Horse Manure Management
by J.G. Davis and A.M. Swinker1
Quick Facts...
- An average 1,000-pound horse produces 9 tons of manure a
year containing valuable fertilizer elements.
- Horse owners have a responsibility to manage the manure
that is a byproduct of their industry.
- Manure is commonly stockpiled prior to use. Adequate
storage area allows for greater flexibility in timing of
manure use.
- Recordkeeping is an essential factor in land application
of manure/compost.
- The total fertilizer value of the manure produced by
Colorado’s horses is estimated to be $10 million per year.
An average 1,000-pound horse produces 9 tons of manure a year
(50 pounds per day) containing valuable fertilizer elements.
(See Table 1.) Add to that an additional cubic foot of bedding
material and you get 730 cubic feet/year from one horse. How the
manure is stored and treated has a substantial impact on its
value. The labor, storage and utilization costs for manure
management can be considerable.
Colorado’s horse industry uses two principal feed management
systems, according to a recent survey. The first system permits
horses to graze full-time on pastures, and the manure is not
collected or treated. Pasture manure usually is spread by harrow
cultivation that promotes decomposition.
The second system confines animal feeding, which relies on
intensive management, and the horses are kept in stalls or runs.
The horses may be housed in box stalls and provided a bedding
source for urine absorption. Alternatively, horses are kept in
corrals or runs, and some runs are attached to stalls. Manure is
managed in one or more of the following ways: 1) compost (manure
is removed daily and composted); 2) stockpile (manure is removed
daily and stored in piles); and, 3) daily land application
(manure is removed daily and spread on cropland).
Marketing Plan
Horse owners have a responsibility to manage the manure that
is a by-product of their industry. Develop a management plan for
manure and soiled bedding. Use it on crop lands, arena surfaces,
trail surfaces, and landscaping. If you don’t plan to use the
manure yourself, develop a marketing plan so others can make use
of it.
Contract or donate compost to crop farmers and community
landscapers or parks, and neighborhood gardeners. Offer a
discount to boarders if they dispose of manure. The people who
come to watch others ride are another potential market for
manure or compost sales. Before you can market the product, it
must be completely and properly composted and free of foreign
material such as pop cans, wire, and syringes.
Make an arrangement or contract with a landscaper, nursery or
crop farmer. Be prepared to handle your own by-product. One
option may be to deliver manure, at your cost, to a site where
contractors do the composting. Pre-determine the bedding types
they prefer in their compost mix.
Manure Collection
Confinement Housing (Stalls, Drylots, and Runs). Daily
maintenance of horses in a confinement setting requires
intensive labor. Horses housed in stalls and sheds require soft
absorbent bedding. The most common bedding sources in Colorado
are pine sawdust (80 percent), pine wood chips (17 percent), and
straw (2 percent). Some other sources are shredded newsprint,
peanut shells, peat moss, rice hulls, etc. Remove manure and
soiled bedding on a regular basis and handle appropriately to
prevent fly infestation and disease transmission.
Pastures. Manure management in pastures depends
primarily on getting good distribution of manure across the
pasture.To avoid manure concentration in isolated spots in a
pasture, distribute grazing evenly. Rotational grazing is one of
the best ways to achieve this goal; however, horse owners don’t
usually have large enough pastures for rotational grazing.
On the other hand, pastures can be split, and the horses
moved back and forth between both parts of the pasture to
distribute the manure more uniformly. Availability of several
watering facilities and moving feeding facilities periodically
will encourage better manure distribution.
Avoid grazing during rainy periods when soils are saturated,
to avoid soil compaction and manure runoff. Restrict access to
streams to avoid manure deposition in or near water bodies. This
can be done by fencing or providing shade away from the streams.
Refrain from excessive stocking rates that lead to overgrazing.
Damaging the grass stand increases manure runoff potential from
pastures.
Storage and Treatment
Stockpiling. Manure is commonly stockpiled prior to use.
