| Literature DB >> 26301092 |
Mohana Devi Subramaniam1, In Ho Kim1.
Abstract
Clays are crystalline, hydrated aluminosilicate molecules composed of alkali and alkaline earth cations along with small amounts of various other elements. The best-known are montmorillonite, smectite, illite, kaolinite, biotite and clinoptilolite. The molecules in these clays are arranged in three-dimensional structures creating internal voids and channels capable of trapping a wide variety of molecules. As a result of this structure, clay minerals are regarded as a simple and effective tool for the prevention of the negative effects of many toxic compounds. Dietary supplementation with clays has been shown to improve weight gain and feed conversion in pigs. Where improvements in performance have been noted, one of the most likely explanations for the improvement is the fact clays increase nutrient digestibility. Clays reduce the speed of passage of feed along the digestive tract which allows more time for digestion. Feeding clays also causes morphological changes in the intestinal mucosa such as an increase in villus height and an increase in the villus height to crypt depth ratio. These changes increase the surface area of the gastrointestinal tract thus increasing nutrient digestibility. Several studies have indicated that feeding clay reduces the incidence, severity and duration of diarrhea in pigs. The mechanism for the reduction in diarrhea is likely due to increases in the numbers of Bifidobacteria and Lactobacillus and decreases in Clostridia and E. coli in the small intestine of pigs fed clays. In addition, the numbers of pigs born alive and weaned, birth weight and weaning weight have been shown to be higher for sows fed clays. Several studies have indicated that clays can help mitigate the effects of mycotoxins. The aim of the present review is to focus on the various clays which have been given attention in recent research and to discuss their potential to improve pig performance.Entities:
Keywords: Animal production; Clay; Clinoptilolite; Feed additive; Montmorillonite; Zeolite
Year: 2015 PMID: 26301092 PMCID: PMC4546348 DOI: 10.1186/s40104-015-0037-9
Source DB: PubMed Journal: J Anim Sci Biotechnol ISSN: 1674-9782
Effect of clay supplementation on the performance of weanling pigs
| Items | Control | Tylosin | Clay (3 g/kg)1 | Clay (6 g/kg)1 | SEM |
|---|---|---|---|---|---|
| Day 0 to 7 | |||||
| Weight gain, g/day | 258 | 295 | 288 | 257 | 15 |
| Feed intake, g/day | 391 | 395 | 399 | 405 | 24 |
| Feed efficiency | 0.66b | 0.75a | 0.72a | 0.64b | 0.02 |
| Day 7 to 21 | |||||
| Weight gain, g/day | 429 | 458 | 466 | 432 | 20 |
| Feed intake, g/day | 554 | 546 | 591 | 560 | 42 |
| Feed efficiency | 0.78 | 0.84 | 0.80 | 0.77 | 0.05 |
| Day 21 to 35 | |||||
| Weight gain, g/day | 526 | 580 | 567 | 517 | 28 |
| Feed intake, g/day | 935 | 913 | 944 | 916 | 37 |
| Feed efficiency | 0.56b | 0.64a | 0.60a,b | 0.56b | 0.03 |
| Day 0 to 35 | |||||
| Weight gain, g/day | 434 | 474 | 471 | 431 | 24 |
| Feed intake, g/day | 674 | 663 | 694 | 672 | 35 |
| Feed efficiency | 0.64b | 0.72a | 0.68a,b | 0.64b | 0.03 |
Yan et al. [28]
a,bValues significant at P<0.05 level
1Clay comprised of 72.6 % SiO2, 8.18 % AL2O3, 9.42 % Fe2O3, 5.25 % K2O and minor amounts of other minerals
Effect of clinoptilolite on the performance of growing and finishing pigs
| Items | Treatment |
| ||||||
|---|---|---|---|---|---|---|---|---|
| Control | Antibioticc | Clinoptilolited | Combination | SD | Clinoptilolite | Antibiotic | C x A | |
