A relocatable ocean model in support of environmental emergencies

Relocatable models have been employed for emergency weather predictions, with results very useful for our society in the cases of severe weather outbreaks, hails, tornados, and hurricanes (e.g., Schroeder et al. 2006; Bender et al. 2007). In the ocean, tidal and shallow water models were likely the first relocatable models (e.g., Dietrich et al. 1993; Blain et al. 2002; Posey et al. 2008), again with multiple societal uses. A pioneering relocatable primitive-equation ocean model was that of the Harvard Ocean Prediction System (HOPS). It has been utilized for real-time shipboard predictions of ocean mesoscale circulations for the first time in the Iceland-Faeroe front region (Robinson et al. 1996). Subsequently, the HOPS relocatable model and its improved versions have been employed to issue real-time forecasts and analyze ocean dynamics in diverse regions of the world’s oceans, including the Atlantic Ionian Stream and Strait of Sicily region (Robinson et al. 1999; Lermusiaux 1999), the Strait of Gibraltar (Robinson and Sellschopp 2002), the Tunisia-Sardinia-Sicily region (Onken et al. 2002), and the Eastern Ligurian Sea (Robinson et al. 2003). Starting in the early 2000s, Maritime Rapid Environmental Assessment (MREA; Robinson and Sellschopp 2002) became one of the drivers for relocatable ocean modeling and forecasting. Such applications required the evaluation of the usefulness of predictions, especially the assessment of the predictive capability (Robinson et al. 2002) of the modeling systems. With this basis, more rigorous evaluations were completed in 2003 and 2004, for the relocatable Mini-HOPS modeling system applied to the Elba region and off the coast of Portugal (Leslie et al. 2008). A relocatable modeling approach for MREA04 has been also applied off the coast of Portugal (Ko et al. 2008). The relocatable HOPS system has been also integrated with the ocean general circulation model of the Mediterranean Forecasting System (MFS) (Russo and Coluccelli 2006). A review of the MREA concepts and applications is provided in Ferreira-Coelho and Rixen (2008). Relocatable models have been also employed recently for studying Lagrangian dynamics and dispersion in the Gulf of Mexico region (Wei et al. 2013a), which is an application related to our research.

Oil slicks caused by oil tanker/ships accidents compose a major source of hydrocarbon pollution for the marine and coastal environment (including seagrass beds, mangroves, algal flats, and coral reefs) and can jeopardize the functional integrity of the marine ecosystem (seabirds populations, fish communities, and marine mammals), as reported in Jackson et al. (1989), Piatt and Anderson (1996),Peterson et al. (2003). Since oil spill evolution depends on the winds, waves, sea temperature, and current conditions, oil spill management strategies need to be developed together with the improvement of meteorological, ocean, and wave forecasting models.

Pioneering examples of oil spill response systems were available during the Braer oil spill (Shetland Islands, UK, 1993) (Proctor et al. 1994) and the Erika oil spill (Brittany coast in the Bay of Biscay, France, 1999) (Daniel et al. 2001), which for the first time allowed operators to develop a response strategy rather than react only to observed information. Further examples of operational forecasting system for developing proper response strategies to oil spill emergencies were available during the Prestige oil spill crisis (Galicia coast, Spain, 2002) (Carracedo et al. 2006; Castanedo et al. 2006; Lermusiaux et al. 2007). In the Mediterranean Sea, an oil-spill decision-support system was developed during the largest oil-release accident in the Eastern Mediterranean, the Lebanese oil-pollution crisis, which occurred in mid-July 2006 (Coppini et al. 2011). During the recent largest accidental marine oil spill in the history of the petroleum industry, effective oil spill monitoring and modeling systems were critical to the rapid responses achieved for the Deepwater Horizon event (Gulf of Mexico, 2010). The value of regional models (with improved resolution and topography) was demonstrated (Mariano et al. 2011), and an ensemble forecast system was developed with a focus on regional and global scales (Liu et al. 2011a, b). An example of a quasi-operational forecasting system composed by a finite-element model and a particle-tracking model was also implemented to provide high-resolution current velocity field and surface trajectories of the oil on the continental shelf and nearshore (Dietrich et al. 2012). However, the majority of the above oil spill rapid response systems have been based on regional or even basin-scale models. Thus, there is a need to analyze the possibility to use relocatable models that can be rapidly implemented in any region of the world, and to assess if they can provide accurate forecasts in a very short time, as required by the management of emergencies produced by oil spills or contaminants releases at sea.

