Environmental impact of micronutrients in livestock feeding

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    The US Environmental Protection

    Agency has placed some metals such

    as copper (Cu), nickel (Ni) and zinc

    (Zn) on their list of priority pollutants,

    as they are considered among the most

    toxic elements in the environment when

    improperly managed. Trace minerals

    cannot be degraded through chemical

    or biological processes, and therefore

    remain in the soil for long periods of time.

    The benets of supplementing copper, zinc and manganese in

    animal feed are critical to animal health and wellbeing, as well as

    overall production and performance improvements. For example,

    pork producers supplement diets with copper for enteric benets.A swine study has shown injected copper could result in a 19.8

    percent increase in weight gain and 16.9 percent improvement

    in feed conversion. These benets, along with 9.4 percent

    improvement in loin muscle weight relative to live body weight,

    underscore the role of available copper in grow/nish pigs. An

    important trace mineral for red blood cell health, reproduction

    and immune function, copper is also a metal co-factor for an

    enzyme responsible for collagen development and is critical for

    strengthening tendons, bones, skin and intestines.In addition, without adequate available zinc in poultry diets,

    young birds may not receive the maximum protective benet of

    a vaccination program. Zinc decient birds are more susceptible

    to diseases, resulting in increased mortality, poor efciency

    and ultimately, economic loss for the producer. Deciencies

    can lead to structural defects, as well as compromised growth

    performance. Because zinc, as well as copper, has low natural

    bioavailability and absorption in the animal, it must be

    supplemented to realize the animal’s full performance potential.

    Many studies have identied both copper and zinc, when

    used at elevated levels, can have a signicant effect on the

    environment through excretion into the manure. Traditionally,

    supplemental copper has been offered in inorganic forms as

    copper sulfate (CuSO4) or tribasic copper chloride (TBCC).

    Depending on the source of minerals fed, as little as 20 percent of

    the inorganic copper may actually be utilised by the animal, with

    the remaining 80 percent excreted in the manure.

    Producers routinely over-supplement inorganic mineral salts,

    believing this is the best way to get the maximum benet of a

    mineral program. However, this over supplementation does not

    necessarily optimise animal performance, and in fact the majority

    of these minerals will be excreted in the faeces. In broilers, for

    example, it can be calculated that 75 percent of the dietary zinc

    is wasted in this way. Over time, these minerals can accumulate

    in the soil and can affect plant growth, crop production andecosystem integrity. The over exposure of some minerals to

    plants can reduce photosynthesis, brown the root tips, inhibit

    growth and ultimately cause death. The microbial population

    in the soil is also affected by minerals contamination when

    accumulation has occurred.

    Environmentalimpact of

    micronutrients in

    livestock feeding by Jake Piel, Sustainability Manager,Novus International

    Agricultural production systems are adapting

    operations to meet the increasing demand for

    wholesome and affordable food. Attention has

    focused on the long-term impact on ecosystems

    of both crop and animal production. With

    reference to animal agriculture, concerns have

    been expressed about the concentration of

    minerals in manure and its subsequent effect on

    soil mineral content and phytotoxicity.

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    Mineral pollution of water resources is also a problem in many

    world areas. This is typically due to heavy industrialisation and

    urbanisation; however, leaching of minerals from the soil into

    water reservoirs often occurs, as well as the transport of soil due

    to heavy rains and runoff. The aquatic environment is highly

    susceptible to the effects of mineral toxicity as these organisms

    are in close and constant contact with soluble minerals over an

    extended period of time.

    Currently, there are limited regulations for mineral pollution

    in many areas. In fact, a recent report indicating poor soil

    environment conditions has ignited talks in China, so much so

    that, “the State will strengthen its regulatory role and set up a

    lifelong accountability mechanism for soil contamination; tighten

    the supervision and inspection on the performances of heavy

    polluters; and strictly control the misuse and abuse of agricultural

    inputs during the agricultural production activities.”

    In Europe, KRAV standards limit the highest average

    applications of copper and zinc over ve years of products

    applied to the soil including feed, feed minerals and medicines to

    500 and 700 g/ha/yr., respectively (KRAV 2006). Much emphasis

    has been placed on strategies for reducing the amount of copper

    and zinc excreted in this region.Recently, the maximum permitted levels of trace minerals

    supplemented to swine diets are 170 mg/kg DM for the growing

    phase and 25 mg/kg DM for the fattening stage (Lopez-Alonso

    2012). It is important for both animal producers and legislative

    authorities to have proper dialogue to encourage positive

    outcomes in terms of animal wellbeing and good environmental

    stewardship.

    Reducing the mineral load in the surrounding environment is a

    component of sustainable agriculture. The single most effective

    measure is the reduction in trace mineral levels supplemented

    in the feed. Furthermore, this can be done while increasing the

    minerals available for metabolic uptake. It is known that mineral

    elements bound to an organic ligand are more stable in the

    gut, as the cation does not interact with the other antagonistic

    components during digestion. As a result, these organic trace

    minerals (OTMs) are delivered to the site of absorption, thus

    increasing their bioavailability to the tissues.

    In 2014, 117 million pigs were produced in the United States.

    Potentially, more than 2 million pounds of copper excreted

    in the environment could have been avoided with the use of

    MINTREX® Cu from Novus. A recommended lifetime loading

    limit for copper in soil is 77 pounds of copper per acre. Using this

    recommendation, and supplementing with MINTREX Cu, means

    that 27,000 fewer acres are required to manage this mineral

    load. This is relatively small if we consider that half of the pigs

    produced in the world, about 476 million, are in China. If all pig

    feed in China was supplemented with MINTREX Cu, as opposed

    to inorganic trace minerals, the result is a savings of 982 million

    pounds of copper excreted to the environment as waste. Using

    the same US copper loading rates, this is equivalent to almost 13

    million acres.As the global population approaches nine billion by 2050,

    food production capacities must increase to accommodate the

    nutritional needs of more people. Technological advances in

    agriculture and livestock production, as well as sustainable

    practices, are critical to achieving this goal. The reduction

    of environmental pollution by minerals is one area in which

    signicant improvements can be made through supplementing

    healthy diets with a more bioavailable mineral solution.

     References available on request 

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