The University of Georgia
Cooperative Extension Service
College of Agricultural and Environmental Sciences
 
 
Livestock Newsletter

May/June 1999


Table of Contents



Environmental Assistance for Swine Producers

Tim Schell
Extension Swine Specialist

As the new environmental regulations for swine are being finalized, there are a few things you can do to prepare yourself and your farm. Two programs offered by the Georgia Pork Producers Association and the National Pork Producers Council (NPPC) can help you improve your environmental stewardship and prepare you for the new regulations. These programs are the Environmental Assurance Program and the On-Farm Odor/Environmental Assistance Program.

The Environmental Assurance Program offers training on the fundamentals of pollution control. The program helps producers evaluate how they are doing environmentally and helps them develop an environmental plan. The training is divided into several areas including odor and emissions, pollution prevention, manure storage and handling, composting and community relations. This program is an excellent way to familiarize yourself with environmental issues in a relaxed atmosphere with other producers. Plans are currently being made to offer this training in the next few months. If you are interested participating in the training, contact the Georgia Pork Producers Association at (800) 537-5988.

The second program, the On-Farm Odor/Environmental Assistance Program offers an on-farm assessment of environmental stewardship. The goals of this program are to promote environmental stewardship and to minimize the impact of swine production on watersheds. This program offers producers an opportunity to get confidential, on-farm, one-on-one advice on environmental issues.

After producers submit a short checklist about their farm, the NPPC assigns two certified assessors to schedule a farm visit and walk the farm and discuss good environmental practices and offer suggestions in areas of concern. The assessors will then prepare a written report that will become the property of that farm. Producers can take advantage of this program at no charge by calling the Georgia Pork Producers Association at (800) 537-5988.

Both of these programs are excellent ways to gain knowledge about how swine producers can improve environmental stewardship. In many cases producers are pleasantly surprised at how many things they are doing right. I encourage you to take advantage of these programs, they can go a long way towards alleviating concerns about new environmental regulations.
 
 


Environmental Responsibilities of the Georgia Pork Industry

Rick Jones, PhD
Professor and Extension Animal Scientist

Introduction

Pork producers have the obligation to operate their farms in an environmentally responsible manner no matter how large or small they might be. State and federal regulations are designed to deal with production systems based on the size of the unit or number of animals housed. The number of animals correlates with the amount of wastes produced and the potential impact that the unit could have on the surrounding environment. It is important for animal science students to be fully aware of the major concerns relative to livestock wastes and to understand the basic principles for the proper storage, handling and use of wastes. It is also critical to understand the potential economic impact (costs and benefits) of proper nutrient utilization on cropping systems and the costs of meeting regulatory requirements.

Major environmental concerns

The major concerns relative to wastes and livestock production that are foremost in the public interest are obviously water and air quality issues. The potential impact of pork production on water quality relates to either contamination of surface waters or groundwater. The main contaminants found in animal wastes can be categorized as nutrients or microbial in nature. In the case of nutrients, the specific compounds of greatest concern are nitrogen and phosphorus. Nitrogen in the elemental form is a colorless, tasteless, odorless gas which constitutes 78 percent of the air we breathe. The environmental issues relative to nitrogen are the potential for the toxic effects of NO3 or nitrates or the increased growth of various plants when provided with ample nitrogen. This plant growth then may negatively impact an environment through oxygen depletion or competitively overwhelming other species.

Excessive plant growth is a key concern with excessive phosphorus loading in the environment. When phosphorus levels no longer limit the growth of plants, a rapid explosion of plant growth results in oxygen depletion in surface waters causing the loss of fish and other aquatic species. Physical clogging of waterways may also occur in extreme cases.

Other nutrients fed to livestock to support normal animal growth have the potential to be toxic, especially when concentrated in the environment over years of dietary use. Zinc and copper are two such nutrients.

The potential for nutrient contamination of surface waters is most likely through over-concentration of animals in watersheds and the action of rainstorms in placing dry forms of nutrients in soluble form in creeks, ponds and other larger water bodies. Also, there is the potential for lagoon effluent to be improperly applied to spray fields resulting in more direct contamination. On rare occasions, lagoon berms have been breeched accidentally (hurricanes, etc.) or intentionally with resulting contamination. More recently, the impact of NH3 (ammonia) from livestock waste systems on the environment has become of interest. The volatilization of nitrogen in the form of ammonia from animal wastes adds to atmospheric NH3 and increases the formation of ammonium salts (NH4Cl, etc.) which fall to earth in rain drops.