An oil spill model is an important component in any emergency response or contingency plan. Oil spill numerical modeling started in the early 80s and, according to state-of-the-art reviews (ASCE 1996; Reed et al. 1999), a large number of numerical Lagrangian surface oil spill models have grown in the last 30 years. These models can vary from simple point source particle-tracking models, such as TESEO-PICHI (Castanedo et al. 2006; Sotillo et al. 2008), to complex models that attempt to comprehensively simulate the three-dimensional advection-diffusion-transformations processes that oil undergoes (Wang et al. 2008; Wang and Shen 2010). Some of the most sophisticated Lagrangian operational models are COZOIL (Reed et al. 1989), SINTEF OSCAR 2000 (Reed et al. 1995), OILMAP (Spaulding et al. 1994; ASA 1997), GULFSPILL (Al-Rabeh et al. 2000), ADIOS (Lehr et al. 2002), MOTHY (Daniel et al. 2003), MOHID (Carracedo et al. 2006), the POSEIDON OSM (Pollani et al. 2001Nittis et al. 2006), OD3D (Hackett et al. 2006), the Seatrack Web SMHI model (Ambjø̈rn 2007), MEDSLIK (Lardner et al. 1998, 2006), GNOME (Zelenke et al. 2012), OILTRANS (Berry et al. 2012), and MEDSLIK-II (De Dominicis et al. 2013a). Which type of model to use depends on the model availability in the area of interest and final objectives: from short-term forecasting to long-term impact assessment. The oil spill model used in this work is MEDSLIK-II (De Dominicis et al. 2013a) that is able to simulate the transport of surface drifters or the transport, diffusion, and transformations of a surface oil slick. It has been used extensively in the past to simulate oil spill accidents (Coppini et al. 2011) and/or drifter trajectories (De Dominicis et al. 2013b), and it proved to be reliable in short-term forecasting.

On January 13th, 2012, the Costa Concordia cruise ship hit a rocky outcrop and ran aground rolling onto its side as it sailed near the Giglio island. With 2,500 t of fuel in its tanks, the Costa Concordia was immediately considered a high-risk accident for possible spills to occur. Though hypothetical, an oil spill scenario could not be totally discarded. MEDSLIK-II has been connected to operational regional (MFS; Pinardi and Coppini 2010) and subregional models, the Western Mediterranean (WMED; Olita et al. 2013) and the Tyrrhenian Sea (TYRR; Vetrano et al. 2010), to simulate scenarios of fuel leaks. In Fig. 1, the geographical domains of the models are presented. The oil spill scenarios and current forecasts have been provided every day and in real time to the Italian Coast Guard. In case of an oil spill, this information would have helped to plan the booms deployment, to place skimmers, to protect a particular piece of coast, or to intervene with airplanes or vessels. Moreover, a high-resolution, relocatable model, called Interactive Relocatable Nested Ocean Model (IRENOM) has been nested in MFS and its currents used as input to the MEDSLIK-II model. The hydrodynamics model core of IRENOM is based on the Harvard Ocean Prediction System (HOPS) (Robinson 1999), and the area of interest of this work is the north-western Mediterranean Sea where the Costa Concordia accident occurred (see Fig. 2).

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To assess the accuracy of the oil spill simulations and of the ocean current predictions, a validation experiment with the release of four I-SPHERE drifters has been performed in the area of the accident. MEDSLIK-II has been used to simulate the drifter trajectories using the current fields output from different operational oceanographic models and from IRENOM. The latter has been shown to produce realistic drifter trajectories with higher accuracy than the coarser resolution regional and subregional models. In this work, the improvements in having high-resolution and accurate forecasts of the ocean currents will be assessed and the sensitivity of the drifter trajectory forecasts to model configuration parameters and to wind fields with different resolutions will be analyzed.

The manuscript is organized as follows: Section 2 overviews the hydrodynamic models and oil spill model, together with the drifters data used for the validation; Section 3 shows the results of the operational support provided during the emergency; Section 4 presents the results of the IRENOM implementation and drifters validation experiments; and Section 5 offers the conclusions.

