RADIONUCLIDES IN OF THE : SPECIES-SPECIFICITY, SEASONALITY, SIZE- AND AGE-DEPENDENT FEATURES OF ACCUMULATION *

A.Ye. Kaglyan **1, D.I. Gudkov 1, V.G. Klenus 1, L.P. Yurchuk 1, A.B. Nazarov 2, N.A. Pomortseva 1 , Z.O. Shirokaya 1, N.L. Shevtsova 1

1InstituteofHydrobiology,Kyiv, 2ChernobylSpecializedEnterprise,Chernobyl,Ukraine

Abstract. The results of studies during 2006-2013 of fish from 12 water bodies with different hydrological mode and levels of radioactive contamination within the Chernobyl exclusion zone are presented. The specific activity of 90 Sr and 137 Cs for 17 species of fish, concerning various ecological groups was estimated. The fish of stagnant water bodies of the Chernobyl exclusion zone continue to be characterized by the high concentration of 90 Sr and 137 Cs. Radionuclide specific activity in fish of closed water bodies of the Chernobyl exclusion zone during our studies in all cases exceeded maximal permissible levels, according to the standards, accepted in Ukraine for fish production: in 53-2892 times on 90 Sr and in 6-212 times on 137 Cs. In fish of the riverbed sites of the River within the Chernobyl exclusion zone some single cases which exceeded the maximal permissible level on 137 Cs, mainly the predatory fish, were registered. The analysis of radionuclide specific activity data in fish of various size, weight and age groups on an example of the common rudd and the European perch from Glubokoye Lake has allowed the revelation of a dependence of 90 Sr and 137 Cs accumulation on the weight of body and the age of . Key words : Chernobyl exclusion zone, radioactive contamination, aquatic ecosystems, fish, 90 Sr, 137 Cs DOI: 10.21175/RadJ.2016.02.020

Vershina, Glubokoye, Azbuchin and Dalekoye); (2) waterbodywithslowwaterexchange(ChernobylNPP 1. INTRODUCTION cooling pond); (3) relatively closed water bodies Radionuclide migration in river systems’ basins is (Yanovsky and Novoshepeletsky crawls, Krasnensky mainly determined by the dynamics of hydrological former river bed within inside section of the dam and biochemical processes of substances turnover in constructions); (4) slow flowing water body the environment. Along with the deposition of (Krasnenskyformerriverbedwithinoutsidesectionof radionuclides in the bottom sediments by way of the dam constructions, that has a channel connection sedimentation and sorption and their precipitating withthePripyatRiver);(5)opencrawlsofthePripyat together with suspended matter, there is another River (Schepochka and Pripyatsky) and (6) flowing important process of radionuclide distribution in waterobject(thePripyatRiver). freshwater ecosystems, namely their accumulation by Thespecificactivityof 137 Csand 90 Srfor17species hydrobionts.Thespecialattentioninthisissueispaid of fish, concerning the various ecological groups, was to fish, occupying the upper trophic levels in aquatic analyzedbythemethods[1].Theradionuclidespecific biocenosis and routinely caught and ingested as a activitywasmeasuredforawholefishbody.For 137 Cs sourceoffood. specific activity theerrorofmeasurement(confidence 90 The aim of our studies was the estimation of the intervals) made up about 15%, and for Sr specific main doseforming radionuclide (137 Cs and 90 Sr) activity – 20% [2]. We have also developed a rapid 137 90 accumulation by fish species of different ecological method of the specific activity of Cs and Sr groupswithintheChernobylexclusionzone(ChEZ)as determinationinfishontheircontentinscalesandfins wellasthedeterminationofseasonality,sizeandage [3,4].Atthesametimethefishwasstayingalive. The dependentfeaturesofradionuclideconcentration. researchdatawereprocessedstatisticallywiththehelp ofcomputingsoftwareMicrosoftExcel2007,Statistica 5.5. Among predatory fish (obligate and facultative 2. MATERIALSANDMETHODS ichthyophagous), the fish that were analyzed were The material was represented by fishes, sampled pikeperchSander lucioperca L.(trophiclevel(TL)4.0 during2006–2013from12waterbodieswithdifferent – http://fishbase.org ), Wels glanis L. hydrological regime and level of radioactive (TL 4.4), chub Leuciscus cephalus L. (TL 2.7), asp contamination within the ChEZ. Depending upon Aspius aspius L.(TL4.5),pikeEsox luceus L.(TL4.1), waterexchangeintensitythewaterbodiesweredivided Europeanperch Perca fluviatilis L.(TL4.4)andrazor into six conventional groups: (1) closed lakes (lakes fishPelecus cultratus L.(TL3.6).Amongpreyfish,we ______ *ThepaperwaspresentedattheThirdInternationalConferenceonRadiationandApplicationsinVariousFieldsofResearch(RAD 2015),Budva,Montenegro,2015. **[email protected] 111

