A Comprehensive Analysis of Andrographis paniculata Herbal Products Conducted to Enhance Potency and Ensure Safety Through the Application of Pertinent Chromatographic Techniques.
Tamilvanan K1, P.V Murali Krishna2*, Vanita Somasekhar3, Rajeshkumar R4
1Department of Pharmaceutical Analysis, KLE College of Pharmacy, Bengaluru - 560 010, Karnataka, India.
2Associate Professor, Department of Pharmaceutical Analysis,
KLE College of Pharmacy, Bengaluru - 560 010, Karnataka, India.
3Professor, Department of Pharmaceutical Analysis,
KLE College of Pharmacy, Bengaluru - 560 010, Karnataka, India.
4Assistant Manager, QC Department, Natural Remedies Pvt Ltd, Bengaluru - 560 100, Karnataka, India.
*Corresponding Author E-mail: pallamurali86@gmail.com
ABSTRACT:
The study aimed to identify and quantify andrographolides in various marketed samples of A. Paniculata and detect pesticide residues. It aimed to improve understanding of the composition, purit, and safety.The TLC technique used an aluminium plate with pre-coated silica gel (E. Merck – Silica Gel 60F254). Samples were spotted using a Linomat IV syringe TLC applicator (CAMAG) and a solvent system consisting of acetone, benzene, and chloroform (20:20:10 ratio). With a LiChrospher 100 RP-18e (5μm) column, a quaternary pump, UV detector, auto injector, column oven, and LC-Solution software, the HPLC system comprised a SHIMADZU LC-2030C Liquid Chromatograph. The Agilent Gas Chromatograph with Electron Capture and Nitrogen Phosphorus Detector 7890A-ECD/NPD (EZ Chrome) and associated equipment, along with a Zebron ZB-1 column (30 m in length, 0.25 mm in diameter, and 0.50 m film thickness), made up the GC-ECD system.The TLC results showed well-developed andrographolide spots in all samples, with sample C having the highest percentage. HPLC quantification confirmed this, with sample C exhibiting the highest total andrographolide content. GC-ECD analysis detected pesticide residues in A. paniculata samples. This comprehensive chromatographic analysis enhances our understanding of A. paniculata composition and purity, ensuring potency and safety in herbal products. These findings provide valuable insights for quality control in A. paniculata-based formulations.Our research emphasises the safety and therapeutic potential of Andrographis paniculata, underscoring its importance in contemporary medicine. By using cutting-edge methods for thorough study, we were able to verify its effectiveness against several diseases.
KEYWORDS: Andrographolide, Andrographis paniculata, Thin layer chromatography, High Performance Liquid Chromatography and Gas Chromatography.
1. INTRODUCTION:
Andrographolide (AP), a C20 labdane diterpenoid is the bitter bioactive principle found in the aerial parts of the plant Andrographis paniculata (Burm f.) Nees (Family: Acanthaceae). It was found to exhibit various pharmacological actions including anti-inflammatory, anti-pulmonary, anti-viral, anti-cancer, anti-bacterial, anti-atheroscleron sis, neuroprotection and liver protection properties by Chakravarti and Chakravarti 1.
Fig.1: Chemical Structure of Andrographolide
In literature study, HPLC and spectrophotometric methods for the determination of AP in A. paniculata and their report 2 revealed that the HPLC method was found to be more accurate and sensitive as compared to the other methods. Some other methods including UV-Spectrophotometry3, Thin layer chromatography-image analysis method4, microemulsion electrokinetic capillary chromatography5, reverse phase high performance liquid chromatography (RP-HPLC), high speed counter current chromatography (Flow-injection chemiluminescence method6, electroanalytical method, miscellar electrokinetic capillary chromatography, HPLC7, rapid solution liquid chromatography (RRLC), high performance thin layer chromatography (HPTLC)8. fourier transform infrared spectroscopy (FTIR), ultra-performance liquid chromatography (UPLC) and chromatographic green method9 were also reported for the determination of AP in herbal formulations. Based on the literature survey, HPLC estimation method was found to be more sensitive and accurate for the determination of AP.10 reported the simplicity, quick standardisation, low operating cost and stability indicating properties of AP using TLC-image analysis method.11 described the trace analysis of multi-pesticides present in the plant Morinda officinalis using GC-ECD. These days, the majority of research efforts are focused on combating dengue, viruses and other infectious diseases. Therefore, TLC, HPLC and GC-ECD methods to determine and quantify AP and to trace analyse the pesticides present in the four different samples obtained from the market compared with the control and standard samples in order to work against the above mentioned pharmacological conditions.
