On-farm
Composting of Livestock and Poultry Mortalities
 |
| Agdex#: |
725/400 |
| Publication Date: |
November
2003 |
| Order#: |
03-083 |
| Last Reviewed: |
November
2003 |
| History: |
Original Factsheet |
| Written by: |
Gary Koebel - Livestock Mortality
Specialist/OMAFRA; Andrew Rafail - Program Assistant/OMAFRA; Jim
Morris - Contract Lecturer/Researcher/Ridgetown College, University
of Guelph |
Table of Contents
- Introduction
- The Composting Process
- What is Composting?
- The Case for Composting
- Planning Your Composting Unit
- Siting the Composting Unit
- Sizing the Composting Unit
- Constructing the Composting Unit
- Getting Ready to Compost
- Choosing Your Substrate
- Equipment and Supplies
- The Mechanics of Composting
- Managing the Process
- Monitoring the Compost
- Finished Compost
- Summary
- References
- Appendix 1
- Appendix 2
- Appendix 3
Introduction
Livestock and poultry producers in Ontario are recognized worldwide
for their progressive approaches to animal husbandry. However, on-farm
mortalities due to disease, accidental death and acts of nature are
inevitable in the livestock production business.
The proper disposal of livestock mortalities is critical in preventing
environmental contamination and the spread of disease. In Ontario, the
Dead Animal Disposal Act (DADA) regulates the disposal of dead
farm animals, specifically cattle, swine, sheep, goats and horses.
Under DADA, producers are required to properly dispose of on-farm
mortalities in a safe and environmentally friendly manner within 48
hours of death. The Act permits the following 3 disposal methods:
- pick-up by a provincially licenced deadstock collector
- burial under 0.6 m (2 ft.) of soil on the farm
- composting on the farm
This factsheet provides an overview of composting on-farm mortalities
and how you can apply composting to your own livestock operation. Although
there are a number of composting system options, the information here
is based on the popular bin composting unit, such as the one illustrated
in Figure 1, which could even be constructed
of straw or hay. Included are the basics of construction and guidelines
for starting, managing and monitoring your composting unit.

Figure 1. A bin composting unit. (Photo courtesy
of Minnesota Department of Agriculture)
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The Composting Process
What is Composting?
Composting is a natural process by which micro-organisms, such as bacteria
and fungi, break down organic material into a product called called
compost. Compost is a stable, dark brown, soil-like material (humus)
that can be applied to land.
The composting process cannot be successful without a balanced integration
of the following five elements:
- carbon
- nitrogen
- oxygen
- moisture
- temperature.
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The Case for Composting
There are a number of advantages to adopting composting for disposal
of on-farm mortalities, not the least of which are its practicality
and environmental soundness. Here are some of the better known benefits
of this disposal method:
Biosecurity
- Improves biosecurity and reduces health risks by eliminating the
need for deadstock personnel and vehicles to visit the farm
- Significantly reduces the number of pathogens through the natural
heating process
Cost Effectiveness
- Requires minimal to moderate start-up costs, depending on design
and materials chosen
- Requires minimal operating costs, especially when using on-farm
materials
- Provides a value-added soil amendment as an end product
- Eliminates processing and service fees associated with mortality
collection
Practicality
- Offers an option for immediate disposal of livestock mortalities
- Accommodates animals of all sizes, as well as afterbirth
- Provides an alternative for disposing of mortalities that are not
accepted for rendering
- Offers a disposal strategy to deal with an unexpectedly high number
of mortalities
- Can generally be done year round
Environmental Soundness
- Provides a stable form of nitrogen and other nutrients
- Eliminates offensive odours and flies when units are well-managed
- Recycles on-farm materials
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Planning Your Composting Unit
Consider the following factors in the planning and design of your on-farm
composting unit:
- site selection
- size of unit
- construction.
Siting the Composting Unit
Select a location that is out of view of neighbours and the travelling
public. Also make sure you know about and can comply with the environmental
guidelines and regulations for your area by checking with the chief
building official and by-law officer in your municipality.
To select an ideal site for your composting unit:
- Choose a high, level, well-drained area away from wells, watercourses
and tile drains.
- Choose a southern exposure where possible.
- Stay away from animal feed and housing units, and wildlife habitat.
- Note any biosecurity risks (e.g., traffic patterns or vermin access)
and make changes needed to reduce the risk of spreading disease.
- Allow space for handling mortalities, substrate and finished compost.
- Ensure easy access to manage and monitor the unit.
- Ensure convenient access to a water supply so that you can add water
to composting bins as needed.
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Sizing the Composting Unit
The size of the composting unit will depend on the size and nature
of your livestock operation and the projected annual number of mortalities.