A.Ye.Kaglyanet al. ,RadionuclidesinFishoftheChernobyl..., Rad. Applic. ,2016,1,2,110113 studied zooplanktonophagous as blue bream Ballerus 1 and varied between 0.02 and 0.38. In the closed ballerus L. (TL 3.2) and bleak Alburnus alburnus L. Yanovsky and Novoshepeletsky crawls, Krasnensky (TL 2.7); bentophagous as crucian carp Carassius formerriverbedwithininsideandoutsidesectionsof carassius L. (TL 3.1), Prussian carp Carassius gibelio the dam constructions, lakes Glubokoye, Vershina, Bloch (TL 2.5), bream Abramis brama L. (TL 3.1), Azbuchin, Dalekoye, the 90 Sr/ 137 Cs specific activity silver bream Blicca bjoerkna L. (TL 3.2), tench Tinca ratio in prey fish species attained as much as 1.78– tinca L. (TL 3.7), roach Rutilus rutilus L. (TL 3.0), 50.00,andinpredatoryfish0.382.11. common carp Cyprinus carpio L. (TL 3.1), and also phytophagous as common rudd Scardinius 5 prey erythrophthalmus L.(TL2.9).Theageoffishesvaried predatory between 1 and 12 years. The absorbed dose rate for 4 fishes was estimated with the help of the software package[5]. 3 Cs ratio

