RESUMEN
Many developing countries are facing a silent increase in deficiency of micronutrients in forage crops that results in decreased levels of essential nutrients in animals. Micronutrients are essential not only for basic metabolic processes of forage crops but also for sustaining animal health. Forage productivity and quality are severely affected by soil micronutrients deficiencies, especially zinc and copper. This review summarizes the literature highlighting the significance of different methodologies used to increase the biomass and quality of forage so as to enhance the micronutrient content of the forage crops through biofortification. Biofortification is a promising and sustainable agriculture-based strategy to reduce micronutrient deficiency in crops. The experiments and trials conducted at different locations of the world showed that copper and zinc concentrations in animal fodders can be enhanced through the process of foliar application. Additionally, agronomic biofortification showed more promising results, and thus is an outstanding, fast, and cost-effective technique for the immediate enrichment of forage in order to overcome malnutrition in animals. © 2022 Society of Chemical Industry.
Asunto(s)
Biofortificación , Zinc , Animales , Biofortificación/métodos , Zinc/metabolismo , Cobre , Agricultura/métodos , Micronutrientes , Productos Agrícolas/metabolismoRESUMEN
Cadmium (Cd) metal extraction through efficient plant roots has attracted much attention as this methodology is environment-friendly and cost-effective. Brassica species are well known for their tolerance towards high Cd concentration in contaminated soils. The tolerance ability may vary among species; hence the assessment of this variability is mandatory for selecting Brassica species. For this purpose, a greenhouse pot experiment was carried out using three Brassica species (Brassica juncea L., Brassica campestris L., and Brassica napus L.). To evaluate the effect of chelating agent ethylenediamine tetraacetic acid (EDTA) on Cd uptake, EDTA (0, 1, and 2 g kg-1 soil) was supplemented along with Cd (0, 5, 10, 20, 40, and 80 mg kg-1 soil). Among different species, B. juncea possessed the highest root dry biomass and lowest root Cd concentration in untreated soil. Overall root dry biomass of all tested Brassica species reduced on increasing Cd and EDTA levels. The trend was appeared to be related to an increase in root Cd concentration on the supplementation of EDTA that formed a complex with the target metal contaminate and resulted in vacuolar sequestration. Roots of B. juncea showed maximum Cd accumulation and highest values at Cd and EDTA levels up to 20 mg kg-1 and 1 g kg-1 soil due to the combined effect of root biomass and Cd concentration in roots. Thus, present findings inferred that Cd and EDTA supplementation might prove as a feasible strategy to improve remediation of Cd-polluted soil using B. juncea as an efficient Cd accumulator.
Asunto(s)
Cadmio , Contaminantes del Suelo , Biodegradación Ambiental , Cadmio/análisis , Suplementos Dietéticos , Ácido Edético , Planta de la Mostaza , Raíces de Plantas/química , Suelo , Contaminantes del Suelo/análisisRESUMEN
Persistence of temephos was studied in soils under field and laboratory conditions in sandy loam soil to evaluate the effect of moisture and formulations on persistence. The insecticide was applied as 50 EC and 1 % S.G. granules @1 kg a.i. ha-1 on surface of the soil' and residues were determined spectrophotometrically. The soil was fortified separately with dilute emulsion of EC and suspension of granular formulation at 5 ppm level and incubated at different moisture levels at 25:1:1 degrees C for 90 days. The residues of temephos from both the formulations persisted upto 55 days in soil when applied @1 kg a.i. ha(-1). In 40 days 92 and 91.43 per cent temephos was dissipated from soil treated with EC and granular formulations, respectively. There was no leaching or downward movement of the toxicant beyond 7.5 cm. The half-life of temephos under field condition for EC and granular formulations were 18.14 and 20.44 days, respectively. Statistically, there was no significant effect of two formulations of temephos on its persistence. But at three different moisture conditions viz. airdry, field capacity and sub-merged, the difference was significant at 5% level.