Trace mineral concentration of forages in connection with sheep dietary requirements

 

 

A. Qudoos^I; U.B. Tahir^II; S. Ahmad^III; M. Tariq^IV; M. Imran^II; R. Nadeem^V; S. Noreen^V; N. Luqman^VI; M. Maqbool^II; I. Jan^VII; Z. Iqbal^VIII; M. Raza^IX; M.S. Sajid^{II, *}; H.M. Rizwan^{X, **}

^ICentral Hi-Tech Laboratory, University of Agriculture, Faisalabad, Pakistan
^IIDepartment of Parasitology, University of Agriculture, Faisalabad, Pakistan
^IIIInstitute of Animal and Dairy Sciences, Faculty of Animal Husbandry, University of Agriculture, Faisalabad, Pakistan
^IVDepartment of Livestock Management, University of Agriculture Faisalabad, Sub-Campus Toba Tek Singh, Pakistan
^VDepartment of Chemistry, University of Agriculture, Faisalabad, Pakistan
^VIVeterinary Officer, Livestock and Dairy Development, Punjab, Pakistan
^VIICollege of Veterinary Sciences, The University of Agriculture Peshawar, 25130, Khyber Pakhtunkhwa, Pakistan
^VIIISection of Livestock Management, Department of Animal Sciences, KBCMA College of Veterinary and Animal Sciences, Narowal Sub campus UVAS, Lahore, Pakistan
^IXSection of Physiology, Department of Basic Sciences, KBCMA College of Veterinary and Animal Sciences, Narowal Sub campus UVAS, Lahore, Pakistan
^XSection of Parasitology, Department of Pathobiology, KBCMA College of Veterinary and Animal Sciences, Narowal Sub campus UVAS, Lahore, Pakistan

 

 

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ABSTRACT

This paper describes the trace and ultra-trace mineral concentration in different forages utilized by sheep (Kajli and Fat tail) in the rangelands of Chakwal district, Punjab, Pakistan. The concentrations of Se, Mo, Zn, Mn, Cu, and Co were assessed using spectrophotometric methods after the digestion of forage samples. The dominant forage species consumed by sheep were Buxus pappillosa, Prosopis juliflora, Ficus palmata, Acacia modesta, Trichodesma indica, Olea permiginea, Lantana camara, Justicia adhatoda, Morus nigra, and Ipomoea carnea. The overall mean concentration of Co (1.27±0.24 mg/Kg of DM), Zn (35.14±1.28 mg/Kg of DM), and Cu (28.06±1.29 mg/Kg of DM) in forages were higher than the requirements for lactating ewes, while the concentration of Se was within the normal range. Molybdenum (0.030±0.004 mg/Kg of DM) and Mn (29.69±1.61 mg/Kg of DM) concentrations were lower than dietary requirements for sheep. In different administrative divisions (tehsils) like Chakwal, Talagang, Choa Saidan Shah, and Kalar Kahar of Chakwal district, the trace minerals Zn, Mn, and Co, showed non-significant variation, whereas Se, Mo, and Cu showed substantial variation. In conclusion, rangeland forages contained a sufficient concentration of most trace minerals (Co, Cu, Se, Zn) to meet the requirements of grazing sheep in the study district. However, Mn and Mo supplementation seems to be essential to maintain the optimal production capabilities of sheep in this area.

