Hepatotoxic cyanobacterial blooms in the lakes of northern Poland

被引:28
作者
Mankiewicz, J
Komárková, J
Izydorczyk, K
Jurczak, T
Tarczynska, M
Zalewski, M
机构
[1] PAS, Int Ctr Ecol, PL-90364 Lodz, Poland
[2] Univ S Bohemia, CZ-37005 Ceske Budejovice, Czech Republic
[3] Univ Lodz, Dept Appl Ecol, PL-90237 Lodz, Poland
关键词
cyanobacteria; phytoplankton; diversity; microcystin; recreational water; health risk; PPIA; HPLC;
D O I
10.1002/tox.20138
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
The lakes of northern Poland are among the recreational sites most valued by Polish and German holiday makers. Given the socioeconomic importance of these lakes, water quality should be maintained at high levels for such intensive recreational purposes. In 2002 studies of species composition, biomass, and toxin production by phytoplankton and the attendant physicochemical variables were performed in order to assess the risk of cyanobacterial blooms in selected northern lakes: Lakes Jeziorak, Jagodne, Szymoneckie, Szymon, Taltowisko, Siecino, and Trzesiecko. The research showed that total phosphorus (0.1 mg P/L) and total nitrogen (1.5 mg N/L) in the studied lakes almost exceeded the permissible limits for eutrophication of water bodies. Most phytoplankton samples were taken in late summer, when cyanobacteria were expected to reach their highest biomass. At the time of sampling most of the lakes were dominated by oscillatorialean and nostocalean species. Average chlorophyll-a concentration was higher than 10 mu g/L in almost all the lakes studied, which corresponded with an average microcystin concentration in the range of 4-5 mu g/L. The main microcystins in the analyzed samples were dmMC-RR, MC-RR, MC-YR, and MC-LR. The results demonstrated a potential for intensive cyanobacterial blooms to appear during the summer in northern Polish lakes. The levels of cyanobacteria found in the lakes investigated indicated that toxicity had reached the first-alert level according to World Health Organization recommendations. If microcystin-producing cyanobacteria dominate, with a microcystin concentration of 2-4 mu g/L, symptoms of toxicity can appear in the swimmers most sensitive to exposure. Analysis of cyanobacterial assemblages in northern Polish lakes also indicated a significant presence of Aphanizomenon species including a Scandinavian species, A. skujae (Skuja) Kom.-Legn. & Cronb. Future investigations of Polish lakes also should assess neurotoxins and study the biology of their producers. This study was the first attempt to evaluate the potential danger of toxic cyanobacterial blooms in the lakes of northern Poland. (C) 2005 Wiley Periodicals, Inc. Environ Toxicol 20: 499-506, 2005.
引用
收藏
页码:499 / 506
页数:8
相关论文
共 36 条
[1]  
[Anonymous], 2001, CYANOTOXINS OCCURREN, DOI DOI 10.1007/978-3-642-59514-1
[2]  
BELL S.G., 1996, AGR CHEM ENV ISSUES, P109
[3]   RELATIONSHIP BETWEEN BODY SIZE OF FILTER-FEEDING CLADOCERA AND MAXIMUM SIZE OF PARTICLE INGESTED [J].
BURNS, CW .
LIMNOLOGY AND OCEANOGRAPHY, 1968, 13 (04) :675-&
[4]   Health effects of toxin-producing cyanobacteria: "The CyanoHABs" [J].
Carmichael, WW .
HUMAN AND ECOLOGICAL RISK ASSESSMENT, 2001, 7 (05) :1393-1407
[5]  
Carmichael WW, 1997, ADV BOT RES, V27, P211
[6]   Health risks caused by freshwater cyanobacteria in recreational waters [J].
Chorus, I ;
Falconer, IR ;
Salas, HJ ;
Bartram, J .
JOURNAL OF TOXICOLOGY AND ENVIRONMENTAL HEALTH-PART B-CRITICAL REVIEWS, 2000, 3 (04) :323-347
[7]   Cyanobacterial toxins, the perception of water quality, and the prioritisation of eutrophication control [J].
Codd, GA .
ECOLOGICAL ENGINEERING, 2000, 16 (01) :51-60
[8]   Cyanobacterial toxins: risk management for health protection [J].
Codd, GA ;
Morrison, LF ;
Metcalf, JS .
TOXICOLOGY AND APPLIED PHARMACOLOGY, 2005, 203 (03) :264-272
[9]  
Falconer IR, 1999, ENVIRON TOXICOL, V14, P5, DOI 10.1002/(SICI)1522-7278(199902)14:1<5::AID-TOX3>3.3.CO
[10]  
2-S