Determining Composting Unit Area
The total area needed for composting units on your farm will depend
on the following:
- number and size of bins needed for composting
- number and size of bins, if needed, for storing carbon sources such
as sawdust or straw (called substrate) and the finished compost
- space needed for traffic flow and the operation of equipment
Determining Number and Size of Bins
For each composting unit, plan for three composting bins. Two bins
are needed for the primary stage of composting (first heat stage), and
a third one is needed for the secondary stage of composting (second
heat stage). Some larger livestock and poultry operations will require
more than one composting unit. One or more bins may also be needed for
storing substrate or finished compost, depending on your operation.
The size of bins required will depend on the weight of mortalities
and the substrate used, so this must be calculated for each individual
operation. Consider the following when sizing bins:
Composting Bins
- Each primary composting bin needs at least 1.25 m3
for every kilogram (20 ft.3/lb.) of average daily mortality
that will be composted if you use sawdust as a substrate. However,
your composting bins should be one-and-a-half times this size to
allow for an unexpected increase in mortality rate or expanded production.
If you plan to use less dense substrates, such as straw and corn
silage, you will need more bin space per kilogram (pound) of mortality.
- Each secondary composting bin should be at least two-thirds the
size of a primary bin (i.e., at least .83 m3 for every
kilogram (13 ft.3/lb.) of average daily mortality that
will be composted). It may be practical to make the secondary bin
the same size as a primary bin.
Storage Bins
- A storage bin for substrate should equal the volume of two primary
bins, depending on your operation and supply of substrate.
- A storage bin for finished compost may be desirable. A bin equal
in volume to one primary bin should be adequate for most operations.
Refer to Appendix 1 for a worksheet to help
you determine the number and size of composting bins needed for your
operation.
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Constructing the Composting Unit
A number of structures lend themselves to efficient on-farm composting,
including newly built, stand-alone units and add-ons to existing buildings.
Even cattle and machine sheds may be adapted for composting. Composting
units may be subject to municipal by-laws or other government standards.
Check with the by-law officer and chief building official in your municipality,
and ensure you can comply with all laws and guidelines before beginning
construction.
Base
Build the base of the unit to prevent leachate (liquid from the pile)
and run-off from affecting the environment ( Figure
2). A well-constructed concrete pad effectively reduces environmental
impact and provides a solid base for operating loaders and equipment
without disturbing sub-soils. A clay soil (at least 1 m (3.3 ft.) of
soil containing 20% clay) is also an acceptable base.

Figure 2. A composting unit with a reinforced floor. (Photo
courtesy of Minnesota Department of Agriculture
Walls
Walls should be 1.4-1.8 m (4-6 ft.) high and be constructed to reduce
leachate permeation. They should also be designed to keep out all animals,
including vermin, and to withstand the demands of turning the composting
piles with large equipment and loaders. Recommended wall materials include
concrete, untreated wood and large tightly packed bales of hay or straw.
Pressure treated wood is not recommended because of the possibility
of heavy metal contamination of the compost. Figure
3 shows a compost unit built of large square bales.
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Wall Height
Recommended wall height for a composting bin is
1.8 m (6 ft.). As a general rule, bins deeper than 1.8 m (6 ft.)
may need a forced aeration system. The potential for spontaneous
combustion increases with greater depth due to the reduced air
space caused by compaction of the pile.

Figure 3. A simple large bale composting unit.
Text
Equivalent of Graphic
Build three-sided bins that allow accessibility for the type of operating
equipment you will use. The opening should be at least 0.6 m (2 ft.)
wider than the loader or turning equipment being used. Bins should be
at least 1.8 m (6 ft.) wide. Installing a gate at the open end of each
bin helps discourage animals from scavenging.
Square bins with a floor area larger than 6 m2 (64 ft.2)
may require a forced aeration system to reduce the potential for spontaneous
combustion due to lack of airflow in the middle of the pile. If the
floor area needed for your operation exceeds that, consider building
rectangular bins no wider than 2.45 m (8 ft.) or build more than one
unit.
Roof
Having a roof or cover, as shown in Figure 4,
will help to control moisture levels by protecting the composting pile
from rain and snow. Excessive moisture increases the risk of leachate
and run-off, and interferes with the composting process, thereby increasing
the risk of odour.

Figure 4. A covered compost unit. (Photo courtesy of Minnesota
Department of Agriculture)
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Getting Ready to Compost
To make composting work, you need to create and maintain the ideal
environment for the micro-organisms to function in your pile. There
are four essential components you must provide to accomplish this.
- Carbon and Nitrogen
The carbon to nitrogen ratio (C:N ratio) in composting is critical
for providing the required environment for the micro-organisms.
