Summary and Conclusions. Discuss your general reactions to the internship--good and bad points. Provide suggestions (if any) for improvement of the internship experience in general and with this company. Ideas include what divisions of the company that you would have liked to have learned more about during your internship. We strongly suggest that you discuss your suggestions with your supervisor prior to writing them up. What aspects of this industry attract or discourage you from a career track in that sector of the industry. What suggestions do you have for fellow students about to begin an internship with this industry and/or firm?
Summary and Conclusions. Within the context of re-employment preference, please check the appropriate category for this evaluation: □ Satisfactory □ Less than satisfactory (no impact on re-employment preference) □ Unsatisfactory Xxxx’x Signature: Faculty Signature: Date: Date: Faculty signature indicates only that this form has been reviewed, and does not indicate agreement with its contents. Pursuant to Education Code Section 87031, faculty have the right to respond in writing to any component of the evaluation summary and to have his/her response included in his/her personnel file. Faculty will have at most 30 days from the receipt of all of the evaluation materials (including the completed student evaluation forms) to submit the response to the xxxx and/or Human Resources. Appendix O (continued) Ohlone College In-Person Classroom Observation Reporting Form Xxxxxxx Xxxx: Observer: Class Observed: Date of Observation: Total Observation Time (Minimum 45 minutes):
Summary and Conclusions. Presents a summary of the results of the HHRA. • Section 9 - References: Provides a list of references cited in the text.
Summary and Conclusions. The HHRA was conducted to evaluate risks to human health at 17 of the 19 parcels that comprise the NRP. Four parcels (9, 10, 11, and 16) were not included because: (1) concentrations of VOCs in groundwater beneath these areas were detected below regulatory criteria, and (2) hazardous materials or wastes at the four parcels, if present, do not appear to have impacted the environment (Xxxxxxx ESE, 200lc). The HHRA evaluated potential health risks to indoor workers, construction workers, adult residents, child residents, and a default 30 year resident (6 years child and 24 years adult). Only the default 30-year residential receptor had multiple xxxxx for which the estimated excess lifetime cancer risks were above lxl0-4. For the other receptors, the lifetime excess risks were mostly within the USEPA risk management range. RME and CTE HIs for the construction worker were greater than 1 for numerous xxxxx, based upon the groundwater volatilization model results. Appropriate use of personnel protective equipment, enforcement of applicable institutional controls, and use of soil TCLs should be sufficient to reduce exposures to acceptable levels. In general, the lifetime excess cancer risks and HIs were highest for xxxxx and buildings within, or just adjacent to, parcel 15. The results of the HHRA are summarized as follows: • Maximum RME lifetime excess cancer risk for construction workers was within the USEPA risk management range (lx 10-6 to lx 10-4) based upon the groundwater volatilization modeling and direct air measurement results. The maximum estimated RME and CTE HIs for the construction worker, based upon the groundwater volatilization modeling and direct air measurements were greater than 1. This is primarily due to direct exposure to the contaminated groundwater. • RME lifetime excess cancer risks for indoor workers, estimated from the groundwater volatilization model, were within or below the risk management range, except for one wen in parcel 15 (W9-35). RME lifetime excess cancer risk estimated from the air measurements was above the risk mJlnagement range (2.3E-4) for four buildings (Building 156, 566, 6 and Hangar 1), but within the risk management range for the remaining buildings. However, lifetime estimated excess cancer risks estimated from xxxxx near Buildings 156 and 566 were an in the lower end of the risk management range. This high estimated lifetime excess cancer risk for Buildings 156 and 566 may due to sources other than contaminated gr...
Summary and Conclusions. We have introduced a RESTful semantic web service that allows indexing and invoking SCs on Ethereum BC via a URI. We extended the EthOn combined with the OWL-S ontology to support Ethereum SCs deployed in the Ethereum blockchain framework. As a result, semantic queries over SCs such as ”finding a SC with the minimal gas payment” can be executed using the existing semantic web platform. We have taken an initial step in connecting SCs with Linked Data. The validation of the framework is under investigation. A system for the demonstration of the proposed SSC has being developed and deployed in our testbeds which offers the dynamism needed to set up experiments and harvest data streaming needed for analyzing the outcomes of our proposed framework. As a part of our SMESEC project, this system will be used to verify and validate our SSC proposal. In the future, performance evaluation along with comparisons between our proposal and other approaches for SCs indexing will be carried out. Moreover, we intend to extend this work to other BC platforms, besides Ethereum, such as Hyperledger Fabric. For this purpose, we plan to migrate the testbed toward the Docker Swarm scheduling tool in cluster computing environments, which increases the simulation scalability of several order of magnitude nodes. Other future works include the usage of the process of semantification, linked data capabilities, on the current distributed ledgers. An important feature of the proposal resides on the logic-based explanation of discovery outcomes, obtained through non-standard inference for match- making among requests and resources. Acknowledgment This research was supported by the European Union’s Horizon 2020 research and innovation programmes under grant agreement No 740787, the Swiss State Secretariat for Education, Research and Innovation (SERI) and the Insti- tute for Information Communications Technology Promotion (IITP) grant funded by the Korea government (MSIT).[2018-0- 00261, GDPR Compliant Personally Identifiable Information Management Technology for IoT Environment]. References [1] X. Xxxxxxx and X. Xxxxxxxx, “Blockchain in logistics and supply chain: trick or treat?” in Proceedings of the Hamburg International Conference of Logistics (HICL). epubli, 2017, pp. 3–18. [2] X. Xxxx, “An agri-food supply chain traceability system for china based on rfid & blockchain technology,” in 2016 13th international conference on service systems and service management (ICSSSM). IEEE, 2016, p...
