|
|
||||||||
PHYSIOLOGY, ENDOCRINOLOGY, AND REPRODUCTION |

* National Wildlife Research Center, Fort Collins, CO 80521; and
Department of Biomedical Sciences and Department of Physiology, Colorado State University, Fort Collins 80523
1 Corresponding author: christi.yoder{at}aphis.usda.gov
| ABSTRACT |
|---|
|
|
|---|
Key Words: Canada goose contraception 4,4'-dinitrocarbanilide mallard nicarbazin
| INTRODUCTION |
|---|
|
|
|---|
Hunting is not a feasible alternative in urban areas (Conover and Chasko, 1985; Heusmann, 1999), and the use of special hunting seasons has had limited success in controlling these resident goose populations (Heusmann, 1999). There are few places that allow goose translocation, and annual roundups have met with public resistance in some areas. Current nonlethal control methods for Canada geese include egg oiling or addling (e.g., shaking the egg). However, these methods require each nest to be located, resulting in several days of intense effort each season. In areas where nests are not easily accessible or adequate personnel are unavailable, contraception may be a reasonable alternative, requiring fewer man-hours to implement. Therefore, contraception may provide an acceptable alternative to help manage goose populations at levels that minimize damage but allow for the existence of geese (Forbes, 1993; Stout et al., 1997).
Nicarbazin (NCZ) is an anticoccidial drug routinely used in the poultry industry since the 1950s to control protozoan cecal and intestinal infections by Eimeria species in broiler chickens. It is an equimolar complex consisting of 4,4'-dinitrocarbanilide (DNC) and 2-hydroxy-4,6-dimethylpyrimidine (HDP). The function of HDP is to increase absorption of the material in the gut, whereas DNC is the active coccidiostat (Cuckler et al., 1955; Rogers et al., 1983). When fed to laying hens, NCZ affects reproduction by either reducing egg hatchability or reducing egg production (Jones et al., 1990b; Hughes et al., 1991; Chapman, 1994). Although these effects are undesirable in the poultry industry, NCZ can potentially be used as a waterfowl contraceptive.
In a previous study using mallards as a model for Canada geese, hatchability was 55% for control mallards compared with 26% for mallards treated with 34 mg of NCZ/kg of BW (Yoder et al., 2006). Because the initial testing indicated that 500 ppm (33.75 mg/kg of BW) was the minimum dose needed to affect reproduction, this study used higher doses of NCZ. Because geese in the field would be given NCZ on treated feed rather than by gavage, we chose to feed NCZ coated onto cracked corn ad libitum for this study.
Many contraceptive studies rely on initial testing using gavage procedures to determine a dose level for further testing. Therefore, we wanted to determine how plasma DNC levels compared when NCZ is given either as a bolus dose or fed continuously throughout the day. We monitored plasma DNC levels for mallards given NCZ either by liquid gavage, capsule, or in the daily feed ration.
The objectives of this study were to determine plasma and egg DNC levels when NCZ was fed ad libitum coated onto cracked corn and whether plasma DNC levels differed between male and female mallards. Further objectives included assessing the effect of NCZ on reproduction by monitoring egg production and hatchability. We also wanted to determine whether NCZ negatively affected general health by monitoring bird weight, hematocrit, and hemoglobin.
| MATERIALS AND METHODS |
|---|
|
|
|---|
All treatment groups received 34 mg of NCZ/kg of BW daily for 12 d. Capsules were loaded with 25% NCZ on wheat middlings (Phibro Animal Health Inc., Fairfield, NJ), such that each capsule contained 34 mg of pure NCZ. Corn oil and water suspensions were made by vortexing 25% NCZ on wheat middlings in the appropriate medium to achieve an even suspension, such that 2 mL of suspension contained 34 mg of pure NCZ. Mallards in the pelleted feed group received a daily ration of 68 g of pelleted feed treated at 500 mg of NCZ/kg of feed.
A total of 3 mL of blood was obtained from the brachial vein on d 2, 4, 6, 8, 10, and 12 of treatment. Blood was centrifuged, and the plasma was stored at 70°C until analysis of DNC concentration using HPLC (Primus et al., 2001).