| Day 25 to 70 | ||||||||
| Weight gain, kg/d | 0.34c | 0.40ab | 0.39b | 0.41a | 0.032 | <0.01 | <0.01 | 0.14 |
| Feed intake, kg/d | 0.68a | 0.64b | 0.68a | 0.66ab | 0.024 | 0.35 | 0.02 | 0.34 |
| Feed conversion | 2.02a | 1.59c | 1.75b | 1.60c | 0.19 | <0.01 | <0.01 | <0.01 |
| Day 71 to 112 | ||||||||
| Weight gain, kg/d | 0.63c | 0.69ab | 0.66bc | 0.71a | 0.04 | 0.09 | <0.01 | 0.72 |
| Feed intake, kg/d | 1.79 | 1.76 | 1.77 | 1.69 | 0.11 | 0.33 | 0.22 | 0.60 |
| Feed conversion | 2.84a | 2.55bc | 2.69ab | 2.38c | 0.22 | 0.03 | <0.01 | 0.92 |
| Day 113-161 | ||||||||
| Weight gain, kg/d | 0.83b | 0.90a | 0.85b | 0.91a | 0.04 | 0.29 | <0.01 | 0.21 |
| Feed intake, kg/d | 2.69a | 2.56b | 2.64ab | 2.61ab | 0.10 | 0.89 | 0.15 | 0.24 |
| Feed conversion | 3.25a | 2.86b | 3.12a | 2.87b | 0.19 | 0.24 | <0.01 | 0.16 |
| Day 25 to 161 | ||||||||
| Weight gain, kg/d | 0.60c | 0.67a | 0.64b | 0.69a | 0.03 | 0.04 | <0.01 | 0.21 |
| Feed intake, kg/d | 1.74 | 1.67 | 1.72 | 1.67 | 0.06 | 0.56 | 0.12 | 0.58 |
| Feed conversion | 2.88 | 2.51 | 2.70 | 2.45 | 0.19 | 0.04 | <0.01 | 0.12 |
Papaioannou et al. [29]
a,bValues significant at P<0.05 level
cAntibiotic was a combination of enrofloxacin and salinomycin
dClinopilolite fed at 2 % of the diet
Effects of including sericite in diets fed to growing pigs on the apparent total tract digestibility of nutrients
| Items | Level of sericite, % | ||||
|---|---|---|---|---|---|
| 0.0 | 0.5 | 1.0 | SE |
| |
| Dry matter | 0.76 | 0.80 | 0.82 | 0.009 | 0.01 |
| Nitrogen | 0.79 | 0.83 | 0.83 | 0.008 | 0.03 |
| Energy | 0.79 | 0.78 | 0.82 | 0.013 | 0.19 |
| Calcium | 0.56 | 0.59 | 0.60 | 0.007 | 0.02 |
| Phosphorus | 0.42 | 0.50 | 0.50 | 0.005 | 0.03 |
Li and Kim [27]
Effects of clay supplementation on nutrient digestibility in growing-finishing pigs1
| Items | Level of clay (g/kg) |
| ||||
|---|---|---|---|---|---|---|
| 0 | 3 | 6 | SE2 | Linear | Quadratic | |
| Dry matter | 0.77b | 0.82 a | 0.77 b | 0.009 | 0.91 | <0.01 |
| Nitrogen | 0.76 b | 0.79 a | 0.74 b | 0.006 | 0.05 | <0.01 |
| Energy | 0.81ab | 0.83 a | 0.78 b | 0.013 | 0.13 | 0.04 |
Yan et al. [34]
a,bValues significant at P<0.05 level
1Clay comprised of 72.6 % SiO2, 8.18 % AL2O3, 9.42 % Fe2O3, 5.25 % K2O and minor amounts of other minerals
Effect of montmorillonite on the intestinal morphology in the jejunum
| Items | Control | Montmorillonite |
|---|---|---|
| Villus height (um) | 440a | 524b |
| Crypt depth (um) | 356 | 309 |
| Villus height: crypt depth | 1.24a | 1.70b |
Xia et al. [32]
a and b Values significant at P<0.05 level
Effect of smectite on the diarrhea scores of pigs experimentally infected with a pathogenic E. coli
| Items | Level of smectite, % |
| ||
|---|---|---|---|---|
| 0 | 0.3 | 0.6 | ||
| Diarrhea score1 | 1.99 | 1.66 | 1.62 | <0.05 |
| Diarrhea days2 | 17 | 5 | 4 | <0.05 |
| Frequency3, % | 24 | 7 | 6 | <0.05 |
Song et al. [5]
1diarrhea score = 1, normal feces, 2, moist feces, 3, mild diarrhea, 4, severe diarrhea, 5, watery diarrehea
2diarrrhea days = number of pig days with diarrhea score greater than 3
3Frequency = diarrhea x 100/pig days
Effect of montmorillonite on the intestinal flora of weanling pigs (log10 CFU/g)
| Items | Control | Montmorillonite |
|---|---|---|
| Total anerobes | 8.4 | 8.2 |
| Total anaerobes | 9.4 | 9.3 |
| Bifidobacteria | 6.9 | 7.4 |
| Lactobacillus | 7.9 | 8.2 |
| Clostridium | 6.5 | 5.8 |
|
| 7.8 | 7.4 |
Xia et al. [32]
Effect of zeolites on sow fertility and diseases
