Hello. I am Kripa Thapa Magar, Public Health Professional. This slide was prepared to train CMAs and health assistant on HCWM by compiling information from different resources.
2. Training content
тАв Standard of health institution in sanitation
тАв Health care waste management
тАв General waste management
тАв Sanitation
3. Presentation outline
тАв Regulations and standard
тАв Organizational bodies
тАв Health care waste introduction
тАв Health care waste management
тАв Waste management in the context of COVID-19
4. Expected outcome
тАв Regulations and standard underlying HCWM
тАв Risks of improper HCWM to understand the
importance of proper HCWM
тАв Waste segregation
тАв Waste treatment methods according to the type
of waste in low resource setting context
тАв Sharps waste management
5. Regulations and Standard
тАв Constitution of Nepal, 2072
тАв National Health Policy, 2076
тАв Public Health Service Act, 2075
тАв Solid Waste Management Act,
2068
тАв Local Level Health Program
Implementation Guideline
тАв 15th Five Year Development Plan
(2019/20-2023/24)
тАв National Health Sector Strategy
Implementation Plan 2016-2021
тАв Guideline for Health Institutions
Establishment, Operation and
Upgrade Standard, 2071
тАв Minimum Service Standard
тАв Health Care Waste Management
Guideline 2014
14. 15th Five Year Development Plan
Strategy 6: Management and regulation of cooperation and
collaboration between public-private and non-government
sector
Action Plan 6: Regulatory mechanism will be developed
and province and local government will be made
responsible for management of health care waste.
15. National Health Sector Strategy
Implementation Plan 2016-2021
Outcome 2 Improved quality of care at point-of-delivery
Output 3 Improved infection prevention and health care
waste management
21. Organizational bodies
Central level
DoHS яГа Management Division яГа Environmental
Health and Health Care Waste Management
Section
Provincial level
Provincial Health Directorate яГа Curative Service
and Disease Control Section
22. Health Care Waste (HCW) Introduction
The term health care waste includes
- all the waste generated within health care facilities
(HCF), research centers and laboratories
- related to medical procedures
In addition, it includes
- the same types of waste originating from minor and
scattered sources,
- including waste produced in the course of health care
undertaken in the home
- (e.g. home dialysis, self-administration of insulin)
- WHO, 2014
23. Sources of HCW
тАв Hospitals
тАв Primary Health Care Centers,
Health Post, Sub Health Post,
Immunization (EPI clinic), Primary
Health Care Outreach Clinic
(PHC/ORC)
тАв Clinics
тАв Laboratories and research centers
тАв Pharmacy and medical store
тАв Mortuary house
тАв Ambulance and emergency care
тАв Animal research
тАв Blood banks
тАв Home health care
тАв Quarantine and Isolation Centres
24. Categories of HCWs
Waste Categories Descriptions and Examples
Hazardous health care waste
Infectious waste
Waste contaminated with blood and other body fluids, such as
laboratory cultures, , blood bag, gauze contaminated with blood etc
Sharps waste
Used or unused sharps, e.g. needles, auto-disable syringes, syringes
with attached needles, infusion sets, scalpels, pipettes, knives, blades,
broken glass
Pathological waste Human tissues, organs, fluids, body parts, fetus, unused blood products
Pharmaceutical
waste, cytotoxic
waste
Pharmaceuticals that are expired or no longer needed, items
contaminated by or containing pharmaceuticals.
Cytotoxic waste containing substances with genotoxic properties, e.g.
waste containing cytostatic drug (often used in cancer therapy)
25. Categories of HCWs
Chemical waste
Waste containing chemical substances, e.g. laboratory reagents, film
developer, disinfectant that are expired or no longer needed, solvents,
waste with high content of heavy metals, e.g. batteries, broken
thermometer, blood pressure gauge
Radioactive waste
Waste containing radioactive substances, e.g. unused liquids from
radiotherapy or laboratory research, contaminated glassware,
packages or absorbent paper, urine and excreta from patients treated
or tested with unsealed radio nuclides, sealed sources
Non-hazardous or general health care waste
Waste that does not pose any specific biological, chemical,
radioactive or physical hazard
- WHO
29. Risk due to HCW
Harmful
characteristics of waste
Effects
Infectious agents
Disease infection such as AIDS, Hep B, Hep
C, cholera, Typhoid etc.
Sharps Injuries and infection
Chemical
Burning sensation, Headache, Poisoning,
dermatitis, conjunctivitis
Pharmaceutical Microbial drug resistance
Cytotoxic/Radioactive
chemical composition
Immediate - Headache, Vertigo, Nausea,
Vomiting
Chronic - Genetic mutation, Birth defect,
Cancer
As there is high risk of
transmission of infection due to
needle price injury, needle is the
most hazardous waste.
