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The Impact of Dairy Bedding On Manure-Management SystemsFew dairy farmers enjoy discussing the problems of manure management. Yet, survivability in this industry may depend on the priority producers place on adequate management of dairy waste. Livestock manure represents a potential pollutant that can adversely affect water quality if allowed to enter surface or ground water sources. The public demand assurance their water supplies are protected. This public sentiment significantly affects manure management on Mississippi dairy farms. Manure-management systems are highly influenced by bedding materials. This publication includes information to consider when planning new waste-management systems on dairy farms or changing a system to meet new regulations and changes in facilities. Mississippi dairy producers
have renewed interest in waste management due to new regulations introduced
in 1992. These regulations are the result of an amendment by the U.S.
Environmental Protection Agency (EPA) to the Federal Clean Water Act established
in the early 1970's. The amendment basically eliminates the provision
for legally discharging from an animal waste lagoon into "Waters of the
State." Any body of water not completely confined within the dairy producer's
property is considered a "Water of the State" by the Mississippi Department
of Environmental Quality (DEQ). This includes streams, ponds, lakes, waterways,
sinkholes, drainage ditches, and groundwater. All new dairy facilities
must be designed and operated as "No Discharge" systems. This means manure,
urine, clean-up water, and lagoon wastewater from dairy operations must
not be allowed to leave your property. A dairy production facility designed
as a "No Discharge" system must contain all wastewater and contaminated
storm water runoff, from a 25-year, 24-hour storm event, on the property. The number of herds
in Mississippi continues to decline; however, the number of cows per herd
and the production per cow are rising. With increasing herd size and the
increase in management intensity, more confinement feeding and housing
are available. These trends have the potential to create new problems
for Mississippi dairy producers. As cows per herd increase,
dairy producers must place additional emphasis on cow comfort and animal
health. This places an additional load on existing waste-management facilities,
and many dairy farms will have to expand any waste-treatment capabilities
or build new ones. To be competitive in
the future, Mississippi dairy producers will need to develop efficient
strategies for handling dairy waste in an economically and environmentally
responsible manner. Generally speaking,
larger herds require more confinement, and cows spend more time in concrete-floored
holding facilities and in potentially uncomfortable environments than
do cows in small herds. Concrete allows for easier cleaning (waste removal)
and reduces mud problems during wet weather conditions. However, cows
on concrete for long periods of time experience a certain amount of stress.
Another factor to consider is the number of disease-causing pathogens
in the cow's environment. The goal of most dairy
managers is to reduce stress by providing comfortable and clean bedding
areas off the concrete and to keep the environment clean, thus reducing
the potential for contact between pathogens and cows. The fact that various
types of environmental stress influence the immune response bears relevance
of dairy cattle to infectious diseases such as pneumonia and mastitis. Providing good cow comfort
while maintaining a low pathogen level is directly related to the management
of dairy waste. Concrete-floored confinement facilities allow manure removal
methods such as "scrape and haul" and "flush" systems. These systems,
when managed properly, can reduce pathogens. Construct your dairy housing
facilities so they provide efficient clean-outs and maximize cow comfort. Techniques used on many
dairies to reduce heat stress also influence a waste-management system.
Providing shade for larger herds necessitates additional confinement,
and therefore, increases the quantity of manure and urine the waste-management
system must process. In addition, sprinkler/mist systems used for cow
cooling produce additional water the current waste system may (or may
not) be able to process. Proper management is
the most important aspect of bedding. No matter which bedding you choose,
proper management determines how effective the bedding is in increasing
cow comfort and reducing mastitis outbreaks. You can use organic and inorganic
bedding materials successfully when managed properly. Base your bedding choice
on your resources available, including labor, time, raw materials (sand,
shavings, sawdust), machinery, and the type of waste-treatment system
used at your dairy. In particular, free-stall bedding choices can have
a dramatic impact on the waste treatment lagoon. Two classifications
commonly used in categorizing bedding materials are organic and inorganic.
Each type of bedding has advantages and disadvantages. Organic bedding
materials (for example, sawdust, shavings, rice hulls) are natural products
containing carbon and other elements. Organic bedding can
provide a suitable substrate for the growth and reproduction of microorganisms.
Substrate is a base material that provides the necessary moisture, nutrients
(food), and pH for microorganisms to reproduce. Sawdust and wood shavings
are the most common organic bedding materials used by Mississippi dairy
producers. These materials work well with liquid-manure handling systems
because the microbial activity of the lagoon eventually breaks down the
bedding. In addition, you can easily remove these types of bedding from
the waste-stream with commercially available manure/solids separators. Sand is an inorganic
bedding material comprised principally of silicon with little or no carbon.
