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One of the most important replacement methods used instead of chemical herbicide and conventional tillage is cover and companion crops' application which is a major factor in sustainable agriculture.
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Another approach that may improve weed control and aid in the stewardship of glyphosate use is to apply a pre-emergence residual herbicide such as flufenacet plus metribuzin prior to a single in-crop application of glyphosate.
After the harvest of the second crop, application of SS had resulted in significantly highest (1.92 %) OC value in the top soil depth (0 to 20 cm) as relative to all treatments, whereas in the lower soil depth (20 to 40 cm), incorporation of wheat residues (with inorganic fertilizer) had significantly highest (1.04 %) OC value.
Under this condition, if USDA is unable to approve or deny a crop application within 90 days of the Farm Bill passage, then the crop would be deemed approved.
In order to assess the potential effect of GM crop application on the cultivable area and yield of OSR, we performed spatial explicit simulations of various coexistence scenarios (assuming different proportions of GM farmers, different regional proportion of OSR cultivation and different isolation distances) with high-resolution land use data.
In February 2013, an implementing regulation on applications for authorization of GM food and feed was adopted, which prescribes that for future GM crop applications, 90-day feeding trials are mandatory [2].
It was previously unable to simulate processes associated with the long-term flooded or saturated soil conditions encountered in rice-based systems, due to its heritage in dryland cropping applications.
The mid-points of the averages calculated for crop applications in the 1960s and the 1980s were used as the estimates for the 1970s.
In agricultural landscapes, rural and municipal residents can be exposed to agricultural pesticides either directly during crop applications or indirectly in air, water, or food.
The estimated intensities in the 1960s and prior, the 1970s, the 1980s and the 1990s, respectively, were 113, 78, 43 and 17 mg/hr for applications to animals, and 236, 147, 58, and 22 mg/hr for crop applications.
The ratio of each decade's average exposure level for crop applications, compared to that for the 1990s, was applied to the applications to animals to derive the 1960s-1980s dechanges changes in exposure rates.
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