On January 13, 2012, only hours after leaving the Italian port of Civitavecchia, the Costa Concordia cruise ship with more than 4,200 passengers and crew on board hit a rocky outcrop, ran aground, and rolled onto its side as it sailed off the Giglio Island. Italian Authorities (Coast Guards and Civil Protection) immediately reacted by deploying search and rescue and risks mitigation measures, including environmental risks. With about 2,500 t of fuel in its tanks, the concern about the potential environmental impact was high. In case of failure of the debunkering operation, a spillage might have polluted the Tuscan Archipelago National Park, a marine environmental protected area. Every day, starting from the 16th of January and until the fuel unloading operations finished, the coupled hydrodynamics and MEDSLIK-II system was run to produce scenarios of the possible oil spill from the Costa Concordia. MEDSLIK-II used the currents (hourly fields) provided every day by the operational ocean models available in the area: MFS, TYRR, and WMED. Thanks to these data, a fuel leak can be simulated to forecast the possible fuel dispersion into the sea and along the coast. The position of the possible oil spill coincides with the ship position in the proximity of the Giglio Island harbor. The amount of oil spilled was decreased on the basis of the quantity debunkered. Daily bulletins were provided to the Italian Coast Guard Operational Center. Those bulletins presented the forecasts of the currents, wind and oil dispersion at surface up to 72 h after the possible spill, supposed to be released continuously in 72 h. Though hypothetical, an oil spill scenario could not be totally discarded, and this information would have been crucial for helping local maritime authorities to be better prepared in setting up prevention measures and optimizing cleaning operations. The bulletin dissemination to other competent authorities was managed under the responsibility of the Italian Coast Guard, and it complemented the information coming from European services (e.g., oil spill detection and monitoring from EMSA, the European Maritime Safety Agency).

Figure 5 shows an example of the information contained into the bulletin provided to the competent authorities. When all the models are in agreement, we might be more confident in the accuracy of the forecasts. Nevertheless, there were times in which the three models gave very different predictions, as shown in Fig. 5. Reasons for the different model forecasts may be due to different numerical code (NEMO, POM), specific grids, parameterizations, data assimilation schemes, and domains. Commonalities are that both WMED and TYRR are nested into MFS, but using different initialization procedure (see Section 2.3). WMED with a daily initialization from MFS cannot deviate much from MFS, while TYRR model uses an initialization period of 7 days, allowing the model to produce its own dynamics. During the Costa Concordia emergency, only a qualitative comparison of the model results has been performed and the different forecasts have been not produced from true ensemble prediction systems based on dynamics. Despite this, a similar methodology was implemented during the Deepwater Horizon oil spill (Liu et al. 2011b, c), and it demonstrated to provide some degree of confidence that any single model alone might not. Although super-ensemble techniques for ocean (Rixen et al. 2009) and weather forecasting (Krishnamurti et al. 2000a, b) are widely used, few examples on using ocean ensembles in Lagrangian trajectory models are available. It has been demonstrated that the trajectories ensemble can generate important uncertainty information in addition to predicting the drifter trajectory with higher accuracy, in contrast to a single ocean model forecast (Wei et al. 2013b). How to combine models results is not obvious and some recent works have been done on this issue. One methodology is the hyper-ensemble technique (Rixen and Ferreira-Coelho 2007; Rixen et al. 2008; Vandenbulcke et al. 2009), which combines multiple model of different physical processes (ocean currents, winds, and waves) and then performs the trajectory simulations using the combined product. The optimal combination is obtained during a training period by minimizing the distance between modeled and observed trajectories and requires comprehensive observational networks. Another option is to combine a posteriori the modeled trajectory obtained using the different velocity fields (Scott et al. 2012). In the future and with a larger drifters dataset, these methodologies will be explored.

