Coot, Fulica atra, and Mallard, Anas platyrhynchos as indicators of mercury contamination in Zarivar wetland from Western of Iran

2019 ◽  
Vol 11 ◽  
pp. 100197
Author(s):  
Younes Hamesadeghi ◽  
Raouf Rahmani ◽  
Ali Mansouri
2013 ◽  
Vol 450-451 ◽  
pp. 326-333 ◽  
Author(s):  
Łukasz J. Binkowski ◽  
Katarzyna Sawicka-Kapusta ◽  
Józef Szarek ◽  
Emilia Strzyżewska ◽  
Mariusz Felsmann

2011 ◽  
Vol 57 (4) ◽  
pp. 795-803 ◽  
Author(s):  
Karin Nuernberg ◽  
Jaroslav Slamecka ◽  
Jozef Mojto ◽  
Jozef Gasparik ◽  
Gerd Nuernberg

2020 ◽  
Vol 69 (2) ◽  
pp. 175-180
Author(s):  
Grzegorz Kopij

Abstract During the years 2003-2010, the numbers of pairs of waterbird species breeding in the city of Wrocław (293 km2) were assessed. The city is situated in Odra valley, where four smaller rivers join it. The city abandons in oxbows, gravel and sand, and clay pits and other water bodies. In total, 20 waterbird species were recorded as breeding in Wrocław. The most common were Anas platyrhynchos (145-212 pairs), and Fulica atra (70-104 pairs). Relatively common were also the Gallinula chloropus (28-37 pairs), Rallus aquaticus (9-25 pairs) and Cygnus olor (9-11 pairs). For each remaining species less than 10 pairs were recorded. Among rare species, the following were recorded as breeding in Wrocław: Grus grus, Mergus merganser, and Porzana porzana. In the few recent decades, the increase in the number of breeding pairs was recorded for Anas platyrhynchos and Cygnus olor; while a parallel decrease was recorded for Fulica atra, Gallunula chloropus, Chroicocephalus ridibudnus, and Tachybaptus ruficollis. Species such as the Aythya fuligula, Aythya ferrina, grebes, gulls and terns avoid the city. Some of them even ceased to breed (Anas quarquedula, Anas clypeata and Botaurus stellaris). The city plays an important role in protecting water bird species such as Grus grus, Cygnus olor, Porzana porzana and Alcedo atthis.


Ornis Svecica ◽  
2008 ◽  
Vol 18 (3–4) ◽  
pp. 135-225 ◽  
Author(s):  
Leif Nilsson

Regular midwinter counts of waterfowl (included in the International Midwinter Counts, IWC, organized by what is now Wetlands International) has been undertaken in Sweden since the start in 1967 and are still going on, now as a part of the National Environmental Monitoring Programme. After the first exploratory years including country-wide surveys in 1971–1973 undertaken both from the ground, the air and boats, the programme was standardized to cover an adequate sample of coastal and inland sites of south Sweden for the production of annual midwinter population indices for important species (areas further north in Sweden are normally ice-covered and without importance for waterbirds in winter). Further large scale surveys were undertaken in 1987–1989, 1993 and 2004 (country-wide survey). The programme did not cover the seaducks in offshore areas (later included in a special programme). The present contribution analyses the first 40 years of midwinter counts in Sweden, especially with the aim to elucidate changes in distribution and numbers of the different species during this time series. During the period there was a marked change in the winter weather and especially the ice situation in Sweden in January, being a factor of importance for the wintering waterbirds. During the years 1967–1987 there were five really hard ice-winters, whereas in the latter part of the period there was no really hard ice-winter. Comparisons between the country-wide surveys in 1971 and 2004 showed a marked increase from 172,000 to 627,000 individuals excluding the offshore species Clangula hyemalis and Melanitta spp. Anas platyrhynchos increased from 67,000 to 150,000, Aythya fuligula from 54,000 to 230,000 and Bucephala clangula from 19,000 to 75,000. Increases were also found in most of the other species. In addition, Anas penelope and Podiceps cristatus established new wintering traditions in south Sweden. Midwinter indices for nine out of ten species showed significantly increasing trends over the 40 years, no species decreasing. In Anas platyrhynchos and Aythya fuligula the indices showed fluctuations around a steady level, then a marked increase followed after the last cold winter, whereas species like Bucephala clangula and Mergus serrator showed increasing trends from the start of the counts. Fulica atra crashed markedly after one cold winter and remained for years on a low level before recovering but the overall trend was increasing. To a large extent the increases found are probably due to the milder winters in later years, which also led to changes in winter distribution within the country, also being reflected in the regional totals for different species. Part of the increases does also reflect genuine population increases as show by comparisons with IWC results from other countries.


1994 ◽  
Vol 30 (10) ◽  
pp. 213-219 ◽  
Author(s):  
Hendrik Pieters ◽  
Victor Geuke

Samples of yellow eel from various locations in the Dutch Rhine area have been analyzed for trend monitoring of mercury since 1977. In the western Rhine delta mercury levels in eels have hardly changed since the seventies, whereas in the eastern part of the Dutch Rhine area a considerable decrease of mercury concentrations in eel has occurred. Because of continuous sedimentation of contaminated suspended matter transported from upstream regions, accumulation rates and concentrations of mercury in eel in the western Rhine delta remained at a relatively high level. Analyses of methyl mercury in biota have been performed to elucidate the role of methyl mercury in the mercury contamination of the Dutch Rhine ecosystem. Low percentages of methyl mercury were observed in zooplankton (3 to 35%). In benthic organisms (mussels) percentages of methyl mercury ranged from 30 to 57%, while in fish species and liver of aquatic top predator birds almost all the mercury was present in the form of methyl mercury (> 80%). During the period 1970-1990 mercury concentrations of suspended matter in the eastern Rhine delta have drastically decreased. These concentrations seemed to be highly correlated with mercury concentrations of eel (R = 0.84). The consequences of this relation are discussed.


2002 ◽  
Author(s):  
Nancy Drilling ◽  
Rodger D. Titman ◽  
Frank McKinney
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