However, Eq (5) states that γse is reduced with increasing xenon

However, Eq. (5) states that γse is reduced with increasing xenon density until it assumes the form γse = [Rb]〈σv〉, while Eq. (1) states that Γ increases with Enzalutamide nmr increasing xenon density. As stated above, the term γse/(γse + Γ) in Eq. (3) does not seem to contribute substantially to the polarization change between mixtures I and II but contributes with a fivefold reduction in the expected polarization between mixture I and III. It can be concluded that Γ > γse at xenon partial pressures somewhere above 30 kPa (i.e. mixture II at 150 kPa total pressure). Based on the observations and assumptions made above, one can conclude

that for mixture III γse  /(γse   + Γ  ) ≈ 0.2 and hence Γ   ≈ 4γse  . From the fitting parameter B   = γse   + Γ   that was determined as (8.5 ± 0.6) × 10−2 s−1 for mixture III one can conclude that γse   ≈ 1.7 × 10−2 s−1 and estimate Γ   ≈ 6.8 × 10−2 s−1

CYC202 for the 93% xenon mixture. This Γ   value is about twice as large as the rate constant T1-1≈3.3×10-2s-1 expected form Eq. (1). However, an increase of the 131Xe T  1 relaxation by a factor of two due to surface contributions and van der Waals complexes in the pump cell is not unreasonable, as can be illustrated by the following estimate: In the Section 3.1 a 131Xe T  1 ≈ 5 s in the 12.6 mm inner diameter NMR tube was found. From the simplified expression T1-1=T1(gas)-1+T1(surface)-1 one obtains T1(surface)−1 ≈ 16 × 10−2 s−1 for this NMR tube neglecting contributions from van der Waals complexes. This value is too high but the relaxation time due to surface interactions scales directly with the surface to volume ratio [64] and the (uncoated) pump cell has a 27 mm inner diameter leading to T1(surface)−1 ≈ 8 × 10−2 s−1 – a value close to that for Γ found above. In addition, the 131Xe surface contribution to the relaxation is expected to be further reduced by the elevated temperature [67] Calpain and by the presence of rubidium metal [32]. In summary, 131Xe polarization

is strongly dependent on the xenon density, most significantly due to rubidium depolarization. However, the 131Xe polarization is further affected by the xenon density dependent quadrupolar relaxation. The consequences of the combined effects is that high density SEOP is even more inefficient for 131Xe than for 129Xe. This inefficiency is illustrated in Fig. 5 where a distinct decrease in optical pumping efficiency was observed in mixture II and mixture III as the pressure was increased. At 100 kPa pressure used for these experiments only 0.03% polarization was generated with mixture III, and the signal was barely observable at higher pressures. However, at the lowest xenon concentration (mixture I), the applied pressure had a negligible effect on the SEOP conditions.

The net effect of D1-receptor - expressing Go cells is to ‘open t

The net effect of D1-receptor - expressing Go cells is to ‘open the gate’ by facilitating recurrent thalamo-cortical information flow, whereas D2-receptor-expressing NoGo cells ‘close the gate’ by blocking thalamo-cortical information flow. By this scheme, a planned motor action represented cortically might trigger the activation of Go cells via a corticostriatal projection, in turn facilitating a projection from thalamus

to the primary motor neurons responsible CH5424802 for enacting specific movements. At the same time, alternative action plans would trigger NoGo cells and so would have negligible thalamocortical influence. A variety of recent evidence has offered novel support for this framework. Go and NoGo cells are coactive when animals are motorically active, but not quiescent [7], in particular when action Ferroptosis inhibitor sequences are being initiated [8] — all consistent with a role for these cells in gating for action selection as opposed to a more general pro-kinetic vs. anti-kinetic dichotomy between Go and NoGo cells. Further evidence for this framework has recently been provided by optogenetic techniques [9••]. Transgenic mice expressing light-activated ion channels in putative Go and NoGo cells chose between one of

the two ports after the onset of a cue. Light-induced firing of Go cells led to an increase in contralateral movements, whereas light-induced firing of NoGo cells led to an decrease in contralateral movements. The effect of stimulation was greatest when the value of the two potential actions was closely matched (as estimated by a computational model), suggesting stimulation was capable of mimicking a small shift in their relative value. Moreover, this stimulation was effective only when delivered simultaneously with the cue, consistent with a particular influence of action value during action selection. As discussed below, these BG-mediated

