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ENVIRONMENT, WELL-BEING, AND BEHAVIOR |


* Department of Animal Sciences, Purdue University, West Lafayette, IN 47907-2054;
Department of Animal Science, Michigan State University, East Lansing 48824-1225; and
Department of Animal and Avian Sciences, University of Maryland, College Park 20742-2311
1 Corresponding author: applegt{at}purdue.edu
| ABSTRACT |
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Key Words: mass balance nitrogen nutrient excretion phosphorus turkey
| INTRODUCTION |
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Overfeeding of dietary phosphorus is common commercially, with excesses of as much as 30% over published requirements commonly observed. Part of this overfeeding is due to the lack of an up-to-date publication on poultry phosphorus requirements. The most recent nutrient recommendations for poultry were published by NRC in 1994, and the recommendations for turkeys are based on data published from 1954 to 1986, respectively. Genetic progress has greatly changed the performance of commercial turkeys since then, so industry nutritionists have limited resources to which to refer for the requirements of their modern genetic strains. Even though the NRC (1994) recommendations are based on turkey experiments conducted from 1954 to 1986, they appear to be consistent with the current needs of the turkey (Roberson and Fulton, 2000; Roberson et al., 2000; Thompson et al., 2002). Although these studies demonstrate that the NRC (1994) feeding recommendations of phosphorus are still adequate, no data are available quantifying the impact of phosphorus feeding programs in turkeys on the mass of nutrients excreted.
This study therefore had several objectives. The first was to confirm the lack of performance differences when turkey toms were fed a typical corn-soybean meal-based industry diet (IND) and a diet containing a reduced concentration of inorganic phosphorus supplemented with exogenous phytase (LP). The second was to determine the nutrient (phosphorus, nitrogen, sulfur, sodium, potassium, and calcium) retention and excretion by turkey toms fed the IND and LP diets. Because nutrient excretion was determined by 2 distinct methods, differences in apparent nutrient retention (nutrient in feed - nutrient in litter) and true nutrient retention (nutrient in ground carcass) were used to calculate apparent nutrient volatilization.
Recently, the American Society for Agricultural and Biological Engineers (ASABE) has updated its Manure Characteristics and Composition standard (D384.2; ASABE, 2005) and has used diet composition as a predictor of nutrient excretion. Because diets differing in phosphorus concentration were fed, data from this study were used to compare the accuracy of the standard D384.2 (ASABE, 2005) equations for turkeys to predict nutrient excretion.
| MATERIALS AND METHODS |
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All animal care and use was approved by the Purdue University Animal Care and Use Committee. Toms were reared in 3.72-m2 floor pens containing 10 cm of wood shavings on top of a concrete floor. A total of 192 male turkey poults were individually weighed and placed into 24 pens with 8 poults per pen such that the mean pen BW between pens was not statistically different. Each diet was fed to 12 replicate pens. Turkey poults were provided with starter feed and water ad libitum for 3 wk, after which poults in each pen were weighed. Five turkeys with the weight closest to the mean of all birds in the pen were retained, whereas the rest were removed from the trial. Feed (and nutrient) intake during this initial period was used for mass balance determinations, whereas the BW of the additional 3 birds (less mortality) was not included in the mass of nutrients retained within the body. Diets were changed at the end of every 3-wk period. At the end of every 3-wk period, turkey BW and feed consumption were determined. At wk 12, 4 pens for each of the diets were randomly selected, and birds were killed, labeled, and frozen for determination of carcass nutrient retention. This same procedure was repeated at wk 15 and 18.
Litter and Turkey Carcass
Before the beginning of the study, wood shavings in each of the pens were weighed. On wk 12, 15, and 18, when birds from 4 pens per diet were killed, all the litter from each pen was collected, weighed, thoroughly mixed (in a 0.254-m3 cement mixer; Crown Construction Equipment; Winnipeg, Manitoba, Canada), and subsampled. The DM content of litter from each pen was determined after drying for 72 h in a forced-air oven at 55°C in duplicate. Dried litter was then ground to pass through a 1-mm screen. Litter mineral content was determined by inductively coupled plasma spectroscopy (University of Arkansas, Central Analytical Laboratory, Fayetteville; AOAC, 1999) after wet digestion. Nitrogen contents of diets, carcasses, and litter were determined by Kjeldahl digestion and distillation (AOAC, 2000). Phosphorus contents of diets, carcasses, and litter were ashed in a muffle furnace at 550°C for 4 h and then digested, and total phosphorus was determined colorimetrically (AOAC, 1980). Feed phytase content was determined colorimetrically (Engelen et al., 1994). One unit of phytase was defined as the amount of phytase needed to liberate 1 µmol of inorganic phosphorus/min from 5.1 mmol/L of sodium phytate at pH 5.5 and 37°C. The litter weight and nutrient content at the beginning of the trial were subtracted from the pen litter content at the end of each phase to determine actual nutrient excretion values.
