Title: International Standard and Guidelines: Health and Agriculture Aspects
1International Standard and Guidelines Health and
Agriculture Aspects
(Ecological Sanitation Symposium, Syria,
11-13.12.2005)
- Christine Werner
- Deutsche Gesellschaft für Technische
Zusammenarbeit (GTZ) GmbH - ecological sanitation program, Division 44
environment and infrastructure
2Contents
- WHO Guidelines
- 1989 version Guidelines for the safe use of
wastewater and excreta in agriculture and
aquaculture - 2005 version (upcoming) Guidelines for the safe
use of wastewater, excreta and greywater - EcoSanRes Guidelines
- Guidelines on the safe use of urine and faeces
in ecological sanitation systems - Guidelines on the use of urine and faeces in crop
production - FAO Guidelines
- FAO irrigation and drainage paper 47 wastewater
treatment and use in agriculture (1992)
3WHO guidelines for the safe use of wastewater and
excreta in agriculture and aquaculture (1989)
Category Use Person / Group exposed NematodesEggs / kg Feacal coliformsnumber / 100 g
A Application to field crop (used for raw food) worker, consumer, public lt/ 1 lt/ 1000
B Application to field crop (for industrial use, feedstock, trees) worker lt/ 1 no suggested standard
C Local application to field crop of cat. B, without contact to persons none not relevant not relevant
4New WHO guidelines for the safe use of
wastewater, excreta and greywater
- Upcoming WHO guidelines, update of the guidelines
from 1989, publication planned in 2006 - 3 Volumes
- safe use of wastewater in agriculture
- safe use of wastewater in aquaculture
- safe use of excreta and greywater
5New WHO guidelines for the safe use of
wastewater, excreta and greywater
- Reuse of wastewater, greywater and excreta in
agriculture and aquaculture is practiced
worldwide on a large scale, however often without
sufficient health proctction measures - WHO recognise the importance of reuse of
wastewater, greywater and excreta for sustainable
food production and improved livelihood - WHO provides guidance on health protection
measures for safe reuse - WHO recognise source-separation as a special and
valid approach
source GTZ
6New WHO guidelines for the safe use of
wastewater, excreta and greywater
- The new WHO-guidelines are
- based on
- scientific consensus and best available evidence,
- health based targets
- good practices and a multiple-barrier approach
- to be adapted to local social, economic, and
environmental factors - striving to maximize overall public health
benefits and the beneficial use of scarce
resources
source GTZ
source GTZ
7new WHO guidelines for the safe use of
wastewater, excreta and greywater
- key issue better methodologies for evaluating
risk - previous guidelines were based on actual risks
using epidemiological evidence - updated guidelines make use of all available
evidence including Quantitative Microbial Risk
Assessment (QMRA-models) - data on different pathogens are used to develop
- health based targets,
- required pathogen reduction and
- miocrobial performance targets of wastewater and
excreta treatment systems
source GTZ
source GTZ
8New WHO guidelines for the safe use of
wastewater, excreta and greywater
- Definition Disability Adjusted Life Years
(DALYs) - DALYs are a measure of population health in terms
of the burden due to a specific disease or risk
factor. - DALYs attempt to measure healthy years of life
lost because of disability or death from a
disease - DALYs account for not only acute health effects
but also for delayed and chronic effects - different health outcomes (e.g., cancer vs
diarrhea) can be compared and risk management
decisions can be prioritized. - adopted protection level for wastewater/excreta
use in agriculture in the new WHO
guideline tolerable additional disease burden
lt 10-6 DALYs or 1 µDaly per person and year
only one of a million human life years
expectancy will be lost due to the potential
additional disease from wastewater/excreta
reuse same protection level as used in the
WHO guideline for drinking water
9New WHO guidelines for the safe use of
wastewater, excreta and greywater
- Pathogen reductions achievable by various health
protection measures for wastewater use in
agriculture
Control measure Pathogen reduction (log units)
Wastewater treatment 1-6
Localized (drip) irrigation (low-growing crops) 2
Localized (drip) irrigation (high-growing crops) 4
Spray drift control (spray irrigation) 1
Spray buffer zone (spray irrigation) 1
Pathogen die-off 0.5-2 per day
Produce washing with water 1
Produce disinfection 2
Produce peeling 2
Produce cooking 6-7
10New WHO guidelines for the safe use of
wastewater, excreta and greywater
11Verification monitoring of wastewater treatment
for the various levels of wastewater treatment in
Options A-G E.coli
12Health-based targets for treated wastewater use
in agriculture helminth eggs
13Example agricultural use of wastewater, Peru
- Coastal region of Peru extremely arid
- Wastewater treatment in stabilisation ponds
- Irrigation with treated effluent for restricted
crops
source Saniplan
14Example greywater recycling through sub-surface
application, India
- Use of greywater in mulch trenches
Mulch filled trench or pit
source GTZ
15Guidelines on the safe use of urine and faeces
in ecological sanitation systems (EcoSanRes)
- public health issues of agricultural reuse of
urine and faeces
16guidelines on the safe use of urine and faeces
in ecological sanitation systems (EcoSanRes)
- focuses on the treatment and handling of faeces
and urine, provides current information on risk
management and assessment of source separation
strategies - technical and behavioural barriers against
disease transmission, sanitation treatment
methods, reuse in agriculture - the scope of guideline is limited to products
from urine diversion devices and dry collection
systems for faeces.
