Animal Nutrition and Welfare Service, Departament de Ciència Animal i dels Aliments, Universitat Autònoma de Barcelona, 08193 Bellaterra, Spain.
J Anim Sci. 2022 Nov 1;100(11). doi: 10.1093/jas/skac328.
Mycotoxicosis are a common problem in livestock, where a group of six major mycotoxins represents a high risk for animal health and production profits. Mycotoxin binders (MTB) can reduce the mycotoxin burden in the gastrointestinal tract of the animal. Mycotoxin binders are classified in inorganic, as clays and activated carbon (AC), and organic, as yeast cell wall (YCW) and micro-ionized fibers. The adsorption of mycotoxins into MTB is due to: 1) chemical interactions where the cation exchange capacity involves different types of bounds like ion-dipole, Van der Walls forces, or hydrogen bonds; and 2) to physical characteristics of MTB like pore size, or mycotoxin structure and shape. The adsorption capacity of MTB is determined using different in vitro tests that mimic the gastrointestinal tract of the animals. A literature search was conducted to identify in vitro research where the efficacy of adsorption of MTB was determined. The search was based on 8 MTB [AC, bentonite, clinoptilolite, hydrated sodium calcium aluminosilicate (HSCAS), montmorillonite (MMT), sepiolite, YCW and zeolite] and 6 mycotoxins [aflatoxin (AF), deoxynivalenol (DON), fumonisin (FUM), ochratoxin (OTA), T-2 toxin and zearalenone (ZEA)]. Sixty-eight papers with 1842 data were selected and analyzed with the PROC MIXED of SAS. The response variable was the percentage mycotoxins adsorption by MTB, and the model included the fixed effects of MTB, mycotoxins, incubation media, pH and their interactions, and the random effect of the study. Differences were considered significant when P < 0.05 and with tendency when 0.05 < P < 0.10. The mycotoxins adsorption capacity was 83% ± 1.0 for AC, 76% ± 3.1 for MMT, 62% ± 1.0 for bentonite, 55% ± 1.9 for HSCAS, 52% ± 9.1 for sepiolite, 52% ± 4.3 for clinoptilolite and 44% ± 0.4 for YCW. For mycotoxins, the adsorption of AF was 76% ± 0.6, for FUM was 50% ± 1.8, for OTA was 42% ± 1.0, for ZEA was 48% ± 1.1, for DON was 35% ± 1.6, and for T-2 was 27% ± 2.8. The pH affected the adsorption capacity of YCW with higher adsorption at low pH, and the adsorption of OTA and ZEA, where OTA adsorption tended to be lower at intermediate pH, and adsorption of ZEA tended to be higher at the two-steps pH. The potential adsorption of some essential nutrients, including amino acids and vitamins, should also be considered. Results should be used as a guide in the selection of the appropriate mycotoxin binder based on the predominant mycotoxin in feeds.
霉菌毒素中毒是家畜中常见的问题,其中六种主要的霉菌毒素对动物的健康和生产利润构成了高风险。霉菌毒素结合剂 (MTB) 可以减少动物胃肠道中的霉菌毒素负担。霉菌毒素结合剂分为无机类,如粘土和活性炭 (AC),以及有机类,如酵母细胞壁 (YCW) 和微电离纤维。霉菌毒素被 MTB 吸附的原因有两个方面:1)化学相互作用,其中阳离子交换能力涉及到不同类型的键,如离子偶极、范德华力或氢键;2)MTB 的物理特性,如孔径大小、霉菌毒素结构和形状。MTB 的吸附能力是通过模拟动物胃肠道的不同体外试验来确定的。我们进行了文献检索,以确定吸附 MTB 效果的体外研究。搜索基于 8 种 MTB [AC、膨润土、斜发沸石、水化钠钙铝硅酸盐 (HSCAS)、蒙脱石 (MMT)、海泡石、YCW 和沸石] 和 6 种霉菌毒素 [黄曲霉毒素 (AF)、脱氧雪腐镰刀菌烯醇 (DON)、伏马菌素 (FUM)、赭曲霉毒素 (OTA)、T-2 毒素和玉米赤霉烯酮 (ZEA)]。从 83 篇论文中选择了 1842 个数据,并使用 SAS 的 PROC MIXED 进行了分析。反应变量是 MTB 吸附霉菌毒素的百分比,模型包括 MTB、霉菌毒素、孵育介质、pH 值及其相互作用的固定效应,以及研究的随机效应。当 P < 0.05 时,差异被认为是显著的,当 0.05 < P < 0.10 时,差异具有趋势性。AC 的霉菌毒素吸附能力为 83% ± 1.0,MMT 为 76% ± 3.1,膨润土为 62% ± 1.0,HSCAS 为 55% ± 1.9,海泡石为 52% ± 9.1,斜发沸石为 52% ± 4.3,YCW 为 44% ± 0.4。对于霉菌毒素,AF 的吸附率为 76% ± 0.6,FUM 为 50% ± 1.8,OTA 为 42% ± 1.0,ZEA 为 48% ± 1.1,DON 为 35% ± 1.6,T-2 为 27% ± 2.8。pH 值影响 YCW 的吸附能力,在低 pH 值下吸附能力更高,OTA 和 ZEA 的吸附也受到影响,其中 OTA 的吸附在中间 pH 值时趋于较低,ZEA 的吸附在两步 pH 值时趋于较高。一些必需营养素的潜在吸附,包括氨基酸和维生素,也应该被考虑。研究结果应作为选择合适的霉菌毒素结合剂的指南,根据饲料中主要的霉菌毒素进行选择。