In this study, we use comprehensive vehicle emission remote sensing measurements of over 230,000 passenger cars to estimate total UK ammonia (NH 3 ) emissions. Estimates are made using "topdown" and "bottom-up" methods that demonstrate good agreement to within 1.1% for total fuel consumed or CO 2 emitted. A central component of this study is the comprehensive nature of the bottom-up emission estimates that combine highly detailed remote sensing emission data with over 4000 km of 1 Hz real driving data. Total annual UK NH 3 emissions from gasoline passenger cars are estimated to be 7.8 ± 0.3 kt from the bottom-up estimate compared with 3.0 ± 1.7 kt reported by the UK national inventory. An important conclusion from the analysis is that both methodologies confirm that gasoline passenger car NH 3 emissions are underestimated by a factor of about 2.6 compared with the 2018 UK National Atmospheric Emissions Inventory. Furthermore, we find that inventory estimates of urban emissions of NH 3 for passenger cars are underestimated by a factor of 17.
legal production of hemp in the United States [1]. The act removed hemp from the definition of marijuana in the federal Controlled Substances Act (CSA) and excluded tetrahydrocannabinols in hemp from the definition of tetrahydrocannabinols in Schedule I of the CSA. The act defines hemp as "the plant Cannabis sativa L. and any part of that plant, including the seeds thereof and all derivatives, extracts, cannabinoids, isomers, acids, salts, and salts of isomers, whether growing or not, with a delta-9-tetrahydrocannabinol concentration of not more than 0.3 percent on a dry weight basis" [1]. Individual states can apply to the US Department of Agriculture (USDA) for regulatory authority of hemp production by submitting a regulatory plan to the Secretary of Agriculture [1]. Individual states can also further restrict or prevent hemp cultivation, but cannot prohibit transportation or shipment of hemp and hemp products lawfully produced. Marijuana and industrial hemp are different strains of the cannabis plant, and the only way to distinguish them is to conduct a quantitative analysis to determine the total Δ 9-tetrahydrocannabinol (THC) concentration that can potentially be obtained from the plant
The employment of chemical weapons by rogue states and/or terrorist organizations is an ongoing concern in the United States. The quantitative analysis of nerve agents must be rapid and reliable for use in the private and public sectors. Current methods describe a tedious and time-consuming derivatization for gas chromatography-mass spectrometry and liquid chromatography in tandem with mass spectrometry. Two solid-phase extraction (SPE) techniques for the analysis of glyphosate and methylphosphonic acid are described with the utilization of isotopically enriched analytes for quantitation via atmospheric pressure chemical ionization-quadrupole time-of-flight mass spectrometry (APCI-Q-TOF-MS) that does not require derivatization. Solid-phase extraction-isotope dilution mass spectrometry (SPE-IDMS) involves pre-equilibration of a naturally occurring sample with an isotopically enriched standard. The second extraction method, i-Spike, involves loading an isotopically enriched standard onto the SPE column before the naturally occurring sample. The sample and the spike are then co-eluted from the column enabling precise and accurate quantitation via IDMS. The SPE methods in conjunction with IDMS eliminate concerns of incomplete elution, matrix and sorbent effects, and MS drift. For accurate quantitation with IDMS, the isotopic contribution of all atoms in the target molecule must be statistically taken into account. This paper describes two newly developed sample preparation techniques for the analysis of nerve agent surrogates in drinking water as well as statistical probability analysis for proper molecular IDMS. The methods described in this paper demonstrate accurate molecular IDMS using APCI-Q-TOF-MS with limits of quantitation as low as 0.400 mg/kg for glyphosate and 0.031 mg/kg for methylphosphonic acid.
Costly props, complicated authoring technologies, and limited access to space are among the many reasons why children can rarely enjoy the experience of authoring room-sized interactive stories. Typically in these kinds of environments, children are restricted to being story participants, rather than story authors. Therefore, we have begun the development of "StoryRooms," room-sized immersive storytelling experiences for children. With the use of low-tech and high-tech storytelling elements, children can author physical storytelling experiences to share with other children. In the paper that follows, we will describe our design philosophy, design process with children, the current technology implementation and example StoryRooms.
Road vehicles make important contributions to a wide range of pollutant emissions from the street level to global scales. The quantification of emissions from road vehicles is, however, highly challenging given the number of individual sources involved and the myriad factors that influence emissions such as fuel type, emission standard, and driving behavior. In this work, we use highly detailed and comprehensive vehicle emission remote sensing measurements made under real driving conditions to develop new bottom-up inventories that can be compared to official national inventory totals. We find that the total UK passenger car and light-duty van emissions of nitrogen oxides (NO x ) are underestimated by 24–32%, and up to 47% in urban areas, compared with the UK national inventory, despite agreement within 1.5% for total fuel used. Emissions of NO x at a country level are also shown to vary considerably depending on the mix of vehicle manufacturers in the fleet. Adopting the on-road mix of vehicle manufacturers for six European countries results in up to a 13.4% range in total emissions of NO x . Accounting for the manufacturer-specific fleets at a country level could have a significant impact on emission estimates of NO x and other pollutants across the European countries, which are not currently reflected in emission inventories.
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