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Guide to Ship Sanitation. 3rd edition. Geneva: World Health Organization; 2011.
6.1. Background
This chapter deals with the management of solid waste (e.g. garbage) and liquid waste (e.g. sewage and greywater) on board ship, including their storage and safe disposal.
6.1.1. Health risks associated with wastes on ships
Unsafe management and disposal of ship wastes can readily lead to adverse health consequences. Humans can become exposed directly, both on ship and at port, as a result of contact with waste that is not being managed in a safe manner. Exposure can also occur via the environmental transfer of disease-causing organisms or harmful substances due to unsafe disposal. However, waste can be managed and disposed of in ways that prevent harm from occurring.
Waste can contain hazardous microbial, chemical or physical agents. For example, sharp objects are in themselves dangerous and may harbour infectious agents. Used syringes are a good example and can transmit disease-causing agents, such as hepatitis C virus and human immunodeficiency virus.
Risks of harm arising as a result of improperly managed ship waste are increasing with the greater number of ships in service and the increase in habitation in port areas. Waste streams on ships include sewage, greywater and garbage, as well as effluent from oil/water separators, cooling water, boiler and steam generator blow-down, medical wastes (e.g. health-care wastes, laboratory wastes and veterinary-care wastes), industrial wastewater (e.g. from photo processing) and hazardous waste (radioactive, chemical and biological wastes and unwanted pharmaceuticals).
Food wastes and refuse readily attract rodents, flies and cockroaches, for example, which are reservoirs and vectors of etiological agents of many diseases (see chapter 7).
Restrictions on depositing hazardous wastes into water bodies mean that ships need to capture and retain those wastes on board for periods of time. The process of packaging and storing hazardous wastes is in itself hazardous to the crew, and the storage of hazardous wastes leads to the risk of harm arising should spills or leaks occur. Waste needs to be appropriately disposed of in accordance with the rules and regulations applicable at the point of disposal.
6.1.2. Standards
Waste management from ships is covered in the IHR 2005 and in more detail in the International Convention for the Prevention of Pollution from Ships (MARPOL 73/78, as amended).1 MARPOL was adopted by the International Conference on Marine Pollution in 1973 and has been subject to numerous amendments as it is updated, including the 1978 protocol and amendments collated into a consolidated version in 2002. Regulations covering the various sources of ship-generated pollution are contained in the six annexes of the Convention:
- Annex I. Regulations for the Prevention of Pollution by Oil;
- Annex II. Regulations for the Control of Pollution by Noxious Liquid Substances in Bulk;
- Annex III. Prevention of Pollution by Harmful Substances Carried by Sea in Packaged Form;
- Annex IV. Prevention of Pollution by Sewage from Ships (date of entry into force, 27 September 2003);
- Annex V. Prevention of Pollution by Garbage from Ships;
- Annex VI. Prevention of Air Pollution from Ships (adopted September 1997).
Medical waste requires special management. Specifically, details of health-care waste management can be found at http://www.healthcarewaste.org/en/115_overview.html and in the Guidelines for safe disposal of unwanted pharmaceuticals in and after emergencies (WHO, 1999).
6.2. Guidelines
This section provides user-targeted information and guidance, identifying responsibilities and providing examples of practices that can control risks. Three specific guidelines (situations to aim for and maintain) are presented, each of which is accompanied by a set of indicators (measures for whether the guidelines are met) and guidance notes (advice on applying the guidelines and indicators in practice, highlighting the most important aspects that need to be considered when setting priorities for action).
Outbreaks and harm associated with waste have been linked to poor storage and disposal practices. Once generated, stored waste becomes a potential source of harm. Therefore, the first disease prevention strategy should be to minimize the amount of hazardous waste generated as far as practicable. It is also necessary to ensure that the systems for collecting and storing waste are adequate given the extent and nature of waste generated on board ship.
In some cases, waste-management treatment systems have failed to perform as required, resulting in unsafe situations. Therefore, reliance should not be placed on treatment and management systems alone. Multiple waste-management barriers should be actively maintained, including:
- considering how waste is generated on board, and choosing activities and practices that produce the least hazardous waste in the first place;
- matching waste-management treatment facilities to their required capacities;
- maintaining sound practices in collecting and storing waste.
Staff at ports and ship crews need to be adequately trained in the protection of the environment, safe operation and relevant legislation. People involved in the collection, handling and disposal of wastes need to be trained in the relevant legislation and the risks posed by wastes.
