Poult. Sci.
HOME HELP FEEDBACK SUBSCRIPTIONS ARCHIVE SEARCH TABLE OF CONTENTS
 QUICK SEARCH:   [advanced]


     


Poult Sci 2008. 87:727-732. doi:10.3382/ps.2007-00403
© 2008 Poultry Science Association
This Article
Right arrow Abstract Freely available
Right arrow Full Text (PDF)
Right arrow Alert me when this article is cited
Right arrow Alert me if a correction is posted
Services
Right arrow Similar articles in this journal
Right arrow Similar articles in ISI Web of Science
Right arrow Alert me to new issues of the journal
Right arrow Download to citation manager
Right arrow reprints & permissions
Citing Articles
Right arrow Citing Articles via HighWire
Right arrow Citing Articles via Google Scholar
Google Scholar
Right arrow Articles by Diaz, G. J.
Right arrow Articles by Blain, R.
Right arrow Search for Related Content
PubMed
Right arrow Articles by Diaz, G. J.
Right arrow Articles by Blain, R.

METABOLISM AND NUTRITION

Aflatoxicosis in Chickens (Gallus gallus): An Example of Hormesis?

G. J. Diaz*,1, E. Calabrese{dagger} and R. Blain{dagger}

* Facultad de Medicina Veterinaria y de Zootecnia, Universidad Nacional de Colombia, Bogotá, D. C., Colombia; and {dagger} University of Massachusetts, Department of Public Health and Health Sciences, Amherst 01003

1 Corresponding author: gjdiazg{at}unal.edu.co


    ABSTRACT
 TOP
 ABSTRACT
 INTRODUCTION
 AFLATOXINS AND HORMESIS IN...
 DISCUSSION
 REFERENCES
 
Poultry has commonly been considered highly susceptible to aflatoxins. However, among domestic fowl there is wide variability in specific species sensitivity to these mycotoxins. Comparative toxicological studies in avian species have shown that ducklings and turkey poults are the most sensitive species to aflatoxins, quails show intermediate sensitivity, whereas chickens are the most resistant. Hormesis is a dose-response phenomenon characterized by low-dose stimulation and high-dose inhibition. The low-dose stimulation is typically maximal at only about 30 to 60% greater than controls. Hormesis has been noted in regards to changes in body weight in numerous studies, including those performed for the US National Toxicology Program, with over 50 chemicals. The present paper assesses how relatively low levels of aflatoxin consumption in feed may affect the growth rate of chickens. In general, multiple independent investigations have shown that such aflatoxin consumption affects growth in a hormetic-like biphasic manner with a low dose stimulation and a high dose inhibition. Such observations were then generalized to other toxic agents and animal models, suggesting that low doses of stressor agents induce adaptive responses as reflected in accelerated growth rates. The implications of such hormetic dose responses are briefly discussed.

Key Words: aflatoxin • hormesis • aflatoxicosis • chicken


    INTRODUCTION
 TOP
 ABSTRACT
 INTRODUCTION
 AFLATOXINS AND HORMESIS IN...
 DISCUSSION
 REFERENCES
 
Aflatoxins are a group of heterocyclic metabolites synthesized predominantly by the fungi Aspergillus flavus Link and Aspergillus parasiticus Speare. Aflatoxins were first identified as the causative agent of the severe outbreak of Turkey X disease, a toxicosis that killed over 100,000 turkey poults in England in 1960 (Asplin and Carnaghan, 1961). Aflatoxins are a major concern because they are human hepatocarcinogens and are considered to play an important role in the high incidence of human hepatocellular carcinoma in certain areas of the world (CAST, 2003).