Adequate storage area allows for greater flexibility in timing
of manure use. Therefore, be sure you have a large enough
storage area to accommodate the manure produced. Over time, the
manure shrinks from decomposition and moisture loss.
Proper site selection for the storage area is important to
safeguard against surface and groundwater contamination. Place
stockpiles at least 150 feet away from surface water (creeks and
ponds) and wells. Establish and maintain grass buffer strips
between water bodies and manure piles. Construct a perimeter
ditch or berm around the storage area, if needed, to prevent
runoff onto or off of the area.
Composting produces a relatively dry end-product that
is easily handled and reduces the volume of the manure (40
percent to 65 percent less volume and weight than the raw
manure). Composting at proper temperatures can kill fly eggs and
larvae, pathogens and weed seeds. Compost has less of an odor
compared to raw manure and is more easily marketed. Composted
manure acts as a slow release fertilizer and an excellent soil
conditioner.
To be done right, composting requires an investment of time
and money. Machinery required includes a tractor, a manure
spreader and a front-end loader. Some ammonia-nitrogen is lost
during the composting process, and an ammonia odor may result
for a short period. When composting is done on a large scale,
additional land and machinery requirements exist.
Microbes that drive the composting process require optimum
conditions of temperature, moisture, oxygen, and carbon:nitrogen
(C:N) ratio. The C:N ratio should be between 25:1 and 30:1;
horse manure has an estimated C:N ratio of 50:1. With the
addition of bedding material (high carbon content), the C:N
ratio will be even higher. Therefore, N has to be added to the
manure for it to compost properly. The addition of grass
clippings, hay, or fertilizer [25 to 30 pounds N/ton of manure
(75 to 90 pounds of ammonium nitrate or 50 to 65 pounds of
urea)] should bring the C:N ratio into the optimum range. When
microbes work properly, the compost temperature will be between
120 and 160 F. Cooler temperatures result from a lack of N. When
the composting process is complete, the temperature will cool
naturally.
It is important to have the right balance of moisture and air
for the microbes to process the manure. The compost should be
moist but not soggy, and may need to be watered or covered with
plastic to maintain moisture. Aerate the compost by turning it
regularly. The manure and bedding particles should be about
one-half inch to one and a half inches in size. Composting does
require effort, but the result is a more easily used and
economically valuable fertilizer.
Utilization
Land Application. Recordkeeping is an essential factor
in land application of manure/compost. It is critical to know
how much manure/compost was applied to each field and when it
was applied. Analyze manure/compost regularly and record the lab
results for future reference. Note changes in nutrient value and
factor them in when calculating future application rates.
Manual loading and land application are labor intensive and
impractical for managing the manure generated by more than 25
horses. Consider mechanical loading and application with a
bobcat or tractor-operated loader when the manure or the land
application becomes large.
Apply the manure/compost uniformly to achieve an acceptable
application rate. The finer textured and more uniform the
manure, the easier it is to apply uniformly. Spreaders apply
manure/compost at different rates depending on ground speed, PTO
speed, gear box settings, discharge openings, and manure
moisture and consistency.
Do not apply manure to land that is highly erodible, frozen
or saturated. To protect water sources from manure runoff, do
not spread manure within at least 150 feet of a water source
(such as a well, creek or pond). Incorporate manure into the
soil as soon as possible. Mixing the manure with the soil
immediately reduces losses of manure nutrients to runoff and
volatilization, and reduces odor problems associated with manure
left on the soil surface.