The impact of nutrients, especially nitrogen, on groundwater quality may be through contamination of well water which is most likely to occur if well heads are not protected from surface water intrusion or if improperly constructed lagoons leak effluent into the aquifer. Proper capping of wells and diversion of storm water may solve some ground contamination problems over time. Synthetic liners for lagoons and other in-ground waste storage facilities have some merit; however, liners may actually be less effective than properly designed clay liners in the event of natural disasters such as earthquakes. Much of the negative reporting on clay lined lagoons relates to older structures designed without proper engineering techniques.

Microbial contamination

The potential for microbial contamination of the environment from livestock waste facilities has been of lesser concern until recently. With the discovery of antibiotic-resistant pathogenic organisms in our environment, the potential for catastrophic exposure of the public to such organisms became more realistic. In general, methods of handling animal wastes will come more under the same scrutiny as municipal or human waste systems.

Air quality/odor production

Currently the impact of livestock facilities on air quality in Georgia is governed mainly through nuisance law relative to odor complaints. In some states there are specific air quality statutes which have been used to regulate livestock production. The main impact of livestock waste facilities on air quality relates to odors although the potential for chronic or lethal toxic effects are well known. Digestion of nutrients in animal wastes by bacteria and Archea produces several hundred different types of gaseous by-products. The design and loading rate of the waste handling system determines the extent of microbial digestion and the relative amounts of these gases.

The main gases of concern are:

Waste handling system effects

The deep-pit waste system involves a high-loading rate and favors minimal digestion of nutrients and production of metabolic end products (gases). With this type of system the gases/odors tend to be predominately H2S (hydrogen sulfide) and VOCs (volatile organic compounds). A manure holding basin is next in the progression toward lower loading rates and typically produces even higher levels of odor possibly correlated to higher VOCs and comparable H2S levels. An under-sized lagoon has lower loading rates that are still too high for existing microbial growth conditions. The result is increased gaseous end products (NH3 and Methane) and still significant VOCs and H2S levels. Perceived odor levels are probably greatest with basins or greatly under-sized lagoons. With a properly designed and managed lagoon, VOCs are minimal and the H2S, NH3 and methane are maximal. Odor intensity tends to subside.

VOCs have been monitored in basins and deep pit systems and it appears that VOCs with potential risks to human health are usually found at concentrations at least one order of magnitude less than permissible exposure levels. Therefore, it would appear that VOC's may be more important from an odor/nuisance standpoint than from a human health perspective.

Waste handling principles

The basic principles driving the design and management of animal waste handling systems were once to "get rid" of the wastes. Anaerobic lagoon processing and storage of waste nutrients has become the most workable, economical system for the climate and agronomic conditions of the South. Use of lagoon effluent to provide the water and fertilizer requirements of rapidly growing bermuda pastures became the accepted system. However, the high proportion of phosphorus relative to nitrogen in pig wastes led to over-fertilization with phosphorus. Many environmentally conscious scientists have been calling for nutrient management to be based on the phosphorus content of the wastes, not nitrogen.

With continued economic and regulatory pressure, the principles are now focused on recapturing economic value of nutrients with methods acceptable to regulatory agencies. The term "Comprehensive Nutrient Management Planning" (CNMP) will soon guide most decisions relative to waste handling in livestock facilities. A CNMP addresses all of the principles relative to feed management, manure handling and storage, land application of manure, land management, record keeping, etc.

The first principle of a CNMP is to manage feed and water resources to minimize the amount of nutrients which end up in pits, lagoons and spray fields. From a dietary standpoint, this means increasing the efficiency with which dietary nutrients are converted to lean, marketable tissues in the animal. One goal is increasing the digestion and absorption of dietary protein so that less nitrogen ends up as urea in the urine. Another approach is to supply more of the needed amino acids as synthetic, highly metabolizable sources such as lysine hydrochloride. Increasing the digestibility of phosphorus supplied by common feedstuffs such as corn can allow the nutritionist to lower overall dietary phosphorus levels thus reducing waste levels. This is currently being accomplished with the use of synthetic phytase in pig diets.