gating mechanisms Depsipeptide ic50 may extend beyond the selection of motor actions and into the more abstract domains of working memory [10] (Figure 1b) and cognitive control (Figure 1c); where they can be used to solve analogous problems of selection and updating. Indeed, the known anatomy of parallel motor, frontal, and prefrontal basal ganglia-thalamocortical circuits hints at analogous computation ( Figure 1d) [11]. And, a variety of computational models have demonstrated the feasibility of such an architecture for solving complex working memory control problems 6, 10, 12, 13, 14, 15, 16, 17, 18, 19, 20, 21, 22•• and 23••. However, only recently have animal and human behavioral, neuropsychological, pharmacological, PET and fMRI studies provided direct functional evidence for multiple BG gating dynamics in WM and their importance for higher thought and action. Gating dynamics provide a powerful solution to the input control problem for working memory 6, 10 and 12.

For calculating the reduction in the power of this radiation as a

For calculating the reduction in the power of this radiation as a result of its passage through the atmosphere we usually use the simplified radiation transfer equation. In Figure 2 we distinguish three stages in the influx of solar radiation to the sea surface, according to which we carry out calculations. In the first stage we define the downward irradiance E↓OA at the top of the atmosphere (block 1 in Figure 2), which is governed directly by the solar radiation flux entering the Earth’s atmosphere. This flux reaching the top of the atmosphere, averaged over time, is known as the Solar Constant (see e.g. Neckel & Labs 1981, Gueymard 2004, Darula et al. 2005); the instantaneous

values of the downward irradiance at the top of the atmosphere E↓OA, associated with the Solar Constant, depend

on the Sun’s position in the sky, and on the distance at the ABT-888 manufacturer instant of measuring between the Earth and the Sun in its elliptical orbit around the Sun. These instantaneous values of E↓OA are calculated from basic astronomical formulae (e.g. Spencer 1971; see also Krężel 1985, Dera & Woźniak 2010) on the basis of the geographical coordinates of the measuring station and time (the day number of the year and the time of day). The second stage in these calculations yields the downward irradiance E↓OS of the solar radiation selleck inhibitor reaching the sea surface from a cloudless sky; here, the influence of clouds on this flux is neglected (Block 2 in Figure 2). What is taken into consideration is the reduction in downward irradiance due to the attenuation of the solar radiation flux on its passage through the atmosphere by scattering and absorption by atmospheric components such as water vapour, ozone and aerosols. These calculations are performed on the basis of more complex models of optical processes taking place in a cloudless atmosphere Anidulafungin (LY303366) (see e.g. Bird & Riordan 1986, Krężel 1997, Woźniak et al. 2008). As already mentioned, they take account of the effects of various constant and variable components of the atmosphere on its optical properties, including the variable contents of different

types of atmospheric aerosols. These are responsible for the greatest changes in the transmittance of the radiation flux in the atmosphere with the exception of the effect of clouds on this flux. Finally, the third stage in these calculations involves determining the values of the real downward irradiance at the sea surface E↓S, associated with the solar radiation flux reaching the sea surface under real atmospheric conditions, that is, when the real states of atmospheric cloudiness are taken into consideration (besides the solar zenith angle; Block 3 in Figure 2). Changes in cloud coverage are responsible in the highest degree for changes in the transmittance of the radiation flux through the atmosphere.

, 2004, Kuroda et al , 2005 and Ling and Trick, 2010) Several fa

, 2004, Kuroda et al., 2005 and Ling and Trick, 2010). Several factors, including temperature, salinity, irradiance and nutrient concentrations, may account for the increased incidence of Heterosigma blooms (Ono et al. 2000, Anderson

et al. 2008). Prior to 2010, only two harmful algal blooms of Noctiluca scintillans (Mohamed & Messad 2007) and Gonyaulax sp. (Zakaria A. Mohamed, King Khalid University, pers. comm.) had been documented in the Red Sea off the southern coasts of Saudi Arabia – those events took place in 2004. In May 2010, a bloom of H. akashiwo was observed for the first time off the Al Shouqyq region, making it the third HAB documented in South Saudi offshore waters. The bloom event was noticed as occurring at a site located in an area receiving water discharge from a nearby shrimp farm. Thus, a link is expected between Heterosigma bloom formation and shrimp

fish runoff into this site in the Red Sea. Metformin Therefore, the aim of this study was to assess the effect of shrimp farm runoff on the formation of an H. akashiwo bloom by the analysis of the environmental and biological characteristics of sea water at the bloom site, which receives fish farm discharge, and at a non-bloom site far away from any aquaculture activities. The study area comprised two sites: site 1, where the Heterosigma akashiwo bloom was observed – this is referred to as the ‘bloom site’; site 2, located about 20 km north of site 1, where no blooms were recorded – this is the ‘non-bloom site’. The two sites are located find more north of Al Shouqyq city on the southern Red Sea coasts of Saudi Arabia

