Episode Analysis of Deposition of Radiocesium from the Fukushima Daiichi Nuclear Power Plant Accident

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<ul><li><p>Episode Analysis of Deposition of Radiocesium from the FukushimaDaiichi Nuclear Power Plant AccidentYu Morino,* Toshimasa Ohara, Mirai Watanabe, Seiji Hayashi, and Masato Nishizawa</p><p>Center for Regional Environment Research, National Institute for Environmental Studies, 16-2, Onogawa, Tsukuba, Ibaraki,305-8506, Japan</p><p>*S Supporting Information</p><p>ABSTRACT: Chemical transport models played key roles in under-standing the atmospheric behaviors and deposition patterns ofradioactive materials emitted from the Fukushima Daiichi nuclearpower plant after the nuclear accident that accompanied the greatTohoku earthquake and tsunami on 11 March 2011. However, modelresults could not be sufficiently evaluated because of limitedobservational data. We assess the model performance to simulate thedeposition patterns of radiocesium (137Cs) by making use of airbornemonitoring survey data for the first time. We conducted ten sensitivitysimulations to evaluate the atmospheric model uncertainties associatedwith key model settings including emission data and wet depositionmodules. We found that simulation using emissions estimated with aregional-scale (500 km) model better reproduced the observed 137Csdeposition pattern in eastern Japan than simulation using emissionsestimated with local-scale (50 km) or global-scale models. In addition, simulation using a process-based wet deposition modulereproduced the observations well, whereas simulation using scavenging coefficients showed large uncertainties associated withempirical parameters. The best-available simulation reproduced the observed 137Cs deposition rates in high-deposition areas(10 kBq m2) within 1 order of magnitude and showed that deposition of radiocesium over land occurred predominantlyduring 1516, 2023, and 3031 March 2011.</p><p> INTRODUCTIONEnormous quantities of radionuclides were released into theatmosphere after the nuclear accident at the Fukushima Daiichinuclear power plant (FDNPP) on 11 March 2011.13 Toestimate the atmospheric behavior of the radionuclides,particularly iodine-131 (131I), and cesium-137 (137Cs), atmos-pheric modeling studies were conducted over local,4 region-al,57 and global2,8 scales. Observational data played a criticalrole in the assessment of model performance. Previous modelsimulations used data primarily from surface monitoring ofatmospheric concentrations and deposition. However, monitor-ing of atmospheric deposition did not start until 18 March2011, and thus model performance could not be evaluated forthe period before 18 March, the period when the largestradiocesium emissions presumably occurred.1</p><p>Recently, data from an airborne monitoring surveyconducted by the Ministry of Education, Culture, Sports,Science, and Technology became available.9 In this study, wemade the first use of these data to assess the performance ofmodels of radiocesium deposition patterns. The airborne surveydata have two advantages for the evaluation of chemicaltransport models. One is the high spatial resolution. Combinedanalysis of this highly resolved observational data withmodeling results helps to reveal the detailed mechanism ofradiocesium deposition. The other advantage is the wide data</p><p>coverage over eastern Japan. Total radiocesium deposition overland in Japan can be estimated from the airborne monitoringdata, and the fact that the simulated total deposition ofradiocesium over land can be validated adds credibility to the137Cs budget analysis.In addition, by using the high-resolution observational data,</p><p>we can assess the suitability of different model settings forcritical modules. Because there was some uncertainty inselecting model settings (e.g., emission and wet deposition),we conducted nine sensitivity simulations and assessed themodel performance. These simulations gave us insight intouncertainties and plausible model settings for simulation ofradiocesium deposition, although a comprehensive uncertaintyanalysis is beyond the scope of this study.We then used the validated model to assess the radiocesium</p><p>budget and deposition mechanisms. Budget analysis andepisode analysis had previously been reported.57 However,the simulated deposition patterns of these analyses were notverified, owing to lack of observational data. Our analysisexplains the mechanism by which the observed high-deposition</p><p>Received: November 12, 2012Revised: February 1, 2013Accepted: February 7, 2013Published: February 7, 2013</p><p>Article</p><p>pubs.acs.org/est</p><p> 2013 American Chemical Society 2314 dx.doi.org/10.1021/es304620x | Environ. Sci. Technol. 2013, 47, 23142322</p><p>pubs.acs.org/est</p></li><li><p>areas formed, and thus it may be the basis for future studies onradiocesium deposition.