post implementation report chapter: yale … noah mccoll mentor #1 david sacco mentor #2 jeremy...
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© 2007 Engineers Without Borders – USA. All Rights Reserved Page 1 of 37
Document 526
POST IMPLEMENTATION REPORT
CHAPTER: Yale Student Chapter
COUNTRY: Cameroon
COMMUNITY: Kikoo, Bui
PROJECT: Kikoo Water Project
PREPARED BY Noah McColl, Elizabeth Marshman, Saalem Adera, Rohan Agarwal, Jonathan Yeh, Dana Miller, Dacia Thompson
Submittal Date: 02/00/2010
ENGINEERS WITHOUT BORDERS-USA
www.ewb-usa.org
Document 526 - Post Implementation Report
Yale Student Chapter
Kikoo Water Project
© 2007 Engineers Without Borders – USA. All Rights Reserved Page 2 of 37
Post Implementation Report Part 1 – Administrative
Information
1.0 Contact Information (Contac Info. Deleted for On-line Use)
Name Email Phone Chapter
Project Lead Elizabeth
Marshman
President Noah
McColl
Mentor #1 David
Sacco
Mentor #2 Jeremy
Smith
Faculty Advisor William
Mitch
Health and Safety
Officer #1
David
Sacco
Health and Safety
Officer #2
Dacia
Thompson
NGO/Community
Contact
Father
Daniel
Education Lead Dieudonne
Tanayen
2.0 Travel History
Dates of Travel Assessment or Implementation Description of Trip
January 2007 Assessment -Community introduction and consultation
-Surveying catchment and storage tank
area.
-Catchment water testing
August 2007 Implementation -Construction of 20,000 L water storage
tank
-Community education on sanitation and
hand-washing and system maintenance
January 2009 Assessment/Implementation -Inspection of existing system. Surveying
for expansion of water distribution network
-Continuing construction of standpipes
-Testing alternative spring supplies to
upper Kikoo
-Continued sanitation education and
teaching of water quality tests
January 2010 Implementation -Initiation of construction of a 12,000L
secondary storage tank providing water to
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Yale Student Chapter
Kikoo Water Project
© 2007 Engineers Without Borders – USA. All Rights Reserved Page 3 of 37
an as-yet-unserved part of the community
-Continued education and teaching of
system use and maintenance
-Investigation of Roh water distribution
system
3.0 Travel Team (Contac Info. Deleted for On-line Use) Name E-mail Phone Chapter Student or
Professional
Noah McColl
Elizabeth Marshman
Dacia Thompson
Jonathan Yeh
Rohan Agarwal
Dana Miller
Dave Sacco
Jeremy Smith
Saalem Adera
4.0 Safety
4.1 Safety Incident Reports
One member of the travel team, Elizabeth Marshman, began feeling ill on January
1. She subsequently developed a fever and began vomiting in the early morning of
January 2, at which time she was escorted to Banso Baptist Hospital and given
medical attention. After 3 days and 2 nights of rest and intravenous re-hydration,
she was discharged from the hospital, feeling fine but fatigued.
Several other members of the team experienced, at various points, malaise and
nausea, but none of these cases were severe and were quickly resolved.
5.0 Budget
5.1 Cost
Expense Total Cost
Airfare 1,9081
Pre-Trip Expenses 2,537
On Ground 3,864
Materials 4,315
Total 29,797
Airfare is 9 @ $2120/pax
Pre-trip Expenses (Supplies, Medications, Visas): $2537
Document 526 - Post Implementation Report
Yale Student Chapter
Kikoo Water Project
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Ground costs:
Van to/from JFK Airport: $515
Douala Lodging: $221
Douala Food: $245
Airport taxis: $19
Bus to and from Kumbo: $638
Taxis to and from Kikoo: $705
Food and Lodging for 9 plus 4 in Kumbo: $1206
Exit visas: $191
Gratuities: $23
Hospital Stay: $80
Misc. $21
To be purchased within the next 2 months:
Materials
Cement, 70 sacks @ 7,000 CFA, $1110
Sand, 2 m3 @ 60,000 CFA, $280
Gravel, 2 m3 @ 50,000 CFA, $230
Rebar, 29 12m bars @ 4,400 CFA, $285
Fittings, assorted, $110
63 mm NP-10 PVC pipe, 500 m @ 2,000 CFA, $2300
6.0 Project Location Longitude: 10°41′6″E
Latitude: 6°12′18″N
Post Implementation Report Part 2 – Technical Information
1.0 INTRODUCTION This document outlines the findings, actions taken, and goals achieved during EWB-Yale's
implementation trip to Kikoo, Cameroon in January 2010.
The primary purpose of this trip was to begin construction on a secondary storage tank to provide
the last third of Kikoo with clean water. In 2006, the partnership between EWB-Yale and Kikoo
started work on a water distribution system for the community. The first 2 trips concerned
supplying the lower two-thirds of Kikoo with water from a clean catchment outside of the
village. Most recently, the 3rd trip was an assessment trip to investigate how water could be
supplied to the final, more elevated third of Kikoo. Analyzing the data from the third trip
permitted EWB-Yale to design the final section of the water distribution system. This January
2010 trip initiated the implementation of these designs and followed up on various aspects of the
existing system and the community of Kikoo. The following report outlines the project‟s history,
what was accomplished during our time on-site, and various considerations and findings
regarding the maintenance and sustainability of the project.
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Kikoo Water Project
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2.0 PROGRAM BACKGROUND The community of Kikoo has historically collected water from polluted streams resulting in
sickness and disease prevalent throughout the village. Originally, the village worked with the
Social Welfare Department of the Catholic Diocese of nearby Kumbo to begin a catchment for a
clean water project. The Diocese has extensive experience supporting water projects throughout
the region, and will provide continuing logistical support for project design and implementation.
The community has continuing to play an extremely active role in the partnership, pressing the
project forward with labor and financial contributions. The initial contact was made by Joshua
Knight, a lay missionary and environmental engineer working with the Diocese. Mr. Knight has
returned to the US but continues to be involved with EWB.
The goal of the project has been to construct a water distribution system for the community of
Kikoo in order to provide a clean and sustainable source of water. An uncontaminated spring has
been located and tapped that provides the source of the community‟s water. The design includes
an overflow tank, a storage tank, public standpipes throughout the community, and a proposed
solution to the problem of bringing water to the farthest third of the village. This last stage of the
project is our current focus. In January of 2009, EWB-Yale conducted an assessment trip to
Kikoo to identify means of providing the final third of the community. From the information
gathered it was decided that a secondary tank would be constructed in the upper village that
would fill up during times of low demand on the system. This trip's purpose is to implement the
designs for this secondary storage tank by starting construction.
The following is a summary of the already completed parts of the Kikoo water distribution
system.
Catchment
Break Tank
Low Point Valve
Primary Storage Tank
Standpipes
Catchment:
The catchment was constructed prior to EWB-Yale‟s involvement. The design is a concrete dam
dug through the soil down to bedrock. Two pipes leave the catchment connecting to the
distribution system. A third pipe serves as an overflow to avoid back pressure within the
catchment. Back pressure was avoided to prevent the groundwater source from seeking
alternative paths due to resistance from the collection system. The catchment is made from stone
masonry with PVC pipe and valves connecting to the distribution system.
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Kikoo Water Project
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Top left: overhead schematic of catchment, top right: photo of catchment on August 2007 trip,
bottom: side view schematic of catchment.
The catchment area is 2km from the village of Kikoo surrounded by grazing lands. Immediately
around the catchment is dense flora which thrives off of the water source. This source was
chosen because of its flow volume, cleanliness and low risk of human contamination due to its
isolation from the village. To prevent livestock from contaminating the catchment trees from a
local nursery have been planted around the source‟s watershed to act as a barricade. Tests
performed on the water source have shown minimal contamination.
Flow from the spring is dependant on the season. During the wet season (May – October), flows
are much higher than the dry season. The pipe sizing was designed to accommodate peak
seasonal flows of up to 3 L/s., while the storage tank was sized for minimal flows so that even
during the dry season sufficient water would be collected to provide for the entire population.
