Hidrológiai Közlöny, 2013 (93. évfolyam)
2013 / 5-6. különszám - LIV. Hidrobiológus Napok előadásai
60 HIDROLÓGIAI KÖZLÖNY 2013. 93. ÉVF.5-6. SZ. 1. táblázat- A vízmintákban mért legfontosabb fizikai, kémiai paraméterek Megjegyzés: a különböző betűk a szignifikáns különbségeket ____________________jelzik.(p<0,05)_____________________ kontrol termál folyó pH 8.70 ± 0.10“ 7.62 ± 0.15b 8.21 ± 0.16c vez.kép. 315.00 ± 2362.60 ± 1166.00 ± (pS/cm) 33.00“ 379.79b 632.32“ 02 tel.% 173.70+17.60“ 89.76 ±11.56b 124.69 ±8.48c la (mg/l) 10.00 ± 7.00“ 0.24 ± 0.20“b 10.31 ±5.23“ C02 (mg/l) 3.87 ± 1.78“ 11.26 ±1.32b 5.02 ± 1.53“ C03 (mg/l) 26.10 ± 4.50 31.80 ±3.54 28.89 ± 1.96 S04 (mg/l) 18.03 ± 5.01“ 121.45 ±26.71b 68.45 ±33.46“ Cl (mg/l) 7.17 ± 0.30“ 602.95 ± 122.37b 227.88 ± 206.03“ KOIsMn (02 mg/l) 0.74 ± 0.57 1.46 ± 0.97 1.42 +0.64 klo.-a (mg/m3) 3.12 ± 0.90“ 0.35 ± 0.54b 0.15b ÖSSZ-P 0.00 ± 0.00 0.02 ±0.02 0.02 + 0.02 nitrit 0.03 ± 0.03 0.05 ± 0.02 0.05 ± 0.04 nitrát 0.11 ± 0.06 0.18 ± 0.23 0.23 ±0.15 nh4* 0.23 ± 0.17 0.73 ± 0.56 0.43 ± 0.20 K-N 0.17 ± 0.09“ 0.69 ± 0.09b 0.26 + 0.18“ Irodalom Felfoldy L. 1981: A vizek környezettana Általános hidrobiológia. Mezőgazdasági Kiadó Budapest, 1-290. Hammer, 0., Harper, D.A.T., Ryan P.D., 2001: PAST: Paleontological Statistics Software Package for Education and Data Analysis. Palae- ontologia Electronica 4(1), 9pp. Németh, J. 1998: A biológiai vízminősítés módszerei. Budapest: KGI, 7: 162pp. Simon E., Puky M., Braun M., Tóthmérész B., 2012: Assessment of the effects of urbanization on race elements of toe bones. Environmental Monitoring and Assessment 184, 5749-5754. 2. táblázat Vízmintákban mért makro és mikro elemek koncentrációja. Megjegyzés: a különböző betűk a szignifikáns különbségeket jelzi k.(p<0,05) kontrol termál folyó Makro elemek P 0.16 ±0.06 0.13 ±0.07 0.18 ±0.09 Ca 33.29 ±5.86“ 140.18 ±20.80b 77.57 ±34.16“ K 0.30 ±0.057“ 16.49 ±4.43b 6.99 ±5.47“ Mg 24.73 ±2.57“ 30.37 ±0.28b 27.33 ± 1.56“ Na 5.05 ± 3.30“ 313.60 ± 56.32b 128.12 ±98.36“ Mikroelemek Ba 0.07 ± 0.01“ 0.22 ± 0.04b 0.12 ±0.03“ Cr 0.46 ±0.12 0.25 ±0.08 0.37 ±0.10 Cu 0.02 ±0.01 0.03 ± 0.01 0.03 ±0.01 Fe 0.77 ± 0.30 0.41 ±0.23 0.41 ±0.20 Li <0,0006“ 1.01 ±0.42b 0.41 ± 0.40“b Ni 0.05 ± 0.01“ 0.17 ± 0.04b 0.11 ± 0.05“b Pb 0.03 ± 0.00 0.04 ± 0.02 0.07 ±0.06 S 14.95 ±9.13“ 161.27 ±47.34b 93.66 ±48.06“b Sr 0.13 ±0.07“ 4.45 ± 1.41b 2.01 ± 1.58“b Zn 0.02 ±0.01 0.09 ± 0.10 0.03 ± 0.01 Simon E., Braun M., Tóthmérész B., 2010: Non-destructive Method of Frog (Rana esculenta L.) Skeleton Elemental Analysis Used During Environmental Assessment. Water Air Soil Pollut 209, 461-471. SPSS Inc. 1998. SPSS for Windows Rel. 8.0. SPSS Inc., Chicago. Köszönetnyilvánítás A publikáció elkészítését a TÁMOP-4.2.2/B-10/1-2010-0024 számú projekt támogatta. A projekt az Európai Unió támogatásával, az Európai Szociális A- lap társfinanszírozásával valósult meg. Analysis of the impact of thermal on receiving river water quality Kundrát J1, Gyulai l\ Mizsei E 1, Braun M 2 and Lakatos Gy1, Simon E ' 'University of Debrecen, TTK, Department of Ecology, 4032. Debrecen, Egyetem tér 1. 2University of Debrecen, TTK, Department of Inorganic and Analytical Chemistry, 4032. Debrecen, Egyetem tér 1. Abstract The impact of thermal on living organism which is used for recreation purposes is a less investigated topic. In 2011 five thermal were assessed which are close to each other in the valley of South-Albania river Lengaricés, The aim of this paper is to study their impact on the river. Beside the five thermal, sample points were designated at the connection point of the river, and additionally one before and after on the river stage. For control, another two fresh water lake were designated far from the primary thermal. In our investigation we measured physical, chemical and element analytical parameters. We observed notable differences between the control and the thermal on the measured physical and chemical parameters. Based on the physical and chemical parameters we observed significant differences among the thermal, these differences were mainly significant at pH, conductivity, phosphorus, nitrite and nitrate. The thermal impact on the recipient river were high in the content of Cl, K, Na, S and Sr. Therefore it can be stated, that the thermal have direct impact on the river Lengarices, influencing its water quality. Keywords: thermal, water chemistry element analytic, water quality
