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Nutritional Characteristics of Arizona Browse Written by
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Table 1. |
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Sierra Ancha Experimental Forest
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| Species |
1960
|
1961
|
1962
|
1963
|
||||
| Leaders | Secondary | Leaders | Secondary | Leaders | Secondary | Leaders | Secondary | |
| Hollyleaf Buckthorn | ||||||||
| Spring |
-
|
-
|
0
|
0
|
88
|
94
|
66
|
68
|
| Summer |
-
|
-
|
0
|
0
|
0
|
0
|
0
|
0
|
| Hairy Mountain Mahogany | ||||||||
| Spring |
24
|
14
|
0
|
0
|
24
|
22
|
60
|
66
|
| Summer |
0
|
0
|
0
|
0
|
2
|
0
|
0
|
0
|
| Desert Ceanothus | ||||||||
| Spring |
92
|
68
|
0
|
0
|
72
|
78
|
84
|
92
|
| Summer |
0
|
0
|
0
|
0
|
0
|
0
|
80
|
90
|
|
From The Arizona Chaparral: Its Growth and
Nutritive Value, 1984, Pond & Schmutz, University of Arizona.
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Table 2. |
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Sierra Ancha Experimental Forest
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| Species |
1960
|
1961
|
1962
|
1963
|
||||
| Leaders | Secondary Twigs | Leaders | Secondary Twigs | Leaders |
Secondary Twigs |
Leaders | Secondary Twigs | |
| Hollyleaf Buckthorn |
-
|
-
|
12
|
12
|
2
|
2
|
6
|
6
|
| Hairy Mountain Mahogany |
2
|
6
|
16
|
24
|
0
|
0
|
2
|
0
|
| Desert Ceanothus |
22
|
14
|
64
|
70
|
28
|
16
|
14
|
16
|
|
From The Arizona Chaparral: Its Growth and
Nutritive Value, 1984, Pond & Schmutz, University of Arizona.
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Drought and Its Effect Upon Nutritional Quality
Since shrubs store food in the stems as well as the roots, the portion of the plant available for browsing tends to hold nutritional quality better than do grasses during drought. Grasses store food resources in the roots. Still, drought will detrimentally affect forage quality of browse. Figure 6 compares crude protein content for clipped winterfat at two different range sites on the Arizona Strip during 1996. Although the two different range sites were of different soil types and elevation, we can draw conclusions about the availability of water and its effect upon crude protein. The crude protein in winterfat dropped with less precipitation. The nutritional quality of browse may not drop as low during drought as it does for grass, but levels will still decline below the nutritional requirements needed for livestock.

Effects of Tannins Upon Nutritional Quality
Tannins are defense compounds which exist in many shrubs. Tannins present in oak species have been used for many years to tan animal hides. The tannins contained in shrubs are mostly of two types, soluble and condensed (Bederski, 1991). Soluble tannins can be absorbed into the blood stream and can cause toxicological effects and death when concentrations in the diet are high. Condensed tannins are not usually digestible but indirectly affect animals by binding with protein and fiber, making the diet less digestible (Bederski, 1991; Reed, 1995). Condensed tannins can also bind with microbial digestive enzymes and make them ineffective (Makkar et al., 1988). Therefore, the ultimate effect of high condensed tannin concentrations is to make the animal both energy and protein deficient, causing reduced growth or weight loss and poor reproduction.When the total content of the diet contains 2% or greater total tannins, the diet is less palatable to the animal and the animal may experience toxicosis and possible death (Dr. Dick Rice, University of Arizona, retired, personal communication).
Arizona shrubs that have been identified to contain high levels of tannins include blackbrush, manzanita, and all the oak species. Blackbrush and manzanita are rarely ingested by grazing livestock, but turbinella oak can comprise large portions of the diet. Turbinella oak is the dominant species in the Arizona Interior Chaparral Grassland and may comprise up to 50% of the diet during some periods of the year (Ruyle et al., 1986).