To facilitate the composting process, you will need to add a substrate
that is high in carbon to balance the high levels of nitrogen contained
in the mortalities. Too low a C:N ratio may cause odours. Too high
a C:N ratio may limit microbial activity, resulting in lowered temperatures
and slowed decomposition. A C:N ratio ranging from 25:1 to 35:1
is recommended.
- Oxygen
Oxygen must be available in the pile to support necessary microbial
activity. The substrate you use in the pile must create the space
that traps air. The type and size of the substrate particles will
affect air space. The substrate also provides insulation for the
pile and absorbs liquid produced by decomposing mortalities.
- Moisture
An adequate moisture level is also needed to ensure proper microbial
activity in the compost pile. The ideal moisture content is 45%,
but levels from 40%-60% are acceptable. Low moisture levels can
reduce microbial action while high moisture levels inhibit the flow
of oxygen and can lead to odour. The presence or absence of a roof,
weather conditions, substrate type, animal species, and the number
and size of the mortalities in the composting bin can each influence
moisture levels.
- Temperature
Heat is the result of the composting process and is necessary for
composting to work. To a certain extent, the more heat there is,
the more heat is produced, and the faster composting proceeds. For
proper composting, the temperature must reach at least 55°C
(131°F) and remain there for several days or weeks, depending
on the size of the mortalities. Lower temperatures will slow the
micro-organisms, resulting in slower decomposition and less effective
reduction of pathogen numbers. Temperatures higher than 71°C
(160°F) will destroy the micro-organisms needed for composting.
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Choosing Your Substrate
You can source substrate material on-farm or off-farm. Cost, availability,
and physical characteristics are important factors to consider. Clean
sawdust has proven to be an excellent substrate for composting mortalities,
although other materials with high carbon content such as wood mulch,
straw, corn cobs and corn silage may be used. Table
1 shows the C:N ratio of some common organic materials found on
farms.
- Consider your options for on-farm or low cost substrates, such as
straw, sawdust or wood shavings. If using an off-farm substrate, care
must be taken to ensure that it does not contain foreign material
such as metal or glass or chemical contamination. When ordering substrate
for pick up or delivery, verify the origin and quality of the material
and any related environmental regulations that may apply.
- Estimate the annual amount of substrate you will likely need, based
on your annual mortality rate and the substrate available, and make
sure you can access adequate quantities of substrate throughout the
year.
- Ensure substrate particles are large enough to ensure adequate airflow
but small enough to decompose or work effectively in the composting
process. If necessary, chop substrate so particle length ranges from
3-13 mm (1/8-1/2 in.).
- Use finished compost as a "starter" for up to half of
the weight of needed substrate, as an option.
Table 1. C:N Ratio of Some Common Organic
Materials
|
High Carbon Sources
|
|
Material
|
C:N
|
|
70:1
|
|
38 - 43:1
|
|
60 - 120:1
|
|
200 - 500:1
|
|
80 - 120:1
|
| Low Carbon Sources |
|
Material
|
C:N
|
|
4:1
|
|
15 - 20:1
|
|
6:1
|
|
30:1
|
|
15:1
|
(On-Farm Composting Handbook, 1992)
How Much Substrate?
The size, number and species of mortalities will determine the amount
of substrate needed for the process. Generally, a weight to weight ratio
of 1.5 sawdust to 1 of mortality (i.e., 1.5 kg:1 kg or 1.5 lb.:1 lb.)
is needed to balance the nitrogen in mortalities. This is approximately
1:1 on a volume to volume basis. More substrate relative to mortalities
will be required if you use a substrate with a lower C:N ratio.
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Equipment and Supplies
Loading and Moving Equipment
Equipment will be needed to move substrate and mortalities, and
to move composting material from a primary to a secondary bin. No specialized
equipment is required, although a tractor-mounted, front-end loader
is commonly used. To determine what is appropriate for your situation,
consider the equipment available on-farm, frequency of usage, amount
of material being handled, size and location of the composting system
and available labour.
Thermometer
Use a thermometer to measure the temperature of composting piles.
A thermometer constructed of stainless steel with a shaft of 6 mm (1/4
in.) diameter and measuring at least 1 m (3 ft.) in length is recommended.
Thermometers may be available at farm supply stores.
Moisture Meter
A moisture meter (e.g., a hay moisture probe) is needed to measure the
moisture level of composting piles. Use a meter that can accurately
measure moisture levels from 30%-70%. Moisture meters may be available
at farm supply stores.
Screen
If you will be composting mortalities that weigh more than 200 kg (440
lb.), a screen 13-25 mm (½-1 in.) will be needed to remove bone
fragments prior to applying the compost to land. Screens may be available
at farm supply stores.
Recording System
A record-keeping system is critical to your composting success.