The minimal flow that has been recorded from this catchment was in January of 2009, during the
dry season, was 0.9 L/s.
Break Tank:
The break tank was designed by EWB-Yale and implemented by local masons. The purpose of
the break tank is to combine the two pipes leading from the catchment into one pipe leading to
the primary storage tank. Two pipes initially leave the catchment because the slope between the
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Kikoo Water Project
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catchment and the break tank is very shallow resulting in limited pipe capacity. The break tank
also serves as an overflow for the system. At this point in the system if the catchment is
supplying more water than will flow through the outflow, water will overflow and be directed
back into the original streambed. The break tank is influential in the system for allowing greater
flow from the catchment to the storage tank.
The tank also has a clean out pipe and valve. Any sediment that is carried in the water from the
catchment to the break tank and precipitates out at the tank will collect in the bottom of the break
tank. The clean out valve allows for this sediment to be manually flushed out.
Low Point Valve:
At the local elevation minimum between the catchment and the storage tank a low point valve
was designed to flush out any potential build up of sediment. In a valve box made from stone
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and concrete a T-joint allows for this point of the system to be flushed out. A build up of
sediment at this point would reduce flows to the system. On the 2009 trip to Kikoo, the low
point valve was opened and flushed out. There appeared to be minimal sediment build up.
Primary Storage Tank:
The primary storage tank was designed by EWB-Yale and construction for the tank began on
EWB‟s August 2007 implementation trip. Local masons finished the construction after the EWB
group had left. The finished tank was inspected on the January 2009 assessment trip.
The tank size is 20,000 liters. This size was based on a population of 2,000 residents, each using
40 L/day, with a minimum inflow from the catchment of 1 L/s. Though the population of Kikoo
was below 1,000 when the designs were made, a greater design population allowed for the
system to support a growing population. 40 L/day is a figure recommended for an individuals
use by the UN. This figure is for basic water uses only covering drinking, cooking and washing
needs. The water provided from the Kikoo water system is not sufficient to cover further
demands such as irrigation and thus should not be used for these purposes. Basing the design off
minimum flows allows for the system to provide for the entire community even during the dry
season when water sources are low. There is sufficient variability in flow rates from the wet
season (May-October) to the dry season (November-April).
A valve box adjacent to the storage tank allows the water committee to control the system. The
set of valves depicted in the diagram bellow allows the water committee to control overflow,
empty the tank for cleaning, and bypass the tank to continually supply the system while the tank
is cleaned. This is an important facet of the design to keep the system dynamic. The ability to
empty and clean the tank is important in the scenario of contamination entering the tank. Having
a bypass route allows the village to continue using water from the spring while the tank is
cleaned. Controlling overflow is important because of the variability in flows from the spring.
In the dry season some overflow from the tank is allowed to go to neighboring farmers fields. In
the wet season when flow is high from the spring all overflow is directed back into the original
streambed. This is because the fields are already saturated and any additional flow has erosion
potential.
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Kikoo Water Project
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The tank was placed on the edge of Kikoo where it would be easily monitored by the water
committee and at sufficient altitude to supply the village. Continual monitoring of the storage
tank is important to ensure that the structural integrity does not decrease allowing for
contamination. Also a convenient location facilitates regular water sampling to monitor water
quality. The elevation relative to the rest of the system is also an important design consideration
because the system is entirely gravity powered. Without a reliable source of electricity in Kikoo,
a gravity-powered system was thought to be the most dependable.
Above left: construction of storage tank during August 2007 trip, above right: Completed storage
tank 2007.
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Standpipes:
The original system design had 14 standpipes located throughout Kikoo. These 14 locations
would serve as central points where residents could easily access clean water. After more
extensive surveying on the January 2009 trip it became apparent that water would not reach
proposed standpipe 13 because it was 8 meters above the elevation of the storage tank. The
system has since been modified to place standpipes 13 and 14 in proximity to the secondary tank.
The standpipes are made of stone masonry and cast-in-place concrete. They are meant to be
durable and accessible. A prototype design was presented to the water committee to be used in
the construction of the standpipes. Upon visiting the project site in 2009, it was discovered that
some variation had been made to the original designs; however, they all appeared to be
functioning well. Concrete supports the standpipes which stand 1 meter high. The faucet and
any exposed pipe is galvanized iron for durability against daily water collection and exposure to
UV light. The foundation of the standpipe is also made of stone and concrete, which keeps the
immediate area free of mud and firmly supports the standpipe stand.
Drywells were also incorporated into the original design. These were 1.2 x 1.6 x 2.1 m wells
filled with rip-rap to aid in the ground absorption of any excess water. By allowing the water to
penetrate deep into the ground through the rip-rap the design intended to avoid above surface
runoff. The dry well design failed in the early standpipes because it became clogged with fine
sediments. Once the drywell was clogged ground absorption was no longer possible and surface
runoff occurred. The most recently constructed standpipes have abandoned the dry well design
an now have a stone and concrete base to maintain soil stability immediately around the
standpipe. Water runs off this foundation, drains onto the ground, and eventually is absorbed or
runs off.
Currently 8 out of the proposed standpipes are constructed and seven are connected to the
distribution system. Trenching for pipes to Standpipes 8-12 had been completed by the village
prior to the January 2010 implementation trip, and standpipe construction and pipe installation
are currently under way. Standpipes 13and 14 will be constructed after the secondary storage
tank is completed.
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Kikoo Water Project
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Above: a completed standpipe with drywell, below: prototype standpipe designs provided to the
Water Committee.
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Kikoo Water Project
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3.0 TRIP DESCRIPTION The following is a summary of the tasks that were accomplished during this trip. More detailed
descriptions and findings from each task are reported, in the same order, in Section 5.1 “Project
Summary”:
Existing System Walkthrough (pgs. 16-24)
A complete system walk-through was conducted, and flow rates and water quality were tested at
each major component of the system, including all tanks and standpipes. The watershed around
the catchment area was also inspected.
Secondary Tank (pgs. 24-25)
A secondary storage tank for the Kikoo system comprised the official focus of this
implementation trip. Once the location of the storage tank was confirmed by our topographic
survey and through input from the Kikoo Water Committee, the tank site was excavated, and
materials were gathered and prepared for the construction of the tank. EWB-Yale also met with
the plumber, mason, and engineering technician who were largely responsible for the
construction of the main storage tank in 2007. We ensured that they understood our designs and
were ready to handle the construction of the secondary tank in our absence. As intended, the tank
will be completed after our implementation trip is over, and we feel confident that the
community of Kikoo will do so successfully.
Community Education (pgs. 26-27)
We visited all four schools in Kikoo and presented lessons on the disease cycle, waterborne
illnesses, and the importance of hand-washing. We also met with four women's cooperatives to
discuss the importance of sanitation from the standpipe to the home, to demonstrate water
testing, and to answer any questions regarding our work. Lastly, we met with the standpipe
presidents (members of the Kikoo Water Committee) to demonstrate and practice water quality
testing using Petrifilm plates.
Percolation Tests for Latrines (pgs. 28-29)
In anticipation of a potential future sanitation project, water percolation tests were conducted at
two sites in the village, and the possibility of a latrine project was discussed with village leaders.
Inspection of Roh Village’s Water Situation (pgs. 29-33)
Previously, people in the neighboring community of Rohvitangtaa (Roh, for short) made an
unauthorized extension from our Kikoo system to a mosque construction site in Roh. In order to
understand their motives for this extension, we made an assessment of the existing water system
in Roh, starting with the catchment and going to the standpipes, of which 3 are publicly
accessible and 4 are private. GPS waypoints and approximate elevations for important system
components were obtained. We also interviewed key members of the community to ascertain any
problems with this system and any of their concerns regarding their water situation.