Proper design and management of feeders can reduce the amount of feed that is wasted by pigs thus reducing the nutrient levels in pits and lagoons. Newer designs for waterers are greatly reducing the amount of waste water which, in-turn, reduces the potential for surface water contamination. Alternatives to lagoon-based waste handling technologies are being touted as the answer to many problems. However, research is currently lacking. Deep-bedded housing of pigs offers one such alternative; however, producing wastes in a solid form may actually aggravate surface water contamination.

Regulatory activities

The pressure from public interest groups and scientists has led to proposal and establishment of more extensive regulations on the federal level (EPA) and more recently the state EPD (Environmental Protection Division - part of the Department of Natural Resources). A year-long stakeholders input exercise coordinated by EPD has involved farmers, environmental activists, environmental lawyers, scientists, public interest lobbyists, commodity organizations and other interested individuals. EPD proposed the basic structure for new regulations out of the deliberations of this stakeholder's process. However, the Natural Resources Board has intervened in the process and forced the hand of EPD to include specific items without further delay. The proposed new regulations are expected later this month (April '99) for 60 day public comment and passage at the June Board meeting. The economic impact on a struggling pork industry is yet to be seen.

Proactive pork industry programs

The U.S. Pork Industry recognized many years ago that environmental issues would be critical to the survival of pork production in the continental U.S. The National Pork Producers Council became proactive and developed an education/certification program known as Environmental Assurance to provide a basis for informed decisions.

NPPC joined with America's Clean Water Foundation to develop a national environmental dialogue on pork production. NPPC also worked with the Environmental Protection Agency to establish the Compliance Audit Program (CAP) to facilitate the up-grading of waste handling systems with minimal penalties for pork producers. Currently, NPPC is operating the On-Farm Odor Assessment/Environmental Assistance program with teams of technicians trained to provide practical solutions to environmental problems.
 
 


Relating Pork Production Operation Size
to Animal Unit Measures

Dr. Rick Jones
Professor and Extension Animal Scientist

Although it has introduced much confusion into the discussions relative to Georgia's Water Quality regulations, the relationship between pork production operation size and "animal unit" (AU) measurements is a necessary evil. The conversion of pig inventories to animal units is to allow comparisons of species on their relative waste output.

The animal unit measure was devised by agricultural engineers and is based on a typical beef cow equaling one animal unit. A sow is considered to equal 0.4 animal units because the typical sow produces 0.4 times (or 40%) as much waste as the base cow. [The validity of this relationship will not be discussed here.] The animal unit conversion of other pigs assumes that each pig over 55 lb body weight also equals 0.4 animal units. This is a crude method of relating the waste production of the average pig to that of a sow and a cow.

The complicated part involves the relationship of AU to more practical measures of the size of a pork production operation. Farrow-to-finish (FTF) operations have been the standard in the industry until the last 5-10 years when multi-site production became more common. Much of Georgia's production is still FTF due to limited growth in recent years. The size of a FTF operation is generally described by the average size of the sow herd itself. This assumes that all of the pigs nursing sows, weaned into nurseries and found on growing-finishing floors are also included in the "size" of the operation.

Therefore, to relate the size of a pork production operation to animal unit basis, one would have to inventory the sow herd (including replacement gilts) and add all herd boars and pigs that weigh over 55 lb. This would exclude the counting of nursing pigs and weaned pigs in the nursery since they weigh less than 55 lb. On a particular operation, this could be accomplished by averaging weekly inventories and is part of modern computer record systems used on some farms. This count is then multiplied by 0.4 to give the number of AU.

To improve the understanding of these size measures for deliberations over environmental regulations, a simple computer model has been devised to relate sow herd size to animal unit inventories. This spreadsheet takes into account the production schedule being used (frequency of farrowing, farrowing capacity, weaning age, breeding days/cycle and percent of capacity attained). It allows input of various performance parameters that influence the number of pigs that will be associated with each sow in inventory. These parameters include: farrowing rate, culling percentage, gilt pool efficiency, matings/service, pre-weaning mortality, nursery mortality, grow-finish mortality, and average market age.