A simple system would allow you to record dates, details about mortalities
added to a pile, substrate used, pile temperature, pile moisture and
general observations (e.g., condition of top substrate layer, amount
of leachate, odours, evidence of scavenging, and actions taken to correct
problems). Create one that best suits your needs. Refer to Appendix
2 for an example of a simple record-keeping system.
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The Mechanics of Composting
A complete composting cycle has three main stages: bin filling, the
primary heating stage and the secondary heating stage. Successful composting
requires management and monitoring throughout this cycle.
Primary Bins--Filling and First Heat Stage
- Fill one of the primary bins over a period of 45-90 days, depending
on the average weight of the mortalities.
- Leave the material in this primary bin to compost for an additional
45-90 days. The pile should heat to temperatures ranging from 55°C-65°C
(131°F-149°F). In general, the pile temperature should remain
within this range for at least 7 days to ensure that composting at
this stage is effective. While one primary bin is composting, you
would be filling another primary bin.
- Move the pile from the primary bin to the secondary bin after the
first heat stage has occurred. By now, the temperature should have
dropped to below 48°C (120°F).
Secondary Bin--Second Heat Stage
- Ensure mortalities protruding from the newly made pile are covered
with at least 0.6 m (2 ft.) of substrate.
- Leave the partially composted material in the secondary bin for
the second heat stage. The pile again needs to heat to temperatures
ranging from 55°C-65°C (131°F-149°F) and remain within
this range for at least 7 days to ensure the composting is effective.
In this heat cycle, the pile will reach the same high temperature
observed during the first heat stage, but it may not remain high for
as long. The main composting process is complete after the second
heat stage has occurred and the temperature has dropped to below 48°C
(120°F).
- Screen the composted material if visible bones remain in the material,
e.g., from mortalities weighing more than 200 kg (440 lb.). Return
any larger remaining bones back to a primary bin for further decomposition.
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Managing the Process
Timing and Flow
Each of the filling, primary heating and secondary heating stages
takes about the same length of time. While the principles of composting
are the same for both small and large animals, the size of mortalities
and the substrate used will influence the time needed for decomposition.
Typically, mortalities under 25 kg (55 lb.) take 45 days for each stage,
for a total of 135 days for the complete cycle. For mortalities 25 kg
and over (55 lb. and over) each stage takes 90 days, for a total of
270 days. However, it may take a year to completely compost mortalities
over 200 kg (440 lb.).
Once the first primary bin in your composting unit is filled and left
to sit, the second primary bin can be filled while the first is heating.
When the first primary bin is ready to turn into the secondary bin,
the other primary bin is ready to sit. Figure 5
shows the movement of material between bins during the compost cycle.

Figure 5. A schematic of the composting process.
Text
Equivalent of Graphic
Building the Pile
Make sure you review and comply with any provincial and municipal
regulations and standards that govern composting on-farm mortalities
before you start to compost, as these may be up-dated from time to
time. Contact the Ontario Ministry of Agriculture, Food and Rural
Affairs your municipal by-law officer to verify the regulations and
standards affecting on-farm composting.
1. Make a Base
- Spread 0.6 (2 ft.) of substrate on the floor of a primary bin
in your composting unit.
- Moisten as needed for substrate moisture level to reach 40%-45%.
(Additional moisture will come from the mortalities so it is important
to start with less moisture in the base layer of substrate than
in upper layers.)
2. Add a Mortality Layer
- Ensure that your veterinarian has examined animals that were euthanized
or died on-farm of an unknown cause, to ensure they did not have
a serious disease.
- Place the mortalities on the substrate at least 0.3 m (1 ft.)
from the exterior edge of the bin.
- Space the mortalities evenly on the substrate, ensuring they do
not touch each other.
- Place a larger mortality on its side to maintain the recommended
pile height of less than 1.8 m (6 ft.). If needed cut the ligaments
and tendons in the legs and fold them down. Cutting open the body
cavity will reduce bloating and promote increased microbial activity.
3. Cover with Substrate
- Moisten substrate as needed for substrate moisture level to measure
from 40%-60%.
- Immediately cover the mortalities with at least 0.6 m (2 ft.)
of substrate.
- Ensure all parts of the mortalities are covered with substrate
and the pile shape is appropriate for your situation (see below
for information about pile shape).
4. Add More Mortalities
- Skim off a portion of the top layer of substrate leaving 0.2-0.3
m (8-12 in.) of substrate on top of the old mortalities.
- Add new mortalities to the pile following steps 2 to 3 above.
Winter Composting Issues
As the temperature drops, it is more difficult to establish microbial
activity in a composting pile. Avoid initiating a new pile from
December to February. If a new pile must be started during the winter,
be sure to use finished compost for up to half of the substrate.
If a mortality is frozen, it should be thawed before being added
to the pile.
