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Water Supply and Department, Government of Faecal Sludge Management in Rural Areas under SBM (G) Training Manual UNITED Nations Children's Fund (UNICEF), August 2018

Permission is required to reproduce any part of this publication. Permission will be freely granted to educational or nonprofit organisations.

Please contact: UNICEF Office for Maharashtra, B-Wing, R2, Technopolis Building, Ground Floor, Mahakali Caves Road, Andheri (East), Mumbai, Maharashtra, India- 400 093

Content: Developed with Technical Support from UNICEF Maharashtra and PriMove, Pune.

Photo: UNICEF, India and PriMove, Pune

Design: Fountainhead India and Sanitation Department, Government of Maharashtra Faecal Sludge Management in Rural Areas under SBM (G)

Training Manual

Training manual on Faecal Sludge Management in rural areas i

Table of contents

Abbreviations ...... v

Chapter 1: About training manual ...... 1

Chapter 2: Important defi nitions ...... 5

Chapter 3: Faecal sludge management ...... 7

Chapter 4: Policy and legal framework for FSM ...... 13

Chapter 5: Faecal sludge and septage management (FSSM) value chain ...... 17

Chapter 6: Various technical options for containment of faecal sludge ...... 21

Chapter 7: Various technical options for collection and transportation of faecal sludge ...... 29

Chapter 8: Treatment for faecal sludge management ...... 35

Chapter 9: Planning, implementation and monitoring of FSM ...... 41

Annex 1: ...... 46

Annex 2: ...... 49

List of references ...... 50

Training manual on Faecal Sludge Management in rural areas iii

Abbreviations

CSR Corporate Social Responsibility MoUD Ministry Of Urban Development

DWSM District Water And Sanitation MSRLM Maharashtra State Rural Mission. Livelihood Mission

FFC Fourteenth Finance ODF Open Free Commission OSSF Other Onsite Sanitation FGD Focus Group Discussion Facilities

FSM Faecal Sludge Management SBCM Social Behavioural Change Management FSSM Faecal Sludge And Septage Management SBM

FSTPs Faecal Sludge Treatment Plant SHGs Self-Help Groups

MAPET Manual Pit Emptying SLRM Solid Liquid Resource Management

MAVIM Mahila Arthik Vikas STPs Treatment Plant Mahamandal TTFSM Treatment Technologies For MAWTS Mirpur Agricultural Workshop Faecal Sludge Management And Training School

MoEF&CC Ministry Of Environment, Forests And Climate Change

Training manual on Faecal Sludge Management in rural areas v

CHAPTER 1 About training manual

Training manual on Faecal Sludge Management in rural areas 1 1.1 Background is an alternative pit for use when the is being converted into manure. However, The central and state governments, along effective is required in with various public and private sector case of single pit and organizations, development partners have type latrines. Once the single pits are fi lled been taking efforts to make India open up, the user has no option but to revert back defecation free. Various community driven to . In septic tanks, many missions like Nirmal Gram Puraskars, Sant times decomposition of waste does not take Gadgebaba Gram Swachhata Abhiyan, place and the waste needs to be pumped out etc. were implemented during early 2000s and treated. The septic tanks are generally to create a movement for sanitation. The not constructed with required retention sector received much needed boost with period in rural areas of Maharashtra, which introduction of Nirmal Bharat Abhiyan and leads to ineffi cient decomposition leading Swachh Bharat Mission. Through Swachh to serious health hazards. Also, there is no Bharat Mission, the central government is proper mechanism and awareness regarding aiming to make the entire country open- management of septage from institutional defecation-free (ODF) before 2nd October and community . Thus, creation of 2019. effective systems for management of faecal sludge is crucial. In 2016, the government of Maharashtra declared its aim to achieve 100% elimination Presently, there is inadequate awareness and of open defecation by March 2018. For knowledge about faecal sludge management achieving the target, the state pioneered among government functionaries and innovative approaches, strengthened community. This manual has been developed institutional arrangements, ensured jointly by Water Supply and Sanitation strong focus on behaviour change and the Department, GoM, UNICEF, Mumbai and environment for learning as well as adapting PriMove, Pune for providing information and new dimensions. The state has now been guidance about faecal sludge management in declared ODF as per the baseline survey of rural areas. 2012. However, building toilets and creating infrastructure is just not enough to ensure and health conditions. 1.2 Content of the manual The sustainable use of toilets and effective The manual presents important defi nitions management of faecal sludge are critical regarding Faecal Sludge Management challenges for sustaining the ODF status and (FSM) followed by the status of sanitation achieving public health goals. in the state, major opportunities and challenges regarding FSM, legal provisions, The toilets in rural areas are primarily of etc., are presented in the next section. following types- twin pit, one pit, biogas Subsequently, various technology options and septic tank type. Effective waste for all components in the FSM service value management in all these types of toilets chain are described in the later sections. is critical for healthy environment. Faecal The last section of the manual discusses the sludge management in case of two pit methodology for planning, implementation type latrines is safe since the excreta is and monitoring of FSM. decomposed naturally in the pits and there

2 Training manual on Faecal Sludge Management in rural areas 1.3 Target users of this 1.4 How to use this manual manual This manual intends to appraise the The manual is targeted for use by DWSM participants about technical information, experts, BRCs, state and district KRCs, PRI legal provisions, service value chain of functionaries at various levels, offi cials and FSM, relevant technologies of containment, offi cers, SHGs contributing to ODF status collection, transportation and methodology achievement, villagers, various organizations for planning, implementation and monitoring working in the fi eld of sanitation and of FSM. For effective use of this manual, facilitators of FSM. the reader needs to read, understand and internalize the subject matter.

Training manual on Faecal Sludge Management in rural areas 3 4 Training manual on Faecal Sludge Management in rural areas CHAPTER 2 Important defi nitions

Training manual on Faecal Sludge Management in rural areas 5 This section presents important defi nitions septic tank or twin-pit are used to collect regarding faecal sludge management which the waste. Since these containment need to be understood before proceeding to structures are located near to the toilets, the next chapters. these are called on-site sanitation systems. Twin pit and septic tanks both are examples 2.1 Faecal sludge of on-site sanitation systems. Faecal Sludge (FS) is the material that is collected from pit latrines, septic tanks or 2.3 Septage management other onsite sanitation facilities (OSSF) and not transported through a sewer. Faecal and faecal sludge Sludge is raw or partially digested, slurry management or semisolid in nature. It contains various harmful physical, biological, chemical Septage Management refers to the components which need to be treated comprehensive program for managing septic properly. tanks and the procedures for desludging, transporting, treating and disposing of septic 2.2 “On-site sanitation” (OSS) tank content. Faecal Sludge Management is system the collection, transport, and treatment of faecal sludge from pit latrines, septic tanks or Places where underground sewage systems are not possible, containment structures like other onsite sanitation systems.

2.4 Other important defi nitions

BLACK WATER A mixture of , faeces and fl ush The total volume of water water along with anal cleansing generated from washing food, water, and/or dry cleansing clothes and dishware, as well as materials. from bathing, but not from toilets.

FAECES SEPTAGE Refers to (semi-solid) excrements Refers to the solid or settled devoid of urine or water contents of septic tanks;

SEWAGE SEWER General term given to the mixture An open channel or closed pipe to of water and excreta (urine and convey sewage. faeces).

SEWERAGE SLUDGE All the components of a system to Refers to the settled solid matter in collect, transport and treat sewage semi-solid condition – it is usually a (including pipes, pumps, tanks etc.). mixture of solids and water deposited at the bottom of septic tanks.

6 Training manual on Faecal Sludge Management in rural areas CHAPTER 3 Faecal sludge management

Training manual on Faecal Sludge Management in rural areas 7 3.1 Background in such cases. Thus, these toilets need to be converted into twin pits by digging a Swachh Bharat Mission is being second pit and connecting it to the by a implemented effectively throughout the junction chamber. country, and as a result many states and districts are in the process of being declared Septic tank type toilets- In case of septic as ‘Open Defecation Free’. This movement tank type toilets, anaerobic bacterial will create necessary sanitation infrastructure environment develops in the tank which in the nation. However, for its sustained decomposes the waste discharged into the use, focus should be on social behavioural tank. The rate of accumulation of sludge change communication (SBCC) and technical is faster than the rate of decomposition. appropriateness of sanitation facilities. Therefore, the accumulated faecal Additionally, it is necessary to create capable sludge must be periodically removed for systems for its operation and maintenance, further management. The systems for generate entrepreneurship opportunities in management of septage are available in sanitation, and also build necessary systemic big cities. However, in case of rural areas and human capacities. or census towns, the septage is disposed of on open spaces or in water bodies. Faecal Sludge Management is an important Considering the harmful impacts of such component of O&M of sanitation facilities. practices, appropriate systems for emptying, Following section presents the toilet typology transportation and management of septage wise nature of FSM requirements- need to be developed. Twin pit latrines- In case of twin pit latrines, the liquid and gases generally infi ltrates into 3.2 FSM in rural and urban the surrounding soil and solids are allowed areas of Maharashtra to decompose through aerobic processes in The nature of services available for faecal the pit. Second pit is connected to the toilet sludge management depends on the when the fi rst pit gets full. First pit is then size of population, location and pattern of closed till the waste decomposes and turns development. This section briefl y describes into manure. This decomposition process the nature of FSM in rural and urban areas of takes at least a year. These types of toilets do Maharashtra. not need external faecal sludge management apart from pit emptying. Before we discuss the nature of FSM, let us fi rst understand the defi nitions of various Single pit latrines- When the single pit gets urban and rural entities as defi ned by the fi lled up, it cannot be used till the waste is Census of India. completely decomposed. The users have no option but to revert to open defecation

8 Training manual on Faecal Sludge Management in rural areas Rural area- Area which is different from urban area and the basic unit is a revenue village

Urban Agglomeration- An urban agglomeration is a continuous urban spread constituting a town and its adjoining outgrowths (OGs), or two or more physically contiguous towns together with or without outgrowths of such towns. An Urban Agglomeration must consist of at least a statutory town and its total population (i.e. all the constituents put together) should not be less than 20,000 as per the 2001 Census.