(19.65–19.80°N) ( Figure 1). Site 1 (bloom site) is closed off by a large shrimp farm and thus potentially receives drainage of farm wastes, whereas there are no aquaculture operations near site 2. Sampling was started when a red tide of Erastin clinical trial H. akashiwo was observed on 27 May 2010 and was continued every week until the bloom disappeared. Phytoplankton samples were collected from the two sites around midday (13:00 hrs) to ensure the presence of Heterosigma on the water surface, as this alga has a diel vertical migration reaching depths of 10 m at night ( Yamochi & Abe 1984). Bloom and phytoplankton samples were taken at 1 m depth by vertical tows, using a plankton net of mesh size 10 μm. Concentrated by plankton tows, phytoplankton cells were sieved through a 60 μm mesh to eliminate larger organisms and then divided into three parts. One part was fixed with 1% Lugol’s solution and preserved in a brown bottle – this was used for the identification and counting of phytoplankton; the second part was placed in a 100 ml polyethylene bottle and used for testing the toxicity of the Heterosigma bloom; the third part was placed in a 250 ml polyethylene bottle and used for the isolation and culturing of Heterosigma.

However, due to the relative strength of the evidence that averag

However, due to the relative strength of the evidence that average temperature18, 25, 26, 27, 28, 29 and 30 and hours of sunshine,6, 14, 18, 31, 32, 33, 34 and 35 are associated with IPD and viral infections it was determined that they were

a logical choice to account for seasonality. We found a 1 month lag in the association between IPD and hours of sunshine, consistent with three PF-02341066 ic50 other studies reporting lags of 2–5 weeks6, 14 and 33 though no lag was reported in 2 other studies.31 and 32 This may be related to the strong, positive effects of sunlight on the immune system due to increased 1,25-(OH)2-vitamin-D metabolism.35 and 36 Other meteorological factors such as rainfall and relative humidity were not included in the models as associations with IPD and viral infections are less consistent.14, 18, 27 and 31 It may be that the use of average temperature as an adjustment for seasonality has led to slightly lower percentages, for some age-groups, of influenza-attributable IPD when compared to previous studies which included seasonal selleck chemicals harmonic curves.11 and 17 However, the use of harmonic curves does not allow for annual variations. From our results using Pearson and Spearman’s correlation coefficients, we could

conclude that there is a very strong association between IPD and the viral infections; however these are rather crude measures of association that cannot be seasonally adjusted, and so are likely to overestimate any association in our data. Further analysis, beyond the use of correlation coefficients, should be considered in similar studies of seasonal diseases in order to formulate more robust conclusions. We investigated a range of regression models; looking at both additive and multiplicative models. Ketotifen It is considered that the additive

model is a more plausible fit for this biological data,37 a multiplicative relationship between the independent variable terms in the model would be hard to substantiate. However, it is difficult to firmly conclude which model is the best as we have no gold standard for comparison (see ref and below).10 The ecological nature of this study restricts the conclusions that can be drawn. Research at an individual level may be more revealing with respect to the true incidence of virus-attributable IPD, but will be more challenging. Potential study designs that could be employed include case-control studies of IPD with serological investigations of recent viral infections. There are further limitations in the use of surveillance systems for the data in this study, under-reporting and changes over time in the reporting thresholds cannot be ruled out.

