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Trace elements: Bioavailability in farm animals

Trace elements

Trace elements are essential dietary components for organisms. They must be ingested in very small amounts, unlike macroelements. Concentrations of specific trace elements within the body are usually <50 mg/kg body weight, with the exception of iron (National Research Council, 2005).

Current recommendations in animal feeding in regards to trace minerals, include total dietary concentrations. This is due to the highly variable concentration levels and bioavailability of plant-based foods which many times don’t meet  animal needs(Suttle, 2010).

In ruminants, there are special recommendations regarding Cobalt in order to address specific requirements of rumen microbiota and promote cobalamin synthesis.

Special forms have also been commercialized in recent years. From which the most significant are probabbly nanoparticles (e.g. nano ZnO).

Within the European Union, feed additives require authorisation in accordance with Regulation (EC) No 1831/2003. The authorisation procedure must ensure that a feed additive is safe for: the animals, personnel handling the product, consumers and the environment. This implies that trace element supplements are used in sufficient quantities in order to minimize total dietary concentrations needed. Avoiding excess accumulation in animals, edible products and the environment.

 

Defining “bioavailability”

The term bioavailability is often used as a synonym for absorption or retention capacity. However, this is misleading as it implies that trace elements are 100% bioavailable as long as they are present as an available chemical compound within the gastrointestinal (GI) tract.

The content of essential trace elements in the body is actively regulated by the intestinal barrier through specific absorption mechanisms, as well as various absorption and excretion mechanisms according to their metabolic state (Windisch, 2002).

Therefore, the bioavailability of a trace element source can be defined as its potential to supply the physiological functions dependent on that specific element, within the animal’s metabolism(O’Dell, 1984).

These physiological functions are closely related to the  organism’s total requirements and the kinetics of that element within the body. In regards to animal nutrition,the bioavailability estimate is related to the estimate of gross requirements, which is expressed as:

“the minimum concentrations of total feed required to provide sufficient bioavailable quantities under ad libitum feeding conditions.”

 

 

Basic concepts of trace element metabolism

[register]Trace elements tend to circulate in their ionic form bound to chemical ligands. The role that these ions play within biochemical reactions as cofactors of the structure and activity of peptides is considered to be irreplaceable by other substances. This highlights the base of their essentiality for animals (Maret, 2016).

In intensive or semi-intensive farm animal production systems, clinical presentations due to trace element deficiencies are rare and most deficiency presentations are subclinical.

A subclinical deficiency compared to a clinical one is defined by the total absence of visible symptoms of pathophysiological adaptations. Therefore, it only becomes evident due to changes in metabolic levels.

 

 Zinc 

Total Zn body content is regulated at the GI tract absorption level and through fecal excretion.

Parallel to the upward regulation of the GI tract absorption capacity, the excretion of endogenous Zn is reduced to a minimum under conditions of Zn deficiency in the diet. Excretion increases when additional Zn supply surpasses the requirements’ threshold (Weigand and Kirchgessner, 1980).

 

Differences between animal species regarding susceptibility to Zn deficiency are predominantly related to their ability to deal with Zn absorption antagonists within the digestive tract.

 

Poultry, and especially broilers, may also experience negative effects due to the presence of phytic acid in their diet. However, recent data suggests that significant degradation of phytate occurs from microbial phytase activity (Zeller et al. , 2015, Sommerfeld et al., 2019).

Brugger et al., 2020 suggest that the Zn status of laying hens may be affected by phytic acid under conditions comparable to those previously applied in weaned piglets (Brugger et al., 2014).

 

Ruminants harbor significant microbial phytase activity in their rumen ecosystem (Humer and Zebeli, 2015). Therefore, their susceptibility to phytate-induced Zn deficiency should be lower than in non-ruminants.

Microbial breakdown of phytic acid in the rumen is generally not complete and can be significantly reduced under conditions where ruminal feed passage increases. For example under conditions of high DM consumption (Humer and Zebeli, 2015).

In addition, forage contamination with soil (especially silage) can produce high concentrations of Fe (up to 1500 mg/kg DM) which have been shown to impair the use of Zn in feed (Standish et al., 1969).