Using this model, standard sized operations were analyzed to give inventories of different phases of production, the total animal unit measures and the projected annual nitrogen production. Certain key operation sizes (100, 600 and 1200 sow herd sizes) and key animal unit levels used in Georgia environmental regulations (300, 1000 and 3000 AU) were used and appear in tables below. The nitrogen production values are calculated using North Carolina State University data and includes nitrogen found in anaerobic lagoon effluent and lagoon sludge. It does not include nitrogen produced but lost to the atmosphere from lagoons. Also in the land application process, a significant portion of this "produced" value might be lost to the atmosphere and has an unknown impact on on-site water quality.
 
Farrow to finish production inventories, animal units and nitrogen production 
Animal units 262 300 1000 1745 3000 3476
Avg. sow inventory 100 115 342 600 1034 1200
Avg. boar inventory 10 11 9 16 28 33
Avg. pigs nursing 111 127 438 763 1310 1518
Avg. pigs in nursery 208 237 820 1429 2454 2845
Avg. pigs in grow-finish 544 622 2149 3747 6434 7459
Lb N prod/year * 7493 8568 29207 50949 87505 101455

* Does not include N lost to atmosphere.
 

Operations other than farrow to finish

The current trend in pork production is to separate the farrow to finish process into phases of production and isolate those phases at different sites which may be on separate farms and may actually be in different states, thousands of miles away. The basic justification for this multi-site approach is the health advantages generally obtained from preventing the transmission of pig diseases from older finisher pigs to younger pigs and the isolation of the breeding herd. This multi-site approach also has a dramatic effect on the partitioning of the waste production and the relative impact of the various phases on waste production and environmental concerns. The farrow to wean portion involves only the sow herd, nursing pigs and boars. Animals in this phase consume relatively small portions of the total feed (12-13%) and therefore produce a small portion of the wastes and nitrogen (8-9%). The next phase is the nursery or wean to feeder pig phase and these pigs normally are from 12 to 45 lb . These pigs consume about 8 -9% of the total feed and produce about 14-16% of the nitrogen. The final phase is grower-finisher or feeder to finish where pigs consume about 78-80% of the feed and produce 75-76% of the nitrogen.
 



 






With this great variation in the proportions of feed consumed and nitrogen produced, the comparisons between a 1000 sow (400 AU) farrow to wean operation and a 1000 pig (400 AU) grow-finish operation show a great disparity relative to waste production. An 11,000 sow farrow to wean operation would only produce the waste nitrogen of a 1000 sow farrow to finish unit.

The table below puts these different phases of operations into perspective relative to numbers of animals and waste produced. The values in the nursery and grow-finish sections correlate to the number of pigs produced by the farrow to wean operations given in the same column.
 
Multi-site production inventories, animal units and nitrogen production 
Farrow to wean  AU 40 240 300 480 1000 3000
Head 100 600 750 1200 2500 7500
N prod* 771 4340 5422 8676 18075 54243
Nursery - only AU NA NA NA NA NA NA
Head 208 1429 1783 2845 5914 17723
N prod* 1168 8039 10026 16002 33262 99680
Grow-finish - only AU 218 1499 1869 2984 6202 18586
Head 544 3747 4673 7459 15505 46464
N prod* 5620 38686 48248 77007 160073 479708

* Does not include N lost to atmosphere.
 
 


Health Management of Catfish from the Egg to Market

Gary J. Burtle
University of Georgia, Animal & Dairy Science

Catfish health is best managed by considering all aspects of production rather than applying treatments whenever an emergency arises. In order to manage for the best fish health possible, a whole farm plan must be made and followed by everyone on the farm.

Catfish Farm Design. This is an key point of planning toward fish health maintenance and disease prevention. When ponds are filled with water from sources other than groundwater of high quality, the health of the catfish grown in those ponds may be compromised. The water supply system should be designed in order to maintain pond water volume during dry periods of the year. Allowing ponds to remain partially full concentrates the fish and nutrients which results in water quality degradation. Facilities for aeration should be available and adequate for the pond sizes used. At least 2 horsepower and up to 4 horsepower of electric paddle wheel aerator per acre of water is needed to maintain dissolved oxygen levels in catfish ponds. Emergency aerators should also be available.