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Yale Student Chapter
Kikoo Water Project
© 2007 Engineers Without Borders – USA. All Rights Reserved Page 13 of 37
4.0 COMMUNITY
4.1 Description of Community The following is a summary of the various community members and groups who were central to
our trip: Kikoo Water Committee
The 27-person Water Committee, chosen from members across the entire Kikoo community, is
responsible for the overall upkeep and maintenance of the distribution system. The chairman and
secretary of the Water Committee are the main overseers of the project and are two of our key
liaisons in Kikoo. Everyone in the village is entitled to the water provided by the system, and the
water committee has already set an agreement for their rights to the water. In addition, each
standpipe has a designated President (typically the person who lives closest to the standpipe),
Treasurer, and Secretary who live in the area served by the standpipe. Thus, the committee is
able to ensure that dues for water usage and maintenance of the system are being collected fairly.
The President, Secretary, and Treasurer of each standpipe are responsible for coordinating any
repairs on their section of the distribution system.
The Water Committee is responsible for keeping the village motivated for both labor and cash
support. The monthly system dues are used to pay for maintenance and repair; only households
who live in areas currently served by standpipes are responsible for paying system dues.
The President of each standpipe is in possession of the key to the standpipe tap, and is
responsible for turning the standpipes for two hours every morning from 8-10 am so households
can collect their water for the day. The limited access to the standpipes was instituted by the
Water Committee to ensure that all standpipe users are paying their monthly dues and to prevent
water from being wasted. When the standpipes were first installed young children would often
play with the taps and leave them running continuously. As the distribution system continues to
expand, the Water Committee may look into staggering access times to different parts of the
system to improve flow rates.
Right: Members of EWB-
Yale stand with the Kikoo
Water Committee, friends in
Kikoo, our local engineering
partners and contacts, and
other members of the local
community.
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Yale Student Chapter
Kikoo Water Project
© 2007 Engineers Without Borders – USA. All Rights Reserved Page 14 of 37
Local Engineering Partners
4 former and current students from the Advanced School of Public Works in Yaounde
accompanied EWB-YSC team members on the January 2010 implementation trip. Ngalim
Adrian Suika and Benoit Ntumnyuy have remained particularly committed to the Kikoo project,
and have made multiple trips to Kikoo to assess construction and system upkeep. They have
expressed great interest in continuing to work with EWB, and possibly forming a chapter of their
own.
Schools
Since the last trip, three new schools have been formed in Kikoo - the Government School (~40
primary and nursery students near standpipe 1), the Community School (~25 primary students
near standpipe 4), and the Family Farm School (~20 secondary students near standpipe 7). The
Catholic School is still the largest with 100 primary school students and an additional 20 nursery
students; it is located across a soccer field from standpipe 8.
Women's Committees
During this trip, for the first time, we had extensive discussions with the 4 women's cooperatives
in Kikoo. These groups, which are often chapters of larger organizations, are composed of
women from neighboring households, who meet regularly to support each other and to raise
rainy-day funds.
Roh Village
The village of Roh, with a population of ~2000 divided into 5 quarters (~3000 in the greater Roh
area), neighbors Kikoo and was an important part of this trip because members of the Roh
community had tapped the Kikoo system without authorization and extended it to a standpipe in
the Sabon Quarter of Roh.
4.2 Community Relations
Kikoo Village
We continued to receive strong enthusiasm and support for our project from the community in
Kikoo, which held a welcoming ceremony and fundraising day to receive our arrival. In the
following days, many villagers contributed time and labor to the excavation of the tank site and
the preparation of materials for the secondary storage tank. Throughout the trip, we had
extensive discussions with the village Water Community regarding many issues pertaining to the
water system, including the maintenance of system components, the periodic testing of water
quality, and the resolution of interpersonal and inter-community water issues. The Water
Committee was very receptive to our concerns, and our group felt that these discussions were
very successful. In addition, we maintained close friendships with many people in Kikoo,
including village elders, active community organizers, schoolchildren, and women's groups.
Roh Village
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Yale Student Chapter
Kikoo Water Project
© 2007 Engineers Without Borders – USA. All Rights Reserved Page 15 of 37
The community of Roh neighbors Kikoo, such that the two villages have relations through kin
and through our water project (Standpipe 3 in our system technically serves a portion of Roh,
and therefore, some Roh residents serve on the Kikoo Water Committee). However, Roh is,
politically, a separate village, and it has its own water system, which was constructed about 4
years ago with the assistance of the Cameroonian NGO Strategic Humanitarian Services
(SHUMAS).
During our investigation, we discovered that this SHUMAS system had a number of technical
issues (discussed later in the report). Perhaps partly due to these flaws, villagers in the Sabon
Quarter of Roh have made an unauthorized extension from the Kikoo system to a partially
constructed mosque. As such, there was some tension between the Kikoo and Roh communities
regarding what should be done with this unintended extension. Some members of Roh expressed
their desire to continue extending this offshoot in order to supply a nearby primary school with
water from the Kikoo system. Members of Kikoo's Water Committee had mixed feelings
regarding the unauthorized extension. However, EWB-Yale advised Kikoo's Water Committee
to eliminate the extension and strictly prohibit any future unauthorized extensions, on the
grounds that technical modifications to the system, if made haphazardly, could lead to dramatic
failure in other sections of the system. Indeed, in the previous year, the Roh extension had
(before being built into a full standpipe) been left continuously flowing and had caused water
shortages in the higher parts of Kikoo (Standpipe 1). Thus, we advised Kikoo to eliminate this
and all future unauthorized extensions on technical grounds.
At the same time, we met with a delegation from Roh and expressed these concerns to them.
Despite repeated invitations to members of the Roh community in general, the delegation
consisted entirely of persons from Sabong quarter. We expressed our desire to maintain the
functionality of the Kikoo system by having it serve only the population it was intended and
designed for. Also, we discussed our technical findings regarding the Roh-SHUMAS system
(again, detailed later), illustrating that Roh's water situation could be drastically improved
through some definite modifications, provided that Roh's community made an effort to organize
itself, raise funds, and commit to an all-public system which did not give perks to big donors and
village leaders. Our group made no promise of EWB involvement in these future activities; our
intention was to preserve our Kikoo project by persuading Roh to organize and act to improve its
own water situation rather than take water from the Kikoo system. We learned that, perhaps due
to community distrust arising from the privatized standpipes in the Roh-SHUMAS system, Roh
has had an unsuccessful recent history of fundraising and community organizing. While public
interest in an improved water system is high, EWB-Yale feels that the abolishment of private
standpipes, along with a strong commitment to organize and maintain a water distribution
system, will be prerequisites to a successful community project with or without EWB. We hope
that Roh makes these organizational improvements, and we plan to follow-up with the
community in future visits.
5.0 PROJECT SUMMARY
5.1 Summary
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Kikoo Water Project
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SYSTEM WALKTHROUGH:
Catchment protection Overall, much progress has been made, because the watershed around the catchment, which was
mostly used as farmland four years ago, has been allowed to lie fallow and is now mostly
protected by a fence. The area around the catchment in particular has thick vegetation. An
interesting aspect of the fences is that a plant very similar to Century Plant (sasaikal in Lamnso)
is frequently incorporated into the structure.
Fence - However, a close inspection of the catchment boundary revealed that there is one place
where a gate is needed to keep livestock from entering the catchment area, as well as a break in
the fence where animal droppings were found along the path, indicating still some livestock
intrusion. The fence is only two-thirds of the way up the hillside that bounds the catchment
watershed, leading to some confusion in the village about whether the protected area extended all
the way up to the top of the ridge or only as far as the fence.
Latrine - The greatest threat to the catchment comes from a crude new latrine (earthen pit with
boards on top) along the path to the break tank. While it is not directly in the watershed of the
catchment, we strongly advised the Water Committee that it must be filled in and that no further
latrines should be built where they could case infiltration into the break tank or pipelines.
Farmstead - At the upper end of the valley, there is a new farmstead which belongs to someone
from Kikoo who is being supported by someone outside the community to farm on the land,
raising concerns about possible latrine or pesticide use. There is some question as to whether or
not he has the legal rights to farm the land - The land for the entire catchment belongs to one of
the village elders, who generously donated it for the water project - and the Water Committee is
pursuing action against him through the Kumbo Urban Council. Just prior to our departure, we
learned that the Water Committee was discussing a resolution to this situation that would allow
the land to be used as an orchard, rather than a farm, provided that no pesticides or fertilizers
would be used and no eucalyptus would be planted.