Base the manure/compost application rate on crop N needs and
available soil and manure N levels. Test your soil and manure
for N levels at a certified laboratory. In general, the higher a
crop yield goal, the greater the N requirements. Irrigated crops
also tend to need more N. If yield goals are lower than those
shown in Table 2, decrease the manure application rate and
increase the land application area. If yields are higher, less
land is needed. Soils high in organic matter and nitrate have
higher available N in the soil and require less N.
| Table 1: Average fertilizer content in horse
manure (as-is basis). |
|
N/ton
|
19 lb
|
|
P2O5/ton
|
14 lb
|
|
K2O/ton
|
36 lb
|
|
Table 2: Average manure application rates and
land base (area) requirements for forages.
|
|
Forage
|
Yield
|
Annual Horse Manure Application
|
Land Base Needed
|
| |
(tons/acre)
|
(tons/acre)
|
*(acres/horses/yr)
|
| Alfalfa |
2.0
|
15
|
0.6
|
| Alfalfa-grass |
2.0
|
10
|
0.8
|
| Bentgrass |
1.0
|
10
|
0.8
|
| Big bluestream |
1.5
|
5
|
1.8
|
| Birdsfoot trefoil |
1.5
|
12
|
0.8
|
| Bluegrass |
1.0
|
10
|
1.0
|
| Bromegrass |
1.5
|
10
|
1.0
|
| Little bluestem |
1.5
|
6
|
1.6
|
| Orchardgrass |
2.0
|
10
|
1.0
|
| Red clover |
1.5
|
10
|
0.8
|
| Reed canarygrass |
2.0
|
9
|
1.0
|
| Ryegrass |
2.0
|
11
|
0.8
|
| Switchgrass |
1.5
|
6
|
1.6
|
| Tall fescue |
2.0
|
13
|
0.6
|
| Timothy |
1.5
|
6
|
1.6
|
| Wheatgrass |
0.5
|
2
|
3.8
|
| *The land base needed is the cropland
requirement for manure application alone, not for
grazing and forage needs. One ton = 2,000 lbs. One acre
= 43,560 sq ft. |
Landfill. Manure and compost are sometimes landfilled,
dumped in gullies and used to repair roads. These are not
recommended practices due to high runoff and leaching potential
from gullies and roadways. If the areas are not vegetated and
are waterways for storm runoff, the potential for runoff of
manure nutrients into creeks and ponds is high. When excessive
nutrients exist in surface waters, plant and algal growth
becomes extreme, the oxygen supply is depleted, and fish can be
killed.
Footing for Riding Arenas. An ideal arena surface
provides resilient footing for optimum horse performance. Drain
the arena well, maintain adequate depth to protect horses’ legs
from contusions, and keep the arena absorbent to hold moisture
efficiently and prevent dust. The arena surface also must be
odor-free. Composted manure/bedding makes an ideal surface
addition when mixed with river sand and wood products.
Uncomposted manure and bedding results in ammonia fumes that can
cause respiratory problems in horses. Surface depth of compost
depends on soil type and climate; too much organic matter can
hold excess moisture and may cause the horses to slip and fall.
| Table 3: Maxium manure application
rates to avoid soil salinity problems. |
| Manure EC* |
|
Soil EC* |
|
| |
1
|
2
|
3
|
|
10
|
84 T/A
|
56 T/A
|
28 T/A
|
|
20
|
30 T/A
|
20 T/A
|
10 T/A
|
|
30
|
18 T/A
|
12 T/A
|
6 T/A
|
|
40
|
12 T/A
|
8 T/A
|
4 T/A
|
| *mmhos/cm; T = Ton; A = acre |
| EC = electrical conductivity
measured in units of millimhos/centimeter. Note: The
manure application rate should be based on N needs of
the crop within this maxium range. This table assumes
that manure is not incorporated, which is typical for
perennial forage crops. |
Precautions
Virtually no viral diseases are transmitted between horses
and humans through fecal material, but some bacteria and
protozoans (such as E. coli and Giardia) can be transmitted in
this manner. Therefore, handle manure carefully to prevent
disease transmission. In addition, horse manure runoff into
waterways may produce fecal coliform contamination levels that
can be potentially hazardous to fish and anyone who drinks that
water.
Runoff. Runoff water from dry lots, pastures, and
manure storage or compost areas carries pollutants (such as
nitrogen, phosphorus, and bacteria) into surface waters. Avoid
overirrigation of pastures. Build berms or trenches to prevent
water from entering or leaving dry lots and manure storage and
composting areas. Do not allow a creek or irrigation canal to
pass through drylots.