Tannin content is highest when the shrub is rapidly growing and tannin poisoning can occur when young or inexperienced livestock consume immature buds in the spring. Tannin content can also increase following summer rains. Research reported by H. S. Gomes at the University of Arizona (1990) for turbinella oak concluded that condensed tannins are highest in the winter with immature leaves and that soluble tannins are highest in immature leaves in the summer through early fall. Maximum growth for turbinella oak in this study occurred from summer to early fall.
The symptoms of oak poisoning include dry, dark colored feces, depressed appetite, frequent urination, fluid accumulation in the chest and belly, and kidney failure (Kingsbury, 1964; Sandusky et al., 1977).
Two different sources (Kingsbury, 1964; Dollahite et al., 1966) established that oak poisoning occurs when the diet contains greater than 50% oak. It must also be assumed that subclinical effects such as decreased digestibility can occur when the diet contains smaller amounts of oak. Ruyle et al. (1986) reported that for oak-containing fecal samples examined by microscope for dietary content, 60 samples out of 438 total samples from cattle had at least 10% oak in the diet. About 42% of samples from this subset contained from 41 to 50% oak in the diet.
Using adapted animals can help counteract some of the effects of tannins in the diet. Adapted animals learn from past experience to avoid eating or to reduce the consumption of forage containing harmful toxins (Provenza, 1996). Adapted animals also develop some physiological adaptations to help counteract harmful toxicological effects of tannins. For example, the rumen microbes from adapted vs unadapted animals will differ (microbes break down cellulose and fiber consumed by ruminants). Figure 7 compares digestibility of turbinella oak for adapted and unadapted goats. Rumen fluid from both types of goats was obtained and immature ground-up urbinella oak leaves were placed in the rumen fluid, kept at a constant temperature and agitated frequently. At the end of 48 hours, the digestibility of the turbinella oak was estimated by the amount of sample remaining. Goats which had been adapted to the oak diet constantly had greater digestibility of the browse than did unadapted goats.

Counteracting the Effects of Tannins
Polyethylene glycol (PEG) is a nearly odorless and tasteless compound widely used in the food industry and in some water soluble lubricants. This compound has been found to be effective in tying up condensed tannins and preventing some of their negative effects. Table 3 reports findings by researchers wherein lambs were fed a diet containing 2.5% condensed tannins with or without added PEG at 40 grams per 2.2 lbs of food. Lambs receiving the diet with added PEG had significantly greater forage intakes and average daily gains than those receiving the control diet and had similar average daily gain to lambs receiving a corn and alfalfa hay diet.
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Table 3. Using PEGs to Counteract the Effects
of Tannins
Lambs Fed Tannin Diet Containing Crob Pulp with 2.5% Condensed Tannins |
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| Tannin Diet w/o PEG | Tannin Diet with PEG | Corn and Alfalfa Diet | |
|
Dry Matter Intake, g/d
|
428
|
685
|
521
|
|
Nitrogen Digestibility, %
|
65.4
|
84.6
|
80.2
|
|
Average Daily Gain, g
|
48
|
140
|
135
|
| Priolo et. al., April 2000 Journal of Animal Sciences 78: 810 - 816. | |||
Although PEG appears to be efficacious in counteracting the harmful effects of condensed tannins, it does not appear to be cost effective for cattle at this time. Using a minimum dose used in some sheep studies of 12.5 grams and multiplying it by 7 for the larger cattle size would necessitate feeding 88 grams per day for cattle. At this time, shipping and freight to bring a commercial grade PEG from a supplier in West Virginia to Arizona increases the cost for a minimum 600 lb. order to $2.59 per lb. The cost per dose for cattle at the low dose of 88 grams would be $ 0.50 per day. At this cost, one could only afford to feed the PEG during short time periods when tannin levels in forage were high. A more cost effective procedure would be to feed around 3 lbs. per day of protein supplement at a cost of $ 0.27 per day during the same time period. Feeding the protein supplement would help counteract negative effects on protein digestibility (by providing additional protein) and provide some additional energy.
