Ethnobotanical Leaflets 14: 856-63. 2010.

 

Analysis of Heavy Metal and Inorganic Element Content in

Barringtonia acutangula Leaf

 

R. Vijaya Bharathi*, A. Jerad Suresh, M. Thirumal, B. Kumudhaveni

 

Department of Pharmacognosy, College of Pharmacy, Madras Medical College, Chennai-03,

Tamil Nadu, India

         *Email: rvbharathi2003 @ yahoo.com

 

Issued August 1, 2010

 

Abstract

 

The estimation of heavy metals and inorganic elements in Barringtonia acutangula leaves were carried out, using Atomic absorption Spectrophotometry (AAS), Colorimetric, Cold Vapour Atomic Absorption, Argentometric, Turbidimetric and sodium 2- (parasulfophenylazo)- 1 ,8-dihydroxy-3,6-naphthalene di sulphonate (SPADNS) colorimetric method. The heavy metals determined were Arsenic, Cadmium, Lead, Mercury and Copper. The inorganic elements present, Fluoride, Chloride and Sulphate were Quantitatively estimated. The results obtained revealed that heavy metals level in Barringtonia acutangula leaves were within the permissible limit and hence seem to be a  safe herbal medicine to health.

Key words: Barringtonia acutangula, Heavy metals, Inorganic elements.

Introduction

Medicinal plants have been in use since for many years to cure a great variety of diseases. Recently with the emphasis of the World Health Organization, the use of traditional herbal medicine has spread not only in the developing countries but also in the industrialized ones, as a complementary way to treat and to prevent illnesses (World Health Organisation, 2003).

Heavy metals, such as zinc, lead, copper, mercury, cadmium, arsenic are extremely toxic in very small amounts. When one or more of these elements are present in the environment at high concentrations, living organisms are subjected to strong natural selection for tolerance. Environmental contamination by metals exerts physiological pressures that are clearly too severe for survival of most species by means of phenotypic plasticity or physiological acclimation, rather than genetic adaptation (Tonguc, 1998).

The pharmacological properties of the medicinal plants have been attributed to the presence of active constituents which are responsible for important physiological function in living organisms. It has been reported that trace elements play an important role in the reactions which will lead to the formation of these active constituents (Serfor-Armah et al., 2001). However, a correlation between elemental composition of medicinal plants and their curative properties have not been established yet. Besides, element concentrations present in medicinal plants are of great importance to understand their pharmacological actions (Serfor-Armah et al., 2002).

 

Materials and Methods

Fresh leaves of Barringtonia acutangula (L.) Gaertn. (Lecythidaceae) were collected from Madras Medical College premises, Chennai, Tamilnadu.  The plant was identified, and authenticated by botanist Dr. P. Jayaraman, Plant Anatomical Research Centre, Tambaram, Chennai.

 

Estimation of heavy metals

Estimation of Arsenic

Arsenic was estimated by using Modified Arsenic estimation apparatus. Take sample in an arsine generator. Add 3 gm of Zinc and 2 ml potassium iodide solution to the generator. Impregnate the glass wool in the scrubber with lead acetate solution. Take 4 ml silver diethyl dithiocarmate reagent in the absorber tube. Take 5 ml conc. Hydrochloric acid and 1 ml Stannous chloride reagent in a measuring cylinder. Connect the generator scrubber absorber assembly and make sure that all connections are tightly fitted. Remove the stopper of arsine generator and immediately close the generator by the stopper. Allow 30 minutes for complete evolution of arsine. Pour the solution from the absorber directly in to 1 cm cell and measure the absorbance of the solution at 535 nm spectrophotometrically. Prepare standard curve by using the standard solution.

Estimation of Mercury

Adjust all control knobs present in the instrument. Remove the stopper and take a suitable aliquot of the blank, standard or sample solution in the reaction vessel. Add 10 % Nitric acid to maintain a volume of 100 ml. add 2 ml of Stannouschloride and replace the stopper immediately. Switch on the magnetic stirrer and stir vigorously for about 5 mnts. Adjust ‘0’ and 100 % T. Leave the filter rod in the position. Switch to ‘HOLD’ mode of operation. Start the pump and allow air to purge through the reaction vessel. Note the absorbance as early as possible with in a min and switch back to ‘NORMAL MODE’. The meter indication should be back to 100 % T. switch off the pump and the magnetic stirrer. Adjust 0 % and 100 % just before each measurement. Repeat the measurements for standard. Plot Absorbance vs. Concentration of Mercury