Marketing to Reduce Disease Probability. Marketing your catfish plays an important role in the control of disease frequency on a catfish farm. Catfish should be sold as soon as they reach the desired market size. Minimizing the time catfish are in your ponds makes good economic sense and reduces the time the catfish are exposed to possible disease pressures. Carrying over older fish and stocking fingerlings under them allows disease transfer. All fish that are captured during seining should be removed from the pond to avoid release of harvest stressed fish. Pond size should be designed so that it matches the volume of fish the market can accept.

Use Clean Seedstock. Fingerling purchase must be controlled. This issue should be given special attention since starting with poor quality fingerlings will be problematic even with the best management thereafter. Fingerling management before purchase should be investigated since nutrition and stocking densities are important to the future health of the catfish. Deliveries of catfish fingerlings should be checked for signs of disease on arrival. Proper treatments should be administered or the fish returned to the source for treatment if disease is discovered. Stocking the fingerling at the right time is important. Hot weather and ESC seasons should be avoided. If the fingerlings are stocked at a time when they will not quickly respond to feeding, diseases may strike the fish as they become nutritionally weakened. Stocking densities of 5,000 to 10,000 catfish fingerlings per acre are used in the industry but the lower stocking densities are less likely to result in disease experiences.

Proper Nutrition. Utilize a completely fortified diet that is obtained from a reliable source. Some commercial diets without certain vitamins have been shown to produce adequate growth under commercial conditions, however, those diets may not be available in areas outside of the Mississippi Delta. Investigate the success of others who have used the diets before switching suppliers. Stick with success. Use the proper particle size for fish size. Inspect each lot of feed as it is delivered for mold, moisture, or fines. Then feed an adequate amount to keep your catfish growing at a rapid rate.

Observation by Trained Personnel. Monitoring catfish ponds for water quality and signs of fish distress is very important. A trained and experienced individual should conduct the monitoring program. Collection of dissolved oxygen values is important on a daily basis and for several times each day. Ammonia and nitrite should be checked weekly. Whenever fish are harvested, a sample should be examined for signs of disease so that the proper treatment can be planned. It is important to remember that monitoring should be a regular task of high priority, even when operations seem to be running smoothly.

Sanitation. Waste disposal is important to the spread of disease. When fish die, they should be picked up out of the pond as soon as possible and preferable within 12 hours. Catfish can be infected by consumption of the dead fish or as pathogens are shed from the carcasses. Burial, incineration, or composing has been utilized for disposal of fish. Local regulations should be investigated before disposing of catfish carcasses. Between crops of fish, the pond should be sanitized by applying chlorine, hydrated lime, or air drying. When ponds are partially harvested, older catfish will transfer any disease they may have to the new stock if an effort is not made to remove most of the old fish. Producers who use water from other ponds should treat and/or filter the water prior to pumping it into new ponds.

Records. Finally, records should be kept of your farm fish health program to allow you to identify areas of potential problems. Missing records usually mean that shortcuts were taken or that treatments were missed. Records will help with the economic evaluation of different treatments and help to decide when to treat a disease or to let it run its course. A good integrated fish health management plan will fit well with a quality assurance program. Both goals are similar in their aim to produce the best fish possible with sound economic principles.
 
 


Too Many Breeds of Cattle?
(an opinion)

Ronnie Silcox
Extension Animal Scientist

It has often been said that the inconsistency in the beef industry is due to too many breeds of cattle. The accompanying table lists the number of registrations for the top 15 U.S. beef breeds. There are over 30 more beef breeds with fewer registrations and the table leaves out one of the largest breeds that contributes to the beef supply, Holsteins. As long as we drink milk we will probably continue to have Holstein beef as a by-product of the dairy industry and there's not much that will change that.

When you look at the accompanying table it does look like there is a tremendous amount of variation in seedstock. There is another way to look at this, however. Instead of counting breeds, lets look at biological types of cattle. Angus, Hereford, Red Angus and Shorthorn are British breeds. Together they make up over 50% of the registrations. Limousin, Charolais, Simmental, Gelbvieh, Maine-Anjou, and Salers are continental breeds. Together they make up about 30% of these registrations. The Brahman and Brahman durative breeds are about 15% of the total. If we can get away from hide color and think more about what is under the hide, we are really looking at 3 biological types of cattle making up most of the registrations in this country.