Reproductive Trial
The experiment consisted of 4 female and 2 male treatment groups as follows: 0 ppm of NCZ (Phibro Animal Health Inc.), 12 females; 0 ppm of NCZ, 5 males; 750 ppm of NCZ, 12 females; 1,000 ppm of NCZ, 13 females; 1,000 ppm of NCZ, 5 males; and 1,500 ppm of NCZ, 13 females. Mallards (Whistling Wings Inc.) were randomly assigned to treatment groups and cages, and were housed individually. Because males would consume treated feed in the wild, they were included to determine the effect of NCZ on male health. All birds were 30 wk of age at the beginning of the study, and a 17L:7D light cycle was maintained throughout. Mallards were maintained on a game bird layer diet (Purina Mills Inc.) that included 3.25 to 4.25% Ca, 0.5% P, and 16% CP. Untreated male mallards were placed with control and treated female mallards, and treated males were placed with untreated females 2 to 3 times each week. Pairs were observed until copulation occurred, and then males were removed.
Doses were made by overcoating cracked corn with 0, 750, 1,000, or 1,500 ppm of NCZ using 5% corn oil and 5% milk powder. Feed was formulated such that a mallard eating 65 g of feed daily would receive 50.4, 67.2, or 100.8 mg of NCZ/kg of BW in the 750, 1,000, or 1,500 ppm groups, respectively. Each mallard was offered 75 g of treated feed daily for 14 consecutive days. Any feed remaining after 24 h was collected, dried in an oven dryer at 93.3°C overnight, and weighed to determine actual dose received.
Prior to treatment, we randomly selected 7 females from each group for blood sampling. The same 7 females from each group were used for blood sampling throughout the study, and blood samples were drawn from all males. A total of 3 mL of blood was obtained from the brachial vein once pretreatment; on d 4, 7, 10, and 14 of treatment; and on d 2 and 5 posttreatment. Two microhematocrit tubes per blood sample were filled and analyzed for hematocrit (Dein, 1986). A 20-µL subsample of blood was analyzed for hemoglobin content using a cyanmethemoglobin method (525-A, Sigma Chemical Co., St. Louis, MO). The remainder of the blood was centrifuged, and the plasma was stored at 70°C until analysis of DNC concentration using HPLC (Primus et al., 2001). All birds were weighed at the time of bleeding.
Egg production and egg weight were monitored daily. For birds included in plasma DNC analysis, eggs laid the day of blood collection were also analyzed for DNC levels. Eggs for DNC analysis were broken open, and the degree of mottling was assessed. Mottling was assessed using the following scale: 0 = no mottling, 1 = mild mottling, 2 = moderate mottling, and 3 = severe mottling. The shells were removed, and the remainder of the egg was homogenized using a handheld blender (Cuisinart, East Windsor, NJ) and was analyzed for DNC content by HPLC (Johnston et al., 2002). Because egg production was severely reduced in all groups during treatment, no eggs were incubated.
Statistical Analyses
Delivery Methods.
Data were analyzed as a mixed effects model (PROC MIXED; SAS Institute Inc., 2003), and significance was defined as P
0.05. Data were analyzed for sex, delivery method, treatment day, and all interaction effects. Means separations were carried out using PDMIX800 (Saxton, 1998).
Reproductive Trial.
We divided the study into 5 periods among groups for all statistical analyses as follows: pretreatment (1 to 14 d), treatment 1 (1 to 7 d), treatment 2 (8 to 14 d), posttreatment 1 (d 2 posttreatment), and posttreatment 2 (d 5 posttreatment). All data were analyzed as a mixed effects model (PROC MIXED; SAS Institute Inc., 2003), and significance was defined as P
0.05 for all analyses. Data were analyzed for sex, treatment, period, and all interaction effects. Means separations were carried out using PDMIX800 (Saxton, 1998). Food consumption decreased significantly in all groups including the control group during the treatment period, resulting in a severe decline in egg production. Because we had no data for the treatment periods for egg mottling scores, mottling data were not analyzed. Correlations were determined between plasma and egg DNC levels and also among plasma or egg DNC levels and numbers of eggs laid, egg weight, BW, hemoglobin, and hematocrit.
| RESULTS |
|---|
|
|
|---|
|
|
|
|
|
|
|
| DISCUSSION |
|---|
|
|
|---|
Nicarbazin suspended in corn oil is likely protected from "prewetting," keeping crystal sizes small. In addition, NCZ is distributed throughout the suspension, making NCZ more available to the gut. The corn oil suspension produced the highest peak DNC levels of any of the delivery methods tested. A water-based suspension would be expected to produce lower plasma DNC levels, because the NCZ is already in an aqueous environment prior to ingestion, and the results of this study confirmed this. Nicarbazin delivered in a capsule produced plasma DNC levels higher than the water-based suspension but lower than the corn oil suspension. Likely, this is because NCZ is dry upon ingestion but is subsequently exposed to the aqueous environment in the gut. This may result in crystal sizes intermediate to those in the corn oil and water-based suspension groups.