Statutory towns- All places with municipality, corporation, cantonment board or notifi ed town area committee etc.

Census towns- Are the areas which are not statutorily notifi ed and administered as a town, but nevertheless whose population has attained urban characteristics has minimum population of 5000, at least 75% of the male working population is engaged in non- agriculture pursuits and a density of population of at least 400 persons per sq. km. CTs are currently administered as rural areas.

Out Growths: A viable unit such as a village or part of a village contiguous to a statutory town and possess the urban features in terms of infrastructure and amenities such as pucca roads, electricity, taps, drainage system, educational institutions, post offi ces, medical facilities, banks etc.

3.2.1 Status of FSM in Out Growths/ done through technologies like tiger biofi lter, urban area/ statutory towns baffl e reactor, DEWAT, etc. In case of urban areas and statutory towns, 3.2.2 FSM in rural areas, census FSM system exists where sewer lines towns and growth centres are created to transport the sewage from latrines. The sewage is collected at a Sewage According to Census 2011, out of the total Treatment Plant (STP) and treated to form 11.2 core population of Maharashtra, the manure or a semi-solid waste or slurry, called size of rural population is 6.2 crore which . After treatment, sewage constitutes 55% of the total population. sludge is generally disposed of in landfi lls, On the other hand, the rural areas are dumped in water bodies or applied to land. characterised by rapid increase of Census Towns (CTs) in the recent years. Between However, such systems are not available 2001 and 2011, CTs in the state have grown in all urban areas. In areas where sewer from 127 to 279. This situation clearly systems are not available, untreated sewage highlights the need for FSM in these areas. is discharged in river bodies or in open. Similarly, urban settlements which are not So far, about 1.10 crore toilets have been connected to the sewer network need to constructed in rural Maharashtra which pump the sewer with help of a truck. include twin pit types, single pit types, In some of these areas, on-site treatment is biogas and septic tank types. In case of

Training manual on Faecal Sludge Management in rural areas 9 twin pit latrines, no external faecal sludge found fl owing smoothly. In another 54.2% management is required, whereas on site HHs though there was pucca drain but the management of faecal sludge is possible same was found chocked and liquid waste in single pit latrines if a second pit is dug. remained stagnant. Further, grey water was However, septage management is a critical seen to overfl ow within 9.3% of the HH issue in these areas. premises.2

Though the data on typology of toilets Therefore, Faecal Sludge Management is not yet available, it is estimated that interventions, including setting up of new approximately 20% (about 22 lakh toilets) of systems as well as expansion, strengthening rural toilets are of septic tank types. In most and upgrading of existing systems is of the census towns and growth centres, necessary in rural areas of the state. there are no sewer lines which connect the toilets to Plants (STPs) 3.3 Need for FSM in the nearby area. Maximum septic tanks are accumulated in this area. The septage Proper management of accumulated faecal generated by the septic tanks in these areas sludge in rural areas poses a challenge are collected and disposed either in water with no formal mechanism in place for its bodies or open land. treatment and management. Ineffi cient treatment of faecal sludge is harmful for As per a recent study by SIGMA Foundation, human health and the environment. In case 9.3% of the surveyed HHs from Nagar of twin pit latrines, though the waste is Panchayats had no drainage system to decomposed on site, shifting to the second carry the waste water while 43.3% of the pit and emptying the used pit needs to be ULBs had kuccha drains. Stagnant water done on time. Single pit latrines need to was found near the source be converted in two pit latrines or some in 51.2% of the ULBs, while water spillage alternative technology needs to be thought on the public road was seen in 45.8% of of. the ULBs. Moreover, grey water was found to be overfl owing within 42.3% of the HH Considering the large number of septic tank premises1. type toilets and their technically incorrect construction; systems for cleaning and In rural areas, management of liquid waste desludging of septic tanks are necessary. villages is not satisfactory. According to a Effective system for desludging of septic recent assessment of status of ODF and tanks is important for sustained use of toilets related factors done by UNICEF and SIGMA and attaining the goal of complete sanitation foundation, 23.4% HHs had no drain to carry in the state. the liquid waste. Only in 1.6% HHs there were soak pits and in another 9.6% HHs there was pucca drain and the water was

1 A report on Status Of ODF Sustainability In The Nagar Panchayats Of Maharashtra by SIGMA Foundation 2 an occasional report on ODF Sustainability and Water for Sanitation in Maharashtra prepared by SIGMA Foundation with Support of UNICEF, Maharashtra

10 Training manual on Faecal Sludge Management in rural areas 3.4 Employment/ 3.5 Challenges in FSM entrepreneurship Following are the key challenges for effective opportunities in FSM FSM in rural Maharashtra –

As mentioned above, there are 1.10 crore Emptying the soak pit and use of manure: toilets constructed in rural Maharashtra, There is a lack of awareness in rural areas most of which are single or twin pits. In case regarding the process and need of emptying of such toilets, there is a need for service the fi lled pits, and use of manure from the providers for pit emptying or construction pit. This generally results in restricted use of of second pit. Service providers for these toilets (due to fear of pits fi lling fast). services may be empaneled/ procured. Digging and connecting second pit to There are approximately 22 lakh septic single pit latrines: Many single pit latrines toilets in the state. Considering the storage have been constructed in rural areas, which capacity of the septic tanks, they need to be are experiencing problems of pit fi lling up. desludged in 3-5 years. Keeping this in mind, Converting these single pit latrines into it can be concluded that 4.40 lakh toilets twin pit latrines and connecting the second will require cleaning every year, amounting pit to the existing latrines (which do not to desludging of 1467 septic tanks per day. have a junction chamber) is a challenge. This means, in each of the 34 district of the Construction of second pit is not possible in state, around 43 toilets will need desludging many cases due to space constraints. There per day. On an average 2 trips are made is a fear of users reverting to open defecation for cleaning one septic tank and around 6 after the pit gets fi lled up. trips are possible in a day. Required number of desludging tankers needs to be made No / Limited access to tanks: Septic tanks available in every district based on the are often placed under toilets, or they are number of septic tanks. In the beginning, sealed, or cemented over which makes FSM services may be set up at cluster or it diffi cult to access them for cleaning/ block level. This clearly depicts that there is emptying which dis-incentivizes their a wide scope for generating employment/ frequent cleaning. The desludging vehicle entrepreneurship opportunities in FSM for can desludge from maximum of 70 meters SHGs, unemployed youths, service providers, distance. Access roads to the rural toilets NGOs, etc. especially in the highly dense habitations are also an issue. In addition to this, involvement of private sector may be sought for desludging septic Inappropriate tank size and design: The tanks. Efforts can be made for funding government has released guidelines for equipped vehicles or setting up of treatment technically correct construction of septic plants. Desludging may be done by private tanks. Yet, septic tanks connected to contractors as per demand or through a individual toilets are often not of proper size sequential desludging of septic tank as per due to lack of awareness about the design exhaustive lists. Appropriate fees may be norms among construction contractors and changed from the users for desludging. masons. As a result, the excreta does not get

Training manual on Faecal Sludge Management in rural areas 11 properly decomposed and hence the tank to establishment of FSM service chain. Entire gets fi lled early. This leads to households sewage is mostly dumped without treatment going for emptying services quickly, making into the rivers, while untreated sludge and it costly and environment polluting. septage is disposed of in a dumping ground or available water body. In peri urban areas, Management of septage: The septage the septage is disposed many times in the from septic tanks is generally discharged urban sewer systems, putting additional load (nallas). in open or in canals It is harmful on the urban systems. environmentally and also for human health. The septage outlet needs to be discharged Poor and Limited Awareness: Faecal in a soak pit for its management. Financial Sludge and septage management has been support for this can be sought from 14th accorded low priority among people and Finance Commission funds and MREGS implementers and there is poor awareness funds. about its inherent linkages with public health.