There are, of course, differences between breeds. Some on average, produce more milk, have lower birth weights or tend to be leaner. So, certain breeds will fit a particular environment or management system better than others. Every breed on this list has a place somewhere. In commercial crossbreeding program there are individuals within all of these breeds that can be crossed with individuals from one or two of the other breeds on the list to produce a choice steer with a 700-800 pound carcass with a yield grade of 3 or less. They can all be worked into a crossbreeding program to "fit the box." Inconsistency is not due so much to too many breeds as it is due to not matching breeds well in crossbreeding, not selecting animals that fit within those breeds and not maintaining a systematic breeding program.

If you eliminate all but two or three of these breeds (which is exactly what an individual commercial cattleman should do in designing his own cross breeding program) you have not solved the problem of inconsistency. There is a great deal of variation with breeds. Selecting the right animal to fit the market is still the problem.
 

TABLE: 1998 REGISTRATION NUMBERS FOR THE LARGEST 15 BREEDS IN THE UNITED STATES.
 

Breed No. Of Registrations % of Total
1. Angus 252,969 35.8%
2. Hereford 83,399 11.7%
3. Limousin 57,862 8.2%
4. Charolais 49,500 7.0%
5. Simmental 48,331 6.8%
6. Beefmaster 47,349 6.7%
7. Red Angus 33,875 4.8%
8. Gelbvieh 29,257 4.1%
9. Brangus 26,941 3.8%
10. Shorthorn 16,406 2.3%
11. Brahman 16,000 2.3%
12. Maine-Anjou 12,000 1.6%
13. Santa Gertrudis 12,000 1.6%
14. Texas Longhorn  11,000 1.5%
15. Salers  10,286 1.5%
Total 706,175

 


Do You Have "Horse" Quality Hay?

Gary Heusner, Ph.D.
Extension Animal Scientist - Equine

This is the time of the year that horse people should be making and/or buying their year's supply of hay. The moisture conditions have many concerned about drought conditions so it is even more important to get the year's supply of hay stored as soon as possible or to begin getting the supply.

What is "horse" quality hay? Horse quality hay is any hay that provides the horse the most nutrients, is free of mold and toxic weeds, is relatively dust free, the horse eats it, and the price is the lowest per unit of nutrient.

The reason a horse needs forage (grass or hay) is that it is a nonruminant herbivore. That is the horse was designed to consume and digest forages to supply nutrients (energy, protein, minerals, vitamins). The horse has a hindgut (large intestine) that contains a population of microrganisms, similar to the microrganisms in the cow's rumen, that breaks down plant (roughage) material that has not been digested by the enzymes of the small intestine. Because the horse's digestive system is designed as such it needs a certain minimum amount of "roughage" in the diet per day. Most equine nutritionists recommend that a horse consume at least 1% of its body weight per day in hay equivalent dry matter to maintain normal digestive system function. Another concern relating to normal digestive function and normal behavior associated with roughage and the fiber portion of the diet is that it appears a horse has a certain daily "chew factor". If a roughage source is fed as a pellet or chopped to a length of less than an inch the horse will not have to chew the roughage as long. Therefore less saliva is produced which has been shown to affect the ph (acidity) of the large intestine. It has been demonstrated that lowering the ph of the hindgut will affect the type of microrganisms present. In addition it is thought that when a horse's minimum daily "chew factor" is not met that the horse may begin to look to chew on other objects such as wood, manes, and tails. This may be due to too little fiber and the corresponding change in gut ph, boredom ( the horse simply may need to do something) or a combination of factors. Whatever the reasons it is important that the horse does meet its "chew factor" requirement.

The main nutrient supplied by hay to horses is energy. Energy requirements for the horse are expressed as megacalories of digestible energy. For example an 1100 pound horse being ridden lightly requires 20.5 megacalories of digestible energy per day. A high quality Costal Bermudagrass hay as shown in Table 1 will contain 0.9 megacalories of digestible energy per pound on a 100% dry matter basis. If the hay is 90% dry matter that means that as the hay is fed out of the bale it will contain 0.81 megacalories of digestible energy per pound. Therefore to meet the 1100 pound horse's energy requirements being ridden lightly the horse would need to consume 25.3 pounds of hay. A horse can consume up to 2.25 to 2.5% of its body weight in forage dry matter per day.