Size and Shape of the Pile
Ensure the composting pile is 1.2-1.8 m (4-6 ft.) high. Piles less
than 1.2 m (4 ft.) high generate insufficient heat, especially in colder
weather, and there may not be sufficient substrate to maintain microbial
activity for adequate decomposition. Piles higher than 1.8 m (6 ft.)
may become compacted and not permit enough airflow for proper composting,
possibly resulting in spontaneous combustion.
The shape of a pile will affect how moisture will filter into the pile.
For a pile with a roof or cover, the top layer of substrate may be left
flat or concave so that any added moisture will be easily absorbed.
However, a convex or peaked shape may be appropriate for an uncovered
pile to limit the amount of rain or snow that will filter into the pile.
Note that although a peak may be desirable during a wet period, the
pile may need to be flattened or dipped to hold moisture during a dry
period.
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Monitoring the Compost
If you're not monitoring, you're not managing your composting unit!
Check the pile daily to monitor the substrate cover, temperature and
moisture, and record the information. Throughout the composting cycle,
watch for and take steps to prevent:
- scavenging by animals
- excessive leachate
- odour.
Substrate Cover
Make sure all mortalities are completely covered with 0.6 m (2 ft.)
of substrate. Factors such as settling of the pile or wind may reduce
the depth of substrate covering the mortalities.
Temperature
Take the internal temperature of the pile at several locations,
including close to the last mortality added. Temperatures should increase
and need to remain between 55°C (131°F) and 65°C (149°F)
for at least 7 consecutive days in the primary and secondary bins. If
temperatures fall below 48°C (120°F), the composting process
is becoming non-active; temperatures higher than 71°C (160°F)
will destroy the composting micro-organisms and may lead to a fire in
the pile. Refer to troubleshooting guide in Appendix
3 to address temperature problems.
Moisture
Check the moisture content of the pile frequently to ensure it ranges
from 40%-60%. You may need to change the shape of the pile and adjust
moisture content. Refer to troubleshooting guide in Appendix
3 if problems with moisture levels occur.
Moisture Control in Uncovered Composting Unit
In the absence of a roof or cover, the shape of the compost pile
will greatly influence its moisture level. A concave or dipped shape
pile will retain moisture from rain and snow. By creating a peaked
shaped pile, moisture will generally run off the sides, with less
absorbed into the pile.
Record Activity and Results
Set up a system to record the following:
- temperature
- moisture
- mortalities (date added, number, species and weight)
- substrate (amount and type used)
- general observations about the composting process, as well as problems
and corrective actions taken.
Refer to Appendix 2 for an example of a simple
system for recording composting information.
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Finished Compost
Properly finished compost has a slight earthy odour and resembles humus,
or potting soil, in colour and texture, as shown in Figure
6. Ensure that visible bones remaining after the secondary heating
are screened out and returned to the primary bin being filled. Once
you ensure larger bones are removed, the compost is ready for on-farm
land application.

Figure 6. Finished compost.
Be sure to get a nutrient analysis of the finished compost to accurately
determine nutrient content, and include it in your nutrient management
plan or strategy. Table 2 shows the nutrient content
of finished compost from a research project on composting swine mortalities.
Table 2. Nutrient Content of Composted
Swine Mortalities with Various Substrates
| Analyte |
Substrate
|
| Sawdust |
Straw |
|
Dry Matter (%)
|
53.50
|
55.70
|
|
Crude Protein (%)
|
12.40
|
18.60
|
|
Crude Fat (%)
|
14.00
|
28.70
|
|
Calcium (%)
|
0.35
|
0.51
|
|
Phosphorus (%)
|
0.16
|
0.32
|
|
Potassium (%)
|
0.22
|
0.78
|
|
Magnesium (%)
|
0.04
|
0.10
|
|
Sodium (%)
|
0.21
|
0.31
|
|
Cooper (ppm*)
|
5.37
|
2.90
|
|
Zinc (ppm*)
|
48.80
|
25.40
|
|
Ash (%)
|
1.94
|
5.79
|
|
Carbon (%)
|
53.10
|
50.10
|
|
Nitrogen (%)
|
1.98
|
2.97
|
|
C:N Ratio
|
42.70
|
24.80
|
* ppm - parts per million
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Summary
With good planning and management, on-farm composting can be an effective
and environmentally friendly way to dispose of livestock and poultry
mortalities. On-farm composting is a legal option for producers bound
by Ontario's Dead Animal Disposal Act. Existing farm resources
such as buildings or straw can be used to construct a bin composting
unit. You must provide a high source of carbon (e.g., straw, sawdust
or wood mulch) for your compost pile to balance the nitrogen contained
in mortalities. You must also make sure the pile has enough oxygen from
trapped air and the right amount of moisture, so it can reach the high
temperatures that are needed for composting. A composting unit can be
used year round, although you should avoid starting a new pile during
the winter. Monitoring the unit regularly will help you ensure the composting
process is working. With a well-managed unit, you should have properly
finished compost for on-farm application in less than a year.