30. Health Care Waste Management
Health care waste management is a process that
ensures proper handling and disposal of health
care waste in a safe way.
Safe HCWM covers three aspects:
1. Unnecessary waste minimization
2. General and risk waste segregation
3. Waste treatment and disposal
31. Process of HCWM
1. Waste Minimization
2. Waste Segregation
3. Waste Collection and Interim Storage
4. Waste Transportation
5. Waste Central Storage
6. Waste Treatment and Disposal
33. Waste Minimization
It is the most preferred method
Approaches:
тЦл Source reduction
тЦл Waste segregation
тЦл Reverse logistics
тЦл Safe reuse
тЦл Recyclable products to vendor
34. Waste segregation
Segregation of waste at source is the key principle of
successful and safe waste minimization and is the most
important step for a successful management of HCW
Basic three-bin system
35. Before After
36
Segregation reduces the quantity of hazardous waste.
Waste handling, treatment and disposal methods depends upon
the types of waste. Only the proper segregation can ensure that.
36. General considerations on segregation
тАв Correct segregation is the responsibility of the waste
generator regardless of the position.
тАв Waste should be clearly identified into the different
categories with proper color and labeling
тАв Segregation must be done at the point of generation
of the waste
тАв Risk waste bin should not be placed where patient
parties can have easy access. Also the segregation
point for risk and non risk waste should be separate.
тАв Once general waste is mixed with risk waste, all of it
is considered as risk waste
37. Color Coding Bin System - HCWMG 2014
Waste category and
labeling
Color Code Type of waste Symbol
Non-
risk
waste
Bio-degradable Green
Leftover food stuffs, gardens,
fruits peels, flowers etc.
Recyclable
waste
Dark Blue
Plastic bottles, cans, metals,
plastics, cardboard, rubber,
saline bottle
Non-
biodegradable
and non-
recyclable waste
Light blue
Other non-risk, non-
biodegradable, non-recyclable
waste such as dust
38. Waste category
and labeling
Color
Code
Type of waste Symbol
HCW
requiring
special
attention
Pathological
waste
Red
Human body parts, organs, human tissues,
removed organs, amputated parts, bone
marrow
Sharps Red
Needles, glass syringes with fixed
needles, scalpels, blades, glass, etc. which
may cause puncture and cuts.
Pharmaceuti
cals
Red Unused and date expired drugs
Cytotoxic Red
Waste with anti-neoplastic effect such as:
alkylated substances, anti-metabolites,
antibiotics, plant alkaloids, hormones, etc.
39. Waste category and
labeling
Color
Code
Type of waste Symbol
Infectious
and
Highly
infectious
Infectious Brown
Items contaminated with blood and
body fluids from patients such as
cotton, dressing material, soiled
plaster, linen, gloves, bandages etc.
Highly
infectious
Brown
Waste generated from the
microbiological cultures, laboratory
waste, such as sputum cultures of TB
laboratories, highly concentrated
microbiological cultures
Other
hazardous
waste
Yellow
Waste with high content of heavy
metals such as batteries, pressurized
container
Radioactive
waste
Black
Waste contaminated with radionuclides
such as Cobalt, Technetium, Iodine,
Iridium
40. Color Coding Bin System - WHO 2017
Waste categories Color of bin
Infectious waste Yellow
Sharps waste Yellow
Pathological waste Yellow
Chemical and pharmaceutical waste Brown
Radioactive waste -
General HCWs Black
41. Since categorization of the waste entirely depends on
the types of the waste generated, available
technology for the treatment and disposal, and the
local environmental conditions of HCFs. If possible,
HCFs should categorize and segregate the HCWs as
mentioned above. However, it is recommended that
HCFs should at least categorize and segregate the
HCWs into non-risk HCW and risk HCW.
If the container with the recommended color is not
available, any colored container can be used to
segregate wastes with proper labeling and hazardous
sign
- HCWM Guideline 2014
42. Color coding bins with proper labeling
Redesign of dressing trolley for point segregation
43. Waste Collection
тАв Waste must be collected regularly тАУ at least once a day
тАв When waste bags/containers are 3/4th full they should
be sealed and removed.
Interim Storage
If the containers are 3/4th full before the collection time,
then it should be temporarily stored in a safe place, away
from people reach until the waste collector arrives and
transports the waste to the designated area. Such storage
practice is known as interim storage.
44. Waste Transportation
Onsite transportation
тАв Should take place whenever possible during less
busy times
тАв Hazardous and non-hazardous waste should
always be transported separately.