Another supplement which has been shown to be effective in helping prevent oak poisoning is to add calcium hydroxide to supplemental feeds at levels less than 10% (Dollahite et al., 1966).
Diet Selection and Browse Utilization
In a study done in the Texas hill country and in South Texas, dietary selection of browse was tracked through the year (as reported in Lyons et al., 1996). Researchers found cattle had 1%, 4%, 15%, and 6% browse in the diet for spring, summer, fall, and winter respectively.
In a study done in the Wyoming Red Desert near Rock Springs, Wyoming, cattle consumed from 28 to 36% of the diet as browse in summer and from 33 to 34% as browse in the winter (Krysl et al., 1984). Dominant shrubs consumed were winterfat, fourwing saltbush, and gray horsebrush.
In the Arizona Interior Chaparral Grasslands in which the available forage is dominated more extensively by shrubs, the contribution to the diet by shrubs appears to be much greater than in the two previously cited studies. Figure 8 shows cattle dietary selection by month for different forage classes on a chaparral dominated ranch in Mohave County (unpublished data, Rob Grumbles, University of Arizona). The composition of the diet for each forage classification was estimated using microscopic analyses of fecal samples.

Following monsoon rains, consumption of browse declined as perennial grasses became more available. During the winter with lesser amounts of grasses being available, the composition of the diet as browse was greater than 50%. From Bederskis research (Figure 7), we would expect the digestibility of the selected diet during winter to decline to levels below that needed for maintenance. [The digestibility or total digestible nutrients (TDN) of the diet needed to maintain a nonlactating cow is around 52%.] As in grasses, shrub digestibility declines with advancing maturity later in the season, though perhaps to a lesser extent. Another problem with shrubs is that much of the energy and protein consumed is contained in stems which are high in lignin. Although chemical analyses may show high digestibility for woody species, these chemical analyses may overestimate what the animal is actually able to digest. Browse species that are less woody in nature like winterfat are more digestible than are woody species such as turbinella oak.

With advancing season and extended time in pastures, livestock will not be able to select a high quality diet when shrubs are browsed more heavily. Figure 9 illustrates the effect of heavier utilization upon fourwing saltbush crude protein levels on the Arizona Strip.
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Table 4. Forage Quality of Shrub Twigs
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Shrub
|
Crude Protein, %
|
Lignin, %
|
| Stems |
6.3
|
20.6
|
| Leaves |
13.0
|
12.3
|
| Current Growth |
11.6
|
15.0
|
| From Cook and Harris (1950) | ||
As grazing pressure increases in browse pastures, livestock will spend more time searching for preferred forage, reducing forage intake. Ultimately, they will be forced to consume more stems and less leaves, diluting forage quality (Table 4). They may also consume less palatable species and possibly increase the intake of harmful secondary compounds contained in these less desirable browse species.

In Figure 10, the crude protein content of the diet consumed by cows on the Wagon Bow Ranch (Figure8) is shown. As stated earlier, the diet selected by cattle was estimated using microscopic examination of cow fecal samples. Hand clipped samples of the respective forages chosen by cattle were then analyzed chemically to determine crude protein content of the diet consumed (estimated by multiplying forage chemical analyses crude protein contents by the percentage estimated to have been consumed). No allowance for reduction in crude protein availability was made for tannin containing browse. The cows were deficient in crude protein in winter and in the summer preceding monsoon rains. The large peak in dietary crude protein in March and April was due to the consumption of globemallow, annual grasses (red brome), and annual forbs (particularly filaree).
Trace Mineral Concentrations in Browse
There is a scarcity of research regarding the concentration of trace minerals in browse. Sprinkle et al. (2000) compared the trace mineral status of shrubby buckwheat vs. cool season and warm season perennial grasses, annual grasses, and forbs at five times during the year in 1997-98 at a ranch near Globe. The trace minerals most commonly deficient in Arizona are copper, selenium, and zinc.