In poultry, intake of feed contaminated with aflatoxins may result in poor performance, decreased organ weight, immunosupression, irreversible liver damage, morbidity, and mortality (Ostrowski, 1984; Leeson et al., 1995). Due to these effects, poultry has commonly been considered highly susceptible to aflatoxins. However, among domestic fowl there is wide variability in specific species sensitivity to this mycotoxin. Comparative toxicological studies in avian species have shown that ducklings and turkey poults are the most sensitive species to aflatoxins and quails show intermediate sensitivity, whereas chickens are the most resistant (Leeson et al., 1995). Body and relative liver weight are severely affected in turkeys fed doses as low as 0.4 ppm aflatoxin B1 in their diet, whereas chickens were not affected at this dietary concentration (Ostrowski, 1984). In fact, some studies have reported a modest enhancement in the body weight of chickens exposed to aflatoxins in their diet.

Hormesis is a dose-response phenomenon characterized by low-dose stimulation and high-dose inhibition. The low-dose stimulation is typically maximal at only about 30 to 60% greater than controls (Calabrese, 2002). This type of response has been described in the past as biphasic, U-shaped, J-shaped, reverse, dual, overcompensation, stimulatory-inhibitory, and others (Calabrese and Baldwin, 2003b). Hormesis has been noted in regards to changes in body weight in numerous studies, including those performed for the US National Toxicology Program, with over 50 chemicals (see Table 1Go to see chemicals tested; Calabrese and Baldwin, 2003a; Calabrese and Blain, 2005). The majority of the dose responses associated with changes in body weight have had maximum stimulatory responses between 110 and 150% of the control (Table 2Go). It should be noted that the hormesis database does not include studies with increases below 110% unless the results are statistically significant (Calabrese and Blain, 2005).


View this table:
[in this window]
[in a new window]

 
Table 1. Summary of the chemical and model information in studies observing hormetic effects on body weight parameters
 

View this table:
[in this window]
[in a new window]

 
Table 2. Breakdown of the dose-response relationships for changes in body weight in the hormesis database by maximum stimulatory response
 
The objective of the present article is to summarize and analyze the scientific evidence that indicates that the body weight data in chickens (Gallus gallus) exposed to dietary aflatoxins fit into the hormesis dose-response paradigm and to evaluate the possible implications of this phenomenon.


    AFLATOXINS AND HORMESIS IN CHICKENS
 TOP
 ABSTRACT
 INTRODUCTION
 AFLATOXINS AND HORMESIS IN...
 DISCUSSION
 REFERENCES
 
A biphasic low-dose stimulation high-dose inhibition response curve for body weight in chickens receiving graded levels of dietary aflatoxin has been extensively reported in the literature. Table 3Go summarizes the results of several studies conducted with dietary aflatoxins in chickens, which observed a low stimulation at the low-dose level tested. In a study conducted in broiler chickens (Huff, 1980) birds receiving dietary total aflatoxin levels of 625 and 1,250 µg/kg had an average body weight of 528 ± 24 g and 515 ± 24 g, respectively. The average body weight of the control chickens was 511 ± 23 g. The body weight stimulation in this experiment was low, with a 3.3% increase at 625 µg/kg of aflatoxins and about 1.0% for 1,250 µg/kg. Huff and coworkers (1986) found that broiler chickens receiving a diet containing 1,250 µg/kg of total aflatoxins for 21 d had an average body weight of 557 ± 28 g compared with 520 ± 20 g in the control chickens. This stimulation in body weight represented a 7.1% increase over the control group. Greater levels of aflatoxin in the diet (2,500 and 5,000 µg/kg) resulted in a significant decrease in body weight (89.2 and 77.1% of the control, respectively). Figure 1Go shows plots of the data published in the above cited articles (Huff, 1980; Huff et al., 1986) where the typical hormetic biphasic response of low-dose stimulation high-dose inhibition is observed. In a study conducted by Diaz and Sugahara (1995), growing broiler chicks fed 3,000 µg/kg of purified aflatoxin B1 from d 4 to 11 of age had and average body weight of 89.1 ± 5.2 g compared with 85.3 ± 3.6 g for the corresponding controls. Day-old male White Leghorn chicks fed 1,000 µg/kg dietary total aflatoxin for 3 wk had a final body weight of 219.7 g compared with 210.3 g for the control group (Dixon et al., 1982). Although the low-dose stimulation of aflatoxins on body weight in these studies was always below 10%, there was a consistency to indicate a real effect. The hormetic stimulation is usually low (normally not more than 30 to 60%; Calabrese and Blain, 2005), therefore causing it to be often overlooked. However, for a broiler chicken producer, any increase in body weight represents a large increase in income.


