Optimal technology policy: subsidies versus monitoring

We analyze the optimal technology policy to solve a free-riding problem between the members of a RJV. We assume that when intervening the Government suffers an additional adverse selection problem because it is not able to distinguish the value of the potential innovation. Although subsidies and monitoring may be equivalent policy tools to solve firms' free-riding problem, they imply different social losses if the Government is not able to perfectly distinguish the value of the potential innovation. The supremacy of monitoring tools over subsidies is proved to depend on which type of information the Government is able to obtain about firms' R&D performance.

Planta de producció d'acetaldehid

L’objectiu d’aquest projecte és el disseny d’una planta de producció d’acetaldehid a partir de l’oxidació d’etilè. Es presenta doncs, un estudi de la viabilitat de la construcció i operació de la planta complint en tot moment amb la normativa i legislació vigent.

Control d'Accés d'Usuaris als Serveis de Xarxa CAUSiX

L'objectiu final d'aquest treball és l'obtenció d'un sistema que permeti regular l'accés de manera fàcil i flexible a determinats serveis de xarxa per a un conjunt d'usuaris que tenen necessitats i atributs diferents d'ús de la xarxa segons el seu perfil i segons el moment.

Association between GIS-based exposure to urban air pollution during pregnancy and birth weight in the INMA Sabadell Cohort

Background: There is growing evidence that traffic-related air pollution reduces birth weight. Improving exposure assessment is a key issue to advance in this research area.Objective: We investigated the effect of prenatal exposure to traffic-related air pollution via geographic information system (GIS) models on birth weight in 570 newborns from the INMA (Environment and Childhood) Sabadell cohort.Methods: We estimated pregnancy and trimester-specific exposures to nitrogen dioxide and aromatic hydrocarbons [benzene, toluene, ethylbenzene, m/p-xylene, and o-xylene (BTEX)] by using temporally adjusted land-use regression (LUR) models. We built models for NO2 and BTEX using four and three 1-week measurement campaigns, respectively, at 57 locations. We assessed the relationship between prenatal air pollution exposure and birth weight with linear regression models. We performed sensitivity analyses considering time spent at home and time spent in nonresidential outdoor environments during pregnancy.Results: In the overall cohort, neither NO2 nor BTEX exposure was significantly associated with birth weight in any of the exposure periods. When considering only women who spent < 2 hr/day in nonresidential outdoor environments, the estimated reductions in birth weight associated with an interquartile range increase in BTEX exposure levels were 77 g [95% confidence interval (CI), 7–146 g] and 102 g (95% CI, 28–176 g) for exposures during the whole pregnancy and the second trimester, respectively. The effects of NO2 exposure were less clear in this subset.Conclusions: The association of BTEX with reduced birth weight underscores the negative role of vehicle exhaust pollutants in reproductive health. Time–activity patterns during pregnancy complement GIS-based models in exposure assessment.

Campaign rhetoric: A model of reputation

We analyze conditions under which a candidate's campaignrhetoric may affect the beliefs of the voters over whatpolicy the candidate will implement in case he wins theelection. We develop a model of repeated elections withcomplete information in which candidates are purely ideological. Voter's strategies involve a credible threat to punish candidates that renege of their campaignpromises, and in equilibrium all campaign promises arebelieved by voters, and honored by candidates. We obtainthat the degree to which promises are credible in equilibriumis an increasing function of the value of a candidate'sreputation.

Les restes humanes del jaciment epipaleolític de la Balma de Guilanyà (Navés, Solsonès)

Les restes humanes deIs períodes epipaleolític i mesolític estan pobrament representades a la Península Iberica, tot i que existeixen dos jaciments mesolítics excepcional s a Muge, Portugal (Moita do Sebastiao i Cabe~o da Arruda), amb uns 67 individus, i un altre de recentment excavat a Oliva (El Collado, Valencia), on s'han trobat uns 15 individus. EIs primers estan datats entre 7.240 i 6.300 a.P. (Ferreira 1994: 664-674), mentre que el darrer té una datació de 7.640-7.570 a.P (Aparicio 1989). Ambdós jaciments es troben en zones properes a estuaris de rius o a la costa, la qual cosa permetia 1'explotació intensiva de recursos marins molt variats. Aquest tipus d' economia condicionava un tipus de vida força sedentaria i a més a més, va permetre un increment en la densitat de població, que hauria tingut lloc probablement entre el 8.000-7.000 a.e. (Ferreira 1994: 664-674). A Catalunya, s'han excavat fins ara pocs jaciments importants d'aquests periodes (Martín y Vaquer 1995: 35-73), tots d'ells en zones d'interior i corresponents presumiblement a grups petits de caçadors-recol·lectors, força diferents dels posteriors assentaments humans més grans com Muge i Oliva. De tots aquests jaciments, només a la Balma de Guilanya (Naves, Solsones) s'han trobat restes humanes que es puguin atribuir sense cap mena de dubte als nivells epipaleolítics.

Use of a pre-sidedress soil nitrate test (PSNT) to determine nitrogen fertilizer requirements for irrigated corn

In the present study, a 2-year N rate response experiment was conducted in different fields to monitor NO3-N soil profiles, N accumulation by the crop and final crop performance, in order to assess if soil NO3-N at pre-sidedressing (Pre-Sidedress Soil Nitrate Test, PSNT) is a reliable indicator for soil N availability for corn in the irrigated area served by canal d’Urgell (Lleida, Spain), and if the test can be used to separate responsive fields from non-responsive fields to sidedress N fertilizer applications. Preliminary soil N availability (N sidedress fertilizer rate + PSNT) critical levels to identify fields that need supplementary N fertilizer applications were established at ca. 300 and 210 kg NO3-N·ha–1, for PSNTrooting–zone and PSNT0–30 cm, respectively (for a yield goal of 14 t grain·ha–1).