6.2.1. Guideline 6.1: Sewage and greywater management
Indicators for Guideline 6.1
- Grease traps are used to manage greasy liquid wastes.
Guidance notes for Guideline 6.1
1. Disposal of sewage and liquid wastes
Ships are not generally permitted to discharge sewage or any other liquid containing contaminating or toxic wastes within an area from which a water supply is drawn or in any area restricted for the discharge of wastes by any national or local authority. Overboard discharge in harbours, ports and coastal waters is subject to the regulations of the governing authorities in these areas. Sewage, food particles, putrescible matter and toxic substances must not be discharged to the bilge.
Any country may provide special barges for the receipt of these wastes or shore connections that input to the sewer system. Where the shore servicing area or barge does not provide a hose or connections to receive these wastes, the ship must provide a special hose and connections large enough to allow rapid discharge of wastes. This hose must be durable and impervious, have a smooth interior surface, be of a size different from that of the potable water hose or other water-filling hoses and be labelled “FOR WASTE DISCHARGE ONLY”. After use, the hose must be cleaned by thorough flushing with clear water and stored in a convenient place labelled “WASTE DISCHARGE HOSE”.
The prohibition against discharge of wastes near a water supply intake or in any body of water where measures for the prevention and control of pollution are in force will require the provision of retention tanks or sewage-treatment equipment on board.
Systems need to be designed and constructed so as not to leak wastes and need to be amenable to ready inspection to check for leaks or bursts. Approved backflow preventers (vacuum breakers) or acceptable air gaps must be installed in the water supply lines to the grinders. All piping should be colour coded and labelled (e.g. according to ISO 14726:2006) at least every 5 m to avoid confusion and possible cross-connection to potable water. Drain, soil and waste pipes need to be maintained frequently to prevent clogging and the backflow of sewage, greywater or contaminated wastes into the fixtures and spaces served by the collection system.
2. Grease traps
All galley wastes, exclusive of ground refuse, that may contain grease must be made to flow through grease interceptors (grease traps) to a retaining box before discharge or treatment on board ship. The design of the interceptors may need to be approved by the appropriate authority of the country of registration. The grease collected may be disposed of by incineration, by storage for shore disposal or by overboard discharge on the high seas. Overboard discharge may occur after a suitable separation distance with the closest line of land, such as 3 nautical miles (12 nautical miles in territorial sea), in compliance with other national rules.
3. Treatment
All ships must be equipped with facilities for managing wastes from toilets and urinals, hospital facilities and medical-care areas, and food refuse grinders. These facilities include treatment systems and/or safe holding tanks, properly equipped with pumps and piping. Wastes from safe holding tanks may be discharged to port connections or to special barges or trucks. The design of treatment systems and waste-holding tanks needs to be based on a suitable volume (e.g. 114 litres of liquid waste per capita per day) and may need to be approved by the appropriate authority of the country of registration.
For ships where the normal wastewater flow to be treated is quite large, exceeding 4750 litres per day, treatment must be designed to produce effluent of a suitable quality, such as biochemical oxygen demand of 50 mg/l or less, a suspended solids content of 150 mg/l or less and a coliform count of 1000 or less per 100 ml.
Excess sludge must be stored for appropriate disposal to land-based facilities or when on the high seas. For ships with a daily flow of wastewater to be treated that is quite small, less than 4750 litres, treatment may be limited to passing the wastes through grinders, followed by disinfection to produce an effluent with a coliform count of 1000 or less per 100 ml.
Chlorination, or an equally effective method of disinfection, may need to be installed, as recommended by the manufacturer, to produce an effluent meeting the coliform requirements set by the relevant authorities.
6.2.2. Guideline 6.2: Solid waste management
Guideline 6.2—Solid waste is safely treated and disposed of.
Indicators for Guideline 6.2
- Garbage is safely stored in appropriately designed facilities.
- Excess sludge is stored safely prior to appropriate disposal.
Guidance notes for Guideline 6.2
1. Facilities for waste storage
To prevent corrosion, the interiors of food and garbage lifts may need to be constructed of stainless steel and meet the same standards required for the storage, preparation and service of food. Decks need to be constructed of a durable, non-absorbent, non-corroding material and have a suitable internal cove, at least 10 mm along all sides. Bulkhead-mounted air vents must be positioned in the upper portion of the panels or in the deckhead. To help with cleaning and removal of spills, a drain at the bottom of all lift shafts must be provided, including the provision of platform lifts and dumbwaiters.