| Items | Control | Zeolite |
|---|---|---|
| Return to estrus | 14.1 | 10.3 |
| Farrowing rate | 78.7 | 86.2 |
| Inappetence | 40.8 | 35.1 |
| Pyrexia | 29.1 | 26.1 |
| Mastitis | 17.5 | 14.4 |
| Vaginal discharge | 6.8 | 8.1 |
Papaioannou et al. [44]
The effects of clinoptilolite on the reproductive performance of sows
| Items | Control | Clinoptilolite |
|---|---|---|
| Piglets born alive | 9.60 | 10.32 |
| Piglets weaned | 8.72 | 9.49 |
| Preweaning mortality, % | 9.16 | 8.04 |
| Birth weight, kg | 1.34 | 1.44 |
| Weaning weight, kg | 6.04 | 6.28 |
Kyriakis et al. [45]
The effect of montmorillonite clay on the performance and total tract digestibility of nutrients in diets fed to nursery pigs after challenge with zearalenone (ZEA)a
| ZEA, mg/kg | 0 | 0.2 | 0.4 | 0.8 | SEM |
| ||||||||
|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
| Clay, g/kg | 0 | 2 | 0 | 0.5 | 0 | 1 | 0 | 2 | ZEA | MC | ZEA x MC | Lin | Quad | |
| Performance | ||||||||||||||
| Weight gain, g/day | 643 | 628 | 622 | 635 | 610 | 634 | 581 | 608 | 26 | 0.03 | 0.29 | 0.21 | 0.03 | 0.21 |
| Feed intake, g/day | 821 | 839 | 920 | 896 | 884 | 929 | 870 | 825 | 20 | 0.01 | 0.17 | 0.14 | 0.18 | 0.04 |
| Feed efficiency | 0.79 | 0.75 | 0.68 | 0.71 | 0.69 | 0.68 | 0.67 | 0.74 | 0.017 | 0-.04 | 0.03 | 0.39 | 0.03 | 0.37 |
| Apparent total tract digestibility coefficient, % | ||||||||||||||
| Dry matter | 0.848 | 0.839 | 0.820 | 0.848 | 0.803 | 0.836 | 0.798 | 0.835 | 0.01 | <0.01 | 0.19 | 0.45 | 0.01 | 0.28 |
| Nitrogen | 0.827 | 0.833 | 0.797 | 0.833 | 0.804 | 0.842 | 0.786 | 0.826 | 0.02 | <0.01 | <0.01 | 0.39 | 0.04 | 0.34 |
| Energy | 0.856 | 0.854 | 0.859 | 0.859 | 0.818 | 0.875 | 0.829 | 0.878 | 0.01 | 0.45 | 0.87 | 0.27 | 0.38 | 0.22 |
aWang et al. [42]
The effects of montmorillonite clay on performance and reproductive tract characteristics of growing gilts after challenge with zearalenone (ZEA)
| ZEA, mg/kg | 0 | 0.2 | 0.4 | 0.8 | SEM |
| ||||||
|---|---|---|---|---|---|---|---|---|---|---|---|---|
| Clay, g/kg | 0 | 2 | 0 | 2 | 0 | 2 | 0 | 2 | ZEA | MC | ZEA x MC | |
| Performance | ||||||||||||
| Weight gain, g/day | 672 | 680 | 651 | 734 | 615 | 686 | 617 | 690 | 18 | <0.01 | <0.01 | 0.25 |
| Feed intake, g/day | 809 | 815 | 819 | 868 | 757 | 832 | 782 | 820 | 20 | 0.02 | 0.25 | 0.33 |
| Feed efficiency | 0.83 | 0.84 | 0.79 | 0.85 | 0.81 | 0.83 | 0.79 | 0.84 | 0.02 | <0.01 | <0.01 | 0.65 |
| Vulva size | ||||||||||||
| Width, mm | 19.18 | 19.17 | 21.09 | 19.72 | 22.26 | 20.10 | 23.39 | 20.09 | 0.6 | <0.01 | <0.01 | 0.22 |
| Length, mm | 22.70 | 22.35 | 25.92 | 23.14 | 26.25 | 23.12 | 27.52 | 23.96 | 0.8 | 0.01 | <0.01 | 0.19 |
| Area, mm2 | 217.52 | 214.01 | 273.27 | 229.17 | 292.16 | 232.26 | 321.88 | 242.37 | 12 | 0.02 | 0.01 | 0.34 |
Wang et al. [42]
Fig. 1Effect of supplemental clay on noxious gas content in feces from weanling pigs. Dietary treatments were as follows: CON: basal diet, PC: basal diet with 44 mg/kg of Tylosin, HC1: basal diet with 3 g/kg Anion plus powder, HC2: basal diet with 6 g/kg Anion plus powder. In this study, the inclusion of HC2 treatment decreased NH3 emission (P < 0.05) compared with other treatments. No difference was observed on H2S. Nitrification of sludge is accelerated by the use of Anion, which selectively exchanges NH4 + from wastewater and provides an ideal growth medium for nitrifying bacteria that can oxidise NH4 + to nitrate. The supplementation of the diet with 3 g/kg Anion concomitantly decreased the noxious gas emission [28]