Eucalyptus trees - A second land use issue exists on the hillside opposite the break tank, where
someone build a fence around a portion of land they were loaning or renting from the landlord,
and sold it to someone from the greater Kumbo region. The new owner has already planted
eucalyptus saplings on the land. Polycarp voiced is specifically concerned that if the trees are
allowed to continue to grow, the deep taproot systems suck up a lot of water. There are streams
in the bottom of the valley which Kikoo might want to draw on to increase their water catchment
as the population grows, which also might be compromised by the eucalyptus. Other concerns
are the erosion and damage to the surrounding area that will result when the trees are harvested
for timber, and the fact that with a shallow spring system with large groundwater inflow, the
taproots systems could actually affect the locations of the springs in the bottom of the valley.
Polycarp reported that the Water Committee has begun looking into this matter but not resolved
it.
Catchment
Tank lid was securely locked, and as of December 31, there were about 8 inches of backpressure
on the line (i.e., top of weir is about 8 inches above the top of inflow pipe). Surprisingly, the
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Kikoo Water Project
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water level varied significantly over the course of our trip; on subsequent visits to the catchment
the water was barely overflowing the weir. We believe this is due to variability in the spring
supply and not leakage or seepage around the catchment.
According to Wilfred, the tank was last cleaned in November. There is some sediment in the
bottom of the grey inlet pipe and the bottom of the tank, but apparently this is mainly due to
termites building tunnels on the sides of the tank. There are termites living in the surrounding
soil have build small cement-walled tunnels passing across the inside of the tank, which either
disintegrate or are knocked into the tank during cleaning.
Feedback
There is slight seepage along the weir, and we recommended to Eugene that this be patched with
concrete plug cement.
“First overflow”
Observations
There are four pipes coming from the catchment,
two of which end in a natural depression roughly 30
meters below the catchment. The water formed a
pool about 2 meters in surface area (December 31),
was not stagnant, and drained to the streambed that
it would have collected in without the catchment.
In future, it could be possible to increase system
capacity by bringing all four pipes down to break
tank, although new pipe might also have to be laid
from the break to main tank to take maximum
advantage of the increased flow. Reportedly, in
rainy season, the pool is not that much larger, but
the water flows more quickly. On the later visit
when the catchment level was found to be lower,
this depression had almost no water in it.
Right: 2 overflow pipes from the catchment empty
into this pool, which runs gradually downhill and
into the spring‟s natural basin
Break tank
Observations
Tank cover is securely bolted. As of December 31st, the overflow at this point was barely active.
Wilfred reports the drain was last cleaned out in August. There was more sediment here
(collecting on floor of tank) than in the main tank or low point tank, perhaps due to the fact that
the water comes out of the pipe, into the concrete box, and passes back into a second pipe,
making this effectively a mini-sedimentation basin. As at the unofficial “first overflow”, the
overflow here goes into the drainage basin that the water would be flowing into if there was no
catchment at the spring.
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Low point
Observations
The interior of tank is entirely dry. Wilfred reports that the valve was last opened in August.
When we opened the valve, there was a small plug of sediment that cleared quickly. It is not
clear whether this sediment was deposited by water in the system, or if it was simply dirt that had
been deposited onto the exposed sediment-clearing pipe. This tank, like all of the other small
tanks, has a concrete lid secured with rebar loops and a metal bar tightened into sockets on either
side with a wrench.
Feedback
Between the low point tank and the break tank, we noticed a new latrine, which is essentially a
pit in the ground covered with wooden boards. It is open to rain, and one of our collaborators
noted that it would very likely overflow during the rainy season, which could release fecal
contaminants and also cause the boards to rot. The latrine is also in an area that drains toward the
break tank and pipeline, so we brought this potential health risk to the attention of the Water
Committee.
Storage Tank
Observations
On December 31, 2009, the main tank was full, the overflow was gushing, and the water
appeared clear with very little sediment, no staining and no smell. According to Wilfred, the tank
was last cleaned last January. The tank has two curved aeration pipes on top, which are over five
feet tall, which allow air to enter in order to maintain atmospheric pressure, but do not allow dust
to fall in.
The valve box is dry but there is some wetness and white mineral buildup on the wall directly
under and closest to the tank. There is an extra piece of pipe in valve box, which is used when
the tank is being drained for cleaning. However, the inside of the valve box is not clean, so water
draining out of the tank through the box would be potentially contaminated.
So, we inquired if it would be possible to connect the inflow pipe to the outflow pipe (toward the
standpipes), in which case it would be possible to drain the tank water into the system, instead of
it all running into the overflow. At present, the Water Committee tells villagers when the tank
will be cleaned so that they will have time to store water for the duration of the cleaning.
The overflow from the storage tank can move along two possible paths: one through a forested
area that drains back to a streambed, and another towards the village and into villagers‟ gardens.
Lastly, a new fence around the storage tank is currently under construction. This fence will
protect the tank from intrusion and damage by livestock or playing children.
Standpipes
General comments:
Locations- Seven standpipes (1-7) were operational as of this trip; SP 8 was constructed but not
yet connected to the pipeline. As of January 23, four additional standpipes had been cast and
were the process of being completed with faucets and flagstones.
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Overflow- In general, overflow streams are channeled through village, and are used to make
bricks, collect water for washing clothes, collect water for livestock etc. This practice of
channeling is already used in the village with water from other sources such as the Kibunjum and
Bambui streams, so there is a fairly extensive network of shallow channels (~4-8 inches) along
the edges of roads to divert this non-potable water to different areas depending on need and
availability. When the streams cross roads in the village, they erode a deeper channels; Adrian
emphasized that for this reason they try to ensure that the overflow streams are never channeled
across pipe that has been laid underground.
Usage – Mainly children (especially girls) are seen collecting and carrying water, this was one of
the reasons we felt it was important to meet directly with the different Women‟s Committees on
this trip. Polycarp indicated that most standpipes are open 7-9 am and 5-7 pm, however this is at
the discretion of the standpipe presidents and not all choose to lock their standpipes in the middle
of the day. However, the Water Committee has seen that standpipes that are locked during the
middle of the day tend to need repairs less frequently, so they are advising all standpipe
presidents to do this.
Funds – Although the original plan for the water system agreed upon by the Water Committee,
the Social Welfare Diocese, and EWB included monthly maintenance and upkeep payments by
all families using the public standpipes (e.g. 200 cfas /household /month), monthly payments
were currently not being collected; funds are collected for standpipe maintenance door-to-to on
an as-needed basis. Unfortunately, in at least the example of SP 2, it seems that the lack of a pool
of available funds to immediately purchase repair supplies is slowing down the process of
repairing the system.
Rubber hoses – All of the rubber hoses and sticks that were attached to faucets last year to reduce
the spray of water have been removed, and it was gratifying to see that testing showed that the
water quality at the affected standpipes has subsequently improved.
Children – There were sometimes a large number of children playing near standpipes and the
associated drywells. Although this many have been due in part to the presence of intriguing
foreign visitors, residents around SP 7 reported that many children stopped to play at the
standpipe on the way to and from school. This particular issue will be addressed for most
students when SP 8 (by the Catholic school) becomes operational in the coming weeks, but in
general it is necessary to address the fact that very young children tend to drink out of the
standpipe by putting their mouths directly on it. This is an educational issue we discussed with
Dioudenne (Catholic school headmaster) and the Women‟s Committees.
Other sources of contamination –Many sheep and goats graze freely around the village, and in
some areas, particularly SP 6, there was animal feces near the standpipe. Yibeh (one of the
women‟s committees) also mentioned that sometimes people bring dishes to the standpipe to
wash, and that this should be discouraged.
Standpipe 1
Water quality: Clean; no fecal coliform detected
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Flow rate: 0.9 L/s Photo:
Notes: -A lot of spray from faucet -Small amount of rubber tied around the back part of the faucet (water does not flow through it).