If used to transport waste, the interiors of dumbwaiters must be readily cleanable and constructed of stainless steel or similar and meet the same standards as other food service areas. The bottom of the dumbwaiter should include a suitable cover.
Garbage chutes, if installed, need to be constructed of stainless steel or similar and have an automatic cleaning system.
In waste-management equipment wash rooms, bulkheads, deckheads and decks need to be constructed to meet the same standards required for the storage, preparation and service of food. A bulkhead-mounted pressure washing system could be provided with a deck sink and drain. An enclosed automatic equipment washing machine or room may be used in place of the pressure washing system and deck sink. Adequate ventilation is required for extraction of steam and heat.
The garbage storage room should be well ventilated, and the temperature and humidity controlled. A sealed, refrigerated space must be used for storing wet garbage. The space needs to meet the same criteria for cold storage facilities for food. The room must be of adequate size to hold unprocessed waste for the longest expected period when off-loading of waste is not possible and must be separated from all food preparation and storage areas.
In all the garbage holding and processing facilities, there need to be easily accessible hand-washing stations with potable hot and cold water, hose connections and a sufficient number of deck drains to prevent any pooling of water. The sorting tables in garbage processing areas must be constructed from stainless steel or similar and have coved corners and rounded edges. Deck coaming, if provided, needs to be adequate, at least 8 cm, and coved. If the tables have drains, they should be directed to the deck drain, which requires a strainer. A storage locker must be provided for cleaning materials to keep them away from foods. Adequate lighting, at least 220 lux, is required at work-surface levels, and light fixtures need to be recessed or fitted with stainless-steel or similar guards to prevent breakage.
To facilitate storage, tops and bottoms must be removed from all empty metal containers or containers with metal ends, and the remaining parts flattened. Containers of paper, wood, plastic and similar materials should also be flattened for convenient space-saving storage. Dry refuse must be stored in tightly covered bins or in closed compartments, protected against weather, wash and the entry of rodents and vermin. The containers must be thoroughly cleaned after emptying and treated with insecticides or pesticides, if necessary, to discourage harbourage of rodents and vermin.
2. Excess sludge
Excess sludge is typically stored appropriately for appropriate disposal to land-based facilities or when on the high seas.
6.2.3. Guideline 6.3: Health-care and pharmaceutical waste management
Guideline 6.3—Health-care and pharmaceutical waste is safely treated and disposed of.
Indicator for Guideline 6.3
- Health-care and pharmaceutical waste is safely treated and disposed of.
Guidance notes for Guideline 6.3
Pharmaceutical wastes produced on board must be managed appropriately in order to prevent harm to the environment and human health. Specific considerations for pharmaceutical wastes include avoiding disposal of non-biodegradable products or products that might harm bacteria involved in wastewater treatment into the sewage system and avoiding burning pharmaceuticals at low temperatures or in open containers.
Health-care waste is any waste generated during patient diagnosis, treatment or immunization. Health-care waste is of two categories: infectious and non-infectious. Infectious health-care waste is liquid or solid waste that contains pathogens in sufficient numbers and with sufficient virulence to cause infectious disease in susceptible hosts exposed to the waste. Non-infectious health-care waste includes disposable health-care supplies and materials that do not fall into the category of infectious health-care waste.
All ships should be equipped with facilities for treating and/or safely storing health-care wastes. Infectious waste must be safely stored or sterilized (e.g. by steam) and suitably packaged for ultimate disposal ashore. Health-care waste should be clearly labelled. Ships properly equipped may incinerate paper- and cloth-based health-care waste, but not plastic and wet materials. Sharps must be collected in plastic autoclavable sharps containers and retained on board for ultimate disposal ashore. Unused sharps must be disposed of ashore in the same manner as health-care waste.
Liquid health-care wastes may be disposed of by discharging them into the sewage system. Non-infectious health-care waste may be disposed of as garbage if it does not require steam sterilizing or special handling. Staff dealing with health-care wastes must be immunized against hepatitis B virus.
Note the WHO International medical guide for ships (WHO, 2007), and note that some country medical guides are also available.
Footnotes
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- Waste management and disposal - Guide to Ship SanitationWaste management and disposal - Guide to Ship Sanitation
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