References
Manitoba Pork Council. 2000. Composting Deadstock: A Producer's
Guide to Effective Mortality Composting. Manitoba Pork Council,
Winnipeg, Manitoba.
Dougherty, M. (ed.). 1998. Composting for Municipalities: Planning
and Design Considerations. Publication NRAES-94. Natural Resource,
Agriculture and Engineering Service, Ithaca, New York.
Dougherty, M. (ed.). 1999. Field Guide to On-Farm Composting. Publication
NRAES-114. Natural Resource, Agriculture and Engineering Service, Ithaca,
New York.
Fulhage, Charles D., R. Wright, J. Feistner and J. Igert. 1993. Composting
Poultry Carcasses in Missouri. Publication WQ205. University Extension,
University of Missouri-Columbia, Missouri.
McGuire, K. (ed.). 1997. Composting Module, Environmentally Assured.
National Pork Producers Council (NPPC), Urbandale, Iowa.
Morse, D.E. 2001.Composting Animal Mortalities. Minnesota Department
of Agriculture, St. Paul, Minnesota.
Morris, J.R., T. O'Connor, F. Kains and H. Fraser. 1997. Composting
Livestock Mortalities. Factsheet 97-001. Ontario Ministry of Agriculture,
Food and Rural Affairs, Guelph.
Rynk, R. (ed.) 1992. On-Farm Composting Handbook. Publication
NRAES-54. Natural Resource, Agriculture and Engineering Service, Ithaca,
New York.
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Do you know about Ontario's new Nutrient Management Act?
The provincial Nutrient Management Act (NMA) and
the Regulation 267/03 as amended regulates the storage, handling
and application of nutrients that could be applied to agricultural
crop land. The objective is to protect Ontario's surface and groundwater
resources.
Please consult the regulation and protocols for the specific legal
details. This Factsheet is not meant to provide legal advice. Consult
your lawyer if you have questions about your legal obligations.
For more information on the NMA call the Nutrient Management Information
Line at 1-866-242-4460 or visit www.omafra.gov.on.ca.
Factsheets are continually being updated so please ensure that
you have the most recent version.
Appendix 1: Worksheet for Sizing Mortality Composting
Units
A. Determine the annual weight of mortalities on your farm
| Line |
Steps |
Sample Farm |
Your Farm |
|
1
|
Enter the number of mortalities per year.
|
60 mortalties/year (E)
|
_______ mortalities/year (E) |
|
2
|
Enter the average weight of the mortalities (refer
to Table A-1, Estimated Average Mortality
Rates and Weight of Various Animals for weights).
|
125 kg/mortality (F)
|
_______ kg/mortality (F) |
|
3
|
Calculate the total weight of annual mortalities
for disposal: multiply the number of mortalities (Line 1-E)
by the average weight (Line 2-F)
|
60 x 125 =
7,500 kg/year (G)
|
(E)_____ x (F)_____
= _____ kg/year (G)
|
B. Determine the volume needed for the composting unit consisting
of two primary bins and one secondary bin, and the number of units required
| Line |
Steps |
Sample Farm |
Your Farm |
|
4
|
Calculate volume of one primary bin:
divide the total weight of annual mortalities ( Line 3-G)
by a conversion factor to account for substrate density and mortality
size (under 25 kg or 25 kg and over). Use conversion factor from
Table A-2, Conversion Factors for Some
Common Substrates. (Note: Conversion factor includes allowance
for expansion or unexpected mortalities.)
|
The conversion factor adjusts
for mortality size and substrate used. See Table
A-2 for conversion factors. Example is based on mortalities
25 kg and over, using sawdust as a substrate.
7,500 kg/year (G) ÷ 703
=
10.7 m3 (H)
(*note - 703 is a standard
number)
|
(G) _____ ÷ _____ = _____ m3 (H)
|
|
5
|
Calculate the volume of one secondary bin:
multiply the volume of one primary bin (Line 4-H) by 0.67*.
|
10.7 m3 x 0.67
= 7.17 m3
(*note - 0.67 is a standard number)
|
(H) _____ x 0.67
= _____ m3
(*note - 0.67 is a standard number)
|
|
6
|
Calculate the number of units:
divide the volume of one primary bin (Line 4-H) by the proposed
pile height (1.4-1.8 m or 4-6 ft.) and divide by a maximum floor
area of 6 m2 (64 ft.2) per bin. (Note: Floor
area may be greater if bins are no more than 2.45 m (8 ft.) wide.) |
(H ÷ pile height ÷ max. floor
area)
10.7 m3 (H) ÷ 1.8
m ÷ 6 m2 = 0.99
|
(H) _____ m3 ÷ _____ m ÷
_____ m2 = _____ |
C. Determine the approximate volume of a storage bin needed for
an annual supply of substrate
| 7 |
Calculate the approximate
volume of substrate storage bin: multiply the volume of one
primary bin (Line 4-H) by 2**. |
10.7 m3 x 2
= 21.4 m3
(*note - 2 is a standard number)
|
(H) _____ x 2
= _____ m3
(*note - 2 is a standard number)
|
*The volume of the secondary bin should be at least 2/3
the volume of one primary bin.