Key words: dietary requirements, rangeland forages, sheep flocks, trace minerals

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Introduction

In livestock production systems, natural vegetation and agro-grazing are the most important components. Regional situation and climate regulate the kind, nature, nutritive value, composition, and distribution of forage plants in different grazing sites and cropping belts (Khan et al., 2007). Experiments, conducted in the Punjab province of Pakistan, identified trace mineral contents of many plant species (Cichorium intybus, Coronopus didymus, Mazus reptans, Cynodon dactyíon, Malva negíecta, Trifolium alexandrinum, Parthenium hysterophorus, and Medicago polymorpha) grazed by sheep and goats (Khan et al., 2007; Rizwan et al., 2019; Ahmad et al., 2020). Identification of feed, soil, and pastures deficient in minerals is important for the rationalization of nutrient supplies, which may result in enhanced production performance and immune status of animals (Rizwan et al., 2021a,b). In reference to livestock, forages, pasture, and supplements (concentrates) are the main sources of trace minerals like Cu, Mn, Co, and Zn. Trace minerals are considered essential for the proper functioning of various physiological systems of the body and are important for normal immune function and protection against oxidative damage to tissues. In livestock, the amount of these trace minerals depends upon environmental conditions, nature, type of soil, plant types, species of plants, the magnitude of dry matter, and the maturity status (Rizwan et al., 2021a,c).

Rangelands, covering more than 60% of the area, are a major part of the agricultural system in Pakistan and offer grazing facilities for livestock (Khan et al., 2007). It is important to explore the triangle of soil-plant-animal to calculate the concentration of trace minerals because of its effects on animal production capabilities (Qudoos et al., 2017). Information regarding the available pastures along with their seasonal nutritive values is a prerequisite to obtaining maximum output from livestock production (Khan et al., 2007; Qudoos et al., 2017; Rizwan et al., 2019). It is well known that the mineral profiles of forages may fluctuate seasonally (Khan et al., 2007). Consequently, it is beneficial to know the mineral profiles of forages and pastures before deciding on a particular mineral(s) supplementation for livestock in a particular season. Limited efforts by Ahmad et al. (2020) and Rizwan et al. (2021b) have been made for this purpose and incomplete data is available regarding the status of trace minerals of forages utilized by rangeland sheep of Chakwal district, Pakistan. Hence, the study was planned to estimate the trace mineral profiles of rangeland forages utilized by sheep in this district. Under natural grazing conditions, forages are the main source of minerals. Determination of trace elements in grazing forages is important to regulate the requirement of animals. Grazing on trace element-rich forages may increase the resilience against infections, particularly in resource-poor countries like Pakistan. This study may elucidate the status of the mineral profiles of available forages to recommend specific mineral supplementation in instances of deficiency.

 

Materials and Methods

The present study was completed in autumn (October to December, 2020) in Chakwal district, Punjab, Pakistan, located in the southern part of Rawalpindi district between 72° 54' east and 32° 56' north. The district of Chakwal, which covers an area of 6,524 km², is subdivided into four tehsils i.e., Tehsil Kalar Kahar, Talagang, Chakwal, and Choa Saidan Shah. Chakwal is in the Potohar plateau and the Salt Range. The southern portion runs up into the Salt Range and includes the Chail peak, 3,701 feet (1,128 m) above sea level, the highest point in the district. The southeast and southern area is hilly and scrub forest covers the rocky surfaces. The climate of Chakwal is sub-humid; rainfall is 350-500 mm and occurs during the monsoon.

Forages that are commonly grazed by sheep were collected in triplicate (n = 3) from each grazing site located in the Kalar Kahar, Talagang, Chakwal, and Choa Saidan Shah tehsils. All stages (seedling, vegetating, budding, flowering, and ripening) of selected forages were collected in equal amounts. The fresh green samples were collected in polythene bags and labelled for shipment to the University of Agriculture, Faisalabad, Pakistan. The forage samples were shipped on the same day of collection. The identification of collected forages was done by a professional of the Botany Department, University of Agriculture, Faisalabad. Hydrochloric acid (1%) followed by distilled water was used to wash the leaves of forages. Forage samples were dried in the open air under shade and then placed in a hot air oven (65 ± 5 °C) for 24 h. An electrical grinding machine (Secura®, Netherlands: Type: Blade Coffee Grinders, Power (W): 3000w, Housing Material: Stainless steel, Model Number: 800Y) was used to grind dried leaves, which were then subjected to wet digestion. In short, 1 g dried sample of the plant was digested with nitric acid (HNO3) and perchloric acid (HClCM) in a 3:1 ratio on a hot plate. The final volume was adjusted to 50 mL with de-ionized water when the material was cleared. Filtration was then done using a Whatman filter (No. 42) and stored in air-tight bottles for determination of the mineral profile (Miller, 1998).