The problem of determining hay quality for horses based on energy content of the hay is that routine laboratory analyzes do not provide digestible energy values. Instead a typical routine forage analysis will provide crude protein, neutral detergent fiber, crude fiber, moisture, and possibly some mineral analyses. It is well documented that as a plant matures crude protein values decline and fiber values increase. Along with the advancing maturity of a plant the digestibility decreases and therefore the digestible energy value decreases. Therefore the higher the neutral detergent and crude fiber values the lower the digestible energy values.

I have attempted to simplify all of the above by putting "Relative Feed Values" on various types of horse hays fed in the southeastern United States. Most all hays are compared to alfalfa so I have put a relative feed value of 100 on a high quality alfalfa. I have listed three levels of relative feed values as well as digestible energy values for each type of hay so that there are three categories into which a hay may fall; excellent, average, and poor quality. Of course this table is useless unless the hay is analyzed for at least dry matter, crude protein, neutral detergent fiber and/or crude fiber.

Table 1. Approximate digestible energy and relative feed values of hays for horses.  (100% Dry Matter Basis)
 

Hay Crude Protein
%
Neutral Detergent 
Fiber %
Crude Fiber % Digestible Energy
Mcal/1lb
Relative Feed Value
Alfalfa >20 <30 <23 1.2 100
16-18 30-47 24-28 1.1 92
<15 >47 >28 1.0 83
Coastal Bermudagrass >12 <65 <30 0.9 75
8-12 66-72 31-35 0.8 67
<7 >72 >35 0.7 58
Bahiagrass >9.5 <68 <32 0.75 63
7-9.5 68-75 32-36 0.7 58
<7 >76 >36 0.6 50
Fescue >12 <65 <26 0.95 79
7-12 66-70 27-30 0.83 69
<7 >70 >30 0.75 63
Orchardgrass >12 <60 <26 0.99 83
7-12 60-65 26-30 0.85 71
<7 >65 >30 0.75 63

 


Controlled Calving Season - Getting Started!

Dan T. Brown
Extension Animal Scientist

A short breeding season (and therefore a short calving season) of 90 or less days is recommended. A short breeding season is usually the most profitable. Assuming a constant weaning date (or marketing date) (most producers do wean all calves at the same time regardless of age) early calving season are born in the summer.

Calves born is summer months (June-August) are approximately 70 pounds lighter at weaning than those dropped at other times. Estimates are that nearly 40 percent of the calves from herds on a year-round calving season are born in the summer.

How to start a controlled calving season is simple - producers must want to. The steps involved are as follows:

Step 1 - Build a good, strong pen or pasture for the bull.

Step 2 - Select a desired calving season, i.e., fall or spring. This depends upon the producer's feed supply, labor, marketing plans and weather (location) to a great extent.

Step 3 - Develop and use schedule and management plan for chosen calving season.

No system of getting started on a controlled breeding program can completely eliminate the delaying of some cows from their current calving schedule, short of culling a bunch of cows the first year. A more reasonable approach is to adopt a 3-year plan for converting down to a 90-day calving season.

The following schedules are designed for a 3-year management program. Dates could be changed to adapt to different desired calving dates. This is based on 283 days of pregnancy. These schedules allow for a minimum of time that the cows will be open and still accomplish the goal of reducing the calving season. The bulls are put back in the herd the first year so that the calving season will be six months long.

The second year, the breeding schedule is such that the calving season will be cut down to about four and one-half months. In the third year, the bull will only be in the breeding pasture for 90 days, therefore the calving season of the cows will be reduced down to the desired 90 days. Further reduction in the calving season is possible, however better management and nutrition are generally necessary.

Replacement heifers are bred 30 days ahead of the cow herd's final long-range planned breeding date each year. This is to provide the heifers with needed extra time after calving the first time to breed back with their second calf. Most first calve heifers will need this extra time in order to "fit into" the mature cows calving season. Controlled breeding seasons are efficient and profitable for cattle operations. They just require commitment on the producer's part, a calendar and a good bull pen. The rewards are well worth the effort!
 