137 2 Sr/ 90 3.RESULTSANDCONCLUSIONS 1

137 90 The specific activity of Cs and Sr in predatory 0 fishspeciesofthePripyatRiver(6th group)duringthe a b c d e f g h Water bodies survey period made up respectively: 22224 Bq kg 1 (here and further on the specific activity is given per 90 137 one kilogram of wet weight) and 116 Bq kg 1, and in Figure1. Sr/ Csratioinpreyandpredatoryfishspeciesof 1 waterbodiesintheChEZ:(a)Krasnenskyformerriverbed prey fish species 1260 and 313 Bq kg . In the withininsidesectionofthedamconstructions;(b)Glubokoye th Schepochka and Pripyatsky crawls (5 group) the Lake;(c)YanovskyCrawl;(d)AzbuchinLake;(e)Krasnensky contentof 137 Csinbothpredatoryandpreyfishspecies formerriverbedwithinoutsidesectionofthedam hardlydifferedfromtherespectivevaluesforfishesof constructions;(f)SchepochkaCrawl;(g)ChernobylNPP thePripyatRiver;however,theconcentrationof 90 Srin coolingpondand(h)thePripyatRiver ichthyophagous was considerably higher 11 119Bqkg 1 ,andinprayfishes41221Bqkg 1. Besides,thePripyatskyCrawlandformerriverbeds Theutmostvaluesof90 Srspecificactivityexceeded withslowwaterexchangeprobablyaccumulatesoluble, more than 6 times the permissible level (PL ) of this biologically available forms of 90 Sr, which at present radionuclide for fish products in accordance with the still come from the radionuclidecontaminated currentUkrainianstandards:150Bqkg 1for 137 Csand catchmentareaandareinvolvedinthebiogeochemical 35Bqkg 1for 90 Sr[6].Thehigherlevelsofradionuclide circulation of matter, concentrating in the biotic specific activity, determined in fish of theKrasnensky componentsofwaterecosystems. formerriverbed(4 th group)45911204Bqkg 1of 137 Cs Ourownsurveyhasconfirmedthatinmostoflotic and973179Bqkg 1of 90 Sr,areregistered.Asregards environments, the total content of 137 Cs in fishes the fish fauna of the Yanovsky Crawl and Krasnensky significantlyexceedsthisvaluefor 90 Sr,whichcomplies former Pripyat River bed (3 rd group), the content of with the traditional concept of the ratio of 137 Cs and 90 Sr in prey fish species exceeded the PL radionuclides,whichcametowaterbodieswithglobal respectively 2.322.6 and 24.8–333.1 times, and in precipitations. However, such pattern is not always predatory species the exceeding made up respectively observed in fishes of the slow runningrivers’sections 6.831.7and17.9235.0time.Inthefishofthecooling within the ChEZ borders, which are distinguished by pond (the 2 nd group) 137 Cs content was registered to the particular ratio of physical and chemical exceed the PL 4.672.7 times, and 90 Sr only 1.221.7 radionuclideforms,causedbyaccidentalemissions[1, times,whichwasassociatedwiththeincreasedflowage 8,12]. ofthiswaterbody[711].Evenmorecontaminatedwith AlmostinallthesurveyedwaterbodiesoftheChEZ radionuclides is the fish fauna in lakes Glubokoye, the most abundant species, also marked by high st Azbuchin, Dalekoye and Vershina (the 1 group), radionuclideaccumulationlevels,includethecommon 137 90 where the specific activity of Cs and Sr are rudd as the prey fish speciesandtheEuropeanperch registered in pray fishes, respectively, 44031859 and as the predatory fish species. These species can be 1 2490101217Bq kg , and in predatory fishes 1730 considered to be the reference species and the most 1 22030and148915584Bqkg . prospectiveonesforradioecologicalmonitoringofthe It is necessary to note, that while 137 Cs is mainly ChEZ freshwater ecosystems and for estimating the accumulated in the muscular tissue of fish, almost all leveloffishfaunacontaminationby 90 Srand 137 Cs[13]. 90 amount of Sr is concentrated in its inedible bone Analysis of data obtained during 20072013 90 137 tissue – scales and skeleton. The Sr/ Cs ratio in indicates that the specific activity of 137 Cs and 90 Sr in predatory fishes of the Pripyat River made up 0.06 theichthyofaunaofalmostallwaterbodiesoftheChEZ 0.52, and in prey fishes 0.150.37 was represented continues to decline gradually. The exceptions are (fig.1 ). closedwaterbodies,locatedontheterritoryoftheleft In the Schepochka Crawl, such ratio for bank dammed floodplain of the Pripyat River ichthyophagous reached 0.251.33, and for prey fish (Glubokoye Lake, Vershina Lake etc.), where with a species rose to 1.012.46. In the cooling pond, the gradual decrease of 137 Cs and 90 Sr specific activity in 90 Sr/ 137 Csratioforallstudiedfishspecieswaslessthan ichthyophagous fish, the reduction of both radionuclidesinpreyfishoccursmuchmoreslowlyor 112

A.Kaglyanet al. ,RadionuclidesInFishOfTheChernobyl..., Rad. Applic. ,2016,1,2,111114 is not observed at all (fig. 2 and 3). The seasonal regards the European perch, higher 90 Sr content dynamics in accumulation by representatives of prey comparedto 137 Csisnoticedinthefirstyearsofitslife; and predatory fish species, with maximum values of however;inthefollowingyears,probablywithgradual radionuclide concentrations during the summer prevalence of small fish in its feeding, 137 Cs specific period,isdetermined. activity begins to exceed that of 90 Sr, which In order to survey radionuclide accumulation by accumulation,onthecontrary,slowsdownwithage. differentagegroupsoffishesintheclosedwaterbodies oftheChEZ,100samplesofthecommonruddandthe 35000 90 Sr EuropeanperchweretakenfromGlubokoyeLake.The 137 Cs 30000 agegroupsconsistedof320specimens. y = 10527x 0,1181