Evaluation of Cu, Co, Zu, and Mn was done at the Central Hi-Tech Laboratory, University of Agriculture, Faisalabad, using an atomic absorption spectrophotometer (Hitachi Polarized Zeeman AAS, Z-8200) using the standard protocols as described by Anan et al. (2001). Standard solutions for Zn, Cu, Mn, and Co were prepared using the available reagent-grade salts. Each standard solution was run one by one for these minerals and their absorbance was recorded. Standard curves for each mineral were constructed by plotting the absorbance of standards against their concentrations. Concentrations of respective minerals in the samples were calculated from their respective standard curves. Values of the atomic absorption spectrophotometer, used for the determination of Cu, Co, Zn, and Mn, are given in Table 1. An inductively coupled plasma-optical emission spectrophotometer (Optima 2100-DV, Perkin Elmer) was used to calculate the ultra-trace minerals, Se and Mo. Zero emission was set by using a blank solution. The emissions of prepared standards were noted and plotted to obtain a calibration curve. The emissions of the samples were determined and concentrations were calculated from the respective calibration curve. Values from the inductively coupled plasma-optical emission spectrophotometer used for the determination of Se and Mo, are given in Table 2.

The mean concentration of each mineral was measured, together with the standard errors. Differences in mineral concentration of forages were evaluated using one-way analysis of variance (ANOVA). Tukey's t-test was used in case of significant (P <0.05) differences between treatment means (Schork and Remington, 2010).

 

Results

The dominant forage species consumed by sheep (Kajli and Fat tail) in the study area were: Buxus pappillosa, Prosopis juliflora, Ficus palmata, Acacia modesta, Trichodesma indica, Olea permiginea, Lantana camara, Justicia adhatoda, Morus nigra, and Ipomoea carnea. The highest concentration of Zn was detected in Buxus pappillosa (39.28 ± 1.34 mg kg¹ of DM), whereas the lowest was in Acacia modesta (31.12 ± 0.93 mg kg¹ of DM). Ipomoea carnea (32.88 ± 0.56 mg kg¹ of DM) had the highest concentration of Cu, while Lantana camara (22.68 ± 0.53 mg kg¹ of DM) had the lowest concentration. The concentration of Mn was highest in Prosopis juliflora (35.23 ± 0.73 mg kg¹ of DM) and lowest in Justicia adhatoda (27.35 ± 0.59 mg kg¹ of DM). The mean concentration of trace minerals (mg kg^-1 of DM) in forages sampled collected from Chakwal district, Pakistan is given in Table 3. The overall concentration of Co, Zn, and Mn in forages collected from the lands of different tehsils was similar (P >0.05). However, the overall concentration of Cu, Mo, and Se in forages reflected a marked fluctuation (P <0.05) in different tehsils. The overall mean trace mineral concentration in forages collected from different tehsils of Chakwal district are shown in Table 4. The overall mean concentrations of Zn (35.56 mg kg^-1 of DM), Cu (28.06 mg kg^-1 of DM), and Co (1.27 mg kg^-1 of DM) in the sampled forages of different tehsils were higher than the recommended dietary requirements for lactating ewes. The overall mean concentrations of Mn (29.69 mg kg^-1 of DM) and Mo (0.030 mg kg^-1 of DM) in forages were lower than the suggested critical dietary concentration for lactating ewes, however; that of Se (0.194 mg kg^-1 of DM) remained within the recommended range. The critical concentration of minerals required by lactating ewes was described by NRC (2007). A compression of overall mean concentration of trace mineral with the critical concentration of minerals required for sheep is given in Figure 1.