View this table:
[in this window]
[in a new window]

 
Table 3. Summary of experiments conducted with dietary aflatoxins in chickens showing the stimulatory effect observed at the low doses tested
 

Figure 1
View larger version (9K):
[in this window]
[in a new window]

 
Figure 1. Examples of the inverted J-shaped dose-response relationship of body weight vs. dietary aflatoxin level. Graphs constructed with data from Huff (1980) and Huff et al. (1986).

 
The above-cited studies provide evidence for a low-dose stimulation and high-dose inhibition response in aflatoxins in chickens; however, the most relevant evidence for the hormetic response of dietary aflatoxins on body weight in chickens comes from the study of Richardson et al. (1987) where 15 doses at very small increments were tested. To properly study the hormetic response a large number of properly spaced doses are required (Calabrese, 2002). In this study, a typical hormetic inverted J-shaped dose-response curve was obtained for body weight vs. aflatoxin dietary level. Further, a quadratic polynomial model was fitted to the curve (Figure 2Go).


Figure 2
View larger version (19K):
[in this window]
[in a new window]

 
Figure 2. Inverted-J dose-response for body weight against the log2 of dietary aflatoxin in chickens. Each clear circle corresponds to the mean body weight of 6 groups of 15 birds per treatment. The lines outside the curve correspond to the 95% confidence limits. The minimum effective dose (MED) of aflatoxin on body weight was calculated to be 1,370 µg/kg for the 2% fat diet (low fat diet) and 1,410 µg/kg for the 4% fat diet (normal diet). Reproduced with permission from the Poultry Science Association from Richardson et al. (1987).

 
The hormetic response of aflatoxins in body weight in chickens has not been observed in other commercial poultry species such as ducks and turkeys. For example, turkey poults receiving diets containing 125, 250, or 500 µg/kg for 21 d had body weights corresponding to 89.0, 81.2, and 65.4% of the control body weight, respectively (Hamilton et al., 1972). Even more sensitive to the effects of dietary aflatoxins are ducks. For example, 2-wk-old Alabio ducks fed dietary levels of 50, 100, and 200 µg/kg of total aflatoxins for 14 d had body weights corresponding to 78.1, 54.3, and 40.3% of the control group, respectively (Ostrowski-Meissner, 1983).


    DISCUSSION
 TOP
 ABSTRACT
 INTRODUCTION
 AFLATOXINS AND HORMESIS IN...
 DISCUSSION
 REFERENCES
 
Several studies designed to evaluate the effect of aflatoxins in chickens have shown the characteristic low-dose stimulation high-dose inhibition pattern of the hormetic dose-response. A study conducted with a large number of doses, spaced at low intervals, has shown the typical inverted J-shaped curve observed in studies where the end-point is adversely affected by the exposure to the xenobiotic (Figure 2Go). It is still speculative why chickens respond in this way to dietary exposure to aflatoxins. Hormesis represents a strategy for the animal to optimize resource allocation and may occur through 2 different mechanisms of action: a direct stimulation and an indirect stimulation resulting from overcompensation to an initial disruption in an attempt to assure that homeostasis is maintained (Calabrese, 2002). Either way, the result is the same: a biphasic response characterized by a modest stimulation compared with controls. It is possible that aflatoxins, being acutely toxic to the liver, stimulate an overcompensation response in the animal that manifests itself as an increase in body mass. The mechanism of action of aflatoxins on the hormetic response in chickens needs to be investigated.