25000 25000 90 Sr 137 Cs

20000 20000

15000 15000

10000 10000 Specific activity, Bq/kg

Specificactivity, Bq/kg y = 5019,7x 0,129 5000 5000

0 0 2007 2008 2009 2010 2011 2012 2013 0 40 80 120 160 200 240 280 Years Weight, g

Figure2.Dynamicsofaverageannualspecificactivityof radionuclidesforpreyfishspecies(thecommonruddas Figure4.Weightdynamicsofradionuclidespecificactivityfor example)inGlubokoyeLake thecommonruddinGlubokoyeLake

Evaluationofradionuclidespecificactivityinfishes 25000 90 Sr ofdifferentsizeandweightgroupsmadeitpossibleto 137 Cs 90 137 findthat Srand Csaccumulationdependuponthe 20000 body weight of the common rudd and the European perchinGlubokoyeLake (fig.4and5). y = 5317,6x 0,5089 15000

20000 90 Sr 137 Cs 10000

15000 Specific activity, Bq/kg activity, Specific 5000 y = 7651,5x 0,1891

10000 0 0 1 2 3 4 5 6 7 8 9 Age, years Specific activity, Bq/kg activity, Specific 5000 Figure5.Agedynamicsofradionuclidespecificactivityforthe EuropeanperchinGlubokoyeLake

0 2007 2008 2009 2010 2011 2012 2013 Years Theabsorbeddoserateestimationshowedthatthe highest radiation doses in the ChEZ water bodies are Figure3.Dynamicofaverageannualspecificactivityof obtainedbyfishesinhabitingthelakeecosystem,where radionuclidesforpredatoryfishspecies(theEuropeanperch thisvaluefordifferentfishspeciesvariesbetween13.0 asexample)inGlubokoyeLake (pelagicspecies)to294.0(bottomspecies)Gyh 1. More intensive accumulation of radionuclides in Theinternaldosecontributionbytheincorporated the early periods of fish life is rather marked. The radionuclides changes from 3.6 to 33.2% of the total 90 approximationoftheobtaineddata,withthestatistical radiation dose. The incorporated Sr contributions significancebeingcomparativelylow,makesitpossible intotheinternalradiationdosemakeup87.194.5%for though to detect specific differences in dynamics of pray fish and 70.878.5% for predatory fish. In the radionuclide accumulation by nonpredator and PripyatRivertheabsorbeddoseratemakesup0.011 1 predator fish species with their size and weight 0.013forpelagicfishspeciesand0.0230.042Gyh parameters increasing. These peculiarities are most forbottomspecies. significantly marked and have high approximation Therefore,thenaturalselfpurificationprocessesin reliability in the fish age–radionuclideaccumulation the reservoirs within the ChEZ are extremely slow, relation (fig. 5). The typical increase in 90 Sr and 137 Cs which causes the specific activity of the main dose specificactivityhasbeenobservedinthecommonrudd formingradionuclidesinfishspeciesofthemajorityof with preferred 90 Sr accumulation, evidently, at the lakes,formerriverbedsandcrawlstoremainatquitea early stages of its postembryonic ontogenesis. As high level. The radionuclides content in fishes of the 113