 

Discussion

Rangelands represent an important source of livestock feed in Pakistan. In the Potohar plateau, small ruminants depend mainly on grazing for feed. In the salt range of Pakistan, 'the forage species (Acacia modesta, Butea monosperma, Olea feruginea, Tamarix aphylla, Ziziphus maritiana, Astragalus psilocentros, Buxus papillosa), preferred for grazing by sheep, have been listed by Nawaz et al. (2012). Various other authors (Qudoos et al., 2017; Rizwan et al., 2019; Ahmad et al., 2020) have also reported the forages found in the present study along with other species which comprise the vegetation potential of this plateau. A diverse flora is consumed by small ruminants in other parts of the world, including Botswana, Kenya, and Nigeria (Odo et al., 2001; Aganga and Mesho, 2008; Lengarite et al., 2013), which vary from forages identified in our study. The difference in forage variety is related to differences in soil composition and structure, the topography of the area, and climatic conditions (Odo et al., 2001). Additionally, patterns of grazing may also affect the diversity of floral species. Forages offer many nutrients including trace minerals to animals in a natural grazing system.

Analyses of forages were done by various scientists for the determination of trace minerals, as they generally reflect the mineral intake profile of grazing livestock (Ogeba and Ayoade, 1995; Khan et al., 2007; Qudoos et al., 2017). The higher-than-recommended critical dietary values of Zn (35.14 mg kg^-1 of DM) for lactating ewes in our analysis are in close agreement with reports published in Pakistan and Kenya (Khan et al., 2007; Lengarite et al., 2013). However, some reports from Pakistan also report a lower concentration of forage Zn than the recommended critical dietary concentration (Khan et al., 2015). Or et al. (2005) and Johannesson et al. (2007) reported much higher values of Zn in forage grazed by sheep than we found. Suggested requirements of Zn for lactating ewes are 20-40 mg kg^-1 DM, which is compatible with our observations (NRC, 2007). Deficiency of Zn has been described in animals grazing on forages with low concentrations of Zn or high in compounds like S, Mn, Mg, Fe, and Cd, which interfere with the utilization of Zn by cattle (Ndebele et al., 2005). The composition of forage minerals differs depending on grazing pressure, type, variety of soil, and fertilizer use. The Zn concentration in forages is also influenced by these factors. Moreover, profiles of trace minerals in plants may vary amongst different species and seasons (Ben-Shahar and Coe, 1992; Khan et al., 2003).

Mean concentration of Cu (28.06 mg kg^-1 of DM) in sampled forages was higher than the suggested concentration for lactating ewes (NRC, 2007). Our findings are supported by those of Ahmad et al. (2020), Rizwan et al. (2021b), Or et al. (2005), and Khan et al. (2003), who reported similar Cu concentrations in forages consumed by small ruminants. Forage species, naturally grown in different geographical localities, may contain lower (Johannesson et al., 2007; Khan et al., 2015) or higher (Khan et al., 2003) quantities than the suggested requirements. The main factor accountable for changes in Cu concentration of forage is low soil pH which raises Fe solubility and thus results in decreased absorption of Cu by plants. A lower concentration of Cu in forages may also be linked to the presence of antagonistic elements such as S, Fe, and Mo (Beeson and Matrone, 1976). The formation of thiomolybdates by the interaction of S, Mo, and Fe with Cu is another cause of Cu deficiency in animals, as this complex is not absorbed by the animals (Spears, 2003). The manganese concentration (29.69 mg kg^-1 of DM) in forage species in our study was lower than the critical concentration of 40 mg kg^-1 DM recommended by the NRC (2007) for lactating ewes, which concurs with earlier reports (Khan et al., 2015; Rizwan et al., 2019; Ahmad et al., 2020). However, higher Mn concentrations in forages have been reported by Johannesson et al. (2007). Forage Mn concentration is generally linked to soil Mn abundance. However, forages, grown even in Mn-deficient soils, have been found to have a sufficient concentration (Beeson and Matrone, 1976). Cobalt deficiency is often considered the most prevalent deficient mineral of grazing livestock in many parts of the world (NRC, 2007). The concentration we found (1.27 mg kg^-1 of DM) in the collected forage species was considerably higher than the critical range (0.1-0.125 mg kg^-1) established by NRC (2007) and reported elsewhere (Johannesson et al., 2007; Ahmad et al., 2020). Deficiencies of Co in forages have also been observed in different geographical areas (Spears, 2003; Lengarite et al., 2013; Nordlokken et al., 2015). However, Rizwan et al. (2019; 2021b) observed a normal concentration of Co in forages. Differences in Co concentration in forage are primarily linked to its uptake by plants, ultimately depending on Mn and Co concentration in soils. Higher concentrations of Mn in soil reduces the uptake of Co in forages (Beeson and Matrone, 1976). Variation in forage Co concentration may also be related to the plant maturity stage because Co concentration tends to decrease as the plant matures (Beeson and Matrone, 1976; Spears, 2003).