The lowest plasma DNC levels were obtained by feeding pelleted feed. Pellets have a lower exposed surface area than suspension- or capsule-based delivery methods. Because of this, less NCZ is immediately available for uptake in the gut, and lower plasma DNC levels result. Male mallards received only 26 mg/kg of BW, rather than the predicted 34 mg/kg of BW dose, but females received a 34 mg/kg of BW dose. Although the lower dose level in the males may have contributed to lower plasma DNC levels overall, no significant differences were found in plasma DNC levels between sexes.
During the reproductive trial, mallards fed 1,000 ppm of NCZ on cracked corn received an average dose of 34 mg/kg of BW. Because mallards in the delivery method trials also received 34 mg/kg of BW doses and both trials used 25% NCZ on wheat middlings, plasma DNC levels can be compared. Mallards receiving cracked corn had higher peak plasma DNC levels than birds receiving treatment via any of the other 4 delivery methods tested (Figure 1
, Table 1
). This may be due to 2 factors. First, coating NCZ onto cracked corn gives more surface area than a pellet, resulting in more NCZ being immediately available to the gut. Second, corn oil was used to help NCZ adhere to the cracked corn, and this likely protected the NCZ from prewetting, resulting in formation of smaller DNC crystals in the gut.
Reproductive Trial
Peak plasma and egg DNC levels were in the range predicted to have a contraceptive effect in waterfowl. A minimum plasma level of 2.9 µg/mL is needed to induce reproductive effects in waterfowl (Jones et al., 1990b; Yoder et al., 2005). Plasma DNC levels in this study ranged from 2.7 to 5.4 µg/mL. Despite decreased food consumption, mallards in the 1,000 and 1,500 ppm groups received enough NCZ to obtain adequate plasma DNC levels to induce contraceptive effects. Reduced egg hatch-ability in chickens was observed at a minimum egg DNC level of 6 µg/g (Jones et al., 1990b), and similar levels are likely needed in waterfowl eggs to prevent hatchability. Egg DNC levels in this study ranged from 10.6 to 22.8 µg/g, indicating that even 750 ppm of NCZ in feed could reduce egg hatchability.
The mallards utilized in this study were accustomed to a pelleted waterfowl diet, and did not accept a cracked corn diet, even in the control group. Egg production and BW decreased as a result of the decreased food intake but began to return to pretreatment levels during post-treatment period 2.
Treatment with NCZ resulted in a decrease in egg weight. This is consistent with the results of previous studies on chickens (Jones et al., 1990a,b; Hughes et al., 1991). Mean egg weights were 50.7 ± 1.1, 47.8 ± 1.2, 46.0 ± 1.1, and 49.4 ± 1.3 g in the 0, 750, 1,000, and 1,500 ppm groups, respectively. During treatment period 1, egg weights were reduced by 10% in the 1,500 ppm group. There were no eggs laid in the control group during treatment period 2 to compare with the treatment groups. Egg weights decreased by 10 and 19.7% in the 750 and 1,000 ppm groups, respectively, during posttreatment period 1. During posttreatment period 2, egg weights were reduced by 21.7, 24.8, and 17.9% in the 750, 1,000, and 1,500 ppm groups, respectively. In the 1,000 ppm group, egg weight decreased as plasma DNC increased.
Male mallards in this study had a higher hematocrit and hemoglobin concentration than females. In geese, administration of estrogen causes a decrease in red blood cell counts (Hunsaker, 1968). Although androgen has no effect on hematocrit in geese, it increases the red blood cell count in chickens and quail (Burton and Smith, 1972; Nirmalan and Robinson, 1972). Although there are differences among species, males tend to have a higher hematocrit than females (Sturkie, 1986). Because hemoglobin concentration is related to hematocrit (Campbell, 1995; Fudge, 2000), males also have a higher hemoglobin concentration than females (Sturkie, 1986).
