ASSESSING EFFECTIVENESS OF SCHOOL POU DRINKING...
Transcript of ASSESSING EFFECTIVENESS OF SCHOOL POU DRINKING...
ASSESSING EFFECTIVENESS OF SCHOOL POU DRINKING WATER TREATMENT OPTIONS IN DANG & KAPILVASTU
Sharing workshop @ ENPHO16 September, 2011
Background
To promote and install POU options at schools, ENPHO with support from UNICEF-USAID/AED HIP project and DWSS/WSSDOs have implemented projects in different phases: Phase I: Selection of school and installation of POU
options; Phase II: Intensive research on technical performance
and social acceptance Phase III: Scale up promotion and installation of POU
options and perform preliminary monitoring in 200 schools at four districts viz. Dang, Kapilvastu, Parsa and Panchthar
Installation of POU options
At the end of third phase (December 2008), respective WSSDOs with technical support from ENPHO installed following POU options in schools at four project districts:
Options Dang K-vastu Parsa Panchthar Total Schools
Large CSF 129 63 56 84 332 141
Clay CSF 303 142 213 - 658 99
Plastic CSF - - - 113 113 30
SODIS bottles 3000 1880 1500 1645 8025 133
Large BSF - 10 - - 10 10
Large Arsenic BSF - 4 - - 4 4
Different POU options
Clay CS Filter
Large Biosand Filter
Plastic CS Filter
Large CS Filter
SODIS
The Project:
One of the major components within Su-SWASTHA project supported by USAID and EAWAG;
Received award of USD 2,000 from The WHO to perform this study
Study Area: Dang and Kapilvastu Study period: April – September, 2011
Objectives
Overall Objective: To evaluate technical performance and acceptance of School Point
of Use (POU) installed at schools of Dang and Kapilvastu districts.
Specific Objectives: To identify critical factors that affect continuous use of School
POU options; To assess and recommend strategies that will help sustainable
use of installed POU technologies at school; To document key challenges, problems, lessons learnt and
provide major recommendations for further scaling up of implementation of School POU promotion programme at other part of the country.
Methodology
1• Desk study• Planning
2• School visit, questionnaire survey, FGD• Water Sampling and Analysis
3• Report preparation• Dissemination of findings
Water Quality Analysis
SN Parameters Instrument Remarks
1. Fecal Coliform DelAqua Incubation at 45 º C
2. pH HANNA
3. Turbidity “Thermo” Turbidity meter
4. Temperature Thermometer
5. Iron and Arsenic ENPHO test kits Selected places
Water Samples were collected in acid washed, sterilized plastic bottles;
Analysis for all parameters were performed in the same day of water sampling
School visit
Monitoring and survey was conducted in 50 schools from: Dang – 27 schools out of 47 schools; Kapilvastu – 23 schools out of 47 schools.
Monitoring and research team:Name Agency District
Bipin Dangol ENPHO Dang
Manorath Bajgain ENPHO Dang & Kapilvastu
Hari Budhathoki ENPHO Kapilvastu
Chintu Thapa ENPHO Dang & Kapilvastu
Raj Kumar Acharya and Raj Kumar Pokharel WSSDO Dang
Yam Lal Jaisi WSSDO Kapilvastu
School Survey
Prepared structured questionnaire form: If the options are in use/operation, interviewed Teachers, Child clubs, Operators
If the options are not in use/operation, interviewedOnly teachers
Monitoring checklist to assess condition of POU options that are in operation;
Focus group discussions with child clubs to understand student’s Knowledge and perception on POU options
Results and discussions
POU Options in operation
Only 12 schools (44.4%) out of 27 visited schools were using at least one POU options;
POU options Distributed No. in use % in use
Large CS Filter 92 33 in 10 schools 36%
Clay CS Filter 119 5 in 3 schools 4%
Tank Chlorination 1 0 0%
SODIS bottles 1750 0 0%
In Dang
Filters in operation, Dang
POU Options in operation
Only 2 schools out of 23 visited schools were using at least one POU options;
POU options Distributed No. in use % in use
Large CS Filter 20 0 0%
Clay CS Filter 52 2 in 1 school 3.8%
Arsenic Biosand Filter 2 0 0%
Biosand Filter 11 1 in 1 school 9%
In Kapilvastu
Filters in operation, Kapilvastu
Reasons for not using Large CS filter
In Kapilvastu In Dang
Breakage of filter spout and candles are main reasons for not using Large CS Filter
Pictures of Large CS Filter not in use
Reasons for not using Clay CS Filter
In Kapilvastu In Dang
Breakage of filter, spout & disc are the main problems; In Kapilvastu users perceived water from artesian well is safe and don’t require
any treatment
Pictures of Clay CS Filter not in use
Reasons for stopping use of BSF
Reasons for stopping use of Arsenic BSF
Reasons for stopping SODIS (both districts)
Taste and Smell of Treated water (Filters in use, Dang)
Treated vs. Raw Water
Teachers Students OperatorsLCSF CCSF LCSF CCSF LCSF CCSF
TasteBad 20
Same 40 66.67 20 33.33 40 33.33Better 40 33.33 80 66.67 60 66.67
SmellBad 20
Same 50 66.67 60 100 70Better 30 33.33 40 - 30 100
All figures are in % LCSF: Large CS Filter; CCSF: Clay CS Filter
Treated vs. Raw WaterTeachers Students Operators
LCSF SCSF LCSF SCSF LCSF SCSF
LookBad 20
Same 50 66.67 40 33.33 50 33.33Better 30 33.33 60 66.67 50 66.67
Temp.Bad 60 20 20
Same 40 33.33 50 50 33.33Better - 66.67 30 100 30 66.67
Appearance and Temperature of Treated water (Filters in use, Dang)
All figures are in % LCSF: Large CS Filter; CCSF: Clay CS Filter
Perception of teachers (not in use, Dang)
Treated vs. raw water Small CS filter Large CS filter SODIS Chlorination
TASTE
Bad 10 100Same 80 50 60Better 20 40 40
SMELL
Bad 100Same 80 60 60Better 20 40 40
LOOK
BadSame 40 30 40 100Better 60 70 60
TEMP.