Shrubby buckwheat had lower copper concentrations than did forbs but was not different from perennial or annual grasses. The zinc content in shrubby buckwheat was less than in forbs, was not different from that found in warm season perennial grasses or annual grasses, but was greater than that found in cool season perennial grasses. The selenium content in shrubby buckwheat was greater than that found in cool season perennial grasses and annual grasses but did not differ from the selenium concentrations found in forbs or warm season perennial grasses. Copper was adequate most of the time in forbs, but marginally deficient in all other forage types. In all forage types measured, zinc appeared to be marginally deficient and selenium was deficient.
In the Arizona Strip Range Forage Quality Analysis Study (Meen, 2001), browse species evaluated (fourwing saltbush, winterfat, and white ratany) appeared to have greater levels of selenium, copper, and zinc than did the grasses. Selenium was adequate in browse and mostly adequate in grasses. Copper was severely deficient in grasses and moderately deficient in browse. Zinc was severely deficient in both grasses and shrubs, though shrubs had about twice the amount of zinc than did grasses.
Based upon the limited data we have at this time, it appears that the trend for browse in trace minerals is similar to that noted for phosphorus. That is, browse probably has higher concentrations of trace minerals than grasses, though not adequate to satisfy animal requirements year round. Concentrations of trace minerals in browse will vary by soil type just as it does for grasses.
Management
Since energy and protein content of browse decreases with advancing maturity and the advent of winter, cattle grazing browse dominated pastures are good candidates for winter protein supplementation (as are cattle in grass dominated ranges). If good quality browse species such as fourwing saltbush and winterfat are prevalent and are lightly (less than 40% utilization) grazed, cattle may be able to winter with minimal supplement provided. However, for ranges consisting of large percentages of oak species, protein supplementation during the winter is critically important.
If we assume the protein contained in diets with predominantly oak forage to be only 65% digestible (Table 3), then we can calculate the amount of crude protein which should be supplemented. If cattle consume 1.7% of body weight in forage and crude protein of the oak is 7%, and the cow weighs 1000 lbs. and is in the last trimester of pregnancy, then approximately 2 to 3 lbs. of a good quality natural protein supplement needs to be fed:
Example Calculation for Protein Supplementation
Cow Requirements: 1.6 lbs. crude protein (CP) per day
CP from diet: 17 lbs. forage x .07 protein x .65 digestible equals .77 lbs. CP from diet
Amount to supplement: 1.6 .77 = .83 lbs. CP
Lbs. of 28% supplement to feed: .83 ÷ .28 lbs. CP/lb. supplement equals 2.96 lbs. of 28% CP supplement
Adjustment for moisture: 2.96 ÷ .90 dry matter = 3.29 lbs. of supplement needed
Some recommendations for protein supplements used on browse
rangelands are that they contain at least 22% crude protein and that they
be derived from natural protein sources (no urea). There are two reasons
urea based supplements should not be used on browse rangelands: 1) for
rumen microbes to effectively process urea they need an easily digestible
source of energy (which many browse species are not); and 2) to break
down the urea molecule and process the excess nitrogen requires additional
energy input from the ruminant animal. For more information on protein
supplementation see Arizona Cooperative Extension Publication # AZ1186
Protein Supplementation (Sprinkle, 2000a).
In the Wagon Bow example shown above in Figures 8 and 10, there are two critical time periods for supplementation.
The most important time period is in the winter. If the cow is not supplemented at this time period, weight loss before calving will accelerate and will compromise reproductive efficiency after calving. Almost all range cows will lose some weight during the first 45 to 60 days of early lactation. If weight loss before calving is stacked on top of early lactation weight loss, then the period after calving prior to conception will lengthen. In the Wagon Bow example, protein would need to be supplemented at least three months during the winter. If protein were not supplemented during December, January, and February when crude protein of the diet is moderately to severely deficient, weight loss of cattle in the last trimester of pregnancy would be severe. Protein supplementation for three months would probably cost somewhere around $25 to $35 per cow.
