converted using a factor of 0.467. Creatinine was assessed via the alkaline picrate method [
30].
Serum glucose. It was estimated spectrophotometrically using the GOD–POD enzymatic method [
31]
.
Calcium and Phosphorus.Serum calcium levels were determined by the OCPC method [
32], while phosphorus was estimated via the molybdate UV method [
33].
Oxidative stress markers. Oxidant and antioxidant markers in serum samples were estimated using available standard procedures. GPx activity was measured based on the oxidation of NADPH [
34]. The Catalase activity (µmol/min/mL) was determined by monitoring the rate of hydrogen peroxide decomposition [
35]. Superoxide Dismutase (SOD) activity was quantified using MTT reduction inhibition assay [
36]. Enzyme activity was expressed in U/mg protein based on percentage inhibition. Malondialdehyde (MDA) was measured to assess lipid peroxidation via the thiobarbituric acid reactive substances (TBARS) assay [
37].
Statistical analysis. All numerical data were analyzed using one-way Analysis of Variance (ANOVA) and Tukey’s HSD post hoc test for intergroup comparisons at different time intervals. Results were expressed as mean ± standard error (SE), and significance was accepted at p ≤ 0.05. Statistical analyses were performed using IBM SPSS Statistics for Windows, Version 27.0 (IBM Corp., Armonk, NY).
3. Results
The ground water samples collected from hand pumps (n=23) near to animal sheds of the study area indicates fluoride contamination in the region with mean 1.496 ± 0.29 and range as 2.54-1.01 mg/L, respectively. The results provide understanding on the impact of slow intake of fluoride through contaminated groundwater under their natural ecosystem and provides ameliorative effect of supplementation of SP compared with DCP as a standard treatment. The results of the field trials are presented below under different subheads.
Serum and Urine Fluoride in calves
Baseline serum fluoride concentrations were significantly elevated (p ≤ 0.05) in all the calves of test groups compared to the baseline healthy control group (I) and remained persistently high in the untreated positive control group II throughout the study duration. In contrast, calves supplemented with SP (Groups III and IV) and in Group V exhibited a progressive and statistically significant reduction in serum F
- concentration from day 15 onwards (
Table 1). Among the test groups, group IV demonstrated the most pronounced F
- clearance by day 60, outperforming the standard therapy in group V, thus indicating superior chelation and systemic detoxification efficacy. A comparable trend was observed in urinary F
- excretion. Elevated urinary F
- levels at baseline in test groups (II–V) persisted in group II calves but significantly declined in the treated groups (III-V) from day 15 onwards. Group IV consistently exhibited the highest urinary F
- excretion, suggesting enhanced renal clearance of the toxicant and reflecting effective systemic mobilization of F
- ions. Affected calves displaying classical signs of fluorosis, including mottled incisors, limb stiffness, and bony exostoses exhibited markedly elevated serum and urinary F
- concentrations.
Hematological changes
Hematological parameters in these cattle calves under different groups indicate that exposure to F
- and its bioaccumulation resulted in a significant reduction in hemoglobin (Hb), packed cell volume (PCV), total erythrocyte count (TEC) and total leucocyte count (TLC) as distinct from the baseline values of day 0. No changes in these indices were observed in groups I and II during the study (
Table 2). However, SP-supplemented groups (III, IV) and group V on standard DCP supplement showed progressive hematological restoration from day 15 onwards. Group IV demonstrated the most substantial recovery across all hematological indices by day 60, with values nearing calves in group I. A transient rise in TLC was observed in groups IV and V on day 45, followed by normalization as in group I calves on day 60, indicating modulation of systemic inflammatory responses during recovery.
3.1. Effect on Hepatic and renal Function
The bioaccumulation of F
- in body affected both liver and kidney function of calves of test group. Hepatic transaminases enzyme (AST, ALT) and ALP levels were significantly elevated in calves on day 0 of study in test groups II–V, indicative of hepatic stress and fluorosis-induced cytotoxicity. SP-supplemented test groups (III, IV) exhibited marked reductions from day 15 onward, with group IV showing the most pronounced decline in hepatic enzyme levels by day 60, suggesting hepatoprotective effects through anti-oxidative and anti-inflammatory mechanisms (
Table 3). Serum TP, albumin, globulin and glucose concentrations were significantly decreased in fluorotic calves relative to controls throughout the initial phase (
Figure 3a). Treatment with SP and DCP led to significant (p ≤ 0.05) recovery in all three parameters from day 15 onwards in groups III-V. However, on day 60, group IV registered the highest serum protein and near normal glucose concentrations, indicative of hepatic functional restoration and improved protein synthesis capacity under the intervention of SP.