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Giving the errors inherent to any model, its forcing fields and its initialization, a validation exercise has been organized to assess the quality of produced forecasts, as described in Section 2.4. As shown in Table 2, nine simulations have been done to evaluate the models performances and the sensitivity of the oil spill model to some parameterizations and to the forcing fields. We performed a first set of simulations using only the hourly surface currents, U _C term of Eq. 1, from MFS, TYRR, and WMED. Then, we carried out a second set of experiments to take into account the Stokes drift effect, U _S term of Eq. 1. The last set of simulations has been performed adding also the wind drag correction, U _D term of Eq. 1, which is equal to 1 % of the wind velocity intensity. In Fig. 6, the comparison between one of the real drifters trajectories (buoy 1 of Fig. 4) and the simulated trajectories is shown. Qualitatively, we can see that the simulated trajectories using MFS and WMED go in the wrong direction. Using TYRR currents, the simulated trajectory are in better agreement with the observed one, but without adding the wind drag correction and the Stokes drift correction (Fig. 6a, b), the displacement of the simulated drifter is underestimated. The best results are obtained with the experiment TYRR-CSD (Fig. 6c) that shows a higher displacement of the simulated drifter in the correct direction. The separation distance, d _24h , and the skill score, s s _24h , after 24 h of simulation have been calculated for all buoys. In Table 3, the values obtained for buoy 1 are listed, together with the average over the four buoys. Exp. TYRR-CSD shows the lowest separation distance (4.15 km) and highest skill score (0.59) in reproducing buoy 1 trajectory, confirming that the best results are obtained using the TYRR currents and using the Stokes drift and wind drag terms. In Fig. 7, the decomposition of the total velocity that drives the simulated buoy 1 in the Exp. TYRR-CSD is shown. It is found that the effect of the wave correction, U _S , and wind drag correction, U _D , can be, as in this case, of the same order of magnitude of the current velocity, U _C .

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Table 2

Sensitivity experiments of modeled trajectories to different OGCMs currents fields and to the particle trajectory equation terms

Exp. name	Current field	U C	U S	U W	U D
MFS-C	Hourly Surface Currents MFS	Yes	No	No	No
WMED-C	Hourly Surface Currents WMED	Yes	No	No	No
TYRR-C	Hourly Surface Currents TYRR	Yes	No	No	No
MFS-CS	Hourly Surface Currents MFS	Yes	Yes	No	No
WMED-CS	Hourly Surface Currents WMED	Yes	Yes	No	No
TYRR-CS	Hourly Surface Currents TYRR	Yes	Yes	No	No
MFS-CSD	Hourly Surface Currents MFS	Yes	Yes	No	Yes
WMED-CSD	Hourly Surface Currents WMED	Yes	Yes	No	Yes
TYRR-CSD	Hourly Surface Currents TYRR	Yes	Yes	No	Yes

Table 3

Results of Table 2 experiments in terms of separation distances and skill scores

Exp. name	Buoy1 d 24h	Buoy1 s s 24h	Mean d 24h	Mean s s 24h
MFS-C	16.73 km	0	14.93 km	0.09
WMED-C	23.06 km	0	20.56 km	0
TYRR-C	9.34 km	0.35	13.16 km	0.33
MFS-CS	13.68 km	0.15	11.78 km	0.30
WMED-CS	20.15 km	0	15.93 km	0.13
TYRR-CS	6.10 km	0.50	11.51 km	0.48
MFS-CSD	11.05 km	0.28	9.55 km	0.46
WMED-CSD	17.63 km	0.06	13.01 km	0.35
TYRR-CSD	4.15 km	0.59	10.34 km	0.54

In order to test the sensitivity to different horizontal grid resolutions, two horizontal domains are chosen. The first domain covers the region from 41.26°N to 43.93°N and from 9.11°E to 12.73°E. The horizontal grid resolution is approximately 3 km and consists of 100×100 points. The second domain covers the region from 41.70°N to 43.12°N and from 9.39°E to 12.29°E. The horizontal grid resolution is approximately 2 km and consists of 120×80 points. The two domains are referred in Tables 1 and 4 as HG1 and HG2, respectively, and are shown in Fig. 2. Both configurations have 25 double sigma levels. The bathymetry for both configurations has been obtained from the US Navy unclassified 1 min bathymetric database DBDB-1, by linear interpolation of the depth data into the model grid.

One of the main differences between the IRENOM configurations and MFS is the topography. Due to the low resolution of the MFS model, the Giglio and Giannutri Islands (see Fig. 2) is not reproduced in the MFS topography, while in the IRENOM model, the land/sea mask has been correctly implemented. Thus, it is necessary to initialize the IRENOM model some days before the day of the deployment of the drifters to let the model correctly reproduce the dynamic of the current between the islands, which drives the drifters transport. The sensitivity to the initialization time (spin-up time) is extensively examined in this work. The spin-up time is defined as the time needed by an ocean model to reach a state of physical equilibrium under the applied forcing. The results cannot be trusted until this equilibrium is reached due to spurious noise in the numerical solution. The sensitivity to a model initialization of 3, 5, and 7 days is tested as indicated in Table 4, where these spin-up times are labeled T11, T09, and T07, respectively.