тАв All waste bags seals should be in place and intact
at the end of transportation
тАв Should be transported by using wheeled trolleys
or carts that are not used for any other purpose
45. Waste Storage (Central)
Different types of waste are brought for safe
retention until it is treated or collected for
transport offsite.
Capacity of store area should be three times the
daily accumulation of waste.
Storage times for infectious waste:
Temperate climate: 72 hours in winter and 48
hours in summer
Warm climate: 48 hours during the cool season
and 24 hours during the hot season
46. Waste Treatment
The purpose of treatment is to reduce the potential hazard
posed by health-care waste, while endeavoring to protect
the environment
The choice of treatment depends on:
тАв Waste characteristics , types and quantity
тАв Capability of HCF - cost, resources, area
тАв Available resources
тАв Public acceptability
тАв Environmental and safety factors
тАв Options available for final disposal
тАв Relevant national regulations and requirements
The method must be selected with a view to minimizing negative
impacts on health and environment.
There is no UNIVERSAL SOLUTION for waste treatment.
Local level implementation
guideline has recommended
autoclave for waste treatment
47. Waste Treatment Methods
1. Autoclaving
2. Incineration
3. Placenta pit
4. Encapsulation
5. Inertization
Less desirable
тАв Burning
тАв Deep burial
тАв Chemical disinfection
48. Autoclave
тАв Steam sterilization under pressure
тАв Operation тАУ 121┬░C and pressure of 15 pounds per
square inch (psi) for 30 minute
тАв Mostly suitable for highly infectious waste,
sharps.
тАв Not suitable for waste containing solvents or
substances that may emit toxic flumes, bleach,
radioactive materials, combustible, flammable
or volatile liquid
49. Incineration
тАв High temperature (850 ┬░C to 1100 ┬░C) dry
oxidation process
тАв Following waste should never be incinerated:
тЦл Pressurized gas containers
тЦл Radioactive waste
тЦл Halogenated plastics (PVC)
тЦл Mercury or cadmium
тЦл Ampoules of heavy metals
тЦл Reactive chemical waste
50. Placenta pit
тАв Suitable for placenta and other pathological
waste
тАв Should be impermeable
тАв Should not be prone to flooding or erosion
тАв A safety distance of at least 1.5 m from the
bottom of the pit to the ground water level is
recommended
тАв Waste should not be treated with chemical
disinfectants
51. 1. Pit
2. Slab
3. Lid
4. Base or lining
5. Permeable soil
6. Drainage channel
7. Mortar layer (at least
10 mm thick)
8. Ventilation pipe
9. Tee with mosquito
netting
10. Water bottle
52. Encapsulation
тАв Process of filling containers with waste, adding
an immobilizing materials and sealing the
containers
тАв Mostly suitable for sharps and pharmaceutical
waste
53. Procedure:
тАв The containers or boxes should be three quarters filled with waste and then filled up
with a medium such as plastic foam, bituminous sand, cement mortar or clay
material
тАв The containers should be made of high-density polyethylene or metallic drums
тАв Drums should not have contained explosive or hazardous materials previously.
54. Inertization
тАв Involves mixing waste with cement and other
substances before disposal
тАв Applicable for pharmaceuticals and incinerated
ash with heavy metal content
тАв Waste is mixed with cement and other
substances in a composition of 65% waste, 15%
lime, 15% cement and 5% water
55. Interim treatment approaches and
emergency situations
Burning
1. Small medical waste incinerators, such as single
chamber, drum and brick incinerators
2. Burning of HCW in a pit (followed by covering
with a layer of soil)
These are less desirable, but it is genuinely the only
realistic option in an emergency and in low
resource settings.
As far as possible, the burning of PVC plastics and
other chlorinated waste should be avoided to
prevent the generation of dioxins and furans.
56. Dioxins and furans are generated by the combustion of health-
care waste which contains chlorine. Dioxins and furans are bio-
accumulative and are highly toxic. They can cause reproductive
and developmental problems, damage the immune system,
interfere with hormones and also cause cancer. One source of
chlorine in health-care waste is the plastic polyvinylchloride
(PVC) in medical devices. For example, gloves or blood bags
can consist of PVC. Therefore, the purchase of PVC-free
devices is recommended.
- WHO, 2017
57. Deep Burial
тАв Not advisable. Only recommended in the conditions
when other methods are not applicable
тАв Area should not be prone to flooding or erosion
тАв Should be relatively impermeable and no shallow well
should be close to the site
тАв The bottom of the pit should be at least 2 m above the
ground water
тАв Inside the pit, alternating layers of waste, covered with
10 cm of soil should be placed
тАв When the pit is within about 50 cm of the ground
surface, the waste should be covered with lime before
filling the rest of the pit with soil and sealed permanently
тАв An earth mound around the mouth of the pit should be
constructed to prevent water from entering
58.