**Generally, the volume of substrate required for one year
of composting will equal the combined volume of the primary bins. A
larger bin may be necessary if a very coarse and low density substrate
is used.
"Purple"
colour indicates a standard number used in
a calculation.
| Top of Page |
Table A-1. Estimated Average Mortality
Rates and Weight of Various Animals
|
Type of Livestock or Poultry
|
Average Mortality Rate |
Average Weight
|
| (%/Year) |
(lb.) |
(kg) |
|
Cattle and Horses
|
|
Birth
|
9
|
100
|
45
|
|
Weanling
|
1.5
|
600
|
273
|
|
Yearling
|
1.5
|
900
|
409
|
|
Mature
|
2.5
|
1,400
|
636
|
|
Sheep and Goats
|
|
Stillborn
|
5.5
|
8
|
4
|
|
Lambs - 1st 10 days
|
7
|
9
|
4
|
|
Lambs Pre-weaning
|
2
|
45
|
20
|
|
Lambs Post-weaning
|
1.9
|
75
|
34
|
|
Total Lamb Mortality
|
16.4
|
20.7
|
9
|
|
Adult Flock
|
4.5
|
170
|
77
|
|
Swine
|
|
SEW Sows
|
5.5
|
440
|
200
|
|
Preweaners
|
19
|
4
|
2
|
|
SEW Weaners
|
2.6
|
29
|
13
|
|
Growers
|
1.7
|
99
|
45
|
|
Finishers
|
2.5
|
194
|
88
|
|
Poultry
|
|
Broiler - Pullets
|
2.5
|
3.8-5.5
|
1.7-2.5
|
|
Broiler - Cockerel
|
3.5
|
5.5-7.7
|
2.5-3.5
|
|
Layers
|
8
|
4.5
|
2
|
|
Breeding hens
|
14.5
|
7.5
|
3
|
|
Turkey - Breeders
|
5-7
|
25.3-26.4
|
11.5-12
|
|
Turkey - Toms
|
7-11
|
30.8
|
14
|
|
Turkey - Hens
|
4-6
|
16.5
|
7.5
|
|
Bison
|
|
Calf (2 - 6 months)
|
2.2
|
100-220
|
45-100
|
|
Weaned Calves
|
1.7
|
400-440
|
180-200
|
|
Adult Cows
|
0.8
|
825
|
375
|
|
Adult Bulls
|
1.7
|
1,760
|
800
|
|
Elk
|
|
Birth
|
2-3
|
35-44
|
16-20
|
|
Weaning
|
2-3
|
290
|
130
|
|
Yearling
|
2-3
|
350
|
160
|
|
Adult Cows
|
2-3
|
620
|
280
|
|
Adult Bulls
|
2-3
|
770
|
350
|
|
Red Deer
|
|
Calf (Birth)
|
|
18-22
|
8-10
|
|
Weaning
|
|
110
|
50
|
|
Yearling
|
2-3
|
143
|
65
|
|
Adult Hinds
|
1-2
|
220
|
100
|
|
Adult Stags
|
1-2
|
330
|
150
|
|
White Tail Deer
|
|
Calf (Birth)
|
|
9
|
4
|
|
Yearling
|
2-3
|
120
|
55
|
|
Adult Bucks
|
|
210
|
95
|
|
Adult Does
|
5
|
120
|
55
|
|
Fallow Deer
|
|
Calf (Birth)
|
2-3
|
9
|
4
|
|
Yearling
|
2-3
|
110
|
50
|
|
Adult Does
|
2-3
|
155
|
70
|
|
Adult Bucks
|
2-3
|
275
|
125
|
|
Mink
|
|
Adult Male
|
3
|
6
|
3
|
|
Adult Female
|
2
|
3.3
|
2
|
|
Mink Kit Birth to Pelting
|
10
|
4.1
|
2
|
|
Carcasses after Pelting
|
|
3.08
|
1
|
|
Foxes
|
|
Adult Males
|
1
|
22.5
|
10
|
|
Adult Females
|
1
|
17.5
|
8
|
|
Male Pups (at Pelting)
|
7.5 (loss prior to pelting)
|
15
|
7
|
|
Female Pups (at Pelting)
|
7.5 (loss prior to pelting)
|
13
|
6
|
|
Carcasses after Pelting
|
|
11
|
5
|
| Top of Page |
Table A-2. Conversion Factors for Some Common Substrates
| Substrate |
Conversion Factor (kg/m3 year) |
Mortalities
Under 25 kg (55 lb) |
Mortalities
25 kg (55 lb.) and Over |
| Sawdust |
1406
|
703
|
| Straw |
730
|
365
|
| Corn Stalks |
595
|
297
|
| Corn Cobs |
1784
|
892
|
| Corn Silage |
2677
|
1338
|
Text
Equivalent of Graphic
| Top of Page |
| Substrate |
Density (kg/m3) |
Table A-3. Density of Some Common Substrates
|
260
|
|
135
|
|
110
|
|
330
|
|
495
|
| Top of Page |
Appendix 2: Composting Record Sheet
(use one sheet per bin)
|
Bin Type
(Primary, Secondary)
|
Bin #
(1, 2, 3...etc)
|
Date Initiated
|
Comments:
|
|
|
|
|
Temperatures must reach 55°C (131°F) and remain between 55°C
(131°F) and 65°C (149°F) during both heating cycles.