Next, in order to test the influence of the topography on the model results, a simulation with alternating direction Shapiro filters is done, see label YS in Table 4. In this case, a fourth-order Shapiro filter is applied and the number of filter applications is set to 2. The model sensitivity to the shallowest allowed topography is also tested by using a topography clipping value of 5 m (see label C5 in Table 4) against the standard 10-m value used for all the other model runs.

The above runs have been performed using the ECMWF model output with 0.25° resolution, which is the forcing used operationally by MFS, WMED, and TYRR. Such coarse atmospheric model gives forcing only every approximately 12×12 grid points of the IRENOM model with 2-km resolution, and it might not give a realistic representation of the wind field forcing for a high-resolution hydrodynamic model. Thus, a sensitivity analysis of the 2-km configuration of the IRENOM model to the horizontal resolution wind forcing has been performed by running IRENOM forced by the SKIRON winds with a resolution of 0.025°. The experiments are indicated in the Table 4 with the label SKI. In theory, higher-resolution wind forcing should give better predictions, but it is not obvious because if the higher resolution forcing does not represent well the smaller weather scales, island structure, etc., the fine-grid ocean simulation with higher resolution forcing may be worse than with the coarse forcing.

Finally, the four buoys have been simulated using the MEDSLIK-II model forced by the currents coming from the 11 different IRENOM configurations. The trajectory simulations have been performed using the currents, the Stokes drift, and the wind drag, because, as it was found in Section 3, U _S and U _D should not be neglected. To be consistent with the IRENOM current fields, U _S and U _D are calculated by MEDSLIK-II using the same wind forcing used to force the IRENOM model.

Figure 8a–c shows the IRENOM sea surface current fields obtained with a horizontal resolution of 3 km, ECWMF 0.25° wind forcing, and with a spin-up time of 7 days (a), 5 days (b), and 3 days (c). A greater spin-up time causes the development of stronger currents especially south of Elba Island and finer spatial scales have a greater time to develop, as is the case of the circulation pattern north of Elba Island. To decide which spin-up time should be used, the general practice (Simoncelli et al. 2011) would suggest to choose the spin-up time which allows the ocean model to reach a state of physical equilibrium, i.e., Total Kinetic Energy (TKE) plateau reached. Figure 9 shows the ratio between the (TKE), on the target day 14 February at 12:00 UTC, of the relocatable model and that of the father model MFS as a function of the spin-up time. The IRENOM model with 3-km resolution does not reach a plateau, as shown in Fig. 9 (blue line), but the slope of the curve diminished between 5 and 6 days of spin-up time. This behavior would suggest better trajectory predictions using the current fields of IRENOM obtained with an initialization time of at least 5 days. However, the circulation pattern depicted in Fig. 8a–c shows that a spin-up time longer than 3 days breaks the flow continuity that is observed along the channel, leading to worse trajectories predictions (presented later in this Section).

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Figure 8d shows the sea surface current fields with a horizontal resolution of 2 km with a spin-up time of 3 days (5 and 7 days spin-up time results are not shown) and forced by ECWMF 0.25° wind forcing. With this finer horizontal grid resolution, different spatial scales develop in comparison to the coarser 3-km resolution. In particular, considering that at the time of drifters release a wind of about 5 m/s was blowing from north east, the development of weaker currents in the calm lee behind the Elba Island is expected. This is actually the case for the finer grid resolution, in contrast to the current field observed in Fig. 8a–c. The ratio between the TKE, on the target day 14 February at 12:00 UTC, of the relocatable model with 2-km resolution and that of the father model MFS as a function of the spin-up time is shown in Fig. 9 (red line); with this resolution, the slope of the curve is lower than in the IRENOM configuration with 3-km resolution, suggesting that the plateau is almost reached after 3 days.

The sensitivity of the IRENOM configuration with 2-km resolution to the atmospheric model horizontal resolution has been also investigated, and in Fig. 8e, the sea surface current fields, obtained with a spin-up time of 3 days, is shown (5 and 7 days spin-up time results are not shown). With this finer wind forcing, stronger westward currents develop south of the two islands, and the current between the Giglio and Giannutri Islands slightly changes its direction (eastward) compared to the currents presented in Fig. 8d, leading to better trajectories predictions (presented later in this section).