2. MATERIALS AND METHODS:
2.1 Chemicals and Reagents:
Four different Andrographis paniculata powder samples were purchased from the local market, one control sample and standard used were obtained as a gift sample from Natural Remedies Pvt Ltd. All chemicals and reagents used were of analytical grade.
2.2 TLC Parameters:
The TLC system used was pre-coated silica gel on aluminium plate. The solvent system used for the chamber saturation was chloroform: acetone: benzene (20:20:10 ratio). The developed plate were detected by observing at wavelengths 254 and 366nm and also by spraying vanillin- sulphuric acid reagent (1.0% Vanillin in ethanol + 10% Sulphuric acid in ethanol). The TLC plate were also run simultaneously with reference solution of andrographolide (100 μg/mL concentration).
2.3 HPLC Parameters:
The HPLC system consisted of Shimadzu LC-2030C Liquid Chromatograph consisting quaternary pump, UV detector, auto injector, column oven and supported by LC- Solution software.The standard and sample were injected into HPLC (20 μL each). The mobile phase used as solvent A was buffer solution (0.136 g potassium dihydrogen orthophosphate + 0,5 ml Orthophosphoric acid – 0.45 µ filter membrane; degassed in sonicator for 3 min) and acetonitrile as solvent B.
2.4 GC-ECD Parameters:
The GC-ECD system consisted of Agilent Gas Chromatograph with Electron Capture and Nitrogen phosphorus detector 7890A-ECD/NPD (EZ Chrome), Electrical stirrer (Remi Motors), Buchi Rotovapor R-200, Buchi Heating Bath B-490, Vacuum pump, Sartorius analytical weighing balance and Agilent Vacuum Manifold. The flow rate of the carrier gas (nitrogen) was 0.979 mL/min. The make-up gas (nitrogen) included was 29.629mL/min and 1.0 µL of the samples and standard were injected into GC.
2.5 Sample Preparation for AP Analysis using TLC:
200 mg of Andrographis paniculata extract were weighed, 50ml of methanol was added and sonicated for 3 minutes. After sonication, the volume was made up to 100ml with methanol. 0.5mg/ml Andrographolide (standard) in methanol were prepared simultaneously. 10 μl of sample, standard and control was spotted using TLC applicator.
2.6 Sample Preparation for AP Analysis using HPLC:
2g of Andrographis paniculata roots/stems/leaves powder was weighed, 75ml of methanol was added and boiled on water bath for 20 min at 70-80 ºC. Then, the sample was cooled and filtered in a separate 250ml beaker. The extraction procedure was repeated 3 more times with 50ml methanol or until extract turns colorless. The filtrate was collected and concentrated to less than 100ml and transferred to 100ml flask, beaker was rinsed with methanol and transferred to same volumetric flask, the volume was made up to 100ml, mixed well and filtered the solution through 0.2 µ membrane filter paper. After filtration, samples were transferred to injector vial for loading HPLC instrument filter with syringe filter then transferred to injector vials. Before being used, all of the solutions were cooled to room temperature and kept at 4 °C.
2.7 Sample Preparation for AP Analysis using GC-ECD:
10g of sample was weighed and transferred to 500 ml beaker containing 350ml of mixture of acetonitrile and water was added. After that, the beaker was blended at high speed for 5mins using electrical stirrer and filtered. After filtration, filtrate was transferred to separating funnel and 100ml of hexane was added and shaken for 5 minutes. Then the hexane layer was transferred to the round bottom flask through a glass funnel plugged with cotton and anhydrous sodium sulphate and the process was repeated twice. After collection of hexane layer in round bottom flask, it was kept for rotary evaporation, dried and evaporated the hexane layer and made up to 10 ml in volumetric flask. From that, 1ml of sample was pipetted out and transferred into the quenchers containing mixture of salt (MgSO4 + Psa + C18 + Gcb) in each quenchers, mixed well for 2 min and kept for centrifugation for 6min. After centrifugation, the supernatant layer was transferred to injector vial and loaded to GC-ECD system.