</p><p> METHODOLOGYSimulation Models. We simulated distributions of 137Cs by</p><p>using the Weather Forecast and Research Model version 3.110</p><p>and a 3D chemical transport model, Models-3 CommunityMultiscale Air Quality (CMAQ),11 for the period from 10March to 20 April 2011. We conducted one standard-casesimulation (STD) and nine sensitivity simulations assummarized in Table 1. The model domain is shown in Figure</p><p>1. The prefectures are indicated by numbers in Figure 1 (e.g.,P1 for Iwate Prefecture and P5 for Fukushima Prefecture). Thebasic model settings are described in our previous article,5</p><p>although the horizontal resolution of the model used in thisstudy (3 km) was finer than that in our previous study (6 km),and emission data were updated to the latest estimate from theJapan Atomic Energy Agency (JAEA).7</p><p>We conducted simulations with three sets of emission data:the estimates from JAEA,7 the Norwegian Institute for AirResearch (NILU),2 and Tokyo Electric Power Company(TEPCO)3 (Figure S2 of the Supporting Information). Allthree emission estimates are based on inversion methods usingsimulation models and observational data. The JAEA analysiscombined local- and regional-scale models, whereas NILU useda global-scale model, and TEPCO used a local-scale model. Themodel used for the JAEA estimate used a mesh size of 3 km,and that of TEPCO was 1 km. NILU used an objectiveinversion, whereas JAEA and TEPCO estimated release ratesfrom a combination of observational data and atmosphericsimulations under the assumption of a unit release rate. JAEAfirst used observed concentrations of radiocesium in air at 10measurement sites1 and then modified their estimate by usingthe air dose rate at three monitoring sites in FukushimaPrefecture4 and surface deposition rates at 19 monitoring sitesover eastern Japan.7 NILU used air concentrations at 45monitoring stations (6 in Japan, 5 in the northern PacificOcean, 12 on the North American continent, and 12 inWestern Europe) and surface deposition rates at 46 monitoringstations over Japan7 and in Tokai-mura in Ibaraki Prefecture.TEPCO used the air dose rate measured from a monitoring carthat moved around the FDNPP, and estimated emission ratesof 131I, 134Cs, 137Cs, and noble gases by assuming emissionratios for the respective nuclides. TEPCO estimated emissionrates during 1231 March 2011, and thus the simulation periodfor the EM3 simulation is 1031 March.We also compared three wet deposition settings. The wet</p><p>deposition modules are described in detail in section S1 of theSupporting Information and briefly described below. In CMAQv4.6, wet deposition rates of accumulation-mode aerosols arecalculated by considering washout time, which is calculatedfrom the ratio of the water content of precipitation and that ofclouds.11 The wet deposition module is process-based, and wetdeposition amounts of aerosols calculated with CMAQ havebeen validated in several previous studies.12,13 We alsoconducted a simulation with the wet deposition module ofthe JAEA model (WD2 case).7 In that model, wet depositionrates are calculated using a scavenging coefficient (), which isa function of the precipitation rate. This wet deposition moduleis an empirical module with fitting parameters included.Simulation with of the JAEA model multiplied by a factorof 10 (WD3 case) was also conducted as shown later.Because the observed diameter of particulate radiocesium</p><p>differs among studies,14 in our previous study we set the meandiameter and standard deviation to 1 m and 1.1, respectively.5</p><p>Recently, observed size distributions of radiocesium havebecome available.15 Activity size distributions of 134Cs and137Cs in aerosols were measured at Tsukuba, a city 170 kmsouthwest of the FDNPP, during 28 April12 May and 1226May 2011. Means and standard deviations of 137Cs aerosoldiameters during the two periods were derived after the datawere fit to log-normal distributions. We used the derived meandiameter (0.65 m) and standard deviation (1.35) in thesensitivity simulation (DD2 case). Aerosol size distributionschange during transport because deposition rates differ byparticle size. However, we did not consider this change in thissimulation.</p><p>Table 1. Setup Parameters Used for Ten Model Simulations</p><p>simulation emissionsa wet depositionb particle diameter</p><p>STD JAEA7 CMAQ11 1 mEM2 NILU2 CMAQ 1 mEM3 TEPCO3 CMAQ 1 mWD2 JAEA Scav. coeff.7 1 mE2W2 NILU Scav. coeff. 1 mE3W2 TEPCO Scav. coeff. 1 mWD3 JAEA Scav. coeff. 10 1 mE2W3 NILU Scav. coeff. 10 1 mE3W3 TEPCO Scav. coeff. 10 1 mDD2 JAEA CMAQ Kaneyasu et al.15</p><p>aJAEA, Japan Atomic Energy Agency; NILU, the Norwegian Institutefor Air Research; TEPCO, Tokyo Electric Power Company. bCMAQ,Community Multiscale Air Quality; Scav. coeff., scavenging coefficient.</p><p>Figure 1. Model domain used in the Community Multiscale AirQuality (CMAQ) simulation. Numbered prefectures: 1, Iwate; 2,Akita; 3, Yamagata; 4, Miyagi; 5, Fukushima; 6, Ibaraki; 7, Tochigi; 8,Gunma; 9, Chiba; 10, Saitama; 11, Tokyo; 12, Kanagawa; 13,Shizuoka; 14, Yamanashi; 15, Nagano; 16, Niigata. The white squareindicates the site of the Fukushima Daiichi nuclear power plant(FDNPP), and the white cross indicates Mount Tsukuba.</p><p>Environmental Science &amp; Technology Article</p><p>dx.doi.org/10.1021/es304620x | Environ. Sci. Technol. 