Furthermore, the model behavior related to initialization time and to the IRENOM and atmospheric model horizontal resolution is further investigated by comparing the model-predicted sea surface temperature (SST) to satellite radiometer observations available from the MyOcean portal (http://www.myocean.eu/) as daily gap-free map at 1/16° resolution over the Mediterranean Sea. Figure 10 shows the root mean square error (RMSE) statistics as a function of spin-up time for 3 and 2-km grid resolution. The HG2 configuration is in better agreement with observed SST, showing a lower RMSE than the HG1 configuration. For both model configurations, there is a progressive increase of RMSE as a function of spin-up time, suggesting that shorter spin-up time should lead to lower error in SST estimates. We have to consider that the father model (MFS) current fields are analysis, thus corrected using the assimilation of SST data. As a consequence, using a longer spin-up time, we let the IRENOM model free to develop its own dynamics, but possibly introducing a greater uncertainty when the model moves away from the MFS initial conditions, as confirmed by the trajectories predictions (presented later in this Section). As shown in Fig. 10, the IRENOM configuration with 2-km resolution and forced by the SKIRON 0.025° wind is in better agreement with the observed SST, showing a lower RMSE than the analogous configuration forced by the low-resolution ECMWF wind forcing.

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The IRENOM configurations has been then validated using the trajectories of the drifters released in the Costa Concordia accident area. Figure 11a shows the trajectory prediction for buoy 1 using the IRENOM currents with resolution of 3 km and different spin-up times, forced by the ECMWF 0.25° wind forcing. The best result is achieved with the IRENOM currents initialized 3 days before the drifter deployment; as shown in Table 5, Exp. HG1- T11 shows the lower separation distances and higher skill scores. Worser results are obtained increasing the spin-up time (Exp. HG1-T09 and Exp. HG1-T07), although little difference in trajectory prediction are observed using a spinup time of 5 or 7 days. As depicted in Fig. 8a–c, a spin-up time longer than 3 days breaks the flow continuity that is observed along the channel. This fact causes a worst trajectory prediction for buoy 1, which follows a quite straight path across the channel. In summary, a greater spin-up time allows the generation of more spatial scales and stronger sea surface current, but it introduces uncertainties in the current fields when the model moves away from the MFS initial conditions, that is corrected using data assimilation. Moreover, in this specific case, longer spin-up time breaks the current which develops straight along the channel between the two islands, leading to a worst trajectory prediction for buoy 1.

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Table 5

Relocatable model perfomances in terms of trajectories separation distances and skill scores

Exp. name	Buoy1 d 24h	Buoy1 s s 24h	Mean d 24h	Mean s s 24h
HG1-T11	3.60 km	0.66	10.47 km	0.53
HG1-T09	6.39 km	0.57	11.56 km	0.48
HG1-T07	7.75 km	0.51	11.24 km	0.49
HG2-T11	2.88 km	0.75	10.06 km	0.59
HG2-T09	3.78 km	0.67	9.02 km	0.59
HG2-T07	4.78 km	0.62	8.87 km	0.58
HG2-T11-YS	2.87 km	0.74	10.15 km	0.58
HG2-T11-C5	3.16 km	0.75	10.21 km	0.57
HG2-T11-SKI	3.41 km	0.79	8.64 km	0.61
HG2-T09-SKI	5.96 km	0.59	7.82 km	0.56
HG2-T07-SKI	7.39 km	0.55	9.80 km	0.44

Figure 11b shows the simulated trajectories using the IRENOM sea surface currents with a horizontal resolution of 2 km and spin-up time of 7, 5, and 3 days, forced by the ECMWF 0.25° wind forcing. The finer grid resolution allows the development of a stronger current in the channel. As a consequence, better trajectory prediction for buoy 1 is achieved. The lowest separation distance after 24 h, 2.88 km, and a skill score of 0.75 is achieved using 3 days of spin-up and 2 km of resolution (Exp. HG2-T11, in Table 5). The spin-up time acts in the same way as for 3-km grid resolution. A 3-day spin-up time gives the best trajectory prediction, while longer spin-up times lead to a poorer trajectory prediction skill. In conclusion, it is suggested that the spin-up time for a relocatable model cannot be decided a priori and it should be a tuneable parameter.