A.Ye.Kaglyanet al. ,RadionuclidesinFishoftheChernobyl..., Rad. Applic. ,2016,1,2,110113 Pripyat River is considerably lower than the ratio.StateStandardofUkraineISO107032001Kyiv: permissiblelevels,beinginforceinUkraine,andonly State Committee for Technical Regulation and in several cases exceeds these values insignificantly Consumer Policy of Ukraine, 2003, 15p. (in (mainlyinpredatoryfishes). Ukrainian). 3. A.Ye. Kaglyan, D.I. Gudkov, Patent UA №106547, The 90 Sr content in fishes of the slowly flowing Ukraine, GO1T 1/16 (2006.01) “Method of assessment Schepochka Crawl exceeds the PL in 23 times at an of specific activity of radionuclides in organs and average.Theradionuclidespecificactivityinfishofthe tissues of fishes on the basis of their concentration in Yanovsky and Novoshepeletsky crawls, Krasnensky scale”,Bulletin,No17,2014(in Ukrainian) . formerriverbedwithininsideandoutsidesectionsof 4. A.Ye. Kaglyan, D.I. Gudkov, V.G. Klenus et al., Patent the dam constructions, lakes Glubokoye, Vershina, UA№107611,Ukraine,GO1T1/16(2006.01)“Method of assessment of specific activity of radionuclides in Azbuchin,Dalekoyeexceedsthe PL in3212timesfor organs and tissues of predator fishes ( Percidae and 137 90 Cs,andin32892timesfor Sr.Thespecificactivity Esocidae families)onthebasisoftheirconcentrationin of 90 Srи 137 Csinpreyfishes(asitcanbeseenforrudd fins”,Bulletin,№2,2015 (in Ukrainian) . in Glubokoye Lake) rises approximatelyin1.7and1.5 5. ERICA Assessment Tool 1.0. The integrated approach timeswiththefishageincreasingfrom1to9years,and seekstocombineexposure/dose/effectassessmentwith in predator fishes (as it can be seen for perch in risk characterization and managerial considerations Glubokoye Lake) – 90 Sr rises in 1.4times, and 137 Cs– (VersionNovember2012)(http://www.ericatool.com). upto3.0timesbythe9 th yearoflife.Suchfishspecies 6. Ministry of Health Protection of Ukraine, National Commission for Radiation Protection of Ukraine as rudd and perch can be used as indicators of 137 90 90 committee “ Cs и Sr content permissible levels in radioactivecontaminationofwaterbodiesby Srand foodproductsanddrinkingwater(PL97)”,Kyiv,1997. 37 Cs respectively. The total absorbed dose range in (in Ukrainian). fishesoflakesGlubokoyeandVershinamadeup13.0 7. D.I. Gudkov, M.I. Kuzmenko, S.I. Kireyev et al., 294.0,YanovskyCrawl1.6027.7,SchepochkaCrawl “Radionuclides in Components of Aquatic Ecosystems 0.040.12andthePripyatRiver0.010.04Gyh 1. oftheChernobylAccidentRestrictionZone”in20Years In the majority of Ukrainianwaterbodies,located aftertheChernobylAccident:Past,PresentandFuture. E.B. Burlakova, V.I. Naidich, Eds. New York: Nova outside the ChEZ borders, this value does not exceed SciencePublishers,2006,pp.265–285. 1 0.01Gy h . Taking into account that for fishes of 8. D.I.Gudkovetal.,“Patternsofthemaindoseforming closed, relatively closed and slowly flowing water radionuclidesaccumulationbyfishinthewaterbodies bodies, 90 Sr is responsible for more thanahalfofthe within the exclusion zone”, Chernobyl Scientific total internal absorbed dose rate, we can come to a Journal, The Exclusion Zone Ecological State Bulletin , conclusion that 90 Sr is the main doseforming №2,2007,pp.34–43 (in Ukrainian). radionuclide for fish in the majority of water bodies 9. D.I. Gudkov et al., “Dynamics of content and withinChEZatpresent. distributionofthemaindoseformingradionuclidesin fishes of the Chernobyl NPP exclusion zone”, Hydrobiological Journal , 2008, №3, pp. 95–113. (in Acknowledgement : This study was supported by Russian) . the National Academy of Sciences of Ukraine and by 10. A.Ye. 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