2013, 47, 231423222315</p></li><li><p>Observational Data. Daily deposition rates of 137Cs weremonitored with bulk samplers over 46 Japanese prefecturesstarting on 18 March 2011.16 We assumed that the depositionrates measured with bulk samplers were between the wetdeposition rates and the total deposition rates (i.e., dry pluswet) as in our previous study.5 As radiocesium deposition wasdominated by wet processes, we believe that uncertainties dueto this assumption are small.In addition, we used data from the airborne monitoring</p><p>survey to evaluate model performance; details of the surveymethodology are available elsewhere,9 and a brief description isgiven in section S2 of the Supporting Information. Note that</p><p>the airborne measurements over eastern Japan were conductedfrom June to November 2011, and thus these data cannot bedirectly compared with simulated deposition during MarchApril 2011. However, the measured amount of depositedradiocesium decreased by about 1.8% for reasons other thanphysical attenuation between 31 May2 July and 22 October5 November 2011.9 In addition, radiocesium discharge wasestimated to be small (0.3% of deposited 137Cs) in a forestedcatchment on Mount Tsukuba (Figure 1) over the year afterthe accident, as detailed elsewhere.17 Although no such budgetstudies have been conducted in other areas, the radiocesiumdischarge from a forest is not expected to be large. These</p><p>Figure 2. Observed (Obs) and simulated (Model) 137Cs deposition rates. Upper panels show deposition rates averaged over 18 March20 April(1831 March for EM3) at 15 surface monitoring sites (Figure 1). Both total and wet deposition rates are indicated because the deposition ratesmeasured with bulk samplers were assumed to fall between the wet deposition rates and the total deposition rates, as noted in the text. Middle panelsshow daily deposition rates over the 15 surface monitoring sites. Lower panels show the comparison between 137Cs total deposition on model gridsas determined from airborne monitoring and model simulation.</p><p>Environmental Science &amp; Technology Article</p><p>dx.doi.org/10.1021/es304620x | Environ. Sci. Technol. 2013, 47, 231423222316</p></li><li><p>results suggest that the decrease in radiocesium due tosediment discharge or resuspension from surfaces was smallduring this period.</p><p> RESULTS AND DISCUSSIONModel Validation with Uncertainty Analysis. We</p><p>compared the observed and simulated deposition data at 15surface monitoring stations (Figure 2 and Figure S3 of theSupporting Information; measurements were not conducted inMiyagi Prefecture, owing to damage to an instrument), and theobserved and simulated precipitation rates at meteorologicalmonitoring stations near surface monitoring sites (Figure S4 ofthe Supporting Information). Temporal variations of precip-itation rates were reproduced by the model with a correlationcoefficient averaged over the 16 monitoring stations (Figure S4of the Supporting Information) of 0.50. Simulations STD,EM2, and EM3 reproduced the total deposition of 137Cs during18 March20 April within 1 order of magnitude for most of themonitoring stations, although cases EM2 and EM3 generallyunderestimated and overestimated the observations, respec-tively. Daily deposition rates were also reproduced within 1order of magnitude for the high-deposition cases (1 kBq m2day1) in the STD and EM3 cases, whereas the EM2 caseunderestimated the observation at some sites in the Kantoregion (P6P12 in Figure 1) during 2123 March. Thisunderestimation was mostly associated with the low emissionestimate for 2122 March. Overall, simulations STD, EM2, and</p><p>EM3 reproduced the observations (1 kBq m2 day1) withina factor of 10 for 75%, 38%, and 75%, respectively (part a ofTable 2). By contrast, for observed depositions higher than 0.1kBq m2 day1, the proportion of observations reproduced bysimulations within a factor of 2 (FA2) or 10 (FA10) werehigher in the EM2 case than in the STD case (part b of Table2), because the EM2 case reproduced the observations better inApril suggesting that the JAEA analysis underestimated the137Cs emission rates in April. For low-deposition cases (</p></li><li><p>case reproduced the observed high-deposition areas well(Figure 3); specifically to the northwest of the FDNPP inFukushima Prefecture (P5), the central part of FukushimaPrefecture (Naka-dori region), Gunma and Tochigi prefectures(P7 and P8), the southern and northern parts of MiyagiPrefecture (P4), and the northeastern and southern parts ofIbaraki Prefecture (P6).Note that the performances of the EM2 and EM3</p><p>simulations using surface deposition data were the oppositeof the performances of the same simulations using airbornemonitoring data. This difference was caused by the differencesin the analytical periods. For the model validation using surfacedeposition data, the analytical period was March 18April 20,and deposition over March 2023 and March 3031 mademajor contributions, as detailed in the next section. By contrast,for the model validation using airborne monitoring data, theanalytical period was March 11April 20, and deposition onMarch...</p></li></ul>

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