Overflow Notes: -Drywell is sloped back towards faucet so water does not drain optimally
Standpipe 2
Water quality: Clean; no fecal coliform detected Flow rate: 1.1 L/s
Photos:
Notes: -On several occasions looked like it was leaking but actually can be shut off all the way. The key used to control the faucet is difficult to turn off (esp. for small children). -According to family living next door to the standpipe, it has been ‘leaking’ for three months, most likely due to worn-out gasket in the turning mechanism for the handle/key which costs 500 cfas to replace. Rubber is tied on the back of the faucet (not in contact with water) to reduce the leak. Leak rate is apparently same in the rainy season. At the time of our visit with Polycarp, this had not yet been reported to the Water Committee.
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-A lot of faucet spray
Standpipe 3
Water quality: Clean; no fecal coliform detected Flow rate: Not available; SP locked on collection date
Photos:
Notes: - No fence yet - Leaking on January 4, but Polycarp had already bought the replacement faucet which was subsequently installed -Leak water was being collected, but not to be used for drinking
Standpipe 4
Water quality: Clean; no fecal coliform detected Flow rate: 1.4 L/s Photos:
Notes: -No leaking! - Faucet is locked and covered with a can that is easy to remove without opening the lock.
Overflow
Notes: -Broken pipe leading from drywell directs water towards overflow -Drywell is apparently still functional
Standpipe 5
Water quality: Clean; no fecal coliform detected
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Flow rate: 0.7 L/s (measured with 1 L bottle; not very precise) Photos:
Notes: -Was open (unlocked) when we visited it -New fence is being built by homeowner next to standpipe -One of the abandoned buildings along the path to sp 5 is the old Catholic church.
Overflow
Notes: -No drywell or direction of overflow, it drains down the overgrown slope immediately in front of it towards a farm.
Standpipe 6
Water quality: Clean; no fecal coliform detected Flow rates: 0.2 L/s Photos:
Notes: -Was open (unlocked) on one visit -On our first visit to the standpipe, there were a lot of goat droppings nearby. After discussion with households nearby about sharing responsibility for cleaning the SP area, the droppings were cleaned up and the area stayed clear for all subsequent visits -Leaking on the third day it was visited
Overflow
Notes: -Drains down across road (in a channel) to Bambui stream.
Standpipe 7
Water quality: Clean; no fecal coliform detected Flow rates: 2.0 L/s
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Photos:
Notes: -New fence. -Stump placed beneath sp allows 20 L containers to sit with tap totally inside to prevent spray, we have emphasized it is important for nothing to touch the brass tap itself. -Feedback from nearby residents that kids play here in the afternoon on the way home from school -They don't cover the tap, but take off the T-key in the middle of the day
Future standpipes:
SP 8 – Standpipe with two faucets (one for school, one for local residents) already installed,
waiting to be connected to water supply
SP 14 - Audilus is the president of sp 14. Wilfred noted that last year Audilus and Didimous
were the only people from this area who attended the Water Committee meetings, now that the
prospect of water is much closer due to the secondary tank many people in the area have come
forward to contribute their labor to the project.
- The Presbyterian Church down the street from the secondary tank is 5 years old, settlement
nearby will continue and they will definitely be building a school, so it would be good if a
standpipe could be built along the road here. There are at least 125 people living in this area (not
including demand for water at church).
Pipeline
- 1.6 kilometers of trench have been dug from SP7, all the way up to the site of the new
secondary tank and toward the future sites of SP11 and SP12. We observed that in some areas,
the trench was as not as deep as is recommended to protect the pipe from UV rays and the
possibility traffic or fire passing over it, so we emphasized the importance of digging trenches
down a full 60 cm.
-More precise survey data collected in January 2009 using the Total Station, rather than GPS as
in the original assessment trip, showed that the system‟s lowest point (just prior to SP4 and 5)
may actually be 10 m lower than we previously believed. Unfortunately, during this trip, we
were not able to check if pipe of adequate pressure rating was installed in at this location. To
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date, water appears to be flowing well to SP4-7. We will advise the community to frequently
check the low point for any leakage indicating pipe failure, and to upgrade the pipe if necessary.
- The original system design called for valves to be installed where each standpipe branches off
the main line, and also in between standpipes, especially in critical low-lying areas. However, to
date, no such sectionalizing valves have been installed in the system. We recommended that in
order to maximize the effectiveness of the second tank, it is crucial that valves are installed along
the main pipeline between SP 7 and 8, between 9 and 10, and between 9 and 11. These valves
will allow the community to isolate a leakage if a pipeline break occurs, and also potentially use
the secondary tank to temporarily “back-feed” water to most of the village, in the event that a
break occurs early on in the system, separating the village from the main tank.
Secondary Storage Tank
Confirmed Tank Elevation In the first two days of work in Kikoo, a team, led by Jeremy Smith, conducted a land survey to
confirm the proposed secondary tank elevation relative to the primary tank. The elevation of this
secondary tank determines whether it can be supplied by water from the main tank and which
standpipes it can service, so we decided that a careful topographical survey between the two
tanks was a worthy use of our time. A Topcon total station was used for the survey, which
revealed the proposed secondary tank site to be 12 m (1998m – 1976 m) below the primary
tank. This is a lower elevation than the one recorded on the January 2009 trip, which the designs
for the storage tank were based on. The tank design was not changed by this new finding; at the
new, lower elevation, the secondary storage tank will simply fill up at a faster rate, and the float
valve should still be able to withstand the pressure of the system when the tank has reached
capacity.
Tank Placement by Community A meeting was held with the water committee to pick a site for the secondary tank. At this
meeting it was explained that the reason for building a secondary tank was because the current
gravity-fed system would only provide a slow flow of water to the upper, eastern portion of
Kikoo. For this reason, the secondary storage tank location could not exceed a certain elevation,
or else it would not fill sufficiently to provide water to that portion of the community. With
these considerations, the Water Committee chose a spot that a landowner had already agreed to
donate for the purpose of housing a water storage tank. This site was in an open field with
relatively flat grade. The only foreseeable issues regarding this site were its proximity to a road
which may be expanded in the future, and an avocado tree. The final site was placed in the field
13 m from the road, leaving an additional 10 m to allow for future road expansion. The avocado
tree was removed, and the site was also placed sufficiently distant from the avocado tree to avoid
unstable soil from root decay.
Tank Site Preparation Tank site preparation began on the Monday of the trip after the New Year holidays came to a
close (January 4). First, an avocado tree had to be removed and excavated from the site; the
owner of the property agreed to the tree‟s removal for the sake of the community‟s well-
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being. Excavation of the land was accomplished using pick axes and shovels by EWB-Yale and
community members. The area being excavated was marked out using with a measuring tape
and sticks in the ground. EWB-Yale members stayed on site throughout the excavation to ensure
that the pit was dug to appropriate depths (1.25 m in the upper bank, 0.5m in the lower
bank). Initially the tank was excavated to a level base. Once this initial excavation was
complete, a cross-slope of 10 cm was added and verified using the total station. The cross-slope
will facilitate tank drainage and cleaning.
Left: 1. EWB-Yale and Kikoo community
members excavate the tank site. 2.
Afterwards, a 10 cm grade is added to the
tank floor. 3. The completely excavated tank
site.
Plans for Completion No further tank construction was completed
in the duration of our trip because not all
building materials were prepared. Sand and
rock arrived at the site during excavation;
however, the pipes from the system did not
yet reach the tank site to provide water for
sand washing or mixing concrete. Also the
gravel from the large rocks needed to be
chipped and the rebar needed to be delivered.
A meeting with the local Diocese‟s
engineering technician, the mason and the
plumber was held before we left to review
the tank plans. This meeting was intended to
answer any questions about how the tank
was to be implemented in our
absence. Because of the poor water access in
that section of Kikoo, the pipeline from the
existing system will be extended up to the
construction site in the upcoming
weeks. Once water has reached the site and
the other required materials have been
delivered the tank construction will
commence. A drainage trench was dug from
the excavated tank site to allow water to
drain in case of a rainstorm; however, the
tank is intended to be finished before the
rainy season begins.
