Arsenic Contamination of Groundwater in Cambodia Sour Sethy - - PowerPoint PPT Presentation

arsenic contamination of groundwater in cambodia
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Arsenic Contamination of Groundwater in Cambodia Sour Sethy - - PowerPoint PPT Presentation

The Asian Science & Technology Seminar in Thailand Arsenic Contamination of Groundwater in Cambodia Sour Sethy Department of Environmental Science, Royal University of Phnom Penh March 10-11, 2008 Contents Background Arsenic


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Arsenic Contamination of Groundwater in Cambodia

Sour Sethy

Department of Environmental Science, Royal University of Phnom Penh

The Asian Science & Technology Seminar in Thailand

March 10-11, 2008

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Contents

  • Background
  • Arsenic Situation
  • Education Program
  • Key Lessons Learned
  • Conclusion
  • Recommendation
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Background

Arsenic was detected in Cambodia in 2001 through National Drinking Water Quality Assessment. Arsenic Inter-Ministerial Sub- Committee (AISC) established in

  • 2002. AISC consists of 5 Ministries

(MRD, MIME, MoH, MoE and MoRAM).

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Background

National As Database established in 2003. Clinical Survey was conducted in 2003. National Drinking Water Quality Standards established in 2004. National Testing, Painting and IEC program established in 2004.

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Background

As 5 Year Strategic Action Plan developed in 2006. Arsenicosis Case Detection and Management was carried out in 2006.

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Arsenic Situation

Survey for 1607 villages showed that:

7 provinces located along the main rivers are the most at risk. As Occurred mainly in sediments near the rivers like Mekong, Bassac, and Tonle Sap River

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Arsenic Situation

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32.40% 20.30% 47.30% 57.50% 26.90% 15.60% 73.10% 13.10% 13.80% 67.00% 25.50% 7.50% 55.90% 38.70% 5.40% 74.50% 21.90% 3.60% 47.90% 50.20% 1.80% 0% 10% 20% 30% 40% 50% 60% 70% 80% 90% 100% Kandal Prey Veng Kampong Cham Kracheh Phnom Penh Kampong Chhnang Kampong Thom

As=0 0<As<=50 As>50

Percentage of the Distribution of Arsenic Concentration in 7 High Risk Provinces

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Approximately 2.25 million persons live in areas the most affected by arsenic. 139 families with a total 309 people identified with suspected symptom:

  • Leukomelanosis

Nodular Keartosis

  • (rain-drop pigmentation on skin)

Arsenic Situation

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Education Program

  • Developed IEC materials

– Poster, Leaflet – Media

‗ Arsenic song

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Education Program

  • Population were Informed

about arsenic:

35,645 Families were educated about the danger of arsenic. 1,356 School teachers and 45,064 school children in 3 provinces were provided with education.

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Education Program

☺Testing and Painting Program

  • A total of 24,683 tube wells tested across the

country-29% has proven to have As level higher than National Standard (50ppb).

Out of the above total, 20,427 tube wells tested in 7 high risk provinces - 35% have As level greater than 50ppb. 1,056 tube wells in school were tested - 6.5% has As >50 ppb. 201 tube wells tested in health care centre - 7% has As > 50ppb.

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Arsenic Mitigation Program

  • Alternative Sources Rain Water Collection System

Treatment Options

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Arsenic Mitigation Program

  • Families beneficiaries:

150 families were supported with shallow wells. 5,000 families were supported with CWPs 300 families were supported with traditional rain water jars 363 families supported with rain water tanks. 1,000 families used water facilities through community piped water systems.

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Key Lessons Learned

Lack of budget for awareness raising and provision of alternate safe water sources along with monitoring and surveillance. Lack of government ownership. Database management is need to be improved.

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Key Lessons Learned

Private/public partnerships in the supply of arsenic- safe water should be promoted. Communication on arsenic contamination of wells seems to be effective in terms of discouraging people from drinking arsenic-contaminated water. However, people may turn to use unsafe surface water which has high biological contamination. It is therefore critical to provide hygiene education and at the same time promote alternative safe water technology such as household filters, rainwater harvesting and community piped water.

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Conclusion

  • The most of highly As affected

contamination is: – Kandal Province (47% of tested wells) while Prey Veng (16%) and Kampong Cham (14%) were found As>50 ppb,

  • Only 0.5% of open wells are

contaminated, and generally at lower concentrations (maximum recorded arsenic value in an open well is 75 µg/L).

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Recommendation

  • Need to improve coordination and

collaboration between line Ministries and NGOs;

  • Increase involvement at each stage of

implementation of the concerned ministries, responsibility, accountability, and ownership;

  • Strengthening capacity building to

governmental staff at all levels;

  • Improvement database management and

information sharing with all stakeholders;

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Recommendation

  • Strengthening the collaboration with

MoEYS, university and institution- School- based Arsenic education, Innovative technology on Arsenic removal, ground water quality study;

  • Improve the capacity of national laboratory;
  • Need to continue to monitor water quality,
  • Need to continue to study the reason of

high arsenic contamination along the Mekong, Bassac and Tonle Sap river.

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Thank you very much !!!

Email: ssethy@yahoo.com

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References

  • MRD, 2006: Powerpoint presentation in the AISC

meeting in August 2006.

  • F., David, 2004: Situation Analysis: Arsenic

Situation Analysis: Arsenic Contamination of Groundwater in Cambodia supported Contamination of Groundwater in Cambodia supported by UNICEF. by UNICEF.

  • Sophary, 2007: Power point presentation of Arsenic

contamination in Cambodia.