Summary and Conclusions. The understanding of the response of the Auger water-Cherenkov detectors (WCD) to muons is of prime importance, not only because muons serve as a convenient means of detector calibration, but also because they are messengers of the hadronic interactions that drive the development of extensive air showers in the atmosphere. With the aim of gaining such understanding, we have designed and deployed a hodoscope based on resistive-plate xxxxxxxx (RPCs). Thanks to the excellent positional and directional performance of the hodoscope, it has allowed us to select single muons and reconstruct their direction with 1◦ ac- 2020 curacy over a large range of zenith angles between 0◦ and 55◦. The measurement of charge of the cor- responding signal in the WCD has enabled us to study its response as a function of the zenith angle. We have then compared the measured data with the expectations from a simulation, which has been implemented by using Corsika to simulate showers and Geant4 to accurately model the response of WCDs and the RPCs. We have found that, down to the level of the response of individual PMTs to muons, the agreement between the data and expectations is at a level of 2%. JINST We have also taken advantage of the most vertical data of the hodoscope to verify one crucial element of the calibration chain, namely the scaling factor of the signal charge between omni- directional and vertical muons. The value we obtained is in good agreement with the value measured 15 years ago, at the very beginning of the operation of the Xxxxxx Xxxxx Observatory. In conclusion, the level of the agreement of the simulation with the presented measurements validates with high accuracy the Auger Offline simulation of the WCD response to muons. Fur- thermore, the updated measurement of the scaling factor used in the WCD calibration shows no evidence of ageing effects. A Surface detector simulation parameters P09002 The amount of Cherenkov light produced by the particles entering a WCD of the surface detector and that reach the PMTs mainly depends on the characteristics of the water and the inner-wall lining made of Tyvek. The first key parameter is thus the water absorption length, which is a function of the wavelength of the photons. For its wavelength dependency we adopt the measurements made with pure water [18]. The next major input into the simulation is the Tyvek reflectivity featuring a strong diffusive and a weaker specular component. The latter is chosen to be constant ...
Summary and Conclusions. This is the most important part of the Report because it is the section that will probably be read most frequently. This section should begin with a clear, concise statement of what, why, and how the project was done. Major results and conclusions of the study should then be presented, using clear, concise statements. Make sure the conclusions reached are fully supported by the results of the study. Do not overstate or over interpret the results. It may be useful to itemize primary results and conclusions. A simple table or graph may be used to illustrate.
Summary and Conclusions. The purpose of the job observation pilot test was to provide validation for the ORS physical elements by comparing the data collected during pre-production to those collected from a different source – observation. Two field economists were assigned to observe the same job for 60 minutes and record the duration of each of the physical elements of the job. Initial results show high levels of inter-rater reliability (measured using prevalence and bias adjusted kappa) among the FEs, suggesting that future observation tests could be done with single observers, with adequate training on definitions and thresholds of the elements. Comparing the observed data to that collected during pre-production proved somewhat more complicated due to the limited length of the observation resulting in some elements classified as not present that were more likely present with very low duration (“seldom”). The prevalence adjusted kappa measures of duration are relatively strong, suggesting that the interview data and observed data have high levels of agreement across most elements. Drilling down to the elements with lower levels of agreement leads us to find some evidence that “present, duration unknown” classifications in pre-production can lead to underestimates of the duration of certain physical elements. The observation test suggests that for several elements the missing duration is distributed very differently than the interview duration, leading to estimates that may under or overstate the frequency of a physical element. However, these conclusions must be qualified by the limited observation period of 60 minutes. References Xxxx & Green, 1983. Reliabilities of Selected Ratings Available from the DOT. Journal of Applied Psychology, 155- 165.
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Summary and Conclusions. This survey shows that voluntary agreement programs that are completely voluntary have less government pressure for participation, along with fewer incentives and no penalties. As a result, most programs that fall within this category show lower participation rates and weaker results. In contrast, programs that threatened to or did implement regulations or taxes often included additional incentives such as the ability to participate in emissions trading, relief from additional regulations or exemption from existing regulations, and reduced or avoided energy or GHG taxes. Some of these programs also included penalties such as a fee, more stringent environmental permitting requirements, increased regulations, and energy or GHG taxes for those companies that failed to meet their targets. As a result of this combination of incentives and penalties, these programs had higher participation rates and generally were more successful at meeting their energy or GHG emissions reduction goals. It is interesting to note that a number of countries that first established strictly voluntary agreements have strengthened their programs in a second or follow-on phase. In France, for example, the completely voluntary program enacted in 1996 was replaced in 2002 with a program that includes a penalty fee for non-compliance and allows for emissions trading (Nollet, n.d.). Similarly, the voluntary Canadian program evolved into a new program for the larger CO2 emitters that also has a penalty fee, allows for emissions trading, and includes financial support from the government for investments in wind energy, audit programs, benchmarking, and CO2 capture and storage (NRCan, 2004). Ireland’s voluntary program of the 1990s has been replaced by a program that includes a CO2 tax (Brabazon et al., 2003). Other countries that have a second generation of agreements, including Finland, Germany, The Netherlands, and New Zealand, all either increased the number of incentives or added penalties to strengthen the programs. Overall, evaluations of experience with voluntary agreements show that results have been varied, with some programs appearing to just achieve business-as-usual savings (Chidiak, 2002; OECD, 2002) or to have weak targets (Xxxxxxxxx and Xxxxxxxxxx, 2000). However, the more successful programs have seen significant energy savings (Xxxxxxx and Xxxxxx, 2002), even doubling historical autonomous energy efficiency improvement rates (Xxxxxxxxxx et al., 2002) and can be cost-effectiv...