Figure 11c shows the simulated trajectories using the IRENOM sea surface currents with a horizontal resolution of 2 km and spin-up time of 7, 5, and 3 days, forced by the SKIRON 0.025° wind forcing. To be consistent with the IRENOM current fields, the Stokes drift correction, U _S of Eq. 7, and the wind drag correction, U _D of Eq. 5, are calculated by MEDSLIK-II using the SKIRON 0.025° wind field. The finer wind forcing produces the change in the direction of the current in the channel, that is in this case more eastward, as shown in Fig. 8e. As a consequence, better trajectory prediction for buoy 1 is achieved. Although the separation distance after 24 h is 3.41 km (Exp.HG2-T11-SKI, in Table 5), higher than in HG2-T11, it is qualitatively evident that the modeled trajectory using the high-resolution wind forcing is in better agreement with the observed trajectories. Indeed, Exp. HG2-T11-SKI shows the highest skill score (0.79) and in this case, as suggested by Liu and Weisberg (2011), the separation distance might not be a good estimate of the trajectory accuracy. In conclusion, higher resolution wind forcing gives a better estimate of the simulated drifter path.

Figure 11d shows the simulated trajectories using the MFS, TYRR, and WMED currents in comparison with the trajectories obtained with IRENOM sea surface currents forced by both ECMWF 0.25° (HG2-T11) and SKIRON 0.025° (HG2-T11-SKI) with an horizontal resolution of 2 km, and spin-up time of 3 days, which are the best ones among the IRENOM experiments. The IRENOM currents give the best results. We believe this is due to the correct topography (Giglio and Giannutri Islands are correctly implemented in the model), to the initialization procedure with a spin-up time of 3 days. In the MFS model, the Giglio Island is not reproduced, and although in WMED and TYRR model the Giglio Island is correctly defined, problems can arise from the initialization procedures: WMED has no spin-up time (cold start from MFS) and TYRR uses 7-days initialization period. Furthermore, the higher-resolution wind forcing further improves the modeled trajectories accuracy, while all the above operational models are forced by the ECMWF 0.25° forcing.

In Table 5, the skills of the trajectory simulations obtained using the IRENOM model with the Shapiro filter applied on the bathymetry for the configuration with 2-km grid resolution (HG2-T11-YS) and using a lower shallowest topography vertical clipping of 5-m value (HG2-T11-C5) with respect to the 10 m used for all the other experiments are shown. There is a meaningless difference in drifter trajectory predictions with respect to the case where the bathymetry is not filtered (HG2-T11). As well as using a lower shallowest topography clipping of 5-m value does not provide meaningful differences in skill trajectory predictions.

Figure 12 compares the trajectory predictions using the different IRENOM models configurations. Buoy 4 presents a looping behavior and the modeled trajectory is able to correctly reproduce the mean direction of the displacement, although it rotated in the opposite direction of the observed one. Moreover, it is evident that the trajectories of buoys 2 and 3 are not correctly reproduced. This might be due to the incorrect positioning of vortex structures that affects the buoys 2 and 3 movement. Indeed, as it is shown in the IRENOM HG2-T11-SKI model configuration vorticity section (Fig. 13), a baroclinic cyclonic vortex extends along the shelf. This vortex might be not correctly reproduced (misplaced or shifted in time) and negatively influences the trajectory predictions of buoys 2 and 3.

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Besides the low performance of the IRENOM simulation in reproducing the buoys 2 and 3, the overall skill scores, listed in Table 5, confirm that the best configuration is the experiment HG2-T11-SKI with an overall skill score of 0.61. The mean separation distance appears to be lower in the HG2-T09-SKI, but as suggested by Liu and Weisberg (2011), the separation distance might not be a good estimate of the trajectory accuracy because looping trajectories may lead to an erroneous decrease of the separation distance, as it is the case of buoy 4.

In this paper, the scientific tools that can be used to aid during an environmental emergencies are utilized and studied, including an evaluation of their performances. The paper presented step by step the improvements that are taken to produce better ocean state prediction. The final outcome is that high-resolution and accurate forecasts of the ocean currents that come from a relocatable ocean model (IRENOM) greatly improve the quality of the operational oceanography products: our best results showed that the skill score in trajectory predictions (and the separation distance) is 0.79 (3.41 km) using the IRENOM model, while using the coarser resolution model model it is 0.28 (11.05 km). Such forecasts and estimates can be given to the competent authorities during environmental emergencies.