The concentration of Mo in forages (0.030 mg kg^-1 DM) reported here was not different from that noted by Johannesson et al. (2007). Plants, grown in soils having an insufficient concentration of certain trace minerals, may contain a reduced concentration of these minerals (Beeson and Matrone, 1976; Spears, 2003). The concentration of Se in the study forages was within the recommended dietary requirements for lactating ewes (NRC, 2007), which supports the findings of Nordlokken et al. (2015). However, lower forage Se concentrations were observed by Johannesson et al. (2007) and Khan et al. (2003). Variations in forage Se concentration might be attributable to variations in S concentration in forages. Consequently, owing to the chemical similarity between Se and S, the availability of S plays a key role in Se accumulation. Moreover, Se uptake by plants increases with increases in soil pH (Pope et al., 1979).

The present study was conducted in a specific period of a specific zone of Pakistan to determine the trace mineral profiles of forages. However, further studies are recommended to compare the variation in forage species in different seasons and their trace mineral profiles. Such kind of studies will be helpful to understand the status of mineral profiles of available forages and to recommend specific mineral supplementation in instances of deficiency.

 

Conclusion

This study on profiles of trace minerals in rangeland forage consumed by sheep suggested that Co, Cu, Se, and Zn concentrations in forages were sufficient to meet sheep requirements in the rangeland of Chakwal district, Punjab, Pakistan. However, forage concentrations of Mo and Mn were below the dietary requirements, and optimal productivity of sheep in this area may require supplementation with these minerals. Forages like Buxus pappillosa (Zn: 39.28±1.34 mg kg¹ DM; Se: 0.268±0.024 mg kg¹ DM), Ipomoea carnea (Cu: 32.88±0.56 mg kg¹ DM), Prosopis juliflora (Mn: 35.23±0.73 mg kg¹ DM), Lantana camara (Co: 1.75±0.18 mg kg¹ DM), and Trichodesma indica (Mo: 0.042±0.004 mg kg¹ DM) showed the highest concentration of trace minerals. It is recommended to use these forages to feed the sheep to fulfil the requirement of trace minerals naturally.

 

Conflicts of Interest

The authors declare that they have no conflict of interest.

 

Acknowledgements

The authors are very grateful to Prof. Dr. Timothy Geary, Institute of Parasitology, McGill University, Macdonald Campus, Quebec, Canada for the English editing of the manuscript.

 

Funding

Financial support for this study was provided by the Higher Education Commission, Islamabad Pakistan, under the project titled "Phytotherapy: An Easy and Economic Way to Cure the Gastrointestinal Parasites in Sheep". The project Number was 20-2666/NRPU/R&D/HEC/12/6974.

 

Authors' contributions

MSS, AQ, and HMR conceived and planned the experiments. MI, NL, RHAN, and IJ contributed to sample preparation and carried out the experiments. NL and ZI contributed to the interpretation of the results. MR, HMR, and AQ took the lead in writing the manuscript. MSS supervised the project. MSS and HMR contributed to the final version of the manuscript. All authors have read and approved the finalized manuscript.

 

Conflict of interest declaration

The authors declare there is no conflict of interest.

 

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Submitted 6 October 2022
Accepted 29 March 2023
Published 9 July 2023

 

 

* Corresponding Authors: drsohailuaf@hotmail.com; hm.rizwan@uvas.edu.pk