Bad 40 50 20Same 40 30 60 100Better 20 20 20
Treated vs. Raw WaterTeachers Students Operator
CSF Biosand CSF Biosand CSF Biosand
Taste
BadSame √ √ √Better √ √ √
Smell
BadSame √ √ √Better √ √ √
Taste and Smell of Treated water (Filters in use, Kapilvastu)
Treated vs. Raw Water
Teachers Students OperatorCSF Biosand CSF Biosand CSF Biosand
Look
BadSame √ √ √Better √ √ √
Temp.
BadSame √ √ √Better √ √ √
Appearance and Temperature of Treated water (Filters in use, Kapilvastu)
Perception of teachers (not in use, Kapilvastu)
Treated vs. Raw water CS filter Biosand filter
Arsenic biosandfilter
TASTE (%)Bad
Same 100 90 100Better 10
SMELL (%)Bad
Same 100 90 100Better 10
Treated vs. Raw water CS filter Biosand filter
Arsenic biosandfilter
LOOK (%)Bad
Same 100 100 100Better
TEMPERATURE (%)Bad 10
Same 100 90 10Better
Perception of teachers (not in use, Kapilvastu)
• Fecal Coliform• Turbidity• Iron and Arsenic• pH
Technical performance
Performance of Large CSF (Fecal coliform)
Average removal 60% 6 out of 13 filters
removed 100% fecal coliforms
5 out of 13 filters have 0% removal
0% 0% 0%
100%100%
0%
97% 100%100%100%100%
87.8%
0%
1 2 3 4 5 6 7 8 9 10 11 12 13
FIlter number
Fecal coliform removal by Large CSF (n=13)
Turbidity removal by large CS Filter
pH in Large CS Filter
7.1
6.7
7 7
7.5
7.7
7.4
7.6
7.3
7.5
7.7
7.1
7.7
7.27.1
7
7.67.7
7.7 7.8 7.8 7.8
7.5
7.8
7.1
7.3
1 2 3 4 5 6 7 8 9 10 11 12 13
FIlter number
pH In pH Out
Efficiency of Clay CSF (n=3)
Filter No.
Fecal coliform (cfu/100ml) Removal (%) District
Raw water Treated water
1. 1000 0 100 Dang
2. 70 0 100 Dang
3. 5 0 100 Kapilvastu
Filter No.
Turbidity (NTU) Removal (%) District
Raw water Treated water
1. 19 5.5 71.1 Dang
2. 5.7 8.2 -43.9 Dang
3. 7.1 3.3 53.5 Kapilvastu
Fecal coliform:
Turbidity:
pH in Clay CS Filter
7.1
7.6
7
7.3
7.9
7.3
1 2 3
Filter number
pH In pH Out
Performance of Biosand Filter
Water Samples pH E.Coli.(cfu/100ml)
Iron(mg/L)
Arsenic(ppb)
Turbidity(NTU)
Raw Water 7.1 132 10 60 17
Treated Water 6.9 8 0 0 3.3
Suggestions from schools, Dang
Suggestions from schools, Kapilvastu
Willingness to re-operate the system
How School can contribute to re-operate the system?
Activities %
Manage electricity 5.88
Buy and change tap/spout from the market 41.18
Buy or repair water pump 35.29
Buy and change filter candles/disc 29.41
Manage space to install filter safely 11.76
Maintain pipeline 5.88
Observations
General observation for filters in use
Storage Condition
Filter Maintenance
Other observations
It was found that the systems that are operating well have been maintained (cleaned) either by operators or by teachers;
Most of the systems maintained (cleaned) by students were found broken;
Schools that were operating systems have also good sanitary conditions (clean school premise, clean toilets)
Conclusions
Only 14 schools out of 50 schools visited are using at least one POU options;
Large CS Filter has average fecal coliform removal of 60% which is satisfactory;
Clay CS Filter has excellent fecal coliform removal (however number of samples is only 3);
In most of the cases, filter user were found satisfied with taste, smell, look and temperature of treated water
Most of the schools are still willing to re-operate the system and ready to contribute if needed;
Filter operation and maintenance was found satisfactory
Recommendations
Before scaling up promotion of POU options in schools, WE NEED TO: Install robust filters/systems (modify the existing or
develop the new one); Develop strong monitoring mechanism at local level; Ensure availability of spare parts and Strengthen
supply chain; Explore possibility of improvement and protection of
water sources; Provide refresher trainings/orientation to school
teachers, operators an child club members
Recommendations
We can promote chlorination in schools having water tanks and using dug wells;
Filters/systems should be installed based on the need and demand from school;
Filter O&M should done only by trained operators and school teachers NOT by child club members;
Need to perform water quality monitoring of POU options in regular basis
Acknowledgements
USAID EAWAG WHO UNICEF DWSS WSSDO Dang and Kapilvastu All school teachers, child clubs and operators
Thank You and Let us
Work Together