Lack of infrastructure, and a regulated To sum up, management of faecal sludge schedule for cleaning: Local bodies often in an environment friendly manner is face fi nancial and personnel constraints in necessary for attaining the goals of Swachh providing service to households - for example, Bharat Mission. Creation and strengthening insuffi cient suction emptier trucks, trained of facilities for transport and treatment of human resource, safety equipment, etc. to sludge is crucial, particularly for rural areas ensure regular cleaning/ emptying of septic in the state. The central government has tanks. taken a step ahead in terms of policy and laws for FSM in urban areas in the country. Treatment and Disposal: Typically, census The subsequent section of this manual towns and rural areas have no funds for describes the policy and legal framework for the construction of FSTPs, STPs, and also FSM. However, application of these laws or there is no clear mandate which defi nes the formation of laws for rural areas will need to responsibility of local authorities with regard be deliberated further.

12 Training manual on Faecal Sludge Management in rural areas CHAPTER 4 Policy and legal framework for FSM

Training manual on Faecal Sludge Management in rural areas 13 4.1 Introduction (1) Discharge of any solid, liquid or other matter into water bodies and on land The central government has issued ‘National is restricted, and requires specifi c prior Policy on Faecal Sludge and Septage approval; and Management’. However this is geared more towards the urban landscape. At present (2) Depending on the type of discharge, and there is an absence of a National policy for whether the discharge is on land or in faecal sludge management for rural areas. water bodies, permissible standards are The urban policy can provide guidance and a prescribed. framework for preparing the policy on FSM in rural areas. Study of the legal framework 4.3.2 Solid waste management regarding FSM is also crucial for decision rules 2016 making which abides to the laws and acts Rules regarding solid waste management of the state. Following section presents the have been notifi ed by the Union Ministry of urban policies and laws regarding FSM. Environment, Forests and Climate Change (MoEF&CC) wherein few activities for 4.2 Urban policies on FSM solid waste management have been made The National Urban Sanitation Policy (NUSP) mandatory. As per the rules, septage and of 2008 brought a paradigm shift from faecal sludge management is necessary ‘conventional centralized network’ for controlling water, land and air pollution. approach of urban sanitation to a more Rules have been fi nalized for use of manures holistic approach. Few states (Tamil Nadu and and landfi lls. Similarly, consideration to (2014), Delhi (2015), Odisha (2016) Building Code of India issued by Bureau of and Maharashtra (2016)) have developed their Indian Standardis mandatory while preparing septage management guidelines. Apart from policies for septage and faecal sludge that, Ministry of Urban Development (MoUD) management. has recently released a primer on faecal sludge and septage management (FSSM) as 4.3.3 The Employment of Manual well as a Rapid Assessment to estimate Scavengers and Construction the budget needs for FSSM. of Dry Latrines (Prohibition) Act, 1993 Study of the urban policies will help in The 1993 act was supplemented by ‘The planning, selection of technology options and Prohibition of Employment as Manual implementation of FSM in rural areas. Scavengers and their Rehabilitation Act, 2013 (the 2013 Act)’. Taken together, the two 4.3 Relevant Acts laws prohibit various activities that involve manual handling of human excreta (defi ned 4.3.1 Environment laws as “”), and lay down The environment laws include the Water conditions and safety standards for activities (Prevention and Control of Pollution) Act, defi ned as “hazardous cleaning”. The 2013 1974 (the “Water Act”) and the Environment Act also requires conversion of insanitary (Protection) Act, 1986 (the “Environment latrines into sanitary latrines within a period Act”). Taken together, the implication of the stipulated by the local authority. environment laws is that:

14 Training manual on Faecal Sludge Management in rural areas 4.3.4 Panchayat Act Following activities may be taken up by the PRIs for FSM- In terms of Constitutional allocation of powers and functions, the State Government (i) Survey insanitary latrines, and monitor has legislative and functional power over the setting up of on-site containment “public health and sanitation”. The Fourteenth structures, Finance Commission (FFC) identifi ed “core functions” of PRIs, which include “sanitation, (ii) Carry out mandatory ‘scheduled solid waste management and drainage”. desludging’, and monitor regular and periodic desludging, The PRIs have the primary responsibility of rural sanitation management. The provisions (iii) Enforce a licensing and monitoring of Panchayat act show that PRIs may already regimen for septage transport services. have the legal mandate to provide for most (iv) Take up the responsibility of setting up FSM related activities. However if there are faecal sludge treatment systems. areas/activities for which there are no legal provisions, they can be formulated by the (v) Effective monitoring of the faecal sludge state government. management systems

Training manual on Faecal Sludge Management in rural areas 15 16 Training manual on Faecal Sludge Management in rural areas CHAPTER 5 Faecal sludge and septage management (FSSM) value chain

Training manual on Faecal Sludge Management in rural areas 17 5.1 Introduction 5.1.1 System for safe containment of the faecal sludge For effi cient Faecal Sludge management and Septage Management, the reader Promoting an appropriate and area-specifi c needs to understand the entire FSSM Value containment technology is vital, for which Chain. The Service Value Chain includes the CPHEEO norms should be followed. safe containment of sludge, safe emptying In rural areas of Maharashtra, twin pit and transportation; treatment and disposal/ latrines and septic tank type latrines are reuse of Faecal Sludge and Septage (refer the predominant. Few points need to be taken diagram below). Each of these Value Chain care of while constructing these latrines. components needs to be addressed properly In case of single or two pit latrines, the to prevent health and environmental impacts location of the pit should not be nearer to the in rural areas due to indiscriminate disposal water source or built on areas having higher of hazardous faecal waste. An overview of ground water tables. Technically correct treatment technologies, together with their construction is crucial in all types of toilets. treatment objectives and functionality, are Inappropriate construction of septic tanks included in detail in this section. can lead to leakages in the tank, limited or

Emptying and Use/ Containment Treatment transportation management

Emptying the Treatment Use or septic tank and of the faecal management System where transportation sludge and turn of the end the faecal into manure. products. sludge is Example: Example: stored. Vacutug Example: Unplanted  Example: Vacuum Manure (for drying bed truck agriculture/  Septic tank Planted kitchen Tractor  Twin pit drying bed gardens) latrines mounted vacuum Tiger bio Use of  Single pit tanker fi lter, treated latrines water Bio-gas Gulper etc. DEWATS, etc.

18 Training manual on Faecal Sludge Management in rural areas of settled solids (sludge) and liquid, resulting in reasonable reduction in the volume of sludge, reduction in biodegradable organic matter and release of gases. A substantial portion of solids escape with the effl uent whenever a septic tank is not desludged for a longer period, i.e., more than the design period. Therefore, the septic tanks need to be desludged by automatic or human operated technologies. It is very important to avoid any human contact directly with faecal sludge, and following the safety measures thoroughly. The common technologies for emptying and transportation are listed below and discussed in detail in the subsequent sections.

Technologies for emptying no access to tanks, chocking up of the toilet, and transportation or inappropriate treatment of the waste, etc. Next section of this manual elaborates – Vacutug – the technology options for containment of faecal sludge and related operation and – Tractor mounted – Gulper etc. maintenance requirements. vacuum tanker

5.1.2 Safe emptying and transportation 5.1.3 Treatment A septic tank is a combined sedimentation In view of the characteristics faecal and digestion tank where settleable solids sludge,its effi cient treatment is critical. Many settle down to the bottom, accompanied by technologies of faecal sludge treatment

Training manual on Faecal Sludge Management in rural areas 19 like Sewage treatment plants (STP) are 5.1.4 Use/management being used in urban areas. However, these The end products of the FS treatment can technologies cannot be used in rural areas be reused and managed well. The treated due to fi nancial constraints and inadequate water from treatment plant can be used for systems for its O&M. Few low cost and agriculture and the can be used as simpler technologies can be used in rural manure for agriculture/ kitchen gardens. In areas for treating the faecal sludge. Some of big cities, the compost can be mixed with these treatments are mentioned below and bio-degradable garbage to produce good described further in the subsequent sections. quality manure through effective garbage disposal. - Unplanted drying Considering the FSM Service Value Chain and bed its components, the selection of appropriate FS Treatment - Planted drying technology option for rural areas and its methods bed effective management is important. Various - Tiger bio fi lter technology options for every component in - DEWATS, etc. the FSM value chain are described in detail in the next section.