First, we introduced the results of the operational support given during the Costa Concordia emergency. We found that a multimodel approach can show some degree of confidence that any single model alone might not. When all the models are in agreement, we might be more confident in the accuracy of the forecasts. Despite being only qualitative comparison, a similar methodology was implemented during the Deepwater Horizon oil spill (Liu et al. 2011b, c) and it has demonstrated to provide some degree of confidence that any single model alone might not. One future solution would be to produce a unified daily product that could be easily used by all responders. We might expect that somehow combining models might improve the trajectory estimates. Few examples on using ocean ensembles in Lagrangian trajectory models are available (Vandenbulcke et al. 2009; Scott et al. 2012; Wei et al. 2013b). Those studies demonstrated that the ensemble can generate important uncertainty information, in addition to predicting the drifter trajectory with higher accuracy than a single ocean model forecast. More extensive new research on using ocean ensembles in Lagrangian trajectory predictions is expected in the near future.

Second, the deployment of drifters showed to be a key instrument to evaluate the models performance, as already demonstrated in other oil spill emergency cases (Caballero 2008; Liu and Weisberg 2011; Liu et al. 2011c Mariano et al.2011). The evaluation of the accuracy of the regional MFS model and subregional WMED and TYRR models is performed by using the drifters trajectory predicted by the oil spill model, MEDSLIK-II. This experiments allowed to calibrate the MEDSLIK-II trajectory model configuration, and we found that the best results are obtained using the Stokes drift and the wind drag correction. It has been found that the effect of wave and wind drag can be of the same order of magnitude of the currents velocity. We showed that using TYRR model with a resolution of 2 km, the lowest separation distance between modeled and observed trajectories is 4.15 km and the highest skill score is 0.59.

Third, we presented how a relocatable modeling methodology can improve the ocean state prediction accuracy. The IRENOM relocatable model has been nested in the MFS operational products and its performances have been evaluated using drifters trajectories. It has been shown that thanks to the possibility to change easily and quickly its configuration, the IRENOM results were of greater accuracy than the results achieved using regional (MFS) or subregional products (WMED and TYRR). We found that the reproduction of the correct topography, taking into account the small islands, that in a low-resolution model, such as MFS, are not correctly resolved, together with the initialization procedure are key configurations settings that should be correctly tuned. Regarding the initialization procedure, the general practice would suggest to choose the spin-up time which allows the ocean model to reach a state of physical equilibrium (Simoncelli et al. 2011). On the other hand, as we found in this work, using a longer spin-up time, the IRENOM model is free to develop its own dynamics, but possibly introducing greater uncertainties when the model moves away from the MFS initial conditions (corrected using data assimilation). Thus, we can conclude that the spin-up time for a relocatable model cannot be decided a priori, but should be a tuneable parameter.

The best configurations of the IRENOM model are obtained using an initialization period of 3 days, a resolution of 2 km that allows the development of the stronger current in the channel between the two islands. Furthermore, the IRENOM currents forced by the wind forcing of SKIRON 0.025° better reproduced the current direction inside the channel. With this configuration (2 km, 3 days spin-up, SKIRON 0.025°), the skill score after 24 h of the MEDSLIK-II simulated trajectory for the buoy located in between the two island (buoy 1) is 0.79 and the separation distance is 3.41 km. On the other hand, with the same IRENOM configuration, two of the buoys were not correctly reproduced. This might be due to the incorrect positioning of vortex structures that affect the buoys movement. We believe that higher prediction skills might be achieved with increased resolution initial/boundary conditions or two-way-nesting to resolve smaller spatial scales. Besides this, the results are still in agreement with the state-of-the-art literature, showing an average separation distance after 24 h of 8.64 km, in agreement with the results found in the literature (Cucco et al. 2012; Huntley et al. 2011; Liu and Weisberg 2011; Röhrs et al. 2012), and the average skill score of 0.61.

Finally, we should remark that few data were available for the models validation during the Costa Concordia emergency case. A specific protocol to acquire data necessary for the models validation in a short time framework should be developed and employed. Rapid environmental assessment methodology for fast understanding of relevant environmental conditions at sea, in order to take tactical decisions, have been extensively developed in the past (Ferreira-Coelho and Rixen 2008) and should be now adapted to the specific scopes of environmental emergencies. Thus, in the future, we should design and validate an innovative methodology for response to oil spill events by using multiplatform observations (satellite, drifters, aerial surveys, and CTD surveys) to improve the models forecast skill. The final aim should be the rapid analysis of environmental and oil pollution conditions in order to set up a specific protocol for response to oil spill pollution at sea.