2.8 Standard Pesticides Preparation for GC-ECD Analysis:
Standard concentration was prepared as mentioned in the USP by suitably dissolving an appropriate quantity of the individual reference standard in n-hexane and diluting with the same solvent. Working Standard was prepared by diluting the stock solution to 50ml as mentioned in the USP. 2.5 ml of the working standard concentration I solution is further diluted to 25 ml [Working standard solution (II)]. The pesticide residues present in the sample were identified by comparing the retention times of the peaks present in the chromatogram of the extract with that of standard. The standard was stored at 2-5oC.
2.9 Calculation:
calculations was carried out using excel sheet. For TLC, the spotted bands of the samples, standard and control were detected at 264 nm using TLC visualizer. Then, the plates were dried at the plate heater and spots were detected at 366 nm. For HPLC, the percentage of andrographolide, neoandrographolide, 14-deoxy-11-12 didehydroandrographolide and andrograponin contents present in the samples and standards from the peak areas were calculated using the formula:
|
Area of the sample |
x |
Weight of the standard (mg) |
x |
Sample dilution (ml) |
x |
Purity of the standard (%) |
|
Area of the standard |
Standard dilution (ml) |
Weight of the sample (mg) |
The percentage of total andrographolide was calculated as a sum of andrographolide, neoandrographolide, 14-deoxy-11-12-didehydroandrographolide and andrograponin. For GC-ECD analysis, the pesticide residues present in the samples, standard and control were calculated using the formula:
|
Residual pesticides (ppm) |
= |
Sample area |
x |
Standard weight |
|
Standard area |
Sample weight |
|
X |
Standard dilution |
x |
Standard purity |
x |
1000 |
|
Sample dilution |
100 |
3. RESULTS AND DISCUSSION:
In this research work, the presence of andrographolide was analysed for the four marketted samples, one control and one standard sample gifted from the Natural Remedies Pvt. Ltd. using HPLC, TLC and GC-ECD methods. The TLC system analysis revealed the presence of andrographolide, neoandrographolide, 14-deoxy-11-12-didehydroandrographolide and andrograponin in all four samples, control and standard spots as given in Fig. 2 after the TLC plate was dried and detected on TLC visualizer at 264 and 366 nm in the solvent system (chloroform, acetone and benzene). For HPLC, the percentage of total andrographolide was calculated as a sum of andrographolide, neoandrographolide, 14-deoxy-11-12-didehydroandrographolide and andrograponin contents present in the standards and samples were calculated from the peak areas and given in Table 1 and 2 and Fig. 3-9. The results revealed the presence of all the above mentioned chemical constituents in both the samples and standards. As compared to four samples, sample C was foun to be the highly quantified with andrographolide.
Fig. 2: A TLC Chromatogram of market available samples, control and standard
Table 1: Standard Values of Andrographolide and other three constituents using HPLC
|
Standard |
Andrographalide |
Neoandrographolide |
14-deoxy-11-12-didehydro andrographolide |
Andrograponin |
|
Standard weight |
26.59 |
5.16 |
4.77 |
1.51 |
|
Standard Dilution |
100 |
100 |
100 |
100 |
|
Purity |
99 |
99 |
99 |
95 |
|
Standard Area |
3916348 |
200229 |
488273 |
84837 |
|
4164813 |
214841 |
517662 |
89053 |
|
|
4032931 |
206368 |
500825 |
86943 |
|
|
Average |
4038031 |
207146 |
502253 |
86944 |
|
3.08 |
3.54 |
2.94 |
2.42 |
Table 2: Estimation of Total Andrographolide Content Present in the Samples Using HPLC
|
Sample Name |
Sample Weight |
Sample Dilution |