Increased plasma DNC was associated with decreases in egg production and BW in this study. This is consistent with the finding that egg production in chickens decreases as the NCZ dose in feed increases (Jones et al., 1990b, Hughes et al., 1991). At levels
100 ppm of NCZ, feed efficiency and weight gain are decreased in chickens (Bartov, 1989a,b; Sorribas et al., 1993).
Plasma and egg DNC levels high enough to induce contraceptive effects were obtained during this study at
1,000 ppm of NCZ in feed. Although NCZ-treated cracked corn produced the highest plasma DNC levels, and would be more readily accepted by geese than pelleted feed, it is also associated with more nontarget hazards to songbirds. Because of this, it is recommended that NCZ be coated onto whole corn instead, because the size of corn kernels will exclude most nontarget songbirds. Geese are accustomed to eating corn in fields during the winter months, therefore, they are more likely to accept corn than pelleted feed with which they have no prior experience. Geese in parks used to being fed by humans may be more likely to accept pelleted feed than geese not normally fed by humans. If pelleted feed is to be used in the field, a higher amount of NCZ must be incorporated into the pellet to allow for the decreased absorption of DNC. OvoControl G is a pelleted NCZ feed registered by the Environmental Protection Agency in 2005 for control of reproduction in resident Canada geese. It contains 2,500 mg of NCZ/kg of feed, requiring a goose to consume 50 g daily to achieve an approximate dose of 31.25 mg of NCZ/kg of BW (Bynum et al., 2006).
| ACKNOWLEDGMENTS |
|---|
Received for publication January 25, 2006. Accepted for publication March 22, 2006.
| REFERENCES |
|---|
|
|
|---|
Bartov, I. 1989a. Lack of effect of dietary factors on nicarbazin toxicity in broiler chicks. Poult. Sci. 68:145152.[ISI][Medline]
Bartov, I. 1989b. Lack of interactive effect of nicarbazin and dietary energy-to-protein ratio on performance and abdominal fat pad weight of broiler chicks. Poult. Sci. 68:15351539.[ISI][Medline]
Burton, R. R., and A. H. Smith. 1972. The effect of chronic erythrocyte polycythemia and high altitude upon plasma and blood volumes. Proc. Soc. Exp. Biol. Med. 140:920923.[Medline]
Bynum, K. S., J. D. Eisemann, G. C. Weaver, C. A. Yoder, L. A. Miller, and K. A. Fagerstone. 2006. Nicarbazin reduces hatchability of eggs laid by resident Canada geese in Oregon. J. Wildl. Manage. (accepted).
Campbell, T. W. 1995. Avian hematology. Pages 319 in Avian Hematology and Cytology, The Iowa State Univ. Press, Ames.
Chapman, D. H. 1994. A review of the biological activity of the anticoccidial drug nicarbazin and its application for the control of coccidiosis in poultry. Poult. Sci. Rev. 5:231243.
Conover, M. R., and G. G. Chasko. 1985. Nuisance Canada goose problems in the eastern United States. Wildl. Soc. Bull. 13:228233.
Cuckler, A. C., C. M. Malanga, A. J. Basso, and R. C. ONeill. 1955. Antiparasitic activity of substituted carbanilide complexes. Science 122:244245.
Dein, F. J. 1986. Hematology. Pages 174191 in Clinical Avian Medicine and Surgery. G. J. Harrison and L. R. Harrison, ed. W. B. Saunders Co., Philadelphia, PA.
Fairaizl, S. D. 1992. An integrated approach to the management of urban Canada goose depredations. Pages 105109 in Proc. 15th Vertebrate Pest Conf. Univ. Calif., Davis.
Forbes, J. E. 1993. Survey of nuisance urban geese in the United States. Pages 92101 in Proc. 11th Great Plains Wildl. Damage Control Workshop. Kansas State Univ., Manhattan.
Fudge, A. M. 2000. Avian complete blood count. Pages 918 in Laboratory Medicine: Avian and Exotic Pets. A. M. Fudge, ed. W. B. Saunders Co., Philadelphia, PA.