An analysis of the hormesis database (Calabrese and Blain, 2005) concerning parameters relating to weight gain indicates that numerous agents (Table 1Go) induce a hormetic-like biphasic dose response in regard to body weight gain. The parameters of the dose responses are those typically observed in hormesis with a maximum stimulatory response between 110 and 150% of the control (Table 2Go) and the width of the stimulatory response usually less than 100-fold with the majority less than 10-fold (Table 4Go). These findings are generally supportive of the examples presented for aflatoxin in chickens and argue for the response being of a more general nature.


View this table:
[in this window]
[in a new window]

 
Table 4. Breakdown of the dose-response relationships for changes in body weight in the hormesis database by width of stimulation range
 
The realization that low doses of dietary aflatoxins and numerous other toxic substances may stimulate growth at low doses may have implications for the poultry industry. For example, the use of feed additives intended to decrease toxicant adsorption in the gastrointestinal tract could be reevaluated within the risk-benefit context. In view of the important economic and public health implications of the hormetic response, it is necessary to investigate the potential occurrence of hormetic responses on commercial animal production in general.

Received for publication September 28, 2007. Accepted for publication December 15, 2007.


    REFERENCES
 TOP
 ABSTRACT
 INTRODUCTION
 AFLATOXINS AND HORMESIS IN...
 DISCUSSION
 REFERENCES
 
Asplin, F. D., and R. B. A. Carnaghan. 1961. The toxicity of certain groundnut meals for poultry with special reference to their effect on ducklings and chickens. Vet. Rec. 73:1215–1219.

Biagini, R. E., G. M. Henningsen, B. Mackenzie, W. T. Sanderson, S. Robertson, and E. S. Baumgardner. 1993. Evaluation of acute immunotoxicity of alachlor in male F344/N rats. Bull. Environ. Contam. Toxicol. 50:266–273.[Web of Science][Medline]

Calabrese, E. J. 2002. Hormesis: Changing view of the dose-response, a personal account of the history and current status. Mutat. Res. 511:181–189.[CrossRef][Web of Science][Medline]

Calabrese, E. J., and L. A. Baldwin. 2003a. Hormesis at the National Toxicology Program (NTP): Evidence of hormetic dose responses in NTP dose-range studies. Nonlinearity Biol. Toxicol. Med. 1:455–467.[CrossRef]

Calabrese, E. J., and L. A. Baldwin. 2003b. Hormesis: The dose-response revolution. Annu. Rev. Pharmacol. Toxicol. 43:175–197.[CrossRef][Web of Science][Medline]

Calabrese, E. J., and R. Blain. 2005. The occurrence of hormetic dose responses in the toxicological literature, the hormesis database: An overview. Toxicol. Appl. Pharmacol. 202:289–301.[CrossRef][Web of Science][Medline]

CAST. 2003. Mycotoxins: Risks in plant, animal, and human systems. Counc. Agric. Sci. Technol., Ames, IA.

Clement, J. G., and A. B. Okey. 1974. Reproduction in female rats born to DDT-treated parents. Bull. Environ. Contam. Toxicol. 12:373–377.[CrossRef][Web of Science][Medline]

Cruzan, G., J. R. Cushman, L. S. Andrews, G. C. Granville, K. A. Johnson, C. J. Hardy, D. W. Coombs, P. A. Mullins, and W. R. Brown. 1998. Chronic toxicity/oncogenicity study of styrene in CD rats by inhalation exposure for 104 weeks. Toxicol. Sci. 46:266–281.[Abstract/Free Full Text]

Cunningham, M. L., and J. R. Bucher. 1998. Pharmacodynamic responses of F344 rats to the mouse hepatocarcinogen oxazepam in a 90-day feed study. Toxicol. Appl. Pharmacol. 149:41–48.[CrossRef][Web of Science][Medline]