The other time period to consider supplementation is in the summer slump period preceding monsoon rains. It may be possible to coast through this time period without supplementation if the calving season is properly timed with the forage quality and quantity nutritional curve. If cattle on the Wagon Bow Ranch in the above example calved in early March, they may be able to replenish body stores prior to the start of breeding. Calves in this example would be born just as nutritional quality is peaking. Granted, if the spring was dry and no annuals were present, there would be a problem with cow body condition. However, looking at the data from the Wagon Bow Ranch, there does not appear to be any other time of the year in which there is a chance for a large increase in forage quality. The second best time to calve would probably be at the start of monsoon rains, but this would produce a lightweight calf at weaning.
It is a good idea to look at the forage quality and quantity curve for your ranch and try to match calving season to fit the curve. Forage samples can be obtained to help determine when forage quality is at its best. For chaparral dominated ranges, a juggling act must be done to try to prevent calving or having early actation cows in pastures dominated by oak brush. Not only is the chance for oak poisoning higher in early spring but the browse dominated pastures also provide more cover for predators. Having a few open pastures available for cows when they calve will enhance nutritional quality and aid in preventing weight loss prior to breeding.
To determine how well you are doing in meeting the cow's nutritional requirements with your management system, closely monitor cow body condition prior to and after calving. By combining protein supplementation with body condition score monitoring on the cowherd and matching calving with the forage urve, some of the challenges of ranching in browse rangelands can be overcome.
For more details on body condition scoring and supplementation, see Arizona Cooperative Extension Publication # 195023 (Sprinkle, 1995) which can be found at ag.arizona.edu/pubs/animal/az9523.pdf.
For more tips, see Arizona Extension Publication #AZ1166 Managing Nutritional Challenges to Reproduction (Sprinkle, 2000b).
The information given herein is supplied with the understanding that no discrimination is intended and no endorsement given by the University of Arizona Cooperative Extension is implied.
Literature Cited
Arthun, D., S. Rafique, J. L. Holechek, J. D. Wallace, and M. L. Galyean. 1988. Effects of forb and shrub diets on ruminant nitrogen balance. II. Cattle studies. Proceedings Western Section American Society of Animal Science. 39:204-207.
Arthun, D., J. L. Holechek, J. D. Wallace, M. L. Galyean, and M. Cardenas. 1992. Forb and shrub effects on ruminal fermentation in cattle. Journal of Range Management 45:519-522.
Bederski, H. J. 1991. Adaptation of goat rumen microflora and microfloral activity of non-adapted cow versus goat microflora to tannin rich Shrub Live Oak (Quercus Turbinella). M.S. Thesis. University of Arizona, Tucson.
Boutouba, A., J. L. Holechek, M. L. Galyean, G. Nunez-Hernandez, J. D. Wallace, and M. Cardenas. 1990. Influence of two native shrubs on goat nitrogen status. Journal of Range Management 43:530-534.
Cook, C. W. and L. E. Harris. 1950. The nutritive content of the grazing sheeps diet on the summer and winter ranges of Utah. Utah Agric. Exp. Stn. Bull. 342.
Davis, E. G., L. E. Bartel, and C. W. Cook. 1975. Control of Gambel oak sprouts by goats. Journal of Range Management 26:216-218.
Dollahite, J. W., G. T. Housholder, and B. J. Camp. 1966. Effect of calcium hydroxide on the toxicity of post oak (Quercus stellata) in calves. J. Amer. Vet. Medical Association 148:908-912.
Gomes, H. S. 1990. Phenolic profile of Shrub Live Oak and its relation to goat diets in Central Arizona. Ph. D. Dissertation. University of Arizona, Tucson.
Hofmann, R. R. 1988. Anatomy of the gastro-intestinal tract. pp. 14-43. In: D. C. Church (Ed) The Ruminant Animal: Digestive Physiology and Nutrition. Prentice Hall, Englewood Cliffs, NJ.