Moisture levels will range from 40%-60%. Substrate cover be at least
0.6 m (2 ft.).
If measured values are outside of expected ranges, refer to Appendix
3, Troubleshooting Guide, for possible solutions.
|
Date
|
Temperature
|
Moisture Level
|
Mortalities Added
(species and weight)
|
Substrate
(amount & type)
|
Observations/ Comments
|
|
Example
|
62°C
|
45%
|
1 calf, 45 kg
|
Sawdust, ~70 kg
|
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|
Appendix 3. Troubleshooting Guide
| Problem |
Cause |
Possible Solution |
|
Improper Temperature
|
|
Too cold
|
Too wet |
Remove pile contents and add substrate.
Protect pile from weather or shape to shed water.
|
| Low C:N ratio |
Evaluate amount and type of substrate and adjust as necessary.
|
| Too porous |
Replace or mix existing
substrate with sawdust or another small-particle substrate. |
| Insufficient substrate
cover |
Add substrate to top
of pile. |
|
Too hot
|
Too dry |
Add water
to mortality area. |
| Problem |
Cause |
Possible Solution |
|
Failure to Decompose
|
Low carbon
Mortalities layered too closely
|
Evaluate amount and type of
substrate and adjust as necessary.
Adjust pile ensuring 0.2 m to 0.3 m (8 to 12 in.) of substrate between
layers. |
| Mortalities placed too closely
together |
Adjust mortalities ensuring
they do not touch each other. |
| Mortalities placed too close to the side
of the bin. |
Adjust pile ensuring mortalities are placed
at least 0.3 m (1 ft.) from the bin wall. |
| Problem |
Cause |
Possible Solution |
|
Odour
|
|
Foul, high sulfur, organic acids
|
Too
wet |
Remove pile contents and add substrate.
Protect pile from weather or shape to shed water.
|
| Not enough
cover substrate |
Add substrate ensuring
0.6 m (2 ft.) of cover. |
| Air flow
restricted |
Evaluate amount and type of substrate and adjust as necessary
Replace or mix existing substrate with a larger particle substrate.
Adjust pile ensuring mortalities are placed at least 0.4 m (1
ft.) from edge of side of the bin.
|
| Excessive
crusting on surface |
Break up
crusting on the surface and avoid using substrate that is frozen
or too wet. |
|
Smell of decaying flesh
|
Not enough
cover substrate |
Add substrate ensuring
0.6 m (2 ft.) of cover. |
| Too cold |
Follow steps outlined
above under "improper temperature". |
|
Ammonia
|
Low carbon |
Evaluate amount and type
of substrate and adjust as necessary. |
| Problem |
Cause |
Possible Solution |
|
Flies
|
Not enough cover
substrate |
Add substrate ensuring 0.6
m (2 ft.) of cover. |
| Poor
sanitary conditions |
Remove leachate from around pile.
Maintain a clean, debris free area around compost site.
|
| Too
cold |
Follow steps outlined
above "improper temperature". |
| Too hot |
Add water to mortality area. |
| Problem |
Cause |
Possible Solution |
|
Animals/Vermin
|
Inadequate
protection |
Add substrate ensuring 0.6 m (2 ft.) of cover.
Construct a fence around the site.
Enclose bin structure.
|
| Top of Page |
For more information:
Toll Free: 1-877-424-1300
Local: (519) 826-4047
E-mail: ag.info.omafra@ontario.ca
|