Daston, G. P., J. M. Rogers, D. J. Versteeg, T. D. Sabourin, D. Baines, and S. S. Marsh. 1991. Interspecies comparisons of A/D ratios – A/D ratios are not constant across species. Fundam. Appl. Toxicol. 17:696–722.[CrossRef][Web of Science][Medline]

Decker, L. E., R. U. Byerrum, C. F. Decker, C. A. Hoppert, and R. F. Langham. 1958. Chronic toxicity studies. I. Cadmium administered in drinking water to rats. AMA Arch. Ind. Health 18:228–231.[Medline]

Diaz, G. J., and M. Sugahara. 1995. Individual and combined effects of aflatoxin and gizzerosine in broiler chickens. Br. Poult. Sci. 36:729–736.[CrossRef][Web of Science][Medline]

Dixon, R. C., L. A. Nelson, and P. B. Hamilton. 1982. Dose-response relationships during aflatoxicosis in young chickens. Toxicol. Appl. Pharmacol. 64:1–9.[CrossRef][Web of Science][Medline]

Gee, J. M., H. Hara, and I. T. Johnson. 2002. Suppression of intestinal crypt cell proliferation and aberrant crypt foci by dietary quercetin in rats. Nutr. Cancer 43:193–201.[CrossRef][Web of Science][Medline]

Giridhar, J., and G. E. Isom. 1990. Interaction of lead acetate with atrial natriuretic factor in rats. Life Sci. 46:569–576.[CrossRef][Web of Science][Medline]

Gould, J. C., K. R. Cooper, and C. G. Scanes. 1997. Effects of polychlorinated biphenyl mixtures and three specific congeners on growth and circulating growth-related hormones. Gen. Comp. Endocrinol. 106:221–230.[CrossRef][Web of Science][Medline]

Gruger, E. H., T. Hruby, and N. L. Karrick. 1976. Sublethal effects of structurally related tetrachlorobiphenyl pentachlorobiphenyl and hexachlorobiphenyl on juvenile coho salmon. Environ. Sci. Technol. 10:1033–1037.

Hamilton, P. B., H. T. Tung, J. R. Harris, J. H. Gainer, and W. E. Donaldson. 1972. The effect of dietary fat on aflatoxicosis in turkeys. Poult. Sci. 51:165–170.[Web of Science][Medline]

Huff, W. E. 1980. Evaluation of tibial dyschondroplasia during aflatoxicosis and feed restriction in young broiler chickens. Poult. Sci. 59:991–995.[Web of Science][Medline]

Huff, W. E., L. F. Kubena, R. B. Harvey, D. E. Corrier, and H. H. Mollenhauer. 1986. Progression of aflatoxicosis in broiler chickens. Poult. Sci. 65:1891–1899.[Web of Science][Medline]

Johnson, W. L., and B. L. Damron. 1982. Influence of lead acetate or lead shot ingestion upon white cheese geese. Bull. Environ. Contam. Toxicol. 29:177–183.[CrossRef][Web of Science][Medline]

Johnston, R. V., D. C. Mensik, H. W. Taylor, G. C. Jersey, and F. K. Dietz. 1986. Single-generation drinking-water reproduction study of 1,2-dibromo-3-chloropropane in Sprague-Dawley rats. Bull. Environ. Contam. Toxicol. 37:531–537.[CrossRef][Web of Science][Medline]

Kato, H., T. Furuhashi, M. Tanaka, Y. Katsu, H. Watanabe, Y. Ohta, and T. Iguchi. 2006. Effects of bisphenol A given neonatally on reproductive functions of male rats. Reprod. Toxicol. 22:20–29.[CrossRef][Web of Science][Medline]

Leeson, S., G. J. Diaz, and J. D. Summers. 1995. Poultry Metabolic Disorders and Mycotoxins. Univ. Books, Guelph, Ontario, Canada.