Both oximes provided adequate therapy for animals to be asymptoma

Both oximes provided adequate therapy for animals to be asymptomatic by the 24 hour observation. Additionally, with the TI dose of MINA, zero lethality was reported Natural Product Library with improvement in the QOL score at 24 h. Treatment of CPO-challenged animals with obidoxime Cl2, MMB4 DMS, HLö-7 DMS, and 2-PAM Cl significantly reduced lethality in the treatment group animals to ≤ 38% compared to 78% in the control group animals (Table 8). Additionally, obidoxime Cl2, MMB4 DMS, HLö-7 DMS, 2-PAM Cl, and RS194B significantly reduced the frequencies of lacrimation, fasciculations, respiratory

distress, and prostration. Obidoxime Cl2, MMB4 DMS, and HLö-7 DMS treatment significantly improved QOL scores in treatment groups compared to the control group at 24 h post challenge, at which time clinical signs in the treatment groups were limited to the mild and moderate categories. Among the oximes offering significantly improved survivability, only obidoxime Cl2 also provided statistically significant reactivation

of both ChEs. Although 2-PAM Cl appeared to improve ChE activities, statistical significance could not be determined. When treated with 2-PAM Cl, HLö-7 DMS, obidoxime Cl2, or MMB4 DMS, the AZD0530 lethality for the pesticides paraoxon and phorate oxon were significantly reduced to rates between 0 and 25%. HI-6 DMS and TMB-4 also provided significant protection against paraoxon with 13% and 25% lethality, respectively. Control group animals challenged with paraoxon and phorate oxon had lethality of 84% and 97%, respectively (Table 9 and Table 10). There was also a significant reduction in frequencies of salivation, fasciculations, respiratory distress, and prostration with 2-PAM Cl, HLö-7 DMS, obidoxime Cl2, or MMB4 DMS. QOL scores for the animals treated with 2-PAM Cl, HLö-7 DMS, obidoxime Cl2, or MMB4 DMS were significantly reduced relative to the control animals at 24 h post challenge, with oxime-treated animals

showing only impaired to moderate this website signs. Against paraoxon, MMB4 DMS and TMB-4 provided reactivation of both ChEs, while HLö-7 DMS reactivated only AChE, relative to control animals. There was no significant difference in cholinesterase activity of survivors within the phorate oxon-challenged animals at 24 h. Fig. 2 presents the 24-hour lethality data collated across the eight OPs tested, and illustrates that MMB4 DMS and HLö-7 DMS offered protection against all OPs except GD, and that 2-PAM Cl and obidoxime Cl2 were effective against all but GD, GF, and (for 2-PAM Cl) GA. A comparison with the equimolar (Fig. 2) and TI lethality (Fig. 3) shows that no significant difference is seen in the lethality results for any agents except a slight improvement for GB when treating with MINA. Fig. 4 presents the mean equimolar QOL scores at the 24-hour observation, and is consistent with the efficacy pattern of the lethality data. Fig.

Model recognition and prediction abilities were defined as the pe

Model recognition and prediction abilities were defined as the percentage of members of the calibration and evaluation sets that were correctly classified, respectively. The statistical package XLSTAT Sensory 2010 (Addinsoft, New York) was employed for all the chemometric calculations. Average spectra obtained for roasted coffee, coffee husks and corn samples are shown in Fig. 1. A comparative evaluation of the average data indicates somewhat similar spectra, with most see more of the significant bands concentrated in

the following ranges: 3000–2800 and 1800–700 cm−1. In general, absorbance values were higher for coffee and lower for corn. Two sharp bands at 2923 and 2854 cm−1 can be clearly seen in the spectrum corresponding to roasted coffee. Such bands have been previously reported present in spectra of roasted Arabica and Robusta coffee samples (Craig et al., 2012b; Kemsley et al., 1995) and also of crude coffee samples (Craig et al., 2011, 2012a). Paradkar and Irudayaraj (2002) also reported two sharp peaks

at 2882 and 2829 cm−1 in samples of caffeinated beverages such as coffee, tea and soft drinks. The band at 2829 cm−1 was attributed to stretching of C–H selleck chemical bonds of methyl (–CH3) group in the caffeine molecule, being successfully used to develop predictive models for quantitative analysis of caffeine (Paradkar & Irudayaraj, 2002). The same bands can be identified in the spectra obtained for roasted coffee husks and roasted corn at 2923 and 2854 cm−1 and at 2925 and 2848 cm−1, respectively. Both bands present lower absorbance values in the spectra obtained for coffee husks and corn compared to coffee. Furthermore, the second band is less evident in coffee husks and corn in comparison to coffee. Coffee husks have been reported to present similar levels of caffeine (∼1 g/100 g dry basis) in comparison to coffee beans,