20 Training manual on Faecal Sludge Management in rural areas CHAPTER 6 Various technical options for containment of faecal sludge

Training manual on Faecal Sludge Management in rural areas 21 There are three important technologies for The water used for fl ushing and the safe containment of the faecal sludge in rural generated during decomposition process areas- is absorbed in the soil surrounding the pit. The manure excavated from the pit is a • Two pit pour fl ush toilet good source of income. While constructing • Septic Tank Toilet this type of toilet, care needs to be taken regarding the type of soil (absorbent soil • Biogas is required) and pollution of ground water It is imperative to construct technically sources around the pits. appropriate toilets for proper management of faecal sludge. It is also important to 6.1.2 Construction of Leach Pits/ understand the components, technical soak pits details, O&M requirements, etc. of each Leach pits / soak pits are brick lining pits technology. constructed below the ground surface. Bricks are arranged in a circular and honey 6.1 Two Pit toilet comb manner to maintain 5-6 gaps of 2” in between each of the alternate brick 6.1.1 Technical details layers. These gaps will allow percolation of The faecal sludge is managed on site in this excess water into the soil. Such gaps are type of toilet construction. As per UNDP not kept in the top 1 feet of the brick layer. report, this technology is safe for human No cement and/or concrete are applied at health and environmental balance. This the bottom and on the sidewalls of the pit. technology uses less water (about 1 to 2 After completing the construction of pit, litres) and needs less space for construction. each one is covered either with a moulded In this technology, excreta get dried and R.C.C. seal or any other local material that start decomposing in the pit due to bacterial is used for fl ooring. For complete and safe reactions in the pit, between the excreta decomposition of the excreta, two pits and soil. Gases generated during the should be used alternately (after fi lling up of decomposition process are also absorbed in a pit). For an average family size of 5-7 people the soil leading to odourless decomposition. a single pit can last for more than 4 years; generating about 1 Cu Ft of compost per annum per person. leach pit 6.1.3 Limitations • Since the leach pits seal are to be constructed underground, the area with rocky strata and areas leach pit where ground water table is high are not suitable for this technology.

22 Training manual on Faecal Sludge Management in rural areas • To construct this type of toilet, the atmosphere; cover them with suffi cient selection of appropriate site is a key factor. quantity of soil and compact it lightly. While selecting a site, the location of • After completing the above mentioned nearby water sources and risk of chemical steps, fl ush a bucketful of water into the and bacteriological contamination of water pan. This will clear the entire path up to should be considered on priority basis. leach pit. Similarly the water seal will • Construction of two pits is necessary also get fi lled with required quantity of as construction of single pit may pose water. problems after getting completely fi lled. 6.1.5 Pit emptying and removal of 6.1.4 What precautions need to be manure taken after the construction The Twin leach pit is easy to construct, of toilet? use and maintain. It saves water and can be Following points should be ensured once the used with less water as compared to other construction part is over or rather during the types of toilets. When leach pits gets fi lled, very last phase of construction. it can be emptied at household level by following the simple steps given here. • Sand, cement, debris etc. from all the toilet components should be cleaned 1. The mineralized manure in the pit needs off. Especially the pan, trap, the platform to be emptied around the pan should be cleaned properly preferably preferably by a wire brush and a jet of in summer water. season. One • Junction chamber, drain pipes should should not be cleaned and there should not be a empty it in the slightest obstacle. rainy season.

• All the holes in the leach pit walls should 2. A family of 5 to 7 members, using twin be cleaned properly. Bottom of leach leach (Pit with three feet should be free from fallen mortar and, if width and 3-4 necessary, it should be made permeable feet depth) by light digging. consistently for 6 to 7 years, • One of the paths from junction chamber shall result in leading to leach pit should be plugged by a one pit getting piece of brick and lean mortar. fi lled. This • Cover the junction chamber with a period may vary depending upon the soil suitable tile and seal the joints. type / strata, size of pit and the amount of water fl ushed during toilet use. • Cover the leach pits with suitable covers and seal the joints between two halves 3. Whether a pit is full or not, can easily of the cover as well as the one between be found out from the toilet pan or the cover and the leach pit wall. chamber by inspection by back fl ow or • Don’t keep the leach pit covers open to choking. If one pit gets fi lled, we need to

Training manual on Faecal Sludge Management in rural areas 23 close the pipe connecting that pit from the day time the chamber (If toilet constructed is of in sunlight. single pit, then Condition of the chamber the material in and a second the pit should pit construction be observed must be carefully. completed before emptying the fi lled pit), Absence of so that the faecal matter will not go to the water, feacal pit which needs to be emptied. matter looking like black or brown soil, 20 to 30% of upper part of pit without 4. Before disconnecting the pipe connecting any feacal material and absence of any the fi lled pit from the chamber, pipe of foul smell along with a cake like sump the second pit needs to be connected are common characteristics of fully so that faecal matter will go in the other composted manure. pit. Precaution should be 7 Before taking taken while out the night connecting the soil manure it second pit to is necessary the chamber. to confi rm that The connection and slope of pipe should feacal matter is be as per technical requirements. Only completely decomposed and there is no then should the new pit be used. dampness in the decomposed matter. (This can be easily checked with the help 5. Filled and closed pit should not be of a hollow iron rod. This rod need to be opened for a minimum of one year. inserted inside the pit till the hard strata During this of the pit. The soil which comes within period, water in the rod needs to be observed carefully.) the pit leaches After confi rming that decomposting is out in the completed, pit should be kept open for surrounding few hours, so that any insects or reptiles soil and the or small animals living inside should come feacal matter out of pit. If possible, this pit should be is digested kept open for and converted as night soil manure. The one complete time for conversion of feacal matter into day. (While decomposed night soil manure may vary keeping this depending upon the water absorption pit open, care capacity of the local soil, the environment should be taken and size, shape and construction of the that no water, pit. children or any animal should 6. A fi lled Pit which is closed for a year for go inside and any accident should not composting should be opened during take place.) Most of the decomposed

24 Training manual on Faecal Sludge Management in rural areas feacal matter is of cake like shape which and it should be sieved with the help of is in the centre of the pit and is away sieving net. This sieved /manure from the outer walls of the pit. should be kept in the gunny bags for use in gardening or farming. While packing the 8. If faecal matter is not fully decomposed, manure, if there is a little moisture, do not then ash should be spread/sprinkled worry and let it be as it helps in protecting on the top some of bacteria. This night soil manure of the partly is commonly called as "Sonkhad/Golden decomposed compost". It has been seen that use of night soil so manure increases production and quality that extra of crop on which it is used, and also dampness/ reduces input fertilizer costs. If not used water content can be absorbed by the in own garden/farm, the manure can be ash. This will make it dry soon. Such pit sold to other local farmers/gardeners. should be kept covered and needs to be inspected regularly and when the night 11. Pit from which night soil manure has soil manure is ready, then only it should been removed, needs to be cleaned, and be emptied. the honeycombing in the walls checked. If it is found 9 To empty the pit, regular farming damaged, then instruments/ like pick, spade, it should be hoe, sickle, iron/plastic pan/basket are repaired with required. Night soil manure which can the help of be easily removed from outside the pit, a mason. Pit should be taken out fi rst. Then remaining should be kept material should be taken out by physically exposed to sunlight for 2 to 3 days, and going inside the pit. For this two persons then kept ready so that it can be reused may be required. One person will go whenever required. inside the pit and take out the manure while the other person will collect the 12. Finally, it may same and spread it on a plastic sheet be noted that kept on the ground. Generally, from one removing night pit, we should be able to get 90 to 130 soil manure kg night soil manure. To empty one pit from twin leach completely, 3 to 4 hours’ time will be pit latrine is required. very simple procedure. 10 This manure is generally bound tightly in It can create the form of lumps. These lumps should good employment opportunities in rural be loosened areas where twin leach pit latrines are and materials constructed largely in numbers. like, sticks, roots of trees, (Reference: Leafl et on ‘Steps for Emptying of clothes, glass, Twin Leach Pit Toilet’ by UNICEF) etc. if found, separated

Training manual on Faecal Sludge Management in rural areas 25 6.1.6 Points to remember removed from the septic tank. The water is taken forward without disturbing the process Removal of manure from the pits is not only of sludge digestion. Organic matter in the easy but joyful. This is organic manure and it sludge and scum layers is broken down by contains almost all the basic plant nutrients bacteria which convert it to liquid and gas. including Nitrogen (1.5%), Phosphorus The process is called sludge digestion. (1.07%), and Potassium (0.5%). It can be Methane and other gases generated during used in any crop and even in the domestic decomposition process are discharged by a garden. Since it is organic manure it gives vent pipe on the tank. very good results and has no ill effects at all. of human excreta into manure is 6.2.2 Construction of leach pits/ our national duty. soak pits 6.2 Septic tank toilet In septic tank toilet, construction up to plinth level and superstructure is similar to pour 6.2.1 Technical details fl ush toilet. Appropriate construction of septic tank is the most important part and This technology too is common in rural areas as mentioned above;the septic tank needs of Maharashtra. A septic tank is designed to be designed with a 45 days retention to allow settlement and decomposition time. Septic tank is divided into either three of waste water. Heavy solids in the water or two chambers. When three chambers settle at the bottom of the septic tank and are provided all the chambers are of equal lighter solids fl oat on the liquid surface in the size. If two chambers are provided the size form of scum. Thus, water with minimum of the fi rst chamber is kept 2/3 and second solid content fl oats in the middle portion of chamber is 1/3 of the length. the septic tank. This partially treated water is supposed to move forward and to be