Gosser, A. L., and M. R. Conover. 1999. Will the availability of insular nesting sites limit reproduction in urban Canada goose populations? J. Wildl. Manage. 63:369373.
Heusmann, H. W. 1999. Special hunting seasons and resident Canada goose populations. Wildl. Soc. Bull. 27:456464.
Hughes, B. L., J. E. Jones, J. E. Toler, J. Solis, and D. J. Castaldo. 1991. Effects of exposing broiler breeders to nicarbazin contaminated feed. Poult. Sci. 70:476482.[ISI][Medline]
Hunsaker, W. G. 1968. Blood volume of geese treated with androgen and estrogen. Poult. Sci. 47:371376.
Johnston, J. J., W. M. Britton, A. MacDonald, T. M. Primus, M. J. Goodall, C. A. Yoder, L. A. Miller, and K. A. Fagerstone. 2002. Quantification of plasma and egg 4,4'-dinitrocarbani-lide (DNC) residues for the efficient development of a nicarbazin-based contraceptive for pest waterfowl. Pest Manage. Sci. 58:197202.
Jones, J. E., B. L. Hughes, J. Solis, D. J. Castaldo, and J. E. Toler. 1990a. Effect of nicarbazin on brown-egg layer-breeders. Appl. Agric. Res. 5:149152.
Jones, J. E., J. Solis, B. L. Hughes, D. J. Castaldo, and J. E. Toler. 1990b. Production and egg quality responses of White Leghorn layers to anticoccidial agents. Poult. Sci. 69:378387.[ISI][Medline]
Manny, B. A., R. G. Wetzel, and W. C. Johnson. 1975. Annual contribution of carbon, nitrogen, and phosphorus by migrant Canada geese to a hard water lake. Verh. Int. Ver. Theor. Angew. Limnol. 19:949951.
Nirmalan, G. P., and G. A. Robinson. 1972. Hematology of Japanese quail treated with exogenous stilbestrol diproprionate and testosterone propionate. Poult. Sci. 51:920925.[ISI][Medline]
Primus, T. M., D. J. Kohler, M. A. Goodall, C. Yoder, D. Griffin, L. Miller, and J. J. Johnston. 2001. Determination of 4,4'-dinitrocarbanilide (DNC), the active component of the anti-fertility agent nicarbazin, in chicken, duck, and goose plasma. J. Agric. Food Chem. 49:35893593.[ISI][Medline]
Rogers, E. F., R. D. Brown, J. E. Brown, D. M. Kazazis, W. J. Leanza, J. R. Nichols, D. A. Ostlind, and T. M. Rodino. 1983. Nicarbazin complex yields dinitrocarbanilide as ultrafine crystals with improved anticoccidial activity. Science 222:630632.
SAS Institute Inc. 2003. Version 9.1. SAS Inst. Inc., Cary, NC.
Saxton, A. M. 1998. A macro for converting mean separation output to letter groupings in Proc Mixed. Pages 12431246 in Proc. 23rd SAS Users Group Int. SAS Inst. Inc., Cary, NC.
Sorribas, V., M. P. Arruebo, H. Navarro, and A. I. Alcalde. 1993. Nicarbazin stimulates intestinal transport of L-leucine in rabbit. J. Vet. Pharmacol. Ther. 16:3237.[ISI][Medline]
Stout, R. J., B. A. Knuth, and P. D. Curtis. 1997. Preferences of suburban landowners for deer management techniques: A step towards better communication. Wildl. Soc. Bull. 25:348359.
Sturkie, P. D. 1986. Body fluids: Blood. Pages 102129 in Avian Physiology. P. D. Sturkie, ed., Springer-Verlag, New York, NY.
Yoder, C. A., J. K. Graham, L. A. Miller, K. S. Bynum, J. J. Johnston, and M. J. Goodall. 2006. Evaluation of nicarbazin as a potential waterfowl contraceptive using mallards as a model. Poult. Sci. 85:12751284.
Yoder, C. A., L. A. Miller, and K. S. Bynum. 2005. Comparison of nicarbazin absorption in chickens, mallards, and Canada geese. Poult. Sci. 84:14911494.
| ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
| HOME | HELP | FEEDBACK | SUBSCRIPTIONS | ARCHIVE | SEARCH | TABLE OF CONTENTS |