Depending on the treatment type and quality, digested or stabilised sludge can be applied to public or private lands for landscaping or agriculture.Mixture of solids and liquids, containing mostly excreta and water, in combination with sand, grit, metals, trash and/or various chemical compounds. A distinction can be made between faecal sludge and wastewater sludge. Faecal sludge comes from on-site sanitation technologies, i.e. it has not been transported through a sewer. It can be raw or partially digested, a slurry or semisolid, and results from the collection and storage/treatment of excreta or blackwater, with or without greywater. Wastewater sludge (also referred to as sewage sludge) originates from sewer-based wastewater collection and (semi-)centralised treatment processes. The sludge composition will determine the type of treatment that is required and the end-use possibilities.Describes technologies for on-site collection, storage, and sometimes (pre-) treatment of the products generated at the user interface. The treatment provided by these technologies is often a function of storage and is usually passive (i.e. requires no energy input), except a few emerging technologies where additives are needed. Thus, products that are ‘treated’ by these technologies often require subsequent treatment before use and/or disposal. In the technology overview graphic, this functional group is subdivided into the two subgroups: “Collection/Storage” and “(Pre-)Treatment”. This allows a further classification for each of the listed technologies with regard to their function: collection and storage, (pre-) treatment only or both.Refers to the methods through which products are returned to the environment, either as useful resources or reduced-risk materials. Some products can also be cycled back into a system (e.g. by using treated greywater for flushing).A functional group is a grouping of technologies that have similar functions. The compendium proposes five different functional groups from which technologies can be chosen to build a sanitation system:
User interface (U), Collection and Storage/Treatment (S), Conveyance (C), (Semi-) Centralised Treatment (T), Use and/or Disposal (U).
A sanitation system is a multi-step process in which sanitation products such as human excreta and wastewater are managed from the point of generation to the point of use or ultimate disposal. It is a context-specific series of technologies and services for the management of these sanitation products, i.e. for their collection, containment, transport, treatment, transformation, use or disposal. A sanitation system comprises functional groups of technologies that can be selected according to context. By selecting technologies from each applicable functional group, considering the incoming and outgoing products, and the suitability of the technologies in a particular context, a logical, modular sanitation system can be designed. A sanitation system also includes the management and operation and maintenance (O & M) required to ensure that the system functions safely and sustainably. The utilisation of products derived from a sanitation system.
A sanitation system in which excreta and wastewater are collected and stored or treated on the plot where they are generated.
The means of safely collecting and hygienically disposing of excreta and liquid
wastes for the protection of public health and the preservation of the quality of public water bodies and, more generally, of the environment.

Waste matter that is transported through the sewer.
An open channel or closed pipe used to convey sewage. See C.3 and C.4
Used water from any combination of domestic, industrial, commercial or agricultural activities, surface runoff/stormwater, and any sewer inflow/infiltration.

Treated sludge (e.g. from Planted Drying Beds: T.10 ) can be used in agriculture, home gardening, forestry, sod and turf growing, landscaping, parks, golf courses, mine reclamation, as a dump cover, or for erosion control. Although sludge has lower nutrient levels than commercial fertilisers (for nitrogen, phosphorus and potassium), it can replace a part of the fertiliser need. Additionally, treated sludge has been found to have some properties superior to those of fertilisers, such as bulking and water retention properties, and the slow, steady release of nutrients.

Design Considerations

Solids are spread on the ground surface using conventional manure spreaders, tank trucks or specially designed vehicles. Liquid sludge (e.g. from anaerobic reactors) can be sprayed onto or injected into the ground. The user must consider the level of treatment of the sludge and the type of use to determine how and when to best apply the sludge. Application rates and usage of sludge should account for the presence of pathogens and contaminants, and the quantity of nutrients available so that it is used at a sustainable and agronomic rate. On-farm Co-Composting T.11 can be used to achieve improved treatment and increase the volume of soil conditioner.

Materials

A vehicle to transport and equipment to spread the sludge are required. This may include conventional manure spreaders, tank trucks or specially designed vehicles.

Applicability

The World Health Organization (WHO) Guidelines for the Safe Use of Wastewater, Excreta and Greywater should be consulted regarding the type of crops and conditions for the safe use of sludge. Depending on the source, sludge can serve as a source of nutrients. The Application of Sludge on land may be less expensive than disposal. Application of Sludge can be considered during the stabilisation and recovery phases of an emergency, when a functional sludge treatment system is in place.

Operation and Maintenance

The equipment used for applying sludge requires maintenance. The amount and rate of sludge application should be monitored to prevent nutrient overloading of both the soil and water bodies.

Health and Safety

Even after treatment, sludge is rarely pathogen-free. The WHO Guidelines for the Safe Use of Wastewater, Excreta and Greywater should be consulted regarding the security measures needed to protect public and environmental health. Workers should wear personal protective equipment (e.g. clothing, boots, masks). Although sludge is sometimes criticised for containing potentially high levels of heavy metals or other contaminants, faecal sludge from pits and tanks should not have any chemical inputs and is, therefore, not a high-risk source of heavy metal contamination. Sludge that originates from large-scale wastewater treatment plants is more likely to be contaminated as it may receive industrial chemicals, as well as surface water run-off, which can contain hydrocarbons and metals. Sludge from domestic wastewater and on-site sanitation systems can be considered safer as it is not contaminated by industrial waste.

Costs

The main cost to consider is the potential transport of the sludge to the fields. The Application of Sludge contributes to revenue generation by increasing agricultural yields. The application of sludge can save money if it replaces commercial fertilisers.

Social Considerations

The greatest barrier to the use of sludge is, generally, social acceptance. However, even when farmers or local industries do not accept sludge, it can still be useful for municipal projects and can provide significant savings (e.g. mine reclamation). Depending on the source of the sludge and the treatment method, sludge can be treated to a level where it is generally safe and no longer generates significant odour or vector problems. Following appropriate safety and application regulations is important. The WHO guidelines should be consulted for more detailed information.