Estimation of Lead, Copper and Cadmium

            The instrument used for analysis was Perkin Elmer Analyser 300. After calibrating the instrument, aspirate a blank consisting of deionized water containing the same concentration of acid in standard and sample. Zero the instrument. Aspirate a standard solution and adjust aspiration rate of the nebulizer to obtain maximum sensitivity. Adjust burner both vertically and horizontally to obtain maximum response. Aspirate blank again and re-zero the instrument. Repeat the same for sample and determine its absorbance (Clesceri et al., 1998).

The metal concentration was estimated on dry weight basis by using the following equation

Metal concentration, mg/kg (dry weight basis) =        A       x       B      x     100

                                                                                     g of Sample               D

Where:  

A-    concentration of metal in digested solution, mg/l

B-    final volume of digested solution, ml

D-    total solids, %

 

Qualitative and quantitative estimation of inorganic elements

Qualitative analysis of Inorganic elements

Prepare ash of drug material. Add 50 % v/v Hydrochloric acid. Keep for 1 hour or longer. Filter. With filtrate perform the following tests (Khandelwal 2006).

Calcium: To 10 ml filtrate, add 1 drop dil. ammonium hydroxide and saturated ammonium oxalate solution. White precipitate of calcium oxalate forms. Precipitate is soluble in Hydrochloric acid but insoluble in acetic acid.

Magnesium: Filter and separate white calcium oxalate precipitate obtained above. Heat and cool the filtrate which with solution of sodium phosphate in dilute ammonia solution gives white crystalline precipitate.

Sodium: To 2 ml test solution, add little uranyl magnesium acetate reagent. Shake well and keep for few minutes. Yellow crystalline precipitate of sodium magnesium uranyl acetate observed.

Potassium: To 2-3 ml test solution, add few drops sodium cobalt nitrite solution. Yellow precipitate of potassium cobalt nitrite observed.

Iron: To 5 ml test solution add few drops of 2% potassium ferrocyanide. Dark blue coloration is observed.

Sulphate: With lead acetate reagent gives white precipitate soluble in sodium hydroxide.

Phosphate: To 5 ml test solution prepared in Nitric acid add few drops ammonium molybdate solution. Heat 10 min. Cool. Yellow crystalline precipitate of ammonium molybdate is observed.

Chloride: To about 5 to 7 ml filtrate, add 3 to 5 ml lead acetate solution. White precipitate soluble in hot water is observed.

Carbonate: With dilute acid liberate carbon dioxide.

Nitrates: With solution of ferrous sulphate yield no brown colour but if sulphuric acid is added (slow from the side of the test tube), a brown colour is produced at the junction of two liquids.

Quantitative estimation of Inorganic elements

Sulphate: Sulphate ion is precipitated in an acetic acid medium with barium chloride so as to form barium sulfate crystals of uniform size. Light absorbance of the barium sulphate suspension is measured by a photometer and the sulphate concentration is determined by comparison of the reading with a standard curve.

Estimation: Sulphate was estimated by Turbidimetric method. Absorbance was measured using Chemito 2100 scanning spectrometer. A suitable portion of sample made up to 100 ml taken into 250 ml Erlenmeyer flask. Add 20 ml buffer solution and mix in stirring apparatus. While stirring, add a spoonful of Barium chloride crystals and begin timing immediately. Stir for 60 + 2 s at constant speed. After stirring period has ended, pour solution into absorption cell of spectrophotometer and measure turbidity at 420 nm. Estimate Sulphate (SO42-) conc. in sample by comparing turbidity reading with a calibration curve prepared by carrying SO42- standards.

Fluoride: Fluoride was estimated by sodium 2-(parasulfophenylazo)- 1 ,8-dihydroxy-3,6-naphthalene disulphonate (SPADNS) colorimetric method and it is based on the reaction between fluoride and a zirconium-dye  lake. Fluoride reacts with the dye lake, dissociating a portion of it into a colourless complex ion (ZrF62-); and the dye. As the amount of fluoride increase, the colour produced becomes progressively lighter. Absorbance was measured using Chemito 2100 scanning spectrometer. 