17Guidelines on the safe use of urine and faeces
in ecological sanitation systems (EcoSanRes)
- Recommendations for urine treatment and use
- The main risks in the use of excreta are related
to the faecal fraction and not the urine
fraction. - Technical constructions should be done in ways to
minimize faecal crosscontamination. - At household level the urine can be used
directly. - Urine should, in large-scale systems, be stored
for one month at 20C before use.
- A withholding period of one month between
fertilization and harvest should be applied. - Urine should be applied close to ground and
preferably mixed with or watered into the soil.
Urine strogae in Sweden (Gebers)
18Guidelines on the safe use of urine and faeces
in ecological sanitation systems (EcoSanRes)
- Recommendations for faeces treatment and use
- Faeces should be treated before use as
fertilizer. - Primary treatment (in the toilet) includes
storage and alkaline treatment by addition of
ash, lime or urea. - 1-2 cups (200-500 ml enough to cover the fresh
faeces) of alkaline material should be added
after each defecation.
- Faeces should additionally be mixed into the soil
in such a way that they are well covered. - Faeces should not be used for fertilization of
vegetables, fruits or root crops that are to be
consumed raw, excluding fruit trees.
Dried faeces (GTZ))
19Guidelines on the safe use of urine and faeces
in ecological sanitation systems (EcoSanRes)
- Recommended storage time and treatment for faeces
Treatment Criteria Comment
Storage (only treatment) at ambient temperature 2-20C 1,5-2 years Will eliminate most bacterial pathogens, substantially reduce viruses, protozoa and parasites, some ova may persist
Storage (only treatment) at 20-35C gt1 year As above
Storage and alkaline treatment pH gt9 during gt 6 months Temperature lt35, moisture content gt25 or lower pH will prolong the time for absolute elimination
20Guidelines on the use of urine and faeces in crop
production (EcoSanRes)
- Agronomic issues of agricultural reuse of urine
and faeces
21Guidelines on the use of urine and faeces in crop
production (EcoSanRes)
- Requirements regarding re-using of excreta for
agricultural purposes, including plant growth,
nutirents in excreta, hygiene treatment of urine
and faeces, etc. are discussed. - Recommendations on using excreta in cultivation
are given. - It emphasizes that urine and faeces are complete
fertilizers. Urine is rich in nitrogen and faeces
are rich in phosphorous, potassium and organic
matter. - guideline is limited to products from urine
diversion devices and dry collection systems for
faeces.
source GTZ
source GTZ
22Guidelines on the use of urine and faeces in crop
production (EcoSanRes)
- Recommendations for use of urine in cultivation
- Urine is a quick-acting nitrogen-rich complete
fertilizer. Best effects from prior to sowing, up
until two-thirds of the period between sowing and
harvest. - Recommended application rate and time should be
based on the desired nitrogen application rate
(based on local recommendations for chemical
nitrogen fertilizers) - Rule of thumb apply the urine from one person
during one day (24 hours) to one square metre of
crop. ( 300-400 m2 per person and year)
Fotos Urine reuse in Havanna, Cuba (GTZ)
23Guidelines on the use of urine and faeces in crop
production (EcoSanRes)
- Recommendations for use of faeces in
cultivation - Faeces should be applied and mixed into the soil
before cultivation starts. Local application in
holes or furrows close to the planned plants
allows for economic use - The application rate can be based on the current
recommendation for the use of phosphorous-based
fertilizers (low application rate with little
improvement due to the added organic matter) - Faeces can also be applied at much higher rates
for improving structure and water-holding
capacity of the soil
source GTZ
Fotos Compost from faeces in Havanna, Cuba (GTZ)
24Beneficial effects of agricultural use of urine
and faeces
source GTZ
25FAO irrigation and drainage paper 47 Wastewater
treatment and use in agriculture
- Covers health aspects and agronomic aspects of
reuse of wastewater in agriculture - Draws on the WHO Guidelines (1989) for health
protection measures
26FAO irrigation and drainage paper 47 Wastewater
treatment and use in agriculture
- FAO guidelines define use restrictions with
respect to salinity, trace elements, nitrogen,
etc. in order to not produce negative effects on
productivity and yields. - Blending conventional water with treated
effluent, or using the two sources in rotation is
possible. - This means that nutrients elimination in
wastewater treatment is not necessary if
reclaimed water can be blended with normal
irrigation water.
source GTZ
27FAO irrigation and drainage paper 47 wastewater
treatment and use in agriculture
- Water quality guidelines for maximum crop
production (example)
28FAO irrigation and drainage paper 47 wastewater
treatment and use in agriculture
- Threshold levels of trace elements for crop
production (example)