whereas corn does not contain any caffeine. Other FTIR studies on corn and corn flour have also reported two bands at 2927–2925 and 2855 cm−1, being respectively attributed to asymmetric and symmetric C–H stretching in lipids (Cremer & Kaletunç, 2003; Greene, Gordon, Jackson, & Bennett, 1992). Although the samples in those studies were not submitted to roasting, the lipids content is not expected to vary during Molecular motor roasting of corn, as it is known to occur with coffee, and the peak assignment to C–H stretching in lipids might still be valid. Furthermore, the reported amounts of lipids (Gouvea, Torres, Franca, Oliveira, & Oliveira, 2009; Moreau, 2002; Oliveira, Franca, Mendonça, & Barros-Junior, 2006) present in coffee husks (1.5–3 g/100 g) are quite low in comparison to coffee beans (12–16 g/100 g) and corn kernels (3–5 g/100 g). Therefore, such bands may be affected by both caffeine and lipids levels in the case of coffee, and are most likely primarily associated to caffeine in the case of coffee husks and only to lipids in the case of roasted corn.

5 mg/kg) was observed here and by Matos et al (2001) However, t

5 mg/kg) was observed here and by Matos et al. (2001). However, this increase was not observed in Ts-DF venom injected animals. Thus, the inability of the T. serrulatus venom from DF to induce Sotrastaurin concentration pulmonary edema could be related to the absence of both cardiogenic and non-cardiogenic effects, such as elevated levels of CK and CK-MB, morphological changes in cardiac muscle, or increased pulmonary vascular permeability. We observed the presence of leukocytes in bronchoalveolar lavage of rats injected with Ts-MG venom. However, this response was not observed in animals

injected with Ts-DF venom, just as in previous studies performed by Matos et al. (1999) who suggested that the recruitment of leukocytes do not play an important role in the development of acute pulmonary edema. Otherwise, it was shown that the T. serrulatus venom stimulates the release of pro-inflammatory cytokines such as TNF-α (tumor necrosis factor alpha) and KC (keratinocyte-derived chemokine), and the activity of MPO (myeloperoxidase

and nitric oxide) and lung perivascular mononuclear and polymorphonuclear cells infiltration ( Comellas et al., 2003, Andrade et al., 2004, Andrade et al., 2007, Coelho et al., 2007 and Peres et al., 2009). Andrade et al. find more (2007) showed that scorpion venom not only increases the expression of mRNA pulmonary inflammatory cytokines but also non-inflammatory cytokines, moreover the expression of IL-1α, IL-1β and IL-6 mRNA was shown to be higher among the remaining detectable cytokines. Recently, Progesterone Filho et al. (2011) demonstrated that the T. serrulatus venom did not cause local inflammation in mice, but it induced an increase of blood neutrophils and serum IL-6, TNF-α and IL-10. In addition, after 360 min of envenomation there was a reduction in the cells number from peritoneum and spleen, but there was an increase in the cell number from lymph nodes ( Filho et al., 2011). It is widely known that different scorpion species have different venom compositions. Interestingly, many studies have reported significant differences in the protein components and venom toxicity within

scorpions of the same species (Kalapothakis and Chávez-Olórtegui, 1997, Pimenta et al., 2003a, Newton et al., 2007, Abdel-Rahman et al., 2009 and Abdel-Rahman et al., 2010). The present work shows that Ts-MG venom is slightly more complex than the Ts-DF and posses a higher number of compounds eluting between 0–25 and 36–40% acetonitrile than Ts-DF. On the other hand, Ts-DF has a higher number of compounds elution between 51 and 60% acetonitrile than Ts-MG venom. The venom of several scorpions of the Tityus genus has been submitted to proteomic analysis ( Pimenta et al., 2001, Diego-García et al., 2005, Nascimento et al., 2006, Batista et al., 2006, Batista et al., 2007, Barona et al., 2006 and Rates et al., 2008). According to Pimenta et al. (2001), T.