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Community Education
We visited the four schools in Kikoo: the Catholic school (years 1-6, 96 primary students and 20
nursery students), the government school (nursery and primary school), the Family Farm school
(secondary school, run by the community and the Social Welfare Diocese), and the community
school (primary school) to teach lessons on sanitation, the disease cycle, and the importance of
washing hands.
Right: 5th
and 6th
graders show off
the posters they made after our talks
on sanitation and good hygiene.
They are also holding letters from a
sister school in New Haven, CT, and
some of their reply letters to their
new American pen-pals.
We also visited the four women‟s groups of Kikoo: Bongsisi, Yibeh, and two Salamant groups to
discuss the role of women in keeping water clean from the standpipe to the house. Some of the
women appeared to already understand the importance of standpipe and household
sanitation. They expressed concerns about the amount of time required to maintain cleanliness,
saying that working longer hours on the farm is sometimes given preference to washing dishes at
home. Additionally, women in areas of the village that did not yet have standpipes wanted to
know what they could do to ensure that their water is clean until the standpipe water reaches
their part of the village. We advised them to boil non-standpipe water for 10 minutes to ensure
clean water.
Members of Bongsisi expressed surprise that people from the U.S. would come to Kikoo not
only to provide free water but also to provide education to women; they asked about our motives
for doing this project and education for free. Our reply was three-fold:
The system isn't „free‟; the community has contributed a lot in both money and
labor. The problem of clean water was initially identified by the community; they are
also the ones who started the project - it would not have been possible without them.
Since women are the key to making sure that clean water actually gets into the house,
without educating women, all the work of system construction would be wasted.
Since we are engineering students interested in water, we are learning a lot from our
involvement with this community – so the benefit moves both ways.
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We met with the Kikoo Water Committee at the end of our trip to present the findings from our
trip and bring the problems that we noticed to the attention of the committee. At least 24 people
were present at the meeting.
Below: A meeting between EWB-Yale members and the Kikoo Water Committee
Water Committee members actively
participated in the meeting, asking questions
and providing feedback to our
suggestions. Regarding the catchment, the
Water Committee asked why they were not
supposed to farm within the catchment‟s
watershed as long as it was outside of the
area demarcated by the fence (the fence only
partially surrounded the watershed). We
discussed the effect of fertilizer and pesticide
runoff on the catchment water quality
anywhere within the catchment‟s watershed.
A concern was raised about the Water Committee‟s authority to deal with standpipes that are not
in compliance with accepted recommendations (cleanliness, updates, etc.). We reminded them
that the Water Committee has the authority to turn off standpipes.
The Water Committee also stressed the importance of clearly communicating to each standpipe
president his/her obligations and the consequences of not meeting his/her
obligations. Furthermore, the president of KICUDA (Kikoo Community Development
Association) emphasized the distinction between individual actions and actions taken on behalf
of the Water Committee, saying that personal relationships should not be affected by committee
decisions.
EWB-YSC suggested that permanent keys with tin can locks might be a better method of
securing the standpipes rather than removing the standpipe faucet knob and using that as a key
because the latter method puts additional wear and tear on the knob, potentially causing it to
need to be replaced faster in the future. The Water Committee responded by saying that tin can
locks made it easier for children to play in the water, so they have decided that although the
removable keys may wear down more quickly, they are still better. EWB-YSC affirmed the
Water Committee‟s decision and thanked them for trouble-shooting.
Regarding the Roh extension, a Water Committee member was concerned that the people of Roh
had already contributed to the Kikoo system and under EWB-YSC‟s recommendations, they
would not be getting any water. EWB-YSC responded by noting that certain neighborhoods in
Kikoo have donated similar amounts of money despite not yet having received water, and, unlike
the Roh village members, they have entered into an agreement with EWB-YSC. Furthermore,
EWB-YSC emphasized that long-term delivery of water to the areas of Kikoo village with higher
elevations would be compromised by the unauthorized Roh extension.
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Percolation Tests for Latrines
Based on demonstrated community interest, we investigated the potential for a latrine project in
the village of Kikoo. Currently, the latrines in the village are somewhat problematic because they
were built haphazardly: some are too shallow, and overflow during the rainy seasons. Others are
simply uncovered pits with overlying wooden planks; these can be unsanitary or dangerous to
use. Over the summer of 2009, Adrian and Benoit, two of the Cameroonian engineers that we
work with, surveyed the village and learned of widespread community interest in receiving
technical feedback for constructing a safer, cleaner latrine. While we were in the village, we
spoke with key village members that also expressed interest.
To investigate this possibility, we conducted percolation
tests in two central locations in the village. These locations
were chosen because by being in central community
locations the latrines would get public attention and then
might be replicated in other parts of Kikoo.
One conducted behind the main Catholic school (P-1)
demonstrated a percolation rate of 10 minutes/inch. A
second test conducted in a location behind the Catholic
church (P-2) had a rate of 20 minutes/inch. Percolation test
P-2 behind the church penetrated a thin stratum of white,
chalky soil roughly 18 inches below grade that was not
encountered in test P-1 behind the school. Aside from this,
the soil profile consisted of 10 to 12 inches of brown, loamy
topsoil over red and silty clay with traces of fine sand and
fine gravel.
Above: Schoolchildren stand around a percolation test pit (approximately 0.5x0.5x1.0 m deep)
dug behind the Catholic church
- Why are percolation tests necessary for latrine construction?
Percolation test results may be used to estimate the extent of infiltration area needed if
one is designing a waste disposal system that will segregate the liquid waste from the
solid waste, and leach the liquid waste into the soil. For a conventional pit-type-toilet, a
percolation rate is not crucial; but if we want to consider alternate types such as
composting latrines, it could be useful to know the percolation rate of the soil.
- What was the exact procedure for the tests?
Each test pole was dug roughly 30 inches deep and 8 inches across. The holes were filled
with water to a depth of roughly 12 inches, and left to soak for one hour. Water was
added periodically to the holes during this time to ensure that they were properly
saturated. After one hour, the water level was topped up to roughly 12 inches depth, and
the depth to the water surface was measured from a reference point every five minutes for
one hour, or until the holes were empty of water. The results are reported as number of
minutes for the water level to drop one inch.
- How do the results compare, what do they mean?
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The results indicate that there is some variability in percolation rate for one location to
another, but both values are within a range that could prove workable for a system that
assumes infiltration of liquid wastes into the native soils. The variability is likely due to
natural variations in soils from one location to another, the inherent inaccuracies of the
test method, or variations in the soil profile below the depth of the test. For example, if
the native bedrock happened to be closer to the bottom of test P-2 than test P-1, that could
have affected the percolation rate enough to result in the variation between the two tests.
For our purposes, we could design on the basis of the more conservative result, and
perform validation tests at actual system locations immediately prior to starting
construction.
Inspection of Roh Village’s Water Situation
Community of Roh Roh has a population of roughly 3000 people, though we are yet to take an independent survey.
However, unlike the neighboring village of Kikoo, it is more densely clustered. According to
Eugene, the principal in-charge of the Roh Health Centre, the approximate radius of the village is
1.5 km, centered at the Health Centre.
History of Existing System
According to Eugene (Adrian‟s cousin) at the Roh Health Center, in the year 2000 plans for a
joint Kikoo-Roh water system with three spring sources were drawn up by Tala J. from the
Kumbo Urban Development Council; however, these plans were never implemented.
The current Kikoo and Roh systems are fed by two of the three springs identified in this design;
the third (which is indicated to have the lowest flow rate) has not been explored by our chapter.
It is worth noting that according to this plan, the flow rate of the Roh spring is almost as high as
the spring for the Kikoo system (0.8 L/s vs. 1.0 L/s).