access covers vent

intel intel-T outlet

scum

sedimentation zone

26 Training manual on Faecal Sludge Management in rural areas 6.2.3 What precautions need to be • Lot of water needs to be used in this taken after the construction technology for preventing chocking of of toilet? inlets and outlets. • Never allow the effl uent of septic tanks • Cost of construction is high. to fl ow in the open or in an open drain. • The septic tanks need to be desludged This can cause water pollution and spread periodically, and no byproduct is produced diseases. This is also against the law. which can generate income. Instead, make a provision of a soak pit or leach pit of appropriate volume to • The methane generated during accommodate the effl uent. decomposition process is harmful for the environment and also cannot be • Always provide a vent pipe to evacuate harnessed as source of fuel. the obnoxious gases from the septic tank. The vent pipe should have 3” diameter, should raise above the nearest building 6.3 Biogas structure, should have a cowl on the top for proper ventilation and a mosquito 6.3.1 Technical details screen wrapped around it to avoid access Biogas is an anaerobic technology where to mosquitoes decomposition of waste material takes place with the help of microorganism that • Empty Septic tank- Emptying of a septic can grow in the absence of oxygen. The tank is very important for the safe use of biogas contains 50-70% Methane, 30-40% it. The septic tank must be emptied after Carbon dioxide and other gases. Methane equal intervals. is a fl ammable gas and can be used as • Keep an eye on the behaviour of septic alternative sources of fuel for domestic and tank – (changes in water level, drainage of commercial use. Calorifi c value of the biogas waste, etc.) is 20 MJ / M3 and its 60% effi ciency can be • Having your septic tank of good material used through burner. is of sheer importance. Strong and reliable Biogas system has four important parts- Inlet septic tank can avoid any problems in the chamber, Digester, Outlet chamber and Gas future. collection chamber. • The septic tank should not be near a tree Inlet chamber – In this chamber solid waste or plant or a tree near a septic tank. The and other biodegradable material such as roots of the trees are very strong, and cow dung are mixed together with water. they can crack the boundaries of the tank.

• Use of adequate water for fl ushing Digester – Digester is a closed chamber. Content in the inlet chamber enters the 6.2.4 Limitations: digester and actual process of decomposition takes place in the digester. If the septic tank is not of appropriate size or if the number of users is more, untreated Outlet chamber – After completion of water starts leaking from the outlet, causing the decomposition process the solids in health and environmental hazards. the slurry form gets collected in the outlet chamber. This slurry is spread on the drying

Training manual on Faecal Sludge Management in rural areas 27 beds and further it can be applied in the • Provide ventilation around all gas lines. agriculture fi elds. • Always maintain a positive pressure in the Gas collection chamber – This chamber is system. located in the upper part of digester. Gas • Metal digesters and gas storage tanks generated during the decomposition process must have wires to lead lightning to the is collected in this chamber. Gas from this ground. chamber is carried through a pipeline and is used as a fuel source. • Gas lines must drain water into condensation traps. Biogas system is available in two types - • No smoking or open fl ames should be Fixed dome biogas and fl oating dome biogas. allowed near biogas digesters and gas Fixed dome biogas further has three types storage tanks, especially when checking namely Janata Biogas, Deenbandhu Biogas for gas leaks. and Malprabha Biogas. Floating dome biogas has further three types namely K.V.I.C. 6.3.3 Limitations Biogas, Water Jacket Biogas and Pragati Biogas. Waste of at least 2-3 cattle is required for functioning of biogas. Biogas cannot be 6.3.2 What precautions need to be generated solely on . Animal taken after the slurry is essential. of toilet? Hydrogen Sulphide gas is produced along • Regularly check the whole system for with biogas. Human contact with the leaks. digester is therefore harmful.

28 Training manual on Faecal Sludge Management in rural areas CHAPTER 7 Various technical options for collection and transportation of faecal sludge

Training manual on Faecal Sludge Management in rural areas 29 The collection of faecal sludge from septic 7.1 Vacutug tank/ soak pit and its safe transportation is the most important aspect in faecal 7.1.1 Technology specifi c sludge management practice as all information subsequent processes primarily depending Vacuum tugs/ Vacutugs are used for on it. At present, there are various types de-sludging and transportation which of technologies available in the market for principally operate on vacuum suction. These collection and transportation of faecal sludge. mechanical systems are used for emptying Some of the globally available technologies pits and septic tanks. The equipment was are provided in the table below: fi rst built by Mirpur Agricultural Workshop and Training School (MAWTS) in Dhaka during Technologies Technologies for the year 2002. This simple portable machine for collection of transportation of is highly navigable through narrow streets to sludge sludge access hard to reach extraction points which Gobbler Vaccutug may be unreachable to large machines.

MAPET Grapler 7.1.2 Technology and working Pit Screw Auger Shilfter principles

Diphragm Dung beetle It is important to automate the task of emptying septic tanks and pit latrines to Omni ingester Vaccum tug UN-habitat avoid manual removal of sludge, and hence these machines have been designed to Gulper Tricycle mounted operate on the principle of vacuum suction. transportation system The Vacutug comprises a vacuum tank having a size of 0.5 cubic meter, connected Most of the above listed technologies are to a sliding vane capable of used globally for collecting and emptying producing a -0.8 bar vacuum. The machine faecal sludge. The required capital is fi tted with a clutch in the form of an investment, O&M and other additional adjustable drive, a throttle and two brakes. expenditures for procuring these services The front wheels are driven by a petrol makes them less preferable and affordable in engine connected either to a vacuum pump rural context. Considering this fact, following or a friction roller, through an adjustable belt technology options which are less capital drive. The vacuum tank is fi tted with 3-inch intensive, having less O&M expenditure diameter valves at the top and bottom of and less expensive service charges are it and the sludge is extracted from the pit summarized in subsequent sections. through a PVC vacuum hose. If the sludge is dense, water is added to the pit/ septic tank so that it can be pumped out easily. After extraction is complete, the sludge is transported to a disposal site where it can be discharged by gravity feed or pump pressure via the fl exible hose.

30 Training manual on Faecal Sludge Management in rural areas • Four wheeler • Engine powers both the pump and equipment • Vertically mounted sludge collection tank • Easy to move • Models – MK I/II/III/IV/V

Capacity of Tank Pump Engine Max Speed 500-2000 L MEC2000/P 10hp/ Diesel 1-5 km/h Weight 950 Kg

7.1.3 Limitations 7.1.5 Maintenance and repairs • Diffi cult to extract sludge in solid form, • For regular cleaning of machine, collection especially when pit is deeper than 2m. and emptying of sludge, maintenance Pipe may get damaged while extracting and repair of the machinery, two trained sludge in dry condition. persons are required.

• Service cost of deploying Vacutug is • Less expenditure required for O&M; bit costlier than informal process of Only regular servicing of the equipment collecting/emptying faecal sludge is importantly required for extending the service life of machine • Vacutug is effective when operated for distance of 1-5 km between the point of • Required safety equipment – Helmet, extraction and location of disposal Hat, safety Glasses, Filter Mask, Apron, Gloves, Gumboots • Max speed of 5 km/h • Frequently required spares – Shovel 7.1.4 Cost* (to open manhole cover), Kerosene (to decrease odour in septic tanks and pit Model Capacity Rs. (in Lakh) latrines), Bleaching Powder (to disinfect Mark I and II 500 6.50 gumboots, gloves, hoses and the area around manhole), Bucket (to carry fresh Mark III 1900 13.00 water, collect sludge spill), Detergent Mark IV 700 9.76 and Soap (to clean gumboots, gloves and Mark IV 1000 9.76 hands)

Source: Faecal sludge management, system approach for operation and maintenance management, edited by Linda 7.2 Gulper Strande, Mariska Rontelta and Damir Brdjanovic.

Note: Actual market rates may vary from the above 7.2.1 Brief about the technology mentioned costs Manual De-sludging Hand Pump or Gulper *Rates may be vary for each technology is the only technology which is portable and reduces sludge contact as it consists

Training manual on Faecal Sludge Management in rural areas 31 7.2.4 Maintenance and repair • To increase the service life of equipment, the pump is required to be cleaned after every de-sludging process

• Blockages resulted by higher amount of non-biodegradable material have to be removed whenever required

• Required safety equipment – Gloves, Gumboots, Filter Mask, Hat, etc. of PVC riser pipe containing two stainless 7.2.5 Limitations non-return butterfl y valves. The Gulper is a • Time required for de-sludging is more recent invention which is inexpensive and easy to operate. Adverse health impact is • De-sludging is not effective/ doable when signifi cantly reduced as there are very less pit is very deep chances of sludge contact. The Gulper can • Solid choke the system and may be built using locally available material and lead to delays in operations manufacture techniques, even those which are common in low-income countries. This • Dried or thick sludge cannot be removed technology is very much suitable for densely populated and low-income areas. 7.3 Vacuum pump (E-VAC)

7.2.2 Description and working 7.3.1 Brief about the technology Principle Vacuum pumps are proven devices in de- The Gulper houses a piston pump on top sludging faecal sludge from pit latrines/ of a pipe with an outlet pipe on the side. septic tanks. Also known as E-VAC, the The upward movement of piston draws vacuum pumps have the benefi t of both the sludge through a valve into the cylinder vacuum suction and the swiftness of a small and then discharges during the downward system for effective operations in densely movement through a valve into the outlet. populated areas. During the de-sludging process, the sludge is accumulated in a bucket placed under the outlet pipe; whereas the bottom of the pipe is kept into the pit or septic tank. The pump is usually operated by 2-3 workers by way of pushing and pulling of lever on top of the Gulper.

