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The present paper utilizes entropy theory and Google earth engine cloud computing technique to investigate system state and river recovery potential in two large sub-basins of the Mahanadi River, India. The cross-sectional intensity entropy (CIE) is computed for the post-monsoon season (October–March) along the selected reaches. Further, a normalized river recovery indicator (NRRI) is formulated to assess the temporal changes in river health. Finally, NRRI is related to a process-based variable-LFE (low flow exceedance) to comprehend the dominating system dynamics and evolutionary adjustments. The results highlight the existence of both threshold-modulated and filter-dominated systems based on CIE and NRRI variabilities. In addition, the gradual decline in CIE and subsequent stabilization of vegetated landforms can develop an 'event-driven' state, where floods exceeding the low-flow channel possess a direct impact on the river recovery trajectory. Finally, this study emphasizes the presence of instream vegetation as an additional degree of freedom, which further controls the hierarchy of energy dissipation and morphological continuum in the macrochannel settings. [ABSTRACT FROM AUTHOR]

The transition towards a modern cleaner energy pathway has been receiving global attention recently. Although nuclear energy has emerged as an alternative cleaner energy source and is receiving immense policy attention, however, the role of nuclear energy in the environmental degradation mitigation remains inconclusive in the extant literature. Therefore, this study examines the dynamic linkages between gross domestic product, foreign direct investment inflows, nuclear energy consumption, trade openness, and CO2 emissions for India within the environmental Kuznets curve framework over the period 1978–2019 through various robust econometric models that takes into consideration the presence of structural break in the data. The present study confirms the existence of an "inverted N shape" environmental Kuznets curve, a phenomenon rarely observed in environmental Kuznets curve literature for India. Besides, the predicted turnaround points of environmental Kuznets curve highlight that India has already reached the positive peak approximately by the year 2015. The empirical findings also confirm the existence of a J-shaped relationship between foreign direct investment inflows and CO2 emissions, which indicates that India is in the transient phase moving from pollution halo towards pollution heaven with progressive foreign direct investment development. Trade openness is also found to have a beneficial effect on environmental quality implying the trade policy of India encourages green trade activities to safeguard the environment. The empirical results also reveal the beneficial effect of nuclear energy consumption on air quality, thereby suggesting an accelerated adoption of nuclear energy in the Indian energy mix. The results also highlight that nuclear energy adoption in this booming phase can facilitate a "tunnelling effect" for sustainable economic growth for India. Hence, these findings may provide key policy recommendations regarding energy transition and environmentally sustainable economic growth. [ABSTRACT FROM AUTHOR]

Dissipation of β-cyfluthrin and imidacloprid was studied following three applications of a combination formulation of Solomon 300 OD (β-cyfluthrin 9% + imidacloprid 21%) @ 60 and 120 g a.i. ha−1 at 7 days interval. Samples of brinjal were collected at 0, 1, 3, 5, 7, 10 and 15 days after the last application and residues of β-cyfluthrin and imidacloprid were estimated on gas liquid chromatography (GLC) and high performance liquid chromatography (HPLC), respectively. Half-life periods for β-cyfluthrin were found to be 1.74 and 1.39 days and for imidacloprid these values were observed to be 2.31 and 2.18 days, respectively, at single and double the application rate. β-Cyfluthrin residues dissipated below the limit of quantification (LOQ) of 0.01 mg kg−1 after 5 and 7 days, respectively, at single and double the application dosages whereas imidacloprid residues took 10 days for both the dosages. Soil samples collected after 15 days after the last application did not show the presence of β-cyfluthrin and imidacloprid at their detection limit of 0.01 mg kg−1. [ABSTRACT FROM AUTHOR]