Below: Map of a joint Kikoo-Roh water system proposed in 2000 (never implemented)
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In 2006, overseas donors provided funding for a project to supply water to the Roh Health Center
exclusively, implemented through the Cameroonian NGO SHUMAS (Strategic Humanitarian
Service, based in Bamenda). Apparently, due to the extremely high pressure in the system
resulting from poor design, an additional two standpipes were constructed (at the market and the
mosque); the combination of high pressures and low-quality faucets means that all three
standpipes run continuously (if the pipes are not broken) and have become de facto public
standpipes. At the time of the SHUMAS implementation, four individuals who made major
contributions to the project (~25,000 cfas) received private standpipes in their homes. For
example, Eugene at the Health Center owns one of these private standpipes. These private
standpipes do not run continuously.
Left: GPS waypoints collected
during this trip. In-set magnifies
the way points collected in Roh
during the walk from the Roh
catchment down to the center of
the village, following the pipeline
most of the way. (Yellow points
are in Kikoo, purple points are in
Roh, red points are for emphasis of
orienting points.)
Roh Catchment
Location-
The catchment is 1.6 km away
from the health center. There is not
significant foliage around the
catchment except at a distance of 7
m from the actual catchment.
There are ploughed fields,
indicating cultivated farms, both
just above the elevation of the
catchment as well as around it.
Design-
Similar to the structure at the
Kikoo catchment, the concrete Roh
catchment captures water from an
artesian well. An underground
concrete wall was built at the site of the spring, in order to channel the water behind it. The
catchment tank is 2.5 m deep. On the west side, there is an inlet of water through a pipe 1 m
above the floor. On the east side there is a pipe outlet near the floor of the tank. There are two
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overflow pipes, one 0.05 m above the floor, and the other at the depth of 0.5 m from the top.
Pipeline to the health center-
We followed the pipeline from the center of the village to the health center. The pipe itself runs
under dirt paths, many fields, and is, at some stream crossing, exposed. In these places, the
pipeline may run the risk of breakage due to physical wear.
Problems with Roh system Catchment protection
As mentioned above, the presence of farms (and the lack of overgrowth and fencing) around the
catchment poses a risk of fertilizers and animal excreta contaminating the water of the catchment.
Property rights may also be a potential obstacle against improving this situation.
Overflow
At a distance of 19.5m, the overflow pipe comes above the ground and opens up, leading to a
free flow of water downhill. However, the overflow that we observed was minor. We also
observed that this overflow increased in volume as it went downstream. One of the proposed
reasons could be the presence of further underground streams, or other sources of water from the
village join the overflow.
Back-Pressure Against Spring
As mentioned in the tank description, the upper overflow pipe is significantly higher than the
catchment water level in the rainy season, but it was reported that the water level rises well
above the lower overflow pipe. Thus, the upper overflow pipe does not result in actual overflow.
This prolonged build-up of pressure against the input pipe and the spring itself may eventually
render the Roh system ineffective.
Pipeline
Because of the extremely high pressure on the standpipes, all of them are left open and there is
continuous flow of water. This not only causes a waste of water, but does not effectively address
the problem of pipeline-rupture. According to health center contacts, intermittent repairs must be
made to the pipe at various points. The lack of a storage tank to modulate flow, therefore, is one
of the largest shortcomings of the Roh system. GPS reading indicate that the elevation change in
the system is roughly 125 meters, or 25 meters above the pressure rating of the commonly
available PVC pipe (NP-10 rating, or 10 atmospheres pressure). This is consistent with the
reports of regular pipe and faucet failures.
Standpipes
There are seven standpipes in the system, four of which are privatized. In addition to the fact that
the three public standpipes must be left continuously running, village members complain of
inconsistent water flow, which we believed may be caused by airlocks or sediment buildup in
relative maxima and minima along the pipeline, respectively.
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Left: The mosque standpipe of
the Roh-SHUMAS system, a
public standpipe which is left
continuously running. During the
construction of the mosque, its
flow was extremely inconsistent,
causing locals to make an
unauthorized extension off the
Kikoo system to provide water to
the mosque for construction and
prayer services (detailed in
Politics section below).
Politics
Roh Village presents several political challenges which must be overcome if community
development work will proceed as smoothly as it has in Kikoo. Firstly, there are four privatized
standpipes in Roh, which were obtained through by high individual donations towards
construction costs. In fact, the two public standpipes aside from the one at the health center were
made public only because of they are unable to be shut off. Also, Roh does not have a
transparent village committee, which exists in Kikoo. For these reasons, villagers are skeptical
that any money that they contribute to a Roh system would be used to benefit the community as a
whole. This distrust and lack of transparency represents a significant hurdle to productive
community work.
Politics Continued: Sabong Quarter
The Sabong Quarter is the quarter of Roh that is nearest to Kikoo. Last year, the villagers of
Sabong made an unauthorized extension off of standpipe 3 of the Kikoo system, effectively
extending the Kikoo system further into Roh than was intended (SP 3 is in actually in Roh, but
this was intended from the beginning of the project). Reportedly, the extension was installed to
facilitate construction of a mosque, but in the period since the 2009 assessment trip the pipeline
and standpipe have been improved and now appear quite permanent. The unauthorized
standpipe in the Sabong Quarter represents a tricky issue because it sets a bad precedent for
future modifications to the Kikoo system which may be unauthorized and technically unsound.
Additionally, the people of the Sabong Quarter, while receiving water from Kikoo, would have
no incentive to contribute to any improvements in the Roh system. During the trip, we advised
the Kikoo Water Committee to eliminate the unauthorized extension and maintain the integrity
of the Kikoo system. However, the presence of familial and political ties between Roh and Kikoo
further complicates the situation, and EWB-Yale must hope that the Kikoo Water Committee and
the Roh community heed our advice on technical grounds, not political ones.
Document 526 - Post Implementation Report
Yale Student Chapter
Kikoo Water Project
© 2007 Engineers Without Borders – USA. All Rights Reserved Page 33 of 37
Left: The standpipe at the end of an unauthorized
extension of the Kikoo system to the mosque in
Roh‟s Sabon Quarter
5.2 Difference Between Planned and Actual Implementation
We originally designed the secondary tank with a general area in mind. Upon arriving in the
village, we met with the water committee to discuss the tank site. They selected a location that
was slightly lower in elevation in order to avoid problems with property rights (please see map
for location). As we started to excavate the site, we were informed that the class of an adjacent
would be changing and the road could be widened, so we moved the tank further (an additional
10 m) from the road to avoid any problems.
We managed to excavate the entire tank site, but we were not able to actually begin building the
tank. Work on the tank was slower than expected because we were in the village for two major
days of celebration. The first was the annual donation ceremony, and the second was New Year‟s
Day. No work was done on these days, which put us behind schedule. Also, construction
materials were not able to be assembled until later in our trip, when gravel-chipping for concrete
was begun. Lastly, pipeline had not yet been extended to the tank site, and we thus did not have a
convenient source of water to make concrete. Despite these obstacles, we were able to meet with
Damian and the other crucial members of the construction team (plumbers, masons, and others
who were involved in building the main tank in 2007) to discuss the plans in detail, and we are
confident that they will be able to build the tank to our designs. The villagers will also be able to
build SP14, in contrast to what we had expected, due to the new, more accurate survey data that
was collected during this trip. Our more accurate data puts the site for SP14 at an elevation of
1969.8 m, which is a lower elevation than was originally planned; this will allow the inclusion of
SP14 into the final completed system, whereas we had thought earlier that it might have to be
omitted.
Document 526 - Post Implementation Report
Yale Student Chapter
Kikoo Water Project
© 2007 Engineers Without Borders – USA. All Rights Reserved Page 34 of 37
5.3 Secondary Tank Design Drawings To be submitted separately
6.0 PHOTO DOCUMENTATION Please see photographs provided throughout Program Background (2.0) and Project
Summary (5.0)
7.0 MONITORING AND EVALUATION
A baseline health survey had been carried out by nursing students at the Banso Baptist Hospital
(BBH) Nursing School before the start of the Kikoo water project, approximately five years
ago. There was some indication via personal testimony of village members that the incidence of
waterborne disease is now lower in Kikoo as compared with before the water system was put in
place. However, a formal follow-up health survey will be necessary to understand the impact on
community health made by the water system.