7.2.3 Cost 7.3.2 Description and working principles Rs. 8000 - 10000/- E-VAC works on similar principles of other Manual Pit Emptying Technology (MAPET); however the fundamental difference is that

32 Training manual on Faecal Sludge Management in rural areas E-VACs are externally powered. The pump 7.3.5 Maintenance and repairs is operated by using a small motor which • Regular oiling and greasing of pump is is powered by onsite electricity or using a required portable generator. A belt drive combines the pump and motor which is then mounted • Equipment is required to be cleaned on a steel trolley. This kind of arrangement frequently in case of spillage and allows the housing of equipment and its overfl ows maintenance. There are two kinds of models • Valves should be cleaned for blockages available in the market. The fi rst one has a and external particles small tank attached to it whereas the second one has an arrangement of connecting pump to any container which is used for 7.4 Conventional vacuum collection and transporting of sludge. In both tankers the models, a fl oat valve is provided so as to prevent sludge from entering into the pump. 7.4.1 Brief about the technology Vacuum tankers comprise of a truck or 7.3.3 Limitations any other vehicle combined with tank and • The rate of emptying is low which restrict a vacuum pump. They use de-sludging the pump’s application only to the small technology having a high tank volume, faster containment systems (pits/ tanks) rate of emptying and high mobility.

• Can only be used for low viscous sludge

• There is a possibility of sludge spillage while transferring the containers

7.3.4 Cost

Sr. Details Cost 1 Suction Machine 4,90,000/- Mounted on Trolley. (Vacuum Emptier) 7.4.2 Description and working capacity 3000 ltr. principles 2 Suction Machine 4,11,700/- Mounted on Chassis. Vacuum tankers can empty pits or septic (Vacuum Emptier) tanks at much higher rate and carry large capacity 3000 ltr. quantity of sludge much faster. They are 3 Suction Machine 6,12,000/- generally fi tted with storage tanks having Mounted on Trolley. capacity of 2000-15000 litres. These tanks are (Vacuum Emptier) fi tted with vane pumps. The pump generates capacity 5000 ltr. a suction pressure inside the tank which 4 Suction Machine 5,60,000/- enables de-sludging of septic tanks through Mounted on Chassis. a hose connected at the outlet of the tank. (Vacuum Emptier) A suitable apparatus is provided to prevent capacity 5000 ltr. sludge getting into the vacuum pump and

Source: As per Rate Card of Ozone Envirotech, Moshi, Pune damaging it.

Training manual on Faecal Sludge Management in rural areas 33 In this type of technology, different types 7.4.3 Cost of vane pumps can be installed based on The capacity of the tank varied from the consideration of cost, capacity and 2000 litres to 15000 litres. The vehicle for liquid range within which the pump is most Vacuum Tankers needs to be assembled suitable to operate. The pump is effi cient locally. Similarly, the pump capacity also enough to suction out the settled thick varies depending on local situations and sludge at the bottom of septic tank very choice of the service provider. Therefore, the conveniently. This type of arrangement cost may vary depending upon the type of consists of three main components: constant vehicle, pump and storage capacity. air drag, air bleed and plug drag.

In general, following things should be noted 7.4.4 Limitations while using this technology and associated • Cannot access all types of roads, features: especially the smaller ones

• Total capacity of storage tank and the level • Diffi culties associated with choking of beyond which the sludge suction should trash at the inlet be tripped off. • Higher capital and operating expenditure • Point of extraction and its connecting road • Requires repairs which can cause long (length and width) in order to assess the delays possible diffi culty while accessing the desired point. 7.4.5 Maintenance and repairs • Scope of total quantity for de-sludging • Regularly check of level of oil in oil cooling • Financial provision tank, hydraulic tank, engine etc.

• Availability of skilled labour, etc. • Checking of coolant • Tire pressure, headlights, indicators to be checked weekly

34 Training manual on Faecal Sludge Management in rural areas CHAPTER 8 Treatment technologies for faecal sludge management

Training manual on Faecal Sludge Management in rural areas 35 8.1 Introduction These layers attributes to percolation and evaporation of percolated leachate when Due to growing concerns of adverse impact loaded with the sludge. About 50-80% of on environment and human health, scientifi c the sludge volume is evaporated or drained treatment of faecal sludge is very crucial. It is off as liquid. The remaining substance is also important to collect and treat the faecal then exposed to drying process. The sludge sludge from septic tank toilets to be further is treated by composting before it can used as soil conditioner. Presently, there are be disposed of or used as a nutrient-rich various globally adopted technologies and soil conditioner in agriculture. However, processes for treatment of faecal sludge. In the compost still contains pathogens and the State, sewage treatment plants are set requires further treatment. up for the treatment and disposal of faecal sludge at city level. However, this is not the sole alternative which is employed at every 8.2.2 Description and working location. In rural context, the treatment principles technologies should not only be evaluated on The technique of reducing the volume of the basis of cost, but also ease of operations sludge and prepare its reuse as fertiliser is and sustainable O&M. On the other hand, one of the simplest and oldest to dewater centralised treatment options- either at block sludge. Perforated pipes are located at the or cluster level should be explored thoroughly bottom of the drying bed to drain away the rather than just selecting an independent leachate. Layers of gravel and sand placed treatment facility for each village. on top of these pipes support the sludge and allow the liquid to permeate. Sludge is laid Based on the above mentioned aspects, on top of gravel beds and is naturally dried several treatment technologies applicable for 10-15 days, after which the moisture in rural context have been reviewed and content is reduced by about 60%. Sludge summarised as below: is applied in batches about once in a week • Unplanted drying bed in layers no more than 200 to 300 mm • Planted drying bed from both the sides. The solid fraction of sludge remains on the fi lter surface and is • Tiger Biofi lter dried by natural evaporation while the liquid • DEWATS fraction percolates. Once the sludge is

8.2 Unplanted drying bed 8.2.1 Brief about the drainage

technology 80cm layer This is a simple technology outlet drainage water, which includes permeable to treatment bed fi lled with a number of drainage layers.

36 Training manual on Faecal Sludge Management in rural areas dried, it is separated from the sand layer and 8.2.5 Limitations transported for further treatment whereas • Treated compost contains pathogens the leachate collected in drainage pipes is which still requires further treatment treated further before fi nal disposal. • Dried sludge is required to be removed 8.2.3 Design factors completely before applying the fresh sludge • Sludge is applied in a batch mode about once per week in layers of no more than • This treatment process requires larger 20 to 30cm.Around 100 to 200kg TS/m2 land area in addition to mechanical power of sludge can be applied on a drying bed, for regular de-sludging on an annual basis. The drying process • Additional sand is required to be added if usually takes 10 to 20 days the thickness of sand layer is reduced • Land requirement is 0.05 square metre per capita for a 10-day cycle 8.2.6 O&M requirements • Before fresh sludge is applied, dried • Trained personnel is required sludge needs to be de-sludged, and then • Dried sludge is required to be removed brought to a composting site generally after 10–15 days

