32Piotr Kamiński et al.StreszczenieZamierzeniem pracy było określenie bazy ekofizjologicznejdla rozwoju piskląt bociana białego Ciconia ciconia,w zróżnicowanych środowiskach Polski, w sezonie lęgowym2006. Oznaczono koncentracje Ca, Mg, Fe, Zn, Cu, Mn, Co,Cd i Pb we krwi piskląt rozwijających się w regionacho różnych podstawach biogeochemicznych. Krew pobieranoz żyły skrzydłowej od piskląt ze środowisk czystych (Kłopot;52°07'56,3'' N, 14°42'10,4'' E; kontrola), terenów podmiejskichZielonej Góry (52°02'03,7'' N, 14°57'24,7'' E), na tereniehuty miedzi i ołowiu k/Głogowa (51°39'32,6'' N,16°04'49,9'' E) i na Pomorzu k/Słupska (54°38'34,5'' N,17°32'31'' S). Przebadano 182 pisklęta, w wieku 19-56 dni,pochodzące z 33 gniazd. Poziom pierwiastków we krwioznaczano metodą AAS.Stwierdzono różnice koncentracji wszystkich analizowanychpierwiastków, z wyjątkiem wapnia, w badanych środowiskach.Stwierdzono wysoki poziom kadmu w regioniepomorskim i na terenach skażonych k/Głogowa, chociażstężenie ołowiu było wysokie tylko w tym regionie skażonym.Zanotowano również wysoki poziom Ca, Mg i Fe naPomorzu i w okolicach Głogowa. Koncentracja pozostałychbadanych pierwiastków była wysoka przeważnie w regionieskażonym i na terenach podmiejskich, chociaż poziom Cui Mn był też wysoki w regionie pomorskim. Może to świadczyćo wysokim zanieczyszczeniu badanego regionu naPomorzu. Można więc wnioskować o istnieniu procesówantropopresji na tych terenach w niedalekiej przeszłości,która zapewne spowodowała tam bioakumulację metalitoksycznych. Ma to istotne znaczenie lokalne, co pozostajew związku z procesami ekofizjologicznymi stwierdzonymiprzez nas wcześniej u piskląt bociana z tych terenów. Możemywnioskować o ważności badań enzymatycznych krwipiskląt, które mogą dać odpowiedź nt. kondycji piskląt bocianarozwijających się w tych środowiskach pomorskich.Key words: chemical elements, heavy metals, blood, chicks, White Stork, Ciconia ciconiaSłowa kluczowe: pierwiastki chemiczne, metale ciężkie, krew, pisklęta, bocian biały, Ciconia ciconiaINTRODUCTIONAccording to the last investigations it can be statedsignificant changes in the number <strong>and</strong> dynamics ofWhite Stork population in Pol<strong>and</strong> <strong>and</strong> West Europeparticularly, <strong>and</strong> increases in the mortality rateamongst chicks, which have been linked to the pollutionof their environment by heavy metals [1, 2, 3].Toxic heavy metals have their unfavourable impactupon the course of lipoperoxidation processes in livingbird. Research by these authors has linked concentrationsof toxic metals in the organs of birds with highermortality amongst chicks, <strong>and</strong> with a fall in fecundity.This indicates a necessity to determine the stages <strong>and</strong>mechanisms by which pollutants enter birds during thetime of their development in the nest. Metals act toincrease the mortality rate of birds, reducing productivityof their populations in types of regions. In addition,they may give rise to many pathological abnormalities,<strong>and</strong> to improper functioning of immunological system[2, 4, 5, 6, 7]. Unfortunately, there is the lack of thesestudies in field conditions. E.g. [8] investigated thereduction of erythrocyte catalase <strong>and</strong> superoxide dismutaseactivities in male inhabitants of cadmiumpollutedareas in Jinzu river (Japan). We can also findseveral research of more widespread, generally, i.e.biogeochemical <strong>and</strong> element-enzyme interactions.Thus some papers have analyzed biogeochemical interactionsaffecting hepatic trace elements in aquaticbirds [9].Among others, [10] studied metal-metal interactionsin rat liver <strong>and</strong> kidney <strong>and</strong> their relations withthioneins activity. The remaining papers assume effectsof laboratory <strong>and</strong> field investigations concerning toxicmetals intoxication during particular physiologicalperiods in birds <strong>and</strong> mammals. E.g. [1] studied ecologicaldeterminations of trace elements in blood collectedfrom birds feeding in the area affected by toxicspill.The aim of this study was to compare the ecophysiologicalbasis for developing stork chicks in variousPol<strong>and</strong> environments. Thus we examined the level ofphysiological elements Ca, Mg, Fe, microelements Zn,Cu, Mn, <strong>and</strong> Co, <strong>and</strong> toxic heavy metals Cd <strong>and</strong> Pb inthe blood of growing chicks, which all were grows <strong>and</strong>feeds in the variety of environmental pollution. Theseregions were also represents the variety of biogeochemicalbackgrounds for soil <strong>and</strong> foraging properties.STUDY AREAThe investigations were carried out in stork breedingseason of 2006. Blood samples were collected fromyoung storks developing in relatively pure environment<strong>and</strong> treated as a control (Kłopot village with absolutelylack of any manufactures in the radius of 150 kmaround [11]; SW Pol<strong>and</strong> (52°07'56,3'' N, 14°42'10,4''E). It was compared with Czarnowo (52°02'03,7'' N,14°57'24,7'' E), a village located 20 km away from
Chemical elements in the blood of White Stork Ciconia ciconia chicks in differentiated regions of Pol<strong>and</strong> 33Zielona Góra (51°56'26,1'' N, 15°30'38,9'' E; SW Pol<strong>and</strong>),<strong>and</strong> treated as suburbs, <strong>and</strong> near Głogów(51°39'32,6'' N, 16°04'49,9'' E; SW Pol<strong>and</strong>), where acopper smelter is situated, with copper manufacture. Itproduced copper <strong>and</strong> lead from lead fields. Głogówplant copper leads an active proecological activity.Green fields constitute about 50% of protective areasof this manufacture complex. The forests present 32%of this area. Acid soils are subjected by calcification.One of numerous proecological ventures of the manufacturewas desulphuring installation <strong>and</strong> modernize ofsulphur acid manufacture. These innovations havecontributed towards rapid decrease of sulphur dioxide.Now the process of modernization of lead departmentis continued. We have also conduct our research inCecenowo, a small <strong>and</strong> relatively pure Pomeranianvillage near Słupsk (N Pol<strong>and</strong>; 54°38'34,5'' N,17°32'31'' S).MATERIAL AND METHODSIn total 91 White Stork chicks from 33 nests weresurveyed in 2006. The age of birds varied from 19 upto 54 days after hatching. For elimination of diurnalrhythm changes all examinations were started at 10 <strong>and</strong>ended at 12 am. Samples of investigated wing venousblood were taken for analyses of chemical elementconcentration. The content of elements was then determinedwith use of Perkin-Elmer atomic absorptionspectrophotometer [12]. St<strong>and</strong>ard curves were preparedusing st<strong>and</strong>ardized Merck samples. Concentration ofelements were given in terms of µg*g -1 d.w. (ppm). Wecollected blood samples via veni-puncture of the brachialvein of stork chicks. They were retrieved fromthe nest <strong>and</strong> placed into individual ventilated cottonsacks. Blood (5 ml) was collected using 5 ml syringewashed up with EDTA. Samples were kept in a chilledcooler before transporting to the laboratory. After centrifugation,plasma samples were frozen at -20 o C <strong>and</strong>stored until analysis. Our behavioral observations aswell as physical examinations of the birds suggestedthat all of them were physically healthy.Statistical Analysis. The results are expressed asmean ± S.D. Significant differences among the meanswere measured using a multiple range test at min.P
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