Three Year Schedules for Converting From Year-Round to 90-Day Calving Season

SPRING CALVING (Jan., Feb., Mar.)

1st Year

  • Remove buss June 22.
  • Pregnancy test all cows August 22 (pregnancy test 60-90 days after removing bulls from herd (or at a convenient time, such as, at weaning).

  •  
    a. Cull - all nonpregnant, dry breeding-age females which have been running with the bull.
    b. Cull - all nonpregnant cows with calves five months of age or older.
    c. Cull all open replacement heifers not bred after exposed for 60 days each year.
  • Put bull back with herd December 23.
  • Start breeding replacement heifers February 22.
  • Remove bull from replacement heifers April 22

  •  

    2nd Year

    3rd Year and Subsequent Years


    FALL CALVING (Oct., Nov., Dec.)

    1st Year

    2nd Year 3rd Year and Subsequent Years
     


    Effective Beef Cow Culling

    Dan T. Brown
    Extension Animal Scientist

    As we approach the hotter, dryer months, producers should consider culling as a viable economic means to not only reduce stocking rates, but to boost the bottom line of returns.

    Efficiency of production and desirability of product is essential today. Producers that do not have and utilize culling standards do not make maximum profits, if any profit at all! Normal rate of culling averages 15-20% per year. The most important criterion in culling a cow is her reproductive efficiency. The second most important measure of cow productively is for growth performance of her offspring.

    Reasons

    There are several reasons for practicing a good well-run culling program in any beef herd - failure to conceive, poor milk production, inferior calf performance, age, genetic improvement (shorting the generation interval), however, these and many more can all be grouped into one major reason - ECONOMICS! Animals that do not efficiently produce a profit every year can not be tolerated.

    Basis

    By the use of your herd or breed association, etc., records, one can objectively cull inferior animals from the herd. Without records, this management job cannot be conducted effectively. Cows should be culled on the basis of their performance in the following categories:

    Trait Standard

    1. Fertility - conceive and produce a live calf every year.
    2. Calving Difficulty - eliminate the vet bill before you bury it.
    3. Birth Weight - discriminate against excessive birth weights in both parental lines.
    4. Mothering Ability - healthy, vigorous calf.
    5. Milk Production - calf at least 50% weight of cow.
    6. Growth Rate - at weaning.
    7. Conformation - at least medium frame, choice calf.
    8. Carcass Merit - calf capable of finishing at a low choice, high yield carcass grade.
    9. Efficiency of Gain - produce a profitable calf at a minimum of upkeep.
    10. Longevity - Longevity is important in a beef herd. Females that can meet the above goals are hard to produce and are not cheap to produce. Good beef cows should be functional at least until they are 10 years of age. Many cows are going strong at 14-15 years of age.

     
     
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    Upcoming Livestock Dates

    BEEF
    June 16-19 Beef Improvement Federation Annual Convention Roanoke, VA
    June 18-19 GPHA Field Day and Juniors Heifer Show Bailes Ranch - Eatonton
    June 19 Georgia Simmental Association Field Day Athens
    July 22-24 Georgia Junior Beef Futurity Georgia Agricenter - Perry
    October 2 East Georgia Junior Heifer Show
    Contact: Myron Fowler (912) 625-3046
    Louisville, GA
    HORSE
    June 22-26 State 4-H Horse Show Georgia Agricenter - Perry
    June 27-July 1 State 4-H Horse School Georgia Agricenter - Perry
    SHEEP
    July 10 West Georgia Summer Classic Lamb Show
    Carroll County Ag Ed Center
    Contact: Todd Baldwin (770) 459-5067
    Don Morris (770) 836-6646
    Carroll County
    July 23-24 GCLPA Futurity Perry
    July 24-25 Block and Bridle Lamb Show Perry
    August 14 North Central GA Progress Lamb Show Madison
    August 21 Northeast GA Lamb Show
    (Breeding Ewe Show will be open to state-wide exhibitors)
    Contact: Dan T. Brown (706) 745-6197
    Gainesville
    OTHER
    June 12 State 4-H Livestock Judging Contest Athens