GHGemissions are usually the result of several simultaneous processes. Furthermore, some gases such as N2 are very difficult to quantify and require special techniques. Therefore, in this chapter, the focus is on stable isotopemethods. Both natural abundance techniques and enrichment techniques are used. Especially in the last decade, a number of methodological advances have been made. Thus, this chapter provides an overview and description of a number of current state-of-the-art techniques, especially techniques using the stable isotope15N. Basic principles and recent advances of the 15N gasflux method are presented to quantify N2 fluxes, but also the latest isotopologue and isotopomermethods to identify pathways for N2O production. The second part of the chapter is devoted to 15N tracing techniques, the theoretical background and recent methodological advances. A range of different methods is presented from analytical to numerical tools to identify and quantify pathway-specific N2O emissions. While this chapter is chiefly concerned with gaseous N emissions, a lot of the techniques can also be applied to other gases such as methane (CH4), as outlined in Sect. 10.1007/978-3-030-55396-8_5#Sec12.
PurposeState-owned enterprises (SOEs) are essential tools to further policy objectives across the world. However, in the past few decades, heated debates on the performance of SOEs vis-à-vis private sector enterprises have surfaced. In India, SOEs have long played an important role in the economy and only recently have undergone the trend of privatization. The purpose of this paper is to analyze existing research and to conclude whether private enterprises perform better than SOEs.Design/methodology/approachA review of available literature on performance comparisons of public and private sector enterprises is carried out, and differences between public and private enterprises are studied. Finally, theoretical propositions on the differences in objectives of public and private enterprises in the Indian context are enumerated. Three propositions are tested using data on Indian SOEs available in the public domain.FindingsPerformance comparisons of public and private enterprises have focused merely on technical productivity or financial aspects and have thus left out the wide scope of social, economic and political objectives of SOEs. Literature on the nature of SOEs indicates that there are certain fundamental differences in the objectives of public and private sector enterprises. Further, the basic theoretical assumptions tested have been found to be, prima facie, valid in the Indian context. The paper thus establishes a case for further research to develop a comprehensive technique for the comparison of public and private sector enterprises in the Indian context.Originality/valueExtant research on the subject of comparing public and private entries has limited itself to technoeconomic considerations and has not taken into account the different objectives/nature of these enterprises. The study established a case for diverging from the present discourse privatization and private sector supremacy. The same could have far-reaching consequences for policymakers, especially in developing countries.
Fall armyworm is an important pest of maize crop and native of America. Fall armyworm distributed in tropical and subtropical regions of many countries in the World. Eggs, larva, pupae & adults are the 4 stages of life -cycle. Eggs are covered with grey -pink colour layer. Larvae are 35-90mm long in size. The size of male & female pupae are 1.3 to 1.5 cm & 1.6 to 1.7 cm. grey, light brown & silver colour wings are observed in fall armyworm. The larvae of Spodoptera frugiperda larvae feed by scrapping green tissue of leaves & grown up larvae feed large amount of leaf tissues. Window pane like damage should be observed on leaves area. Fall armyworm affects on leaf corn and all sweet tissue part of the maize crop. Deep ploughing before onset of rains & wide sowing practices is best cultural practices for the management of all armyworm. Using of sex pheromone traps @2traps/acre at the time of sowing & hand picking and squashing of eggs are also found effective to control fall armyworm. Spraying of azadirachtin 1 Ec @2ml/liters of water, Emmamectin benzoate 5 SG @0.5g/liters of water, Chlorpyriphos 50% + Cypermetharin 5% Ec. @2ml/liters of water, lambada-Cyhalothrin 5% EC. @2ml/liters of water should be found effective chemical control on armyworm.
Agricultural lands make up approximately 37% of the global land surface, and agriculture is a significant source of greenhouse gas (GHG) emissions, including carbon dioxide (CO2), methane (CH4) and nitrous oxide (N2O). Those GHGs are responsible for the majority of the anthropogenic global warming effect. Agricultural GHG emissions are associated with agricultural soil management (e.g. tillage), use of both synthetic and organic fertilisers, livestock management, burning of fossil fuel for agricultural operations, and burning of agricultural residues and land use change. When natural ecosystems such as grasslands are converted to agricultural production, 20–40% of the soil organic carbon (SOC) is lost over time, following cultivation. We thus need to develop management practices that can maintain or even increase SOCstorage in and reduce GHG emissions from agricultural ecosystems. We need to design systematic approaches and agricultural strategies that can ensure sustainable food production under predicted climate change scenarios, approaches that are being called climate‐smart agriculture (CSA). Climate‐smart agricultural management practices, including conservation tillage, use of cover crops and biochar application to agricultural fields, and strategic application of synthetic and organic fertilisers have been considered a way to reduce GHG emission from agriculture. Agricultural management practices can be improved to decreasing disturbance to the soil by decreasing the frequency and extent of cultivation as a way to minimise soil C loss and/or to increase soil C storage. Fertiliser nitrogen (N) use efficiency can be improved to reduce fertilizer N application and N loss. Management measures can also be taken to minimise agricultural biomass burning. This chapter reviews the current literature on CSA practices that are available to reduce GHG emissions and increase soil Csequestration and develops a guideline on best management practices to reduce GHG emissions, increase C sequestration, and enhance crop productivity in agricultural production systems.
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