Estimation: Prepare fluoride standards in the range of 0 to 1.40 mg F-/L by diluting appropriate quantities of standard fluoride solution to 50 ml with distilled water. Pipette 5 ml each of SPADNS solution and zirconyl-acid reagent or 10 ml mixed acid-zirconyl-SPADNS reagent, to each standard and mix well. Avoid contamination. Set photometer to zero absorbance with the reference solution and obtain absorbance readings of standards. If the sample contains residual chlorine, remove it by adding 1 drop (0.05 ml) NaAsO2 solution/ 0.1 mg residual chlorine and mix. A portion of sample is diluted to 50 ml with distilled water. Adjust sample temperature to that used for the standard curve. Add 5 ml each of SPADNS solution and zirconyl-acid reagent, or 10 ml acid-zirconyl-SPADNS reagent; mix well and read absorbance at 570 nm.

Chloride: In a neutral or slightly alkaline solution, potassium chromate can indicate the end point of the silver nitrate titration of chloride. Silver chloride is precipitated quantitatively before red silver chromate is formed.

Estimation: Chloride was estimated by Argentometric method. A suitable portion of sample was diluted to 100 ml. If the sample is highly colored, add 3 ml Aluminiumhydroxide suspension, mix, let settle and filter. Directly titrate samples in the pH range 7 to 10. Adjust sample pH to 7 to 10 with Sulphuricacid or Sodiumhydroxide if it is not in this range. Add 1 ml Potassium chromate indicator solution. Titrate with standard Silvernitrate titrant to a pinkish yellow end point.

Result and Discussion

The crude powder was ashed and acid digested were analysed for the presence of Heavy metals like Arsenic, Lead, Mercury, Cadmium and Copper were found to be within the permissible limit (Table 1). The presence of essential element copper in the leaves confirms the potentiality of the drug in various ailments. The Qualitative and quantitative estimation reveals the presence of inorganic elements like Chloride, Fluoride and Sulphate (Table 2). The estimation of heavy metals and inorganic elements content in this medicinal plant represents one of the factors for the evaluation of their quality. The present study provides valuable information for authentication of this medicinally useful plant. The results obtained revealed that heavy metals level in Barringtonia acutangula leaves were within the permissible limit and hence seem to be a  safe herbal medicine to health.

  


Table 1. Quantitative estimation of Heavy Metals

S. No

Parameters

Quantity (mg/kg)

1

Mercury  (WB)

<0.005

2

Copper  (DB)

<0.0015

3

Lead  (DB)

<0.015

4

Cadmium  (DB)

<0.0008

5

Arsenic  (DB)

<0.001

WB- wet basis and DB- Dry basis

 

Table  2.   Qualitative and Quantitative analysis of the leaf powder.

S. No

Inorganic elements

Result

Quantity (mg/kg)

1

Calcium

--

--

2

Magnesium

--

--

3

Sodium

--

--

4

Potassium

--

--

5

Iron

--

--

6

Sulphate

+

<45  (WB)

7

Phosphate

--

--

8

Chloride

+

< 10703  (WB)

9

Carbonate

--

--

10.

Nitrate

--

--

11.

Fluoride

+

<0.1  (WB)

(+)   Present, (-) Absent, WB- wet basis

 

References

Clesceri LS, Green berg AE, Eaton AD. 1998. Standard methods for the Examination of water and waste water. 20th edn, American Public Health Association, Washington.

Khandelwal KR. 2006. Practical Pharmacognosy. 16th edn, Nirali Prakashan, Pune.

Serfor-Armah Y, Nyarko BJB, Akaho EHK, Kyere AWK, Osae S, Oppong-Boachie K, Osae EKJ.2001. Activation analysis of some essential elements in five medicinal plants used in Ghana. J. Radioanal. Nucl. Chem., 250 (1): 173–176.

Serfor-Armah Y, Nyarko BJB, Akaho EHK, Kyere AWK, Osae S, Oppong-Boachie K.2002. Multielemental analysis of some traditional plant medicines used in Ghana. J. Trace Microprobe Tech., 20 (3): 419–427.

Tonguc O.1998. Determination of Heavy metal levels in some moss species Around Thermic power Stations. Turkey Journal of Biology (28): 171-80.

World Health Organization. Traditional Medicine, Fact sheet No. 134, May 2003. Available at:  owww.who.int/mediacentre/factsheets/2003/fs134/en4 Access in: 07/08/2003.