Parasite Prevention and Control. Horses pick up
parasites by ingesting grass, feed, or water that is
contaminated with parasite larvae and eggs. The most common
internal parasites of horses are the ascarids, strongyles (large
and small), pinworms and bots.
Insect Control. Excellent fly-breeding conditions
occur in mixtures of manure, spilled feed and decaying bedding.
To help eliminate these areas, remove and spread the manure
regularly and prevent accumulation of other wastes. Composting
at proper temperatures inhibits fly development. Several
pesticides can be used on manure piles to kill maggots. Cover
manure stockpiles or compost sites to exclude flies and prevent
their development.
Noncomposted manure piles can provide an ideal environment
for the bumble flower beetle white grub. White grubs feed on
decaying manure; however, these grubs do not damage home lawns.
Therefore, there is no need to control them.
Mosquitoes require standing water to reproduce; therefore, it
is imperative to prevent ponding of water in manure storage
areas.
Salinity. Manure tends to be high in salts, which when
land applied at excessive rates, contribute to soil salinity.
Soil salinity causes plants to become water stressed or, in
extreme cases, die. When manure is not soil-incorporated, as in
applications to pasture, the salts accumulate on the soil
surface unless they are leached into the subsoil. Irrigation or
rainfall may move salts out of the topsoil and move them into
deeper depths of the soil profile. If salinity levels in the
soil and manure are known, use Table 3 to determine acceptable
maximum rates of manure application for most forages to avoid
excessive soil salinity (>4 mmhos/cm).
Weeds. A weed is an unwanted, out-of-place plant.
Weeds compete with crops for limited resources of water,
nutrients and light. Manure has contributed to weed problems
where it has been applied to cropland. Use composted manure to
avoid these problems. When manure is composted, the high
temperatures achieved during the composting process kill most
weed seeds. Some weed infestations may be the result of
overgrazing, not due to manure applications.
Parasite Preventions and Controls
Deworm all horses on a regular schedule using an
anthelmintic. Contact a veterinarian for anthelmintic
recommendations.
Manure management:
A. Remove all manure from stalls, small corrals, and paddocks on
a daily basis.
B. Compost all manure to a temperature of 145 F for at least two
weeks to kill most parasite eggs, or compost at lower
temperatures for longer periods of time.
C. Spread manure on pastures only after composting.
D. Manure that has not been composted should be spread only on
crop land or other ungrazed, vegetated areas.
Pasture management:
A. Mow two to four times a year and chain harrow (drag) to
break up manure piles and expose parasite eggs to the
elements.
B. Don’t overstock.
C. Practice rotational grazing if possible.
D. Graze young horses separately from older horses; the
younger horses have a higher susceptibility to parasites.
E. Follow horses with cattle or sheep before returning a
pasture to horses. This interrupts the life cycles of horse
parasites.
F. Deep harrow or plow pastures that are badly
parasite-infested. Deep plow pastures and reseed every three
to five years. This also helps break parasite cycles.
Feed and water management:
A. Use feeders, racks, bunks or mangers for feeding hay and
grain. This will prevent feed from getting mixed with feces.
Don’t feed off the ground.
B. Provide horses a clean, fresh drinking water supply.
C. Avoid water contaminated with feces.
Resources
Spencer, W., and D. Tepfer. 1993. 3.762, Economics of
composting feedlot manure. Colorado State University Extension.
Wilson, C.R., and J.R. Feucht. 1991. 7.212, Composting yard
waste. Colorado State University Extension.
Waskom and Davis. 1999. BMPs for Manure Management, Colorado
State University bulletin no. 568a.
1J.G. Davis, Colorado State University
Extension environmental soil specialist and professor, soil and
crop sciences; and A.M.Swinker, former Extension horse
specialist and associate professor, animal sciences. Reviewed
1/2002. |