Since carbon is the building block for all living things, inorganic bedding
materials do not provide a hospitable substrate (nutrients, pH) to support
the growth and reproduction of microorganisms. Unfortunately, these types
of bedding can cause problems in the waste-treatment system. The waste-management
system used in your dairy should influence bedding choices. Dairies that
use scrape and haul waste-removal system (no lagoon) can use organic or
inorganic bedding with little or no problematic ramifications. Since scrape and haul
systems use standard manure spreaders for land-applying the waste, the
incorporation of sand (inorganic) and/or organic bedding materials into
the waste stream typically does not cause problems. In fact, the incorporation
of inorganic bedding on receiving land areas can be advantageous from
a soil structure standpoint. Large dairies, which
are becoming typical in Mississippi, often use flush-type waste removal
systems. Flush systems use the hydraulic energy of large quantities of
water released quickly to wash manure, waste bedding, and urine into the
treatment lagoon. These systems have advantages in that they allow free-stall
and holding areas to be kept clean by facilitating multiple clean-outs
each day. Flush waste-removal systems necessitate the incorporation of
a waste-treatment lagoon. Lagoon-treatment systems
(typically anaerobic in the southeastern United States) use naturally
occurring bacteria to break down organic substances into simpler substances
and water. In addition, some nitrogen volatilization (loss of nitrogen
gas to the air) occurs in most lagoons. Lagoons are designed to treat
a specific quantity of organic waste such as manure, urine, and limited
quantities of other organic materials such as bedding. Organic bedding materials
such as shavings and sawdust will break down in the lagoon, but it may
take a long time to do so. These materials sometimes float on the surface
of the lagoon and may increase surface crusting on the lagoon. Since chunks
of bedding and other large debris will be in the lagoon, you must use
specialized irrigation equipment (systems with nozzles large enough to
pass bulky solids) to land-apply the lagoon wastewater. If you own or
have access to a propeller agitator and solids-handling irrigation equipment,
the influx of organic bedding into the lagoon should not cause problems. If you use standard
irrigation equipment for land-applying lagoon wastewater, or if the receiving
lagoon is undersized, you can install a manure/solids separator upstream
of the lagoon to remove most bedding solids. Inclined-screens, screw presses,
hydro-cyclones, and drag screens are typical manure/solid separators. These systems screen
large bulk solids, while allowing liquid and smaller manure solids to
pass through. These systems are effective in removing organic bedding
and some manure solids. Generally these systems will screen enough solids
to allow the use of standard (clean water) irrigation equipment. In addition,
research indicates that solids removed by these separators can be reused
as animal bedding in some instances. The obvious disadvantage of these
systems is moving parts. Any mechanical device placed in an animal-waste
stream will require upkeep and maintenance. The tremendous hydraulic
energy of flush-type manure-removal systems also transports waste sand
bedding to the treatment lagoon. In free-stall barns bedded with sand,
virtually all of the sand is eventually washed into the lagoon. This is
unfortunate, since lagoons are not capable of breaking down inorganic
substances such as sand or limestone. As inorganic bedding
(sand) is flushed into the lagoon, the liquid volume of the lagoon is
decreased. Since lagoons are designed on a volumetric basis, the addition
of large quantities of sand can, over time, severely reduce the lagoon's
ability to function as designed. This can result in lagoon overflows and/or
odor levels above those normally associated with a properly functioning
lagoon. Fortunately, sand is
easy to remove from the flush water with the addition of a sand trap upstream
of the treatment lagoon. A sand trap is nothing more than a concrete sump
that allows the velocity of the flush water to be reduced such that the
sand settles in the trap. Generally, reducing the flush water velocity
to 1 foot per second or less, with a retention time of 1 to 2 minutes,
is sufficient to trap sand. Design your sand traps
to allow easy access by front-end or skid-steer loaders (access ramps
with 10:1 to 12:1 slope are typically sufficient). Base the size of the
sand trap on the size of the herd, number of hours of confinement, and
clean-out interval. Clean-out interval is a management decision, but should
not exceed 2 weeks. Contact the Natural Resources Conservation Service
(NRCS) for specific design information. Design the outlet from
the sand trap to handle the largest surge of flush water from the housing
facilities or the flow from a 10-year, 1-hour storm event, whichever is
greatest. Do not confuse sand traps with gravitational manure/solids settling
basins, which are larger and have a much longer retention time (velocity
1 foot per second maximum, retention time 2 hours or more) than sand traps. Screen-type manure/solids
separators, which are excellent for removing organic bedding materials,
typically do not remove significant quantities of sand. Dairy producers
using sand bedding should not consider these an an alternative to a well-designed
sand trap. The increase in cows
per herd and the change in state environmental regulations have increased
interest in waste management on Mississippi dairy farms. Most dairy farmers
with partial or full confinement systems are forced to make major modifications
or to construct new waste management systems. The bedding used in
housing facilities is a major factor to consider when making these changes.
Bedding affects the cleaning system, waste storage needs, separation technologies
needed, cow comfort, and the environment for disease-causing pathogens.
Exercise careful and extensive planning, considering the cow and the environment,
when planning or changing a dairy-waste-management system. Mississippi
State University does
not discriminate on the basis of race, color, religion, national origin,
sex, age, disability, or veteran status. Publication
2195 Copyright by Mississippi
State University. All rights reserved. |
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