In other words, these high values could simply indicate that a mu

In other words, these high values could simply indicate that a much larger catchment is producing much more flow. To verify if this scale issue actually magnifies the performance of the models, we re-performed the multiple regression analyses using specific runoff (in m3 s−1 km−2) as dependent variables and computed NSE based on volumetric runoff for the two sets of power-law models predicting either specific or volumetric runoff. According to this efficiency coefficient, the models predicting

specific runoff were found not to outperform those described in this paper and are therefore not reported here. Except for the model predicting maximum daily flow which has one of the lowest values for Rpred2, the models predicting the higher half of the FDC (0.05 ≤ flow percentiles ≤ 0.60), HIF inhibitor have a mean Rpred2 (92.97%) higher than that (90.41%) of the models predicting the lower half of the FDC (0.70 ≤ flow percentiles ≤ 0.95 and “Min”). This comparison only considers the best model (highest Rpred2) for each flow metric (Table 3). The better prediction of high flow, compared to low flow, suggests that the explanatory

variables tested in this analysis (mainly geomorphological and climate characteristics) do not correspond to the catchment characteristics that predominantly control low flows. Similar contrast between the predictive power of high-flow and low-flow models has been observed selleck products under various hydrological conditions (Thomas and Benson, 1970), suggesting that more efforts are needed to generate catchment characteristics suitable for multivariate low flow predictions. Fig. 2 illustrates this contrast in performance by comparing

observed (Qj,obs) and predicted (Qj,pred) flow in each studied catchment j for mean annual flow ( Fig. 2a and c) and for the model predicting the 0.95 flow percentile with the best performance ( Fig. 2b and d). Runoff values are volumetric (m3 s−1) in Fig. 2a and b and specific (m3 s−1 km−2) in Fig. 2c and d. The NSE values calculated with volumetric runoff ( Fig. 2a and b) are greater than those obtained with specific runoff ( Fig. 2c and d), reflecting the mass balance effect Abiraterone (i.e. larger catchments produce more flow) explained above. Although the scatter plots in Fig. 2a and b align well along the first bisector, 30% and 50% of the catchments, respectively, have an absolute normalized error (ANEj for catchment j, Eq. (8)) greater than 40%. These errors result from the assumptions of the modeling method and from possible inaccuracies in the original flow values used in the model parameterization. Even though cross-validation has been performed, extrapolation to ungauged catchments still adds non-measurable uncertainty. Therefore, we encourage users of these models to cross check predicted flow with other flow prediction methods, if they are available. equation(8) ANEj=Qj,pred−Qj,obsQj,obs Fig.

It sum, bio-logging initiated beyond the

limits of the te

It sum, bio-logging initiated beyond the

limits of the territorial sovereignty or resource jurisdiction of coastal states is consistent with international law, and in particular, UNCLOS. Coastal states may not purport to require their permission and marine scientists are not compelled to seek it, even if tagged marine species later migrate into the territorial sea or EEZ. As in many areas of society, technology has leapfrogged existing legal regimes. Bio-logging illustrates how the authority of coastal states to monopolize information about, and direct and control the study of, marine migratory species has diminished. The use of bio-logging does not mean, however, that coastal state sovereignty over the territorial sea, or exclusive resource rights in the EEZ have contracted. Instead, new methods of Nutlin-3a in vivo MSR have by-passed the existing regulatory

PI3K activity regime, much as satellite remote sensing did decades earlier. Likewise, just as remote sensing advanced understanding of the Earth, bio-logging is expanding the horizon of marine science, and improving the ability to develop and support programs for marine conservation. This paper benefited from data produced by Barbara Block, Carsten Egevang, Jerome Bourjea, Mayeul Dalleau and Ari Friedlaender, and from insights from Joe Bonaventura and John Norton Moore. The research was supported by the Mary Derrickson McCurdy Visiting Scholar program and Duke University Marine Laboratory. “
“Preparing for the third reform of the common fisheries policy (CFP), the European Commission published a Green Paper [1] reviewing the problems of the existing CFP. The Green Paper identified five main structural failings: fleet overcapacity, imprecise policy objectives, short-term focus, insufficient industry responsibility, and poor industry compliance. In its analysis, the Commission

emphasized the vicious cycle set off by overcapacity and overexploited resources, which generate pressure on authorities to make derogations and exemptions Florfenicol from particular regulations, and leads to a demand for more regulations. The outcome is what the Commission terms “micromanagement”, a myopic management system that is becoming increasingly complex, ineffective, difficult to understand and costly to maintain [1] and [2]. The Commission suggested “results based management” (RBM) as a way to overcome micromanagement: “”The industry can be given more responsibility through self-management. Results based management could be a move in this direction: instead of establishing rules about how to fish, the rules focus on the outcome and the more detailed implementation decisions would be left to the industry. Public authorities would set the limits within which the industry must operate, such as a maximum catch or maximum by-catch of young fish, and then give industry the authority to develop the best solutions economically and technically”" [1].