By pen, frozen turkey carcasses (including feathers) were ground twice through a large meat grinder (Model 810 Gear Head, Autio, Astoria, OR). The ground carcasses were thoroughly mixed, and 25% of the total was subsampled and frozen for further preparation. Dry matter was determined in a portion of the sample by oven-drying duplicate samples (25 g) at 60°C for 72 h. The rest of the sample was partially dried (to approximately 70% DM) in a freeze-drier, frozen, and then ground in a freeze-grinder (Model 6850 Freezer/Mill, SPEX CertiPrep Inc., Metuchen, NJ) with liquid nitrogen. After grinding, the sample was lyophilized and stored frozen until analyzed. Samples were analyzed for mineral content by inductively coupled plasma spectroscopy after acid digestion (AOAC, 1999).
Calculation and Statistical Analysis
Nutrient retention and excretion were estimated on both a weight and a percentage basis. True nutrient retention was determined as the mass of nutrient in the carcass of the bird, whereas apparent nutrient retention was determined as the difference between the mass of nutrient in the feed consumed and the mass of nutrient in the litter. Additionally, true nutrient excretion was determined as the difference between the mass of nutrient fed and the mass of nutrient in the carcass, whereas apparent nutrient excretion was defined as the mass of nutrient in the litter. Unaccounted for nutrient content was subsequently calculated as the difference between true and apparent nutrient excretion (i.e., this difference is likely the nutrient that was apparently volatilized). Data were analyzed as a completely randomized design by ANOVA to determine differences attributable to dietary regimen within each age (SAS Institute, Cary, NC). A pen of birds was the experimental unit.
Additionally, the formulated dietary nitrogen and phosphorus concentrations were used with actual feed consumption data for each pen to predict nitrogen and phosphorus excretion according to the prediction equations of standard D384.2 (ASABE, 2005). The D384.2 publication (ASABE, 2005) uses an average nutrient excretion value for turkeys based on published literature from 1985 to 2002 (Applegate et al., 2003). The publications used only values from turkeys fed corn-soybean meal-based diets and diets that were closer to the age-specific nutrient requirements of the bird. The references and apparent nitrogen and phosphorus excretion values are presented in Table 2
. The average apparent nitrogen and phosphorus excretion values were 41.2 ± 8.3% and 52.0 ± 7.2%, respectively. The equations in standard D384.2 (ASABE, 2005) for apparent excretion were then used to calculate apparent excretion based on feed nutrient content and intake from the current study. Thus, the comparisons were between the standard D384.2 (ASABE, 2005) equation estimations of nutrient excretion and the measured apparent excretion values. Comparisons were then made between predicted nitrogen and phosphorus excretion (via standard D384.2; ASABE, 2005) and measured apparent nutrient excretion by ANOVA within age and dietary regimen. All statements of significance were P < 0.05 unless indicated otherwise.
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| RESULTS |
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Nitrogen, phosphorus, sulfur, sodium, potassium, and calcium excretions are reported in Table 6
. The relative amount of nitrogen excreted increased with age. When nitrogen excretion was estimated by the difference between nutrient intake and the nutrient in carcass (true excretion), nitrogen excretion was greater in toms fed the IND diet (wk 15), whereas there was no difference at either 12 or 18 wk. Diet affected nitrogen excretion (apparent nitrogen excretion, as determined from litter) with the apparent excretion from LP birds being greater at 12 wk but less than that of the IND-fed birds at 15 wk. Although the trend in nitrogen excretion was similar, the estimate of nitrogen excretion from the litter was approximately 50% of that determined from the carcass method. True phosphorus excretion, both in percentage and in grams per bird, was greater for the IND diet, and there was a relative increase in phosphorus excretion with age. True sulfur excretion (in grams per bird) was greater for toms on the IND diet (wk 12 and 15) and at wk 15 and 18 (in percentage, apparent method). Diet did not affect sodium and potassium excretion (grams or percentage) at any age evaluated in this study. Mineral excretion per turkey increased with age, with nitrogen, phosphorus, sulfur, sodium, potassium, and calcium true excretion at wk 18 (IND diet) being 939, 201, 38, 84, 306, and 241 g/bird, respectively. The corresponding values for apparent excretion were 482, 209, 39, 170, 334, and 253 g/bird. Apparent mineral excretion of aluminun, copper, iron, manganese, magnesium, and zinc at wk 18 (IND diet) was 5.8 (±0.3), 0.49 (±0.03), 54.4 (±3.1), 28.5 (±1.6), 60.6 (±3.2), and 5.7 (±0.3) g/bird, respectively (mean ± SEM; data not shown).