Marks, T. A., G. L. Kimmel, and R. E. Staples. 1989. Influence of symmetrical polychlorinated biphenyl isomers on embryo and fetal development in mice. 2. Comparison of 4,4'-dichlorobiphenyl, 3,3',4,4'-tetrachlorobiphenyl, 3,3',5,5'-tetrachlorobiphenyl, and 3,3'4,4'-tetramethylbiphenyl. Fundam. Appl. Toxicol. 13:681–693.[CrossRef][Web of Science][Medline]

Masutomi, N., M. Shibutani, H. Takagi, C. Uneyama, N. Takahashi, and M. Hirose. 2003. Impact of dietary exposure to methoxychor, genistein, or diisononyl phthalate during the perinatal period on the development of the rat endocrine/reproductive systems in later life. Toxicology 192:1149–1170.

Mayes, M. A., D. C. Dill, K. M. Bodner, and C. G. Mendoza. 1984. Triclopyr triethylamine salt toxicity to life stages of the fathead minnow (Pimephales promelas Rafinesque). Bull. Environ. Contam. Toxicol. 33:339–347.[CrossRef][Web of Science][Medline]

Newbold, R. R., W. N. Jefferson, E. Padilla-Banks, and J. Haseman. 2004. Developmental exposure to diethylstilbestrol (DES) alters uterine response to estrogens in prepubescent mice: Low versus high dose effects. Reprod. Toxicol. 18:399–406.[CrossRef][Web of Science][Medline]

Ostrowski, H. 1984. Biochemical and physiological responses of growing chickens and ducklings to dietary aflatoxins. Comp. Biochem. Physiol. C 79:193–204.[Medline]

Ostrowski-Meissner, H. T. 1983. Effect of contamination of diets with aflatoxins on growing ducks and chickens. Trop. Anim. Health Prod. 15:161–168.[CrossRef][Web of Science][Medline]

Richardson, K. E., L. A. Nelson, and P. B. Hamilton. 1987. Effect of dietary fat level on dose response relationships during aflatoxicosis in young chickens. Poult. Sci. 66:1470–1478.[Web of Science][Medline]

Til, H. P., C. F. Kuper, and H. E. Falke. 1997. Nitrite-induced adrenal effects in rats and the consequences for the no-observed-effect level. Food Chem. Toxicol. 35:349–355.[CrossRef][Web of Science][Medline]

Vergouwen, R. P. F. A., R. Huiskamp, R. J. Bas, H. L. Roepersgajadien, J. A. G. Davids, and D. G. Derooij. 1995. Radiosensitivity of testicular cells in the fetal mouse. Radiat. Res. 141:66–73.[CrossRef][Web of Science][Medline]




This article has been cited by other articles:


Home page
Poult. Sci.Home page
T. J. Applegate, G. Schatzmayr, K. Pricket, C. Troche, and Z. Jiang
Effect of aflatoxin culture on intestinal function and nutrient loss in laying hens
Poult. Sci., June 1, 2009; 88(6): 1235 - 1241.
[Abstract] [Full Text] [PDF]


This Article
Right arrow Abstract Freely available
Right arrow Full Text (PDF)
Right arrow Alert me when this article is cited
Right arrow Alert me if a correction is posted
Services
Right arrow Similar articles in this journal
Right arrow Similar articles in ISI Web of Science
Right arrow Alert me to new issues of the journal
Right arrow Download to citation manager
Right arrow reprints & permissions
Citing Articles
Right arrow Citing Articles via HighWire
Right arrow Citing Articles via Google Scholar
Google Scholar
Right arrow Articles by Diaz, G. J.
Right arrow Articles by Blain, R.
Right arrow Search for Related Content
PubMed
Right arrow Articles by Diaz, G. J.
Right arrow Articles by Blain, R.


HOME HELP FEEDBACK SUBSCRIPTIONS ARCHIVE SEARCH TABLE OF CONTENTS