• To improve drying and percolation, sludge • Top layer should be replaced when it gets application can alternate between two reduced or more beds. About 50–80% of the initial volume is removed by percolation, resulting in a total solid (TS) content of 8.3 Planted drying bed 20–70%, depending on the local weather 8..3.1 Brief about the technology conditions and climate In this technology, a shallow pond consisting • A splash plate has to be provided at the of several drainage layers are provided to inlet to prevent erosion of the sand layer separate the liquid fraction of faecal sludge and to allow for even distribution of the by way of percolation and evaporation. The sludge planted bed is advantageous as the fi lters • While designing unplanted drying beds, ensuring accessibility sludge plants ventilation pipe to people and trucks into the site for regular maintenance at all times wall

is absolutely essential screen grit chamber 8.2.4 Cost drainage layer outlet

Approximately Rs 1,675 per mesh gravel/rocks sand drainage pipe person3

3 Cost is calculated based on Wai and Sinnar plants

Training manual on Faecal Sludge Management in rural areas 37 do not need to be de-sludged after every • A general design for layering the bed is: drying cycle. This enables the application of ° 250 mm of coarse gravel (grain fresh sludge directly on top of the previously diameter of 20 mm); applied layer. Also, the plants and their roots help in maintaining the porosity of the fi lter. ° 250 mm of fi ne gravel (grain diameter Planted drying beds require de-sludging only of 5 mm); and once after 5-10 years. The removed sludge, ° 100 to 150 mm of sand (EAWAG/ being a nutrient-rich soil conditioner, can be SANDEC 2008). directly reused in agriculture. • Free space (1 m) should be left above the 8.3.2 Description and working top of the sand layer to account for about principles years of accumulation. The bed frame is typically made from • Ventilation pipes connected to the concrete or a plastic liner having bottom drainage system contribute to aerobic surfaces slightly sloped in order to facilitate conditions in the fi lter percolation and drainage. After that, general • Reeds, cattails, antelope grass and layering of the bed is constructed by laying papyrus are suitable plants, depending on 250 mm of coarse gravel, 250 mm of fi ne the climate. Local, non-invasive species gravel, and 150 mm of sand layer. Depending can be used if they grow in humid upon the local climatic conditions, suitable environments non-invasive plant species like Reeds, Cattails, Antelope grass and Papyrus are • Sludge should be applied in layers planted on top of the bed. between 75 to 100 mm thick and reapplied every 3 to 7 days, depending After preparing the bed as mentioned on the sludge characteristics, the above, the sludge is applied in layers having environment and operating constraints thickness of about 100 mm after every 3 to • Planted beds do not need de-sludging 7 days. Such layer is created by placing the before each new application as the sludge into a grit chamber constructed on root system of the plants maintains the one side of the bed. Solid fraction of sludge permeability is screened at the grit chamber whereas the liquid fraction fl ows down towards • Sludge application rates of 100 to 250 the planted bed through outlet. The plants kg/m2/year have been reported in warm enhance evaporation by transpiration. This tropical climates. In colder climates, such process is continued for about 5 to 10 years as northern Europe, rates up to 80 kg/m2/ and yields a nutrient-rich soil conditioner. year are typical • It is best to stop applying sludge one or 8.3.3 Design factors two years before removing it • The bed frame is usually made from concrete or a plastic liner with the bottom 8.3.4 Cost surfaces slightly sloped in order to Approximately Rs 1,700 per person4 facilitate percolation and drainage

4 Cost is calculated based on discussions with Wai and Sinnar plant technicians

38 Training manual on Faecal Sludge Management in rural areas 8.3.5 Limitations and hence there is no need to separately • The treatment process involves risk of manage the sludge unlike other faecal sludge health hazards and thus necessitates the treatment options. Apart from this, a nutrient- use of protective wear, gumboots and rich soil conditioner is generated which can gloves by workers be further used for agriculture and gardening.

• In dry climatic areas, low moisture content 8.4.2 Description and working creates harsh conditions for plant growth principles • Due to odour issues, the bed should be Tiger Bio fi lter is divided into two main parts: located at a distance from the human one is fi lter media and second is bio media. settlements In fi lter media, good quality of aggregates, • Percolates from sludge drying beds contain sand etc. are used as simultaneous layers. pathogens and need to be further treated These layers are used for supporting the bio media and fi ltering water. Bio media layer 8.3.6 O&M requirements consists of earthworms, bacterial culture and its ecosystem as well as bio culture. • Skilled labours are not required as planted beds are easy to operate The impurities in wastewater are trapped • Maintenance activities should ensure that inside these layers and fi ltered water trees do not grow in the bed as roots can percolates and gets collected in the storage damage the lining of the drying bed tank located at the outlet. Waste which is trapped inside the layers is converted • During the fi rst growing season it is into compost with the help of worms and important to remove weeds that can bacterial culture. This process is followed on hinder the growth of planted vegetation daily basis which in turn eliminates the odour • Distribution pipes should be cleaned at generation and mosquito/fl ies breeding. least once a year 8.4.3 Technology specifi cations: 8.4 Tiger biofi lter Tiger toilet system requires a single Pit incorporating vermifi lter, specifi cations of 8.4.1 Brief about the technology which have been presented below. Tiger Biofi lter technology is based on the process Tank of vermi fi ltration. In this technology, various types of fi lter media and bio media Pour space/ are used together with passive aeration worms and bacterial culture, which contributes to easy U-bend to Worm Bedding prevent smells layer And Worms and natural purifi cation of and fl ies wastewater. The percentage bed of water recovery is about 90-95%. During the process, Effl uent infi ltrates soil no sludge is generated

Training manual on Faecal Sludge Management in rural areas 39 Component Specifi cations Basic functioning Schematic of a Vermifi lter Unit

RCC Cover Single Pit Inner diameter- 1 m Rapid decomposition Waste in RCC Ring of excreta in Media Depth - 1.2 m the pit due to a Drainage specially designed Layer Vermifi lter. No solid Effl uent Out accumulation.

8.4.4 Benefi ts • No smells as the system is aerobic Following are the benefi ts of the technology- • No risk of mosquito breeding

• No need of handling sludge as faecal 8.4.5 Cost sludge is rapidly converted Into vermicompost Approximately Rs 850-900 per person

• Safer and easier emptying as 8.4.6 Limitations vermicompost is stable, soil-like material and can be readily removed • Wastewater containing chemical impurities and solids requires pre- • No energy requirements as it is a passive processing Process • The compost generated by the process • Cheap to construct and run, the contains pathogens and thus need to be Vermifi lter is not expensive like the other handled properly technologies in the market and does not require special tanks to be constricted. 8.4.7 O&M requirements It can be easily installed in existing pit design. Dosage of media is required only Generally, the compost should be removed once to get the system running. once in 6-8 months

• Compact with a smaller footprint than a Proper action would be required if the septic tank or a twin pit latrine content of grit is more

• Little or no maintenance needed

40 Training manual on Faecal Sludge Management in rural areas CHAPTER 9 Planning, implementation and monitoring of FSM

Training manual on Faecal Sludge Management in rural areas 41 The urban systems for FSM are not suitable 9.1.1 Baseline survey and for rural areas due to various reasons like validation based on FSM inadequate fi nance, insuffi cient availability of value chain skilled human resources, scale of operations, The fi rst step in the planning process is etc. Therefore, in rural areas, it will be more to carry out a baseline survey of the area appropriate to create systems for FSM at where FSM systems need to be set up. Area block or cluster level. Following section specifi c policy for faecal sludge management presents the methodology of planning for may be decided based on local conditions FSM. and specifi c issues.

9.1 Methodology of 9.1.2 Finalization of project area planning for FSM As discussed above, it will be appropriate to Various steps need to be followed for set up FSM systems at block or cluster level. effective planning of FSM in rural areas. The A cluster of 10-15 GPs can be fi nalized for key steps in planning are presented in the FSM based on digital maps procured from adjacent schematic and described below in government or online web based services. detail. Connectivity between the GPs, location of the GPs and no. of septic tanks can be the criteria for selection. Baseline survey and validation 9.1.3 Organization of FGD at Finalization of project area cluster level A meeting of Sarpanch/ gramsevaks from the Organization of FGD selected GPs may be organized at cluster/ block level. During this meeting, fi rstly the status of sanitation and faecal sludge Household Survey management in the block based on type of toilets may be discussed. Then, information Collection of secondary data about the selected villages may be provided and clarity may be brought about the Analysis of collected information activities to be done at various levels of the FSM value chain. Support requirements from the GPs may be discussed in the end. Preparation of budget 9.1.4 Household survey Implementation After the FGD, household survey may be conducted in the selected GPs to collect data Monitoring on type of toilets, technical appropriateness of the toilets, etc. A draft tool for the Operation, maintenance and repairs household survey is presented as annex.

42 Training manual on Faecal Sludge Management in rural areas 9.1.5 Collection of secondary data In case of non-availability of the treatment plant, setting up of a new treatment plant Next step is to collect information about the will be proposed. Location of the plant existing FSM service providers in the area. will be fi nalized in such a way that the Information of FSM service providers will distance between the desludging and be collected based on the steps in value treatment locations will be minimal. This chain, type of technology used, whether will save the cost of transportation. Other the providers are private or government important criteria for location fi nalization empanelled, cost of services, etc. will be availability of electricity connection, distance from the settlement (so as to 9.1.6 Analysis of collected save the people from foul smell), density of information population, type of soil, characteristics of the A. Analysis of the household survey data treated water, and cost of O&M.