Andrographolide |
Neoandrographolide |
14-deoxy-11-12-didehydro Andrographolide |
Andrograponin |
Total (%) |
||||
|
Area |
Result |
Area |
Result |
Area |
Result |
Area |
Result |
|
|||
|
Sample A |
2029.2 |
100.0 |
191819.0 |
0.062 |
7006.0 |
0.009 |
50220.0 |
0.0 |
9542.0 |
0.008 |
0.10 |
|
Sample B |
2003.1 |
100.0 |
2355727.0 |
0.767 |
40627.0 |
0.050 |
382859.0 |
0.2 |
28285.0 |
0.023 |
1.02 |
|
Sample C |
2044.5 |
100.0 |
5035490.0 |
1.606 |
127457.0 |
0.154 |
686959.0 |
0.3 |
32513.0 |
0.026 |
2.10 |
|
Sample D |
2031.8 |
100.0 |
920392.0 |
0.295 |
41564.0 |
0.050 |
438020.0 |
0.2 |
29449.0 |
0.024 |
0.57 |
Fig. 3: HPLC Chromatograms of Standard A
Fig. 4: HPLC Chromatograms of Standard B
Fig. 5: HPLC Chromatograms of Standard C
Fig. 6: HPLC Chromatograms of Samples A
Fig. 7: HPLC Chromatograms of Samples B
Fig. 8: HPLC Chromatograms of Samples C
Fig. 9: HPLC Chromatograms of Samples D
The pesticide residues present in the sample were identified by comparing the retention times of the peaks present in the chromatogram of the extract with that of the standards. The results showed the presence of mixture of pesticides including delta-HCH, cyclorpyrifos-methyl, parathion methyl, vinchlozoline, alachlor, heptachlor, paraxon ethyl, chlorpyrifos-ethyl, dichloflunid, bromofos-methyl, heptachlorepoxide, procymidon, beta-endosulphon etc in the standards which was in the range of 7.600 ppm and the pesticide residues present in the samples was around 0.032 – 0.091 ppm which is lesser than the standards. The GC-ECD chromatogram of the standards and the samples were given in the Tables 3-6. and in Fig. 10 to 14
Table 3: List of Pesticides Present in the Sample A
|
Name |
RT (min) |
Area (Hz-s) |
Area % |
Amount (ppm) |
|
Alpha-HCH |
13.013 |
289.072 |
5.359 |
0 |
|
HCB |
13.451 |
418.442 |
7.757 |
0.001 |
|
Delta-HCH |
15.835 |
1764.966 |
32.719 |
0.003 |
|
Chlorpyrifos-ethyl |
21.076 |
198.607 |
3.682 |
0.001 |
|
2,4 DDE |
25.118 |
128.797 |
2.388 |
0 |
|
2,4 DDD |
27.571 |
275.378 |
5.105 |
0.001 |
|
4,4 DDD |
29.872 |
45.326 |
0.84 |
0 |
|
2,4 DDT |
30.072 |
209.216 |
3.878 |
0.001 |
|
4,4 DDT |
32.194 |
188.896 |
3.502 |
0 |
|
Cypermethrin-II |
43.412 |
44.217 |
0.82 |
0.001 |
|
Cypermethrin-III |
43.919 |
1491.232 |
27.645 |
0.015 |
|
Fenvalerate-I |
47.585 |
340.159 |
6.306 |
0.008 |
|
Sum |
0.032 |
Table 4: List of Pesticides Present in the Sample B
|
Name |
RT (min) |
Area (Hz-s) |
Area % |
Amount (ppm) |
|
Alpha-HCH |
12.971 |
147.036 |
0.944 |
0 |
|
Beta-HCH |
14.304 |
2354.307 |
15.107 |
0.009 |
|
Gamma-HCH |
14.596 |
7134.315 |
45.78 |
0.012 |
|
Delta-HCH |
15.841 |
1816.741 |
11.658 |
0.003 |
|
Chlorpyrifos-ethyl |
21.073 |
384.857 |
2.47 |
0.002 |
|
2,4 DDD |
27.637 |
52.844 |
0.339 |
0 |
|
4,4 DDD |
29.877 |
18.931 |
0.121 |
0 |
|
2,4 DDT |
30.054 |
222.33 |
1.427 |
0.001 |
|
4,4 DDT |
32.175 |
84.947 |
0.545 |
0 |
|
Cypermethrin-II |
43.457 |
503.996 |
3.234 |
0.017 |
|
Cypermethrin-III |
43.925 |
1354.256 |
8.69 |
0.014 |
|
Fenvalerate-I |
47.511 |
1509.289 |
9.685 |
0.033 |
|
Sum |
0.091 |
Table 5: List of Pesticides Present in the Sample C
|
Name |
RT (min) |
Area (Hz-s) |
Area % |
Amount (ppm) |
|
Delta-HCH |
15.838 |
1884.964 |
25.761 |
0.003 |
|
Chlorpyrifos-ethyl |
21.085 |
118.806 |
1.624 |
0 |
|
Alpha-ENDOSULPHON |
25.38 |
344.707 |
4.711 |
0.001 |
|
4,4 DDE |
27.07 |
185.998 |
2.542 |
0 |
|
2,4 DDD |
27.578 |
145.106 |
1.983 |
0.001 |
|
4,4 DDD |
30.005 |
13.801 |
0.189 |
0 |
|
2,4 DDT |
30.022 |
147.527 |
2.016 |
0 |
|
Endosulphon |
31.938 |
1327.488 |
18.142 |
0.004 |
|
Lamda-cyhalothrin |
38.467 |
210.964 |
2.883 |
0.001 |
|
Cypermethrin-ii |
43.385 |
139.652 |
1.909 |
0.005 |