BUN and serum creatinine were significantly elevated and glucose in fluorotic calves compared to controls (
Table 3). While Group II showed no change, Groups III–V exhibited progressive decreases from Day 15 onwards. Group IV showed the most effective BUN reduction, whereas Group III demonstrated the sharpest creatinine decline, collectively indicating nephroprotective effects and improved nitrogenous waste clearance.
3.2. Mineral Homeostasis
Hypocalcemia was prominent in fluorotic groups, with significant improvement observed in all treatment groups (
Figure 3b and table as supplementary file). Group IV achieved near-normal calcium levels by day 60, underscoring improved mineral metabolism. Serum phosphorus, elevated at baseline, showed a biphasic response in groups III and IV, with an initial decline through day 45 and mild resurgence by day 60. Group V, however, demonstrated a consistent downward trend, suggesting a differential mechanism of phosphate handling between SP and DCP as standard therapy.
3.3. Oxidative Stress Markers
Markers of oxidative stress showed significant dysregulation in fluorotic calves at baseline (
Figure 4). GPx, CAT and SOD activities were significantly diminished, while MDA levels, a marker of lipid peroxidation were markedly elevated. SP supplementation led to significant upregulation of antioxidant enzymes (GPx, CAT, SOD) from Day 15 onwards. Group IV consistently exhibited the most robust antioxidant recovery, indicating enhanced cellular redox regulation. Concurrently, MDA concentrations declined significantly, particularly in Group IV, reflecting reduced oxidative membrane damage and improved systemic anti-oxidative defense.
3.4. Multivariate Heatmap and Cluster Analysis
A heatmap was generated to visualize complex temporal and treatment-based physiological trends (
Figure 5a), integrating multiple biochemical and oxidative markers across all groups and time points. The heatmap revealed distinct temporal dynamics and “hot spot” zones—specifically during early stages (Day 0 and Day 15) in Groups II, III and V—characterized by high ALP, ALT, AST and BUN levels, suggesting acute hepatic and renal stress.
Group IV showed comparatively muted enzyme elevations, with delayed but more pronounced metabolic normalization evident by Day 30, supported by elevated glucose levels. Later time points (Days 30–60) demonstrated convergence toward normative ranges in ALP, ALT and AST in all treatment groups, further reinforcing progressive organ recovery.
Principal Component Analysis (PCA) of 17 key physiological and biochemical markers revealed four distinct clustering patterns, delineating the temporal and treatment-related dynamics of recovery in fluorosis-affected calves (
Figure 5b and
Figure 5c).
Cluster 1 consisted exclusively of samples from Group I (I0 to I60), which served as the healthy control group. These samples were characterized by consistently elevated levels of beneficial biomarkers such as glucose, TLC, TEC, calcium, SOD, globulin, GPx, TP and albumin. These variables showed strong positive loadings on the first principal component (PC1), indicating a physiologically stable and balanced systemic state.
Cluster 2 comprised samples from the early stages of all fluorotic groups, including Groups II, III, IV and V at baseline (Day 0) and extending up to Day 60 for the untreated Group II. These samples demonstrated high concentrations of stress-associated variables—namely ALT, AST, serum F-, urinary F-, BUN and MDA. These markers exhibited strong negative correlations with PC1, signifying a fluorosis-affected or metabolically compromised state.
Cluster 3 included samples from Groups III and IV at Days 45 and 60 (i.e., III45, III60, IV45, IV60). These samples represented an intermediate phenotype showing substantial improvement in hepatic and antioxidant parameters while moving away from the fluorotic cluster and aligning closer to the control cluster, indicating a partial but definitive trend toward physiological recovery under Spirulina supplementation.
Cluster 4 encompassed transitional stages in recovery across different treatment groups, specifically samples from Days 15 to 60 of Groups III, IV and V (IV15, III30, IV30, V30, V45, V60). These samples showed elevated levels of beneficial variables such as glucose, albumin, TEC and SOD but remained distinct from the healthy cluster, suggesting ongoing systemic improvement but incomplete normalization. Notably, samples within this cluster exhibited lower PC2 values compared to samples from Cluster 1, indicating residual metabolic stress despite significant therapeutic progress.
Collectively, the PCA results affirmed a clear separation between healthy and fluorotic states, with Spirulina treated groups, particularly at higher doses exhibited a more pronounced shift toward metabolic normalization over time.