Based on the data collected at various stages of planning, the number of households from 9.1.7 Preparation of budget the selected GPs which require desludging After collecting the required data of services will be fi nalized. Additionally, a service providers at various stages of FSM list of toilets with technically inappropriate service value chain, communication will construction or tanks without lids will be be established with the service providers listed and submitted to the GP. The GP will for empanelment/ procurement. If such be asked to provide instructions to the facilities are not available at cluster/ block households regarding fi xing lids on the tanks. level, contractors from outside may be procured. Innovative, low cost technologies B. Analysis of the pit empting and may be selected which will require less transportation services skilled human resources. Based on the Once the number of toilets requiring above, a budget for setting up FSM system desludging services is fi nalized, the capacity will be prepared and get approved from the of the selected technology would be concerned department. decided. An overview of how many service providers exist and are ready to provide 9.1.8 Resource mobilization services would be undertaken. Additionally, Resources will need to be mobilized for the a timetable, frequency and route for following three types of activities regarding desludging will be decided. FSM. C. Analysis of the treatment services A. Pit emptying and transportation Treatment of the faecal sludge is very Two options can be considered for important. First of all the volume of faecal undertaking these activities- one, to set up sludge to be treated per day would require pit emptying and transportation systems to be calculated. Based on this data, in a big GP/ census town in the cluster capacity of the available treatment plant and provide services through this GP; and will be reviewed. Communication with the second, to motivate SHGs for providing these concerned government department will be services. In case of the fi rst option, funds done to avail the facilities. from 14th fi nance commission grants from

Training manual on Faecal Sludge Management in rural areas 43 all selected GPs in cluster can be pooled as sanitation tax on the villagers. Simultaneously a resource pool for FSM services. In case desludging and transportation of faecal of the second option, SHGs can be provided sludge can be charged for revenue generation. fi nancial support through Maharashtra State Rural Livelihood Mission (MSRLM), 9.1.9 Human resource management MAVIM, CSR, bank loans, etc. However, The human resources required for various for its operationalization, there needs to steps of FSM are presented in the be effective convergence between various schematic. In case skilled human resources government departments at block and district are not available, unskilled HR may be trained level. The SHGs will also require technical through various training programs. assistance in the beginning.

B. Setting up of treatment plant Drivers As mentioned above, funds from 14th Skilled labour fi nance commission grants from all selected GPs in the cluster can be pooled to form Supervisors resource pool for setting up of treatment Unskilled labour plant. Apart from this, 14th FC funds can be used for preparation of DPRs. If the treatment plant is to be set up by the GPs, Emptying, the cost will be distributed between the GPs. transportation It is important for the GPs to have trust in and treatment each other to arrive at unanimous decision.

C. Operation and maintenance 9.1.10 Monitoring Regular operation and maintenance of the FSM systems need sustained availability Monitoring of any process is important for of required funds. Few cost heads like effective implementation of the steps and salaries, electricity bills, cleaning material and ensuring the expected outcomes. Following chemical, fuel, periodic repairs, etc. need table presents the monitoring framework at regular funds. The participant GPs can levy various steps of FSM.

No Step Monitoring activities 1 Pit emptying Adhering to the security norms Following Manual Scavenging Act 2013. Collection of pit emptying tax 2 Transportation Regular repairs of vehicles. Application of GPS units in all vehicles and monitor their routes Discharging the faecal sludge safely in the treatment plant

44 Training manual on Faecal Sludge Management in rural areas 3 Treatment Discharging the faecal sludge in the treatment plant as per its capacity Ensuring that the treated byproducts are of the specifi ed characteristics Regular pumping out of dried sludge 4 Use Following Water pollution and environment security act Testing the quality of manure Charging appropriate price for the manure

Satisfaction of consumer is the motto of consumers. Various methods like complaint any service provider. However, considering register kept at the GP or using software various types of consumers of FSM services, applications can be considered for setting it is not possible to get service related up effi cient complaint redressal systems. A feedback from every consumer. A complaint supervisor may be appointed for monitoring redressal system is therefore necessary the complaint redressal mechanism. to resolve any complaint/ grievance of the

Complaint Complaint Supervisor's Review by the registration review offi cial

Training manual on Faecal Sludge Management in rural areas 45 ANNEX 1 Household survey format

No Question Option 1 Format no. 2 Details of the habitation 1 Gaothan 2 Habitation 3 Name of the habitation Name

4 Ward no. 1 No.

5 Type of property 1 Household 2 Institutional 3 Business 4 Other (details) 6 Type of house (if option 1 ticked in 1 Bungalow question no. 5) 2 Row house 3Hut 4 Temporary structure 5 Permanent structure 6 Other ______7 Type of institute (if option 2 ticked in 1 Hospital question no. 5) 2PHC 3 School/ college

4 Religious institute 5 Other ______

46 Training manual on Faecal Sludge Management in rural areas No Question Option 8 Type of business (if option 3 ticked in 1 Industry question no. 5) 2 Shop 3 Hotel/ lodging 4 Other ______

9 Name of head of the family 1 ______10 Contact no 11 Is there and individual toilet in your house? 1 Yes 2No 12 If yes, no. of toilets Number______13 No. Of users In case of business, mention Children (Below 6 years ) ______approximate number of users) Men ______Women ______14 Type of toilet 1 Septic tank 3 Single pit 6 Other (Mention) 15 In case of septic tanks, please mention no. 11 of tanks 22 33 4 4 Don’t know 16 Use of toilet (Individual / shared / public) 1 Individual 2 Public 17 What is the shape of septic tank? 1 Square 2 Round 3 Don’t know 4 Rectangle 18 Dimensions of the septic tank 1 Length 2 Breadth 3 Height 19 Where is the septage discharged 1 Soak pit 2 Open gutter 3 Closed gutter 4 Open space 5 Other ------6 Don’t know

Training manual on Faecal Sludge Management in rural areas 47 No Question Option 20 When was the tank emptied 1 6 months ago 2 6 – 12 months ago 3 12 – 24 months ago 4 24 – 36 months ago 5 More than 36 months ago 6 Never emptied 7 Don’t know 21 Reason behind empting the septic tank 1 Toilet blocked 2 Water leakage from chamber/ lid 3 Foul smell 4 Other ______5 Don’t know 22 Problems faced during emptying 1 High distance for transportation 2 Narrow road 3 Did you need to break the fl ooring for emptying septic tank? 4 Did you need to break the cement lid for emptying septic tank? 5 Did you face problems in identifying the location of septic tank? 6 Was there foul smell during for emptying septic tank? 7 Any other issue in emptying the septic tank? 8 No problems faced

9 Others 10 Don’t know

23 Was the suction truck easily available for 1Yes emptying the septic tank? 2No

48 Training manual on Faecal Sludge Management in rural areas ANNEX 2 Report template

1. Background 6. Implementation of the proposed activities 2. About the project area • Process for purchasing desludging and • Name of the fi nalized cluster, details, transportation equipments centre of the cluster, distance between • Administration of the treatment plant GPs, etc. • Capacity building • Profi le of the participant GPs- population, number of households, • IEC details of toilet coverage (households • Others with and without toilets, types of toilets, etc.) 7. Operation and maintenance

3. Process for report development • Systems • Secondary data collection • Collection of service tax • Focus group discussion • Planning • Study of the FSM value chain • Work methodology

• Household survey 8. Monitoring • Data validation • Methodology, levels and frequency • Documentation

4. Status of faecal sludge management in the project area • Type and quality of toilets • Desludging • Transportation • End treatment • Use

5. Proposed activities for faecal sludge management • Desludging • Transportation • End treatment • Use

Training manual on Faecal Sludge Management in rural areas 49 List of references

1. Book on Solid Liquid Resource 9. Advisory Note on SEPTAGE Management – Faecal Sludge MANAGEMENT IN URBAN INDIA, Management, Ministry of Drinking Water Ministry of Urban Development and Sanitation, Government of India. Government of India.

2. Faecal Sludge Management (FSM), 10. Compendium of Innovative Technologies Sandec Training Tool 1.0 – Module 5 by December 2016 by Indian Institute for Department of Water and Sanitation in human settlement, DEWAT association, Developing Countries Kestone.

3. Methods and Means for Collection and 11. Faecal Sludge Management: Wadhwan Transport of Faecal Sludge by Georges City by Alka Palrecha,Mukta Ramola, Mikhael, David M. Robbins, James E. Vipashyana Priyadarshini. Ramsay and Mbaye Mbéguéré 12. Compendium of Sanitation Systems 4. National Policy on Faecal Sludge and and Technologies, 2nd revised edition, Septage Management (FSSM), Ministry Elizabeth Tilley, Lukas Ulrich, Christoph of Urban Development, Government of Lüthi,Philippe Reymond and Christian India. Zurbrügg.

5. Primer on Faecal Sludge and Septage 13. Note on Steps for Emptying of Twin Leach Management, Ministry of Urban Pit Toilet by UNICEF Mumbai Development Government of India. 14. An Occasional Report On ODF 6. Septage Management, A Practitioner’s Sustainability and Water For Sanitation Guide, Urban India's journey beyond in Maharashtra, Prepared By SIGMA ODF, Ministry of Urban Development, Foundation with Support of UNICEF Government of India. Maharashtra

7. Guidelines for Septage Management 15. A report on Status Of ODF Sustainability in Maharashtra, Swachh Maharashtra In The Nagar Panchayats Of Maharashtra Mission (Urban) Urban Development by SIGMA Foundation Department, Government of Maharashtra

8. Some concepts and defi nitions, Statistics department.

50 Training manual on Faecal Sludge Management in rural areas UNITED Nations Children's Fund (UNICEF), August 2018

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