 

Studies carried out in pigs detected competition of both ions through transport mechanisms in the GI tract mucosa (Bertolo et al., 2001).

 

 

Copper

Hepatic Cu represents the body’s primary Cu storage site(Suttle, 2010).It is stored bound to the enzyme Metallothionein (MT) or undergoes the synthesis of Cu protein (especially ceruloplasmin (CP)), biliary excretion or it is directly transferred to other tissues for Cu peptide synthesis.

The particular purpose of Cu transport depends on animal’s Cu state and its requirements(Bremner, 1993):

 

Dietetic phytate can chelate Cu and block its absorption. This is especially true in non-ruminant farm animals.

The addition of phytase in pig diets increased the utilization of Cu in feed in the trial by Adeola et al. (1995), but a meta-analysis of 14 studies showed no effects of exogenous phytase on the availability of Cu from growing pigs (Bikker et al., 2012).

In fact, phytate has a much higher affinity for other ions such as Ca2+ and Zn2+. Therefore, the association of Cu with phytate is less likely when there are considerable amounts of such ions(Humer et al., 2015).

Therefore, dietary Cu deficiencies in pigs fed with common ingredients are usually rare(Suttle, 2010).

There appear to be no practical observations of Cu deficiency in poultry. Cu availability indifferent ration ingredients has been thoroughly assessed. Although Cu availability for chickens is reduced in the presence of high phytate concentrations, the apparent absorption does not drop to zero.

 

Ruminants tend to be the most susceptible to Cu deficiency. Increased intake of sulfur (S) and molybdenum (Mo), mainly from fiber, leads to the formation of thiomolybdates in the rumen. These quelate Cu, which extremely reduces the apparent absorption of Cu to <1%, e.g. in sheep (Suttle, 1983, Allen and Gawthorne, 1987).

 

Spears et al. (2004) demonstrated that Cu supplemented as tribasic Cu chloride for growing cattle has superior bioavailability compared to Cu sulphate under conditions of high levels of Mo and S in the diet. This appears to be due to lower solubility in the rumen of tribasic Cu Chloride and therefore reduced susceptibility to thiomolybdate antagonism.

  • In contrast, Hanauer (2017) suggested that this superiority can be reversed when the Mo and S in the diet are moderate, because the lower solubility can become a disadvantage in terms of bioavailability, as demonstrated in non-lactating cows.

In turn, excess Mn in the diet may further promote molybdenum-associated hypocupremia, as demonstrated in growing cattle (Hansen et al., 2009).

More in “Nutritional aspects of Copper for animal production”

 

Manganese

Manganese is one of the least abundant essential transition metals in animal tissues (Suttle, 2010). Given the narrow range of concentrations of Mn that fulfills its biochemical purpose, its body reserves must be strictly regulated.

 

There are reports of clinical Mn deficiency under field conditions, mainly in high-intensity poultry production systems. It seems that especially chickens are less efficient than other species in absorbing Mn.

The high concentrations of phytate and fiber are the most relevant antagonisms in this regard. There is another antagonism between excessive levels of P in the diet and gastrointestinal absorption of Mn (Baker and Odohu, 1994).

In addition, excessive supply of Fe in the diet can cause Mn deficiency in all livestock species (Suttle, 2010).

 

The content of Mn in forage is quite variable depending on its geographical origin. In addition, it also depends on other factors, such as:

In alkaline soils, the absorption of Mn by plants can be affected (Suttle, 2000). Conversely, acidic soils can harbor so much Mn available to plants that animal poisoning could become a problem (Grace and Lee, 1990).

Therefore, the determination of Mn in food is especially important for feeding ruminants.

 

 

Conclusions

Flows of essential trace elements are actively regulated in response to dietary intake levels that vary below or above metabolic requirements.

There are relative differences in bioavailability with different sources of trace elements in the diet, as well as between different animal species

Source: Abstract taken from Review: Bioavailability of trace elements in farm animals: definition and practical considerations for improved assessment of efficacy and safety”Brugger et al., 2022

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