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Assessment of mercury concentration in major drains of hospitals in Bhopal, (M.P.) India

Anoop Chaturvedi1 * , D.K. Soni1 and Praveen Jain2

1 Central pollution Control Board, Bhopal, 462 016 India

2 M.P.Bhoj open university, Bhopal, 462 033 India

DOI: http://dx.doi.org/10.12944/CWE.2.1.20

The concentration of mercury in nearby drain of health care units was studied during 2005-06. The enrichment of mercury in wastewater discharge from various hospitals / health care facilities (HCF) have been reported in the present study. The concentration of mercury ranges between Below Detectable Limit (BDL) to 0.02 mg/l. Maximum concentration of mercury reported in the wastewater coming from Priyadershani market area where cluster of HCFs are located and the drain near Sultania hospital. The concentration of Mercury in these locations were found twofold than the prescribed limit by the Central Pollution Control Board. In the second year of study the concentration mercury got reduced remarkably at all location due to precautionary measure taken by the hospital authority.


Major Drains; Health Care; Mercury Concentration; Bhopal Hospitals

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Chaturvedi A, Soni D.K, Jain P. Assessment of mercury concentration in major drains of hospitals in Bhopal, (M.P.) India. Curr World Environ 2007;2(1):93-95 DOI:http://dx.doi.org/10.12944/CWE.2.1.20

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Chaturvedi A, Soni D.K, Jain P. Assessment of mercury concentration in major drains of hospitals in Bhopal, (M.P.) India. Curr World Environ 2007;2(1):93-95. Available from: http://www.cwejournal.org/?p=649


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Article Publishing History

Received: 2007-02-24
Accepted: 2007-04-11

Introduction

Water pollution due to heavy metal particularly mercury resulting from various anthropogenic sources are causing serious ecological problems in many part of the world. Poor environmental management with respect to use of mercury in the society to meet our day to day requirement may aggravate the adverse effect on the various component of environment. This may leads to the transformation mercury from one compartment of environment to another, including the biota with detrimental effects. Literature shows the sufficient accumulation of the mercury in biota through food chain transfer, there is also an increasing toxicological risk for man.

A famous episode of Minanata disease occurred in Japan in fifties due to consumption of fish contaminated by methyl mercury.
Mercury in natural water can exists in truly, colloidal and suspended forms.

The mercury is used in various medical devices particularly temperature and blood pressure measuring gadgets. The following are the major equipment in which mercury is used.

  • Clinical and normal thermometer
  • Sphygmomanometer
  • Dilators
  • Dental amalgam
  • Lab chemicals such as zenkers solution, histological fixatives


In normal case leakage or spillage of mercury from thermometer or any devices, clean up without use of protective gears and proper disposal system. This not only exposes the health workers who are handling mercury spills but also the community at large in long term. The waste spilled mercury is thrown in community dustbin, flushed down the sewer or incinerated. When incinerated, it may volatilize and become airborne or eventually settles in water bodies from where through bioaccumulation and bio magnification route may reach to humans kind. The accumulation of mercury in muscle tissue may jeopardize cell division, binds with DNA interfering with replication of chromosomes and protein synthesis.

Material and Methods

The Bhopal city, capital of Madhya Pradesh state is situated above 500 m. above MSL between 23.16 N latitude and 77.36 E longitude having population figure just over 1.8 million, has been selected for the study. During the study both kind of drains, which cover private and government hospitals were covered. In Bhopal more then 250 health care facilities are operating at various part of the city.

Five monitoring location on various hospital drains were identified to assess the contribution of mercury to public sewer. The sampling was carried out on quarterly basis for two year continuously during January 2005 to October 2006. Sampling schedule were fixed in the first week of every quarter month of year in the morning hour between 10.00 am to 1.00pm.The details of the sampling location are as given in Table -1.

The standard methods as prescribed in APHA adopted for analysis of wastewater samples during study.
1,4 The primary conditioning of the samples were carried at the site followed by analysis in the laboratory using Mercury analyzer, Electronic Corporation model -5840.2,6 The instrument work on cold vapor atomic absorption spectroscopy technique at 353nm.

Take a suitable aliquot of the sample, blank and standards in a reaction vassal. Add the required amount of 10% HNO
3 to maintain a vol. of 10 ml. Add 2 ml of 20% SnCl2 in sample and placed the stopper immediately, switch on the magnetic stirrer. The cold vapor of the Hg is produced. Measure the absorbance of the sample and extra polote the Hg concentration from analytical calibration graph. Plot the analytical calibration graph of absorbance vs concentration of Hg in micro gm/l.

                                       mg value by graph x dilution
Calculation :Hg mg/l :   _____________________________
                                            Vol. of sample


Table -1

S.No.
Nearest hospital from drain
Owned by
Drain ultimately joins to
1
Hazela hospital near P&T square
Private sector
Shahpura lake
2
J.P.Hospital
Government
River Betwa
3
Kasturba Hospital
Public sector
River Betwa
4
Sultania hospital
Government
Halali dam
5
Cluster of hospital near Jawahar chowk behind Priyadershani market.
Govt. & Pvt.
Chotta Talab in the city.


Results and Discussion

Concentration of mercury in studied drains is presented at table. The results, shows that concentration of mercury well within the discharge limits set by CPCB3 except at two drains i.e. near Priyadershni market and Sultania hospital. The highest concentration i.e. 0.02 mg/l were recorded at these locations. This higher concentration in the aquatic environment may pose serious threats to aquatic biota, which may ultimately reflect to human health. Concentration of mercury at other location ranges between BDL to 0.005 mg/l. In the month of July 2005 and 2006 mercury value found BDL due to dilution by rainwater.

Table - 1: Mercury Concentration in major public sewers near hospitals

Location(Drain Near) Jan 2005 Apr. 2005 Jul. 2005 Oct. 2005 Jan 2006 Apr 2006 Jul 2006 Oct. 2006
Hazela hospital ,P&T squre 0.002 BDL BDL 0.001 BDL 0.004 BDL BDL
J.P.Hospital BDL 0.004 BDL BDL 0.001 0.001 BDL BDL
Kasturba  Hospital 0.002 BDL BDL 0.001 0.002 BDL BDL 0.002
Sultania hospital BDL 0.005 BDL 0.02 0.002 BDL BDL BDL
Priyadershani market 0.002 0.001 BDL 0.02 BDL 0.005 BDL 0.002

All the values are in mg/l BDL-Below detectable limit

Conclusion

Variation in the concentration of mercury with relation to time and locations were observed in the study. In the second year of study i.e. 2006, the concentration of mercury reduced remarkably. Major causes for the reduction of mercury concentration may be due to replacement of the traditional mercury based instrument by digital instrument as well as strict implementation of BMW ( M & H) rule by the hospital authority.

Acknowledgements

The authors are thankful to In charge Zonal Officer ,CPCB Bhopal for the facilities provided to carry out this study.

References

 

  1. APHA, American Public Health Association, standard methods for the examination of water and waste water, 20th edition New York
  2. Laboratory analysis technique /17/2004- 2005 CPCB
  3. Pollution control acts rules and notifications issued there under series PCLS/02 (2006).
  4. Sawyer N.C.McCarty P L and Parkin, GF “Chemistry for Environmental engineering”.
  5. Pariwesh newsletter of CPCB (2005).
  6. Manual of mercury analyzer ECL, Hydrabad.