|
Sum |
0.043 |
Table 6: List of Pesticides Present in the Sample D
|
Name |
RT (min) |
Area (Hz-s) |
Area % |
Amount (ppm) |
|
Alpha-HCH |
12.98 |
769.521 |
6.706 |
0.001 |
|
Beta-HCH |
14.304 |
1126.623 |
9.818 |
0.004 |
|
Gamma-HCH |
14.595 |
2672.486 |
23.289 |
0.005 |
|
Delta-HCH |
15.84 |
1182.768 |
10.307 |
0.002 |
|
Chlorpyrifos-ethyl |
21.091 |
577.625 |
5.034 |
0.002 |
|
Alpha-endosulphon |
25.374 |
552.294 |
4.813 |
0.001 |
|
4,4 DDE |
27.076 |
288.946 |
2.518 |
0.001 |
|
2,4 DDD |
27.645 |
61.079 |
0.532 |
0 |
|
4,4 DDD |
29.877 |
46.846 |
0.408 |
0 |
|
2,4 DDT |
30.038 |
405.254 |
3.532 |
0.001 |
|
4,4 DDT |
31.938 |
1605.54 |
13.991 |
0.004 |
|
Cypermethrin-I |
43.174 |
85.511 |
0.745 |
0.002 |
|
Cypermethrin-III |
43.908 |
2100.768 |
18.307 |
0.021 |
|
Sum |
0.044 |
Fig. 10: GC-ECD Chromatogram of the Standard
Fig. 11: GC-ECD Chromatogram of the Sample A
Fig. 12: GC-ECD Chromatogram of the Sample B
Fig. 13: GC-ECD Chromatogram of the Sample C
Fig. 14: GC-ECD Chromatogram of the Sample D
4. CONCLUSION:
Our research strategically addresses global health challenges, particularly focusing on combating dengue and viral infections. The exploration of A. paniculata has uncovered a myriad of pharmacological activities, notably its pronounced antimicrobial and antiviral properties. In light of the contemporary surge in the adoption of Ayurveda and natural herbal products, our study aims to contribute valuable insights into the safety and potency of human consumption. The meticulous evaluation of samples, employing advanced analytical techniques, not only confirms the therapeutic potential of A. paniculata but also underscores its safety profile. This provides a solid foundation for its integration into modern healthcare practices. The TLC results revealed the well-developed spots of andrographolide along with different constituents present in all four samples of A. paniculata. The HPLC method was applied for the determination of andrographolide in the market available samples and the results showed that the sample C was highly quantified with andrographolide which is summed up with other constituents including neoandrographolide, 14-deoxy-11-12-didehydroandrographolide and andrograponin. GC-ECD analysis identified and quantified various pesticide residues present in the samples of A. paniculata as compared with the standards.This research serves as a testament to the synergy between traditional knowledge and cutting-edge scientific methodologies, offering substantial contributions to addressing current health concerns.
5. ACKNOWLEDGMENT:
We thank the Management of Natural Remedies Pvt. Ltd. and Principal of KLE College of Pharmacy for giving constant support and encouragement for writing this research article.The authors received no financial support for the research, authorship and publication of this article.
6. CONFLICT OF INTEREST:
The authors declare no potential conflicts of interest with respect to research, authorship and/or publication of this article.
7. ABBREVATIONS:
TLC - Thin layer chromatography, HPLC - High Performance Liquid Chromatography and GC-ECD Gas Chromatography-electron capture detector, HCH- Hexachlorocyclohexane, DDE –dichlorodiphenyldichloroethane, DDT-Dichlorodiphenyltrichloroethane,DDD-dichlorodiphenyldichloroethane.
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Received on 17.05.2024 Revised on 10.11.2024 Accepted on 07.04.2025 Published on 13.01.2026 Available online from January 17, 2026 Research J. Pharmacy and Technology. 2026;19(1):69-75. DOI: 10.52711/0974-360X.2026.00011 © RJPT All right reserved
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