Holechek, J. L., A. V. Munshikpu, L. Saiwana, G. Nunez-Hernandez, R. Valdez, J. D. Wallace, and M. Cardenas. 1990. Influences of six shrub diets varying in phenol content on intake and nitrogen retention by goats. Tropical Grasslands 24:93-98.
Kingsbury, J. M. 1964. Poisonous plants of the United States and Canada. Prentice-Hall, Englewood Cliffs, NJ. pp. 444-446.
Krysl, L. J., M. E. Hubbert, B. F. Sowell, G. E. Plumb, T. K. Jewett, M. A. Smith, and J. W. Waggoner. 1984. Horses and cattle grazing in the Wyoming Red Desert: I. Food habits and dietary overlap. Journal of Range Management 37:72-76.
Lyons, R. K., T. D. A. Forbes, and R. Machen. 1996. What range herbivores eat -and why. Texas Agricultural Extension Service Bulletin B-6037.
Makkar, H. P. S., B. Singh, and R. K. Dawra. 1988. Effect of tannin-rich leaves of oak (Quercus incana) on various microbial enzyme activities of the bovine rumen. British Journal of Nutrition. 60:287-296.
Meen, A. 2000. Grazing intensity and forage quality on the Arizona Strip. Rangelands 22:12-15.
Meen, A. 2001. Forage quality on the Arizona Strip. Rangelands 23:7-12.
Pond, F. W. and E. M. Schmutz. 1984. The Arizona Chaparral: Its Growth and Nutritive Value. University of Arizona Agricultural Expt. Sta.Bull. 8475.
Priolo, A., G. C. Waghorn, M. Lanze, L. Biondi, and P. Pennisi. 2000. Polyethylene glycol as a means for reducing the impact of condensed tannins in carob pulp: Effects on lamb growth performance and meat quality. Journal of Animal Science 78:810-816.
Provenza, F. D. 1996. Acquired aversions as the basis for varied diets of ruminants foraging on rangelands. Journal of Animal Science 74:2010- 2020.
Radostits, O.M., D.C. Blood and C.C. Gay. 1994. Veterinary Medicine, 8th Ed., Radostits, Blood, and Gay (Ed.). Bailliere Tindall, Philadelphia, PA.
Reed, J. D. 1995. Nutritional toxicology of tannins and related polyphenols in forage legumes. Journal of Animal Science 73:1516-1528.
Ruyle, G. B., R. L. Grumbles, M. J. Murphy, and R. C. Cline. 1986. Oak consumption by cattle in Arizona. Rangelands 8:124-126.
Sandusky, G. E., C. J. Fosnaugh, J. B. Smith, and R. Mohan. 1977. Oak poisoning of cattle in Ohio. J. Am. Vet. Med. Assoc. 171:627-629.
Sprinkle, J. E. 1995. Matching forage resources with cow herd supplementation. University of Arizona Cooperative Extension Publication # 195023. 8 pp. Available at: http://ag.arizona.edu/pubs/animal/az9523.pdf
Sprinkle, J.E. 2000a. Protein supplementation. University of Arizona Cooperative Extension Publication # AZ1186. 5 pp. Available at: http://ag.arizona.edu/pubs/animal/az1186.pdf
Sprinkle, J.E. 2000b. Managing nutritional challenges to reproduction. University of Arizona Cooperative Extension Publication # AZ1166. 4 pp. Available at: http://ag.arizona.edu/pubs/animal/az1166.pdf
Sprinkle, J. E., E. J. Bicknell, T. H. Noon, C. Reggiardo, D. F. Perry, and H. M. Frederick. 2000. Variation of trace minerals in forage by season and species and the effects of mineral supplementation upon beef cattle production. Proceedings Western Section American Society of Animal Science. 50:276-280.
Stuth, J. W. and R. K. Lyons. 1999. Grazing steer fecal output dynamics on south Texas shrub-land. Journal of Range Management 52:275-282.
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Document located http://cals.arizona.edu/pubs/animal/az1273/
Published February 2002
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