4. Discussion
To our knowledge, this is the first field-based study to investigate systemic fluoride accumulation and the potential for therapeutic intervention of fluoride intoxication in naturally occurring fluoride-exposed cattle calves from the Middle Indo-Gangetic Plain (MIGP), addressing a major knowledge void in the epidemiology of livestock fluorosis [
11,
12]. Groundwater fluoride concentrations in this region are at mean levels of 1.77 mg/L, which facilitates the accumulation of fluoride in blood serum and urine (as urine fluoride is a biomarker for recent systemic exposure to fluoride and indicates systemic fluoride determinants), as well as increases in urine fluoride concentration as a result of ingesting feed and straw cultivated under contaminated irrigation [
7,
20]. Spirulina supplementation can reduce serum fluoride concentrations by facilitating urinary fluoride excretion, suggesting the detoxification process via bioavailability of previously deposited fluoride from tissues and enhanced renal elimination processes, indicating biological detoxification. This superior capacity to detoxify fluoride is evident at the 650 mg/kg dosage, which indicates a clear dose-dependent response to Spirulina by way of its high biological-value protein, phycocyanin-rich antioxidants and essential minerals, all of which work synergistically to promote erythropoiesis, maintain hepatoprotection and nephroprotection and maintain mineral homeostasis [
18,
39,
40,
41]. Similar study conducted on endemic exposed lambs in Morocco also reports ameliorative potential of SP @ 500 mg/kg body weight/day and reduced the plasmatic levels of fluoride, proteins, GSH, and MDA compared to control [
19]. The hematological depression, increased levels of ALP; AST; BUN and creatinine; as well as the clinical signs observed are consistent with chronic fluoride poisoning due to extended duration of environmental exposure, not acute toxicity [
41,
42,
43]. In addition to being a means to detoxify fluoride from the body, supplementation with spirulina has many additional health benefits systemically such as an increase in the antioxidant defense system, an increase in protein synthesis, correction of hypocalcemia and a return to normalized metabolic function overall [
19,
41,
44]; thus, there is a significant benefit to the use of Spirulina as a multi-therapeutic agent. Also, the higher dose of Spirulina nutritional supplementation produced results comparable to those produced by conventional DCP therapies, making Spirulina a cost-effective, viable, and sustainable option for managing fluorosis in endemic scope livestock systems.
5. Conclusion and Future Directions
The findings indicate that supplying SPP to fluorosis-impacted calves at a dose of 650 mg/kg body weight produces positive therapeutic results. Specifically, SPP decreased the systemic burden of fluorine in these calves and improved their blood cell count and metabolism; improved and/or normalized their liver and kidney functions; and brought the oxidative status of these calves back to a normal state. In addition, the results from Group IV were often found to be as good as or better than what was observed in cattle treated with traditional Dicalcium Phosphate therapy.
The high level of nutrients contained in SPP along with its high content of antioxidants makes it a very good sustainable and biologically appropriate approach to treating livestock for fluorosis. Currently, there may be some cost barriers associated with purchasing commercial Spirulina; however, it may be possible to create localized areas for growing Spirulina as a crop and incorporating it into existing livestock management systems, thus reducing cost and improving access to it for livestock producers. Future research should focus on examining the longer-term effects of the use of Spirulina under field conditions, economic impacts of its use, and any potential synergistic relationship between Spirulina and conventional treatment for fluorosis so that it can be more widely utilized by rural animal health programs.
Author Contributions
All the authors contributed to conception and design. SS, PK, DM, AD conceptualized and designed the study. SS and BKS conducted field research and data collection among farmers. SS prepared the initial draft and tables. All authors contributed to revising and editing the manuscript. JS prepared graphs and GIS map. AD contributed in project administration and supervision. The final manuscript was approved by all authors.
Funding
This research was supported by intra-mural project of I.C.A.R.-R.C.E.R., Patna for contingency and chemical purchase.
Acknowledgments
The authors thank Dr. Kamal Sarma- Head, Division of Livestock and Fisheries Management, I.C.A.R R.C.E.R., Patna for providing the facilities to carry out this research work.
Competing Interests
The authors declare that they have no competing interests.
Ethical Approval
All authors have reviewed, understood and where applicable, adhered to the guidelines outlined in the “Ethical Responsibilities of Authors” provided in the Instructions for Authors. The animal study was approved by the Institutional Animal Ethics Committee (IAEC) at ICAR-RCER under the approval number IAEC/ICAR-RCER/20/08-Status of Fluorosis dated 08/01/2025.:
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