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0.17). The values were within 8.1 and 17.2% of each other (for apparent nitrogen and phosphorus excretion, respectively). When analyzed within a particular age or diet; however, differences between the estimates and measured values were evident (Table 8
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| DISCUSSION |
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To quantify the amount of nitrogen and sulfur volatilized during the course of the experiment, the difference between the 2 methods of estimating nutrient retention and excretion was used. The true retention values were the quantity of a specific nutrient found in ground carcass, whereas true excretion was the difference between the nutrient consumed in the diets and nutrient retained in the carcass. Apparent retention values were determined as the difference between the nutrient consumed in feed and the nutrient in the litter, and apparent excretion was the quantity of the nutrient found in the litter. Any appreciable difference between the true and apparent values would be an indication of the direction and magnitude of losses attributable to volatilization from the litter or contamination from the diet or drinking water. Using unaccounted for phosphorus as a nonvolatilized indicator of the sensitivity of this measurement (i.e., the difference between true and apparent excretion), an average of 9.5% error was associated with these measures.
True retention values for phosphorus in grams per bird or percentage were relatively greater than the corresponding values from apparent retention. This may be a result of feed contamination in the litter, which may eventually have resulted in a greater phosphorus content in the litter. Phosphorus from the drinking water may also have contributed to observed differences. Feed contamination could also be responsible for the relatively low apparent sulfur retention values relative to the true value. Retention of sulfur increased with age (grams per bird), likely in part because of feather growth. Unlike phosphorus and sulfur, the apparent retention for nitrogen was more that 100% greater than the corresponding values for true retention. This observation indicates that a huge amount of nitrogen was unaccounted for at all 3 ages evaluated. Wu-Haan et al. (2007) noted, in measuring emissions from laying hens, that 99.7% of ammonia, nitrous oxide, and nitrogen dioxide emissions were as ammonia. Therefore, the overwhelming majority of unaccounted for nitrogen likely was emitted as ammonia in this study.
This difference between apparent and true phosphorus excretion ranged between 1 and 18.5%. Unlike what was seen for phosphorus, however, the difference between true and apparent excretion for sulfur and nitrogen was a net loss. The loss was between 27 and 34% for sulfur and 27 and 40% for nitrogen. These minerals that could not be accounted for were assumed to have been lost as either hydrogen sulfide or ammonia. Further calculation shows that the unaccounted for nitrogen as a percentage of excreted nitrogen for the IND diet or LP diet for wk 12, 15, and 18 was 45 or 34, 39 or 47, and 46 or 45%, respectively.
When comparing apparent excretion of nitrogen values, the predicted nitrogen excretion value (standard D384.2; ASABE, 2005) based on literature reports (41.2%) was somewhat less than that in the current study (47.3%). This difference was not substantial and, on average, underestimated apparent nitrogen excretion by 8.1%. The predicted phosphorus excretion value (standard D384.2; ASABE, 2005) based on literature reports (52.0%) was numerically, but not significantly, different from that in the current study (58.05%). The estimated phosphorus excretion therefore underestimated phosphorus excretion by 17.2%. Much of this underestimation could be accounted for largely by birds fed the IND diets.
In conclusion, the mass of phosphorus excreted at 0 to 12, 0 to 15, and 0 to 18 wk of age was 37, 46, and 40% greater for birds fed the IND diets compared with birds fed the LP diets. These results indicate that feeding birds more closely to nutrient requirements with supplemental phytase did not affect bird performance but could substantially reduce the amount of phosphorus excreted.
| ACKNOWLEDGMENTS |
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Received for publication January 31, 2008. Accepted for publication August 7, 2008.
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