During this trip, contact was made with Margaret Ngwayu (Contact Info. Deleted for On-line Use) at
the BBH nursing school, Derry Stella (BBH laboratory personnel, (Contact Info. Deleted for On-line
Use)), Donald Buri (BBH laboratory personnel, (Contact Info. Deleted for On-line Use)), and Peter
Kakute (Life Abundant Pastoral Center Administrator (Contact Info. Deleted for On-line Use))) to
begin planning a post-system completion follow-up health survey for Kikoo. Peter Kakute
coordinates the health surveys, and he said that January or February 2011 would be a good time
for a follow-up survey.
8.0 LESSONS LEARNED
During this trip, the importance of effective communication with the villagers became clear. The
local language, Lamnso, is spoken throughout the village, and English is rare, which could have
potentially created major communication barriers. However, we worked closely with the team
members that were from the area to improve dialogue and interaction with the villagers. During
meetings with the Kikoo Water Committee, standpipe presidents, and the women‟s groups,
translators were always present. We also made an effort to learn common Lamnso phrases
ourselves, and we bought an English-Lamnso reference book. The people of Kikoo were thrilled
even with small phrases, and even if we ended up needing a translator anyway, this enabled a
more substantial relationship with the average villager.
Additionally, this trip filled in a lot of social gaps left by trips in the past that focused on
technical aspects of the project. Talking to the women's committees was important to ensure the
cleanliness of the water because they are responsible for getting water from the standpipes and
keeping it in the homes. Speaking with them also allowed them to feel involved with the system
Document 526 - Post Implementation Report
Yale Student Chapter
Kikoo Water Project
© 2007 Engineers Without Borders – USA. All Rights Reserved Page 35 of 37
and to address their own questions or problems. Although the water committee overlooked minor
issues when speaking with us, the women informed us of several potential issues that we could
then address with the water committee.
When meeting with the water committee of Kikoo and representatives of Roh, we had to
emphasize that we were not a source of unlimited money and materials, and that we too had to
work very hard in order to raise money to fund the project. We will have to make this clear from
the very beginning of future projects: what our commitment is, technically, socially, and
financially, so that when unauthorized changes in the system are made, we have that hard line
reasoning to fall back on. Additionally, it will be necessary and beneficial to shut down
unauthorized taps immediately, rather than waiting a year and hoping the water committee
determines how to deal with it. Empowering the water committee and clarifying how much
authority they have is also something to make clear earlier in the project, because they were
faltering a bit due to perceived lack of control.
Our relationship and partnership with our Cameroonian engineering counterparts has proved
both ideal and entirely invaluable. Working with students who get a different type of engineering
education than we do, as well as who can help us translate lingually and culturally, has been an
incredibly educational and interesting experience. Our relationship has been mutually beneficial,
with no problems of one group being more involved or more in charge than the other, and we
become a reasonably integrated group upon arrival in Kikoo.
Finally, in terms of technical adjustments that could be made for the project, we heard from the
Kikoo Water Committee that water quality testing was extremely inconvenient because it
requires samples to be incubated overnight at the laboratory of Banso Baptist Hospital, a half-
hour taxi cab ride away. As such, we attempted to find more readily available incubation
methods, which might encourage more frequent testing of water cleanliness. We discovered that
incubating Petrifilm samples for 48 hours in a fairly warm place (for example, inside of a brick
container or shelf during the daytime) produced comparable results with incubation at the
laboratory. However, over-heating the films (such as by placing them on a tin roof during the
daytime) ruined the samples and produced no usable results. In the future, we may search for
alternative water quality testing methods that do not require incubation and/or produce fairly
immediate results, with the hope that instructing the Water Committee in these methods will
enable and encourage them to easily monitor the quality of the water flowing to Kikoo.
9.0 NEXT PHASE OF THE PROGRAM After our implementation trip, construction of the secondary storage tank will proceed, as
intended, in our absence. We estimate that the Kikoo community, with assistance from local
masons and engineers, will be able to complete this tank within 2-3 months (by late March
2010). With the secondary storage tank in place, the final standpipes and the pipelines leading to
them can be completed by the Kikoo community without minimal further technical assistance
from EWB-Yale. Therefore, the Kikoo water distribution system should be completed within the
year (by December 2010). Through our partners in Cameroon, we will remain in frequent contact
with Kikoo in the event that they need guidance or assistance during this time.
Document 526 - Post Implementation Report
Yale Student Chapter
Kikoo Water Project
© 2007 Engineers Without Borders – USA. All Rights Reserved Page 36 of 37
After the completion of the Kikoo project, EWB-Yale plans to undertake a final wrap-up trip in
order to assess the condition of the finished distribution system and ensure that the community
understands how to maintain it. Additionally, in conjunction with nursing students at the Banso
Baptist Hospital in Kumbo, who conducted a health survey in Kikoo in 2006, we plan to conduct
a follow-up survey in order to assess if the construction of a water system has had any immediate
effects on the health of the Kikoo community. We have established contacts at Banso Baptist
Hospital, and we will coordinate with them to plan this survey during the coming year.
Finally, though the water project in Kikoo is coming to a close, EWB-Yale has established many
friendships in Kikoo and in Cameroon, and we are interested in potentially continuing our
relationship with this community through future projects. As such, we plan to continue assessing
the possibility of several aforementioned projects. First, we will examine the information
obtained from percolation tests conducted at test sites near the village center. We will continue to
communicate with the Kikoo community, and if their interest remains high, we would be ready
to apply for a project to construct model latrines in Kikoo by 2011. Secondly, the community in
Roh has expressed great interest in improving the system which currently provides them with
water. However, EWB-Yale has significant concerns regarding Roh‟s commitment to
organizing, fundraising for, and maintaining a community-owned project, especially given the
existence of privately-owned standpipes in their current system. Without promising future
involvement, we have already expressed these concerns to members of the Roh community.
During our next trip, we hope to see that Roh has taken actions toward changing these problems
and establishing a water committee that represents the entire village. If this is the case, and if
Roh is still interested, EWB-Yale may be able to consider a collaborative project with the Roh
community at that time, and a detailed survey effort to more fully evaluate the existing system
and its shortcomings could be included in a future trip. In any event, EWB-Yale expects to close
out the current Kikoo water project in approximately one year.
10.0 MENTOR ASSESSMENT The trip was reasonably productive and very informative. Progress on the secondary tank
construction was limited by days lost to holidays, illness and lack of materials. However, the
team is comfortable leaving completion of the tank in the hands of the local community with
assistance from a local engineering technician, Damien Kongso. In addition, we can rely upon
our Cameroonian engineering contacts Tata Benoit Ntumyuy and Ngalim Adrian Suika to review
progress. This team proved very effective in completing the primary storage tank in 2007.
A significant amount of effort was put into community education on good sanitation, the disease
cycle and proper water handling through the local schools and women's groups. These groups
were very attentive and appreciative of the sessions. The outreach to women's groups was given
a high priority for this trip since the women have the primary responsibility for collecting,
storing and using water in the households.
Extensive water testing indicated that the source continues to be clean and that the system is
delivering clean water to the community water points. This was an improvement from the
previous trip when unsanitary practices at some standpipes resulted in contamination upon
collection. A system walk-through indicated that the greatest threat to water quality was a farm
Document 526 - Post Implementation Report
Yale Student Chapter
Kikoo Water Project
© 2007 Engineers Without Borders – USA. All Rights Reserved Page 37 of 37
recently established in the catchment watershed. The group emphasized the importance of
addressing this matter, and at the end of the trip it appeared that the water committee was
reaching a resolution with the farmer and landlord to remove the farm. It may be replaced by an
orchard, and the chapter emphasized that no pesticides or fertilizers should be used in the
catchment watershed if an orchard is established.
The travel team was effective at identifying and prioritizing daily tasks and organizing itself into
teams to tackle each job. This was true even while the principal mentor was absent and dealing
with the illness of a team member.
The chapter's ongoing involvement with Cameroonian engineering students (now graduates)
continues to be a fruitful means of transferring skills, interacting effectively with the community
and developing a more complete understanding of local concerns, politics and dynamics.