Geotube - Filtration

Geographic location

Rakhine
Myanmar (Burma)

Main treatment objectives

BOD / COD Reduction
Pathogen reduction
Solid/liquid separation
TSS and TDS reduction

Opex per real input flow

12 USD/m³

Required space

0.12 m²/m³ of design input flow

Technologies employed

Anaerobic baffled reactor
Anaerobic filter
Constructed wetland
Incineration
Infiltration

Design input flow

35 m²/day

Source of sludge

Flush toilet
Pit latrines affected by groundwater infiltraton
Public toilets

Final outputs

Effluent
Sludge

Skills level

FSM specialist for design
FSM specialist for operation and maintenance
Geographic location

Rakhine
Myanmar (Burma)

Main treatment objectives
BOD / COD Reduction
Pathogen reduction
Solid/liquid separation
TSS and TDS reduction
Technologies employed
Anaerobic baffled reactor
Anaerobic filter
Constructed wetland
Incineration
Infiltration
Source of sludge
Flush toilet
Pit latrines affected by groundwater infiltraton
Public toilets
Final outputs
Effluent
Sludge

Time construction and commissioning

Opex per real input flow
12.16 USD/m³
Required space
0.12 m²/m³ of design input flow
Design input flow
35.00 m²/day
Skills level
FSM specialist for design
FSM specialist for operation and maintenance

Description of the emergency context

The project site – Unichiprang is a hilly area and is currently hosting an estimated 21,300 Rohingya refugees (ISCG Full Situation Report, 11 March 2018). Refugees are continuing to cross the border into Bangladesh, with a total of 3,236 new arrivals reportedly entering the country in February 2018 alone, bringing the number to over 5,000 newly arrived refugees so far in 2018. The population is predominantly Muslim.

Description of the treatment process

No description

Assessment & design (feasibility)

The latrines provided for the refugees are simple pit latrines. Pits are emptied approximately every 4 to 8 weeks depending on the number of users. In the hilly terrain of Cox’s Bazaar, the transportation of the sludge is challenging and time consuming. The pit latrines are desludged by trained operators using an Oxfam pump (Atalanta Pelican 351 Diaphragm sludge pump with Lombardini 15LD225 diesel engine) with a capacity of approximately 10 min for a 500 L pit. The sludge is transported in a 50 L barrel fixed to a pole and jointly carried by two emptiers (manual transport, see pictures below). The Lime treatment is carried out in 50 L barrels. Prior to the collection and transport of faecal sludge, 15 g/l lime (CaOH2, 2 kg per barrel) is added to the empty barrels.

The faecal sludge from the pit latrines is removed from different ways: manual using buckets, manualy pumped using submersible pump and pumping with dedicated Oxfam trash/sludge pumps, which facilitates the mixing of the lime and the faecal sludge. Bucket desludging is used in place where it’s difficult to access with the heavy Oxfam pump. The lime creates a highly alkaline environment, which results in the inactivation of pathogens and stabilizes the sludge (if the alkaline environment of pH>12 is sustained for at least 1 hour). From the barrels, the sludge is poured through a screen (to remove any solid waste) and into the Geotube. The time the leachate filters into the sand portion of the filtration unit still need to be determined. The primary filtration units are comprised of three layers of filter media. The bottom layer is 17 cm of coarse gravel 1’’ the second layer is 14 cm of medium size gravel ½’’, topped off by a 20 cm of 2.5 fineness modulus (FM) sand appropriate for filtration. After this filtration phase, the liquid drains through a 6’’ pipe installed below the filtration media and flows through gravity force to a secondary filtration unit comprised of a 20 cm layer of medium size gravel ½’’.

The effluent from the secondary filtration phase is then discharged into the environment. The Geotube and primary filtration unit are protected with a roof to keep rain water out of the system. The solid phase of the faecal sludge is retained in the Geotube and is then emptied after a time to be determined. The Geotubes are single use and a new one must be installed after it is emptied. For the final disposal, two options are planned, depending on the final characteristics of the sludge. The first one is direct disposal of the remaining dried sludge into onto land in a nearby area and the second is, incineration of the dried sludge with basic equipment. The system was developed and designed by the Sanitation Technical Advisor of Solidarités International in coordination with the Faecal Sludge Management Technical Working Group of the WASH Cluster. There is a risk of contamination of ground water through the discharge effluent, hence the technology needs to be placed in a safe distance from boreholes, wells and other drinking water sources.

Construction

Operation and maintenance

Lessons learned

Strengths

Weaknesses

Sharable project files

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