59. Chemical disinfection
тАв Mostly applicable for infectious waste
тАв Local level implementation guideline has
recommended chlorine solution, phenyl
тАв Chlorine use тАУ 0.5% chlorine solution for at least
30 minutes
60. Treatment methods based on type of waste
Waste
category
Two
chambers
incineratio
n
Single
chamber
incineratio
n
Autoc
lave
Chemical
disinfectio
n
Sanitary landfill
Infectious Yes Yes Yes Yes
Yes (pretreatment
for highly
infectious)
Pathologic
al
Yes
Yes No No No
Sharps Yes Yes Yes Yes
Yes for small
quantities with
encapsulation
Pharmace
utical
Small amount
only
No No No
Yes for small
quantities with
encapsulation
/inertization
61. Sharp Waste Management
DoтАЩs DonтАЩts
Use needle cutter DonтАЩt recap sharps
Separate sharps from
other waste
DonтАЩt bend or
manipulate needles
Use rigid puncture
proof disposal bin
DonтАЩt remove needle
from disposable
syringes
Empty sharps bin when
they are 3/4th full
DonтАЩt press down
sharps to make room in
sharp bin Locate needle cutter near
the point of generation
65. Sharp waste
Needle
Autoclave/0.5% chlorine then
encapsulation (Needle cut
compulsory)
Scapel, glasses
Autoclave/0.5% chlorine then
encapsulation
Infectious
waste
Cotton, gauge,
blood bag,
Autoclave/Burial
PPE
Reusable
Cleaning with soap and water then
autoclave/0.5% chlorine for 10
min then cleaning with water &
sun dry
Disposable
Autoclave/0.5% chlorine for 10
min then cleaning with water &
sun dry
Waste Type Treatment/Disposal
66. References
тАв Solid Waste Management Act 2068, GoN
тАв Health Care Waste Management Guideline 2014, DoHS, MoHP, GoN
тАв Local Level Health Program Implementation Guideline 2074/75, MoHP,
GoN
тАв Health Care Waste Management in the context of COVID-19 Emergency
(Interim Guidance) 2020, MoHP, GoN
тАв Safe Management of Wastes from Health Care Activities 2014, WHO
тАв Safe Management of Wastes from Health Care Activities 2017, WHO
тАв Medical Waste Management 2011, ICRC
Waste Minimization
Source reduction
Choosing products that generate less waste less wrapping material, for example
Choosing suppliers who take back empty containers for refilling; returning gas cylinders to the supplier for refilling
Purchasing policy geared to minimizing risks
Purchase of PVC-free equipment (choosing PET, PE or PP) - see Health Care Without Harm site.
Purchase of mercury-free equipment: mercury-free thermometers (ICRC standards), mercury-free blood pressure gauges).
If possible, purchase of new safe injection and blood sampling systems (where the needle is withdrawn automatically).
Opting for the least toxic products (cleaning products, for example).
Stock management
Centralized purchasing.
Chemical and pharmaceutical stock management aiming to avoid a build-up of expired or unused items: тАЬfirst-in тАУ first outтАЭ stock management, expiry dates monitoring.
Choice of suppliers according to how promptly they deliver small quantities and whether unused goods can be returned
A placenta pit or trench should be dug about 10 feet deep.
(The dimension of the pit is context specific. In principle, 0.5 liters of soil infiltration per placenta and a maximum of 5 liters of total space per placenta, if all the bloody liquids are collected and no infiltration is occurring, should be allowed)
The top 50 cm (or more) of the pit should be reinforced with concrete to prevent surface water infiltration.
The base of the pit should be made from concrete to stabilize the structure and to slow the downward movement of liquid towards the water table.
A safety distance of at least 1.5 m from the bottom of the pit to the groundwater level is recommended.
Placenta pits can also be constructed from a standard concrete ring with diameter of about 1 m.
The top slab should be above ground level and made from water tight concrete to prevent surface water infiltration.
The top should be closed by a lockable hatch
It should have a vent pipe of at least 2.5 m height.
A pit or trench should be dug about 2-3 meters deep and 1-2 m wide.
The bottom of the pit should be at least 2 m above the groundwater.
The bottom should be lined with clay or permeable material.
An earth mound around the mouth of the pit should be constructed to prevent water from entering.
Inside the pit, alternating layers of waste, covered with 10 cm of soil should be placed.
When the pit is within about 50 cm of the ground surface, the waste should be covered with lime before filling the rest of the pit with soil and sealed permanently.
A fence should be constructed around the area to prevent unauthorized entry