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A note on centrifugation for improving freshwater invertebrate sample conservation

100%

Valdecasas A. G., Garcia-Jimenez R., Campoamor M. M. F.

Acta Biologica

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2020

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tom 27

2

Spatial changes in phytoplankton, zooplankton and macrobenthos communities in Drawa River

75%

Czerniawski R., Gozdzik I., Krepski T., Slugocki L., Pilecka-Rapacz M., Domagala J.

Teka Komisji Ochrony i Kształtowania Środowiska Przyrodniczego

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2013

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tom 10

3

Species - area relationships for sandy beach macrobenthos in the context of intertidal width

75%

McLachlan A., Dorvlo A.

Oceanologia

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2007

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tom 49

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nr 1

The marine species richness (MSR) recorded in 159 sandy beach surveys was analysed in relation to beach width (W). MSR is the number of macrobenthic species collected in a standard intertidal transect survey, excluding insects. Beach width (W) was estimated by dividing the spring tide range [m] by the beach face slope, to give a value in [m]. The relationship between MSR and W was best described by a semilog (exponential) model, which was highly significant: MSR = −5.2+ 10.8 logW. The fit of a power model (MSR = cWz) was also significant. The steep slope of the curve for a power model (z = 0.49) suggests that beaches function as isolated rather than contiguous habitats and that the nature of the habitat becomes more benign as beaches widen. There are some latitudinal effects, with tropical beaches displaying a higher species-area relationship for any beach width than other regions.

4

Assemblages of Chironomidae larvae in the Hanczanska Bay [Lake Wigry]

75%

Jablonska I., Koszalka J.

Natural Sciences

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2000

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tom 05

5

Comparison of macroinvertebrate communities associated with various habitats in anthropogenic reservoirs

75%

Jatulewicz I.

Oceanological and Hydrobiological Studies

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2007

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tom 36

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nr Suppl.4

6

Links between biota and climate-related variables in the Baltic region using Lake Onega as an example

63%

Sharov A. N., Berezina N. A., Nazarova L. E., Poliakova T. N., Chekryzheva T. A.

Oceanologia

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2014

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tom 56

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nr 2

7

How lonely they are? A degree of isolation among macrozoobenthos species in the Marine Protected Area, the Bay of Puck, the Southern Baltic

63%

Weslawski J. M., Kryla-Straszewska L., Warzocha J., Urbanski J., Wlodarska-Kowalczuk M., Kotwicki L.

Oceanological and Hydrobiological Studies

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2013

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tom 42

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nr 3

8

Benthos and drift of invertebrates, particulary Chironomidae, in a selected cross-section profile of the River Widawka (Central Poland)

63%

Grzybkowska M., Pakulska D., Jakubowski H.

Acta Hydrobiologica

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1987

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tom 29

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nr 1

9

Ecohydrological conditions in two catchments in the Gorce Mountains: Jaszcze and Jamne streams - Western Polish Carpathians

63%

Radecki-Pawlik A., Bucala A., Plesinski K., Oglecki P.

International Journal of Ecohydrology and Hydrobiology

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2014

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tom 14

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nr 3

10

Some features of the quantitative distribution of sipunculan worms (Sipuncula) in the Central and Southern Barents Sea

63%

Garbul E. A., Anisimova N. A.

Oceanologia

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2012

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tom 54

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nr 1

The article reports on the current state of the sipunculan fauna of the central and southern parts of the Barents Sea. The main quantitative parameters (biomass and abundance) of the sipunculan populations are obtained, and the contribution of sipunculids to the total benthos biomass is assessed. The major factors causing long-term variations in Sipunculidae distribution and abundance are evaluated for the area in question. The investigations show that the most commonly encountered sipunculan species are Nephasoma diaphanes diaphanes, N. abyssorum abyssorum and Phas- colion strombus strombus. The main contribution to the total benthos biomass comes from the two species most typical of the Barents Sea benthic fauna: Golfingia margaritacea margaritacea and G. vulgaris vulgaris. It is possible that the reduction in Golfingia biomass between the 1970s and 1990s, described in the article, is due to changes in the sampling methodology.

11

Ecological description of the Southern Caspian Sea in the oil-field region of Guneshly

63%

Kasymov A., Rogers L.

Polish Ecological Studies

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1996

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tom 22

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nr 3-4

12

The use of benthic macroinvertebrates in the biomonitoring of river water quality - how do we interpret faunistic data?

63%

Kownacki A.

Acta Hydrobiologica

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2000

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tom 42

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nr 3-4

13

Diversity, distribution and ecology of benthic amphipods [Amphipoda, Gammaridea] in the Barents Sea sublittoral

63%

Bryazgin V.

Polish Polar Research

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1997

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tom 18

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nr 2

14

Benthic bacteria of Lake Chelmzynskie [Poland]

63%

Kalwasinska A., Donderski W.

Polish Journal of Environmental Studies

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2005

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tom 14

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nr 6

Research was conducted on the number, secondary production and physiological properties of benthic bacteria in the eutrophic Lake Chełmżyńskie. It was found that the number of psychrophilic bacteria (CFU) occurring in the bottom sediments of the studied lake and the rate of bacterial production (BP) were all characterized by a distinct seasonal variability and depended on the location of the study site and the type of bottom sediments (ANOVA, p-value <0.05). The maximum total number of bacteria (TNB), CFU and BP were observed in summer. Muddy sediments were characterized by a greater number of bacteria than sandy ones. A higher number of heterotrophic microorganisms and greater rate of secondary production were found at the sites located in the part of the studied waterbody near the town than at the sites located far from the town. The most numerous benthic bacteria were strains of hydrolyse fat, protein and cellulose. The least numerous were pectinolytic and chitinolytic bacteria.

15

Seasonal and bathymetric trends of the amphipod fauna in Heraklion Bay [Aegean Sea]

63%

Plaiti W., Akoumianaki I., Eleftheriou A.

Polskie Archiwum Hydrobiologii

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2000

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tom 47

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nr 3-4

16

Populational parameters of trichopterans [Trichoptera] in dominant habitats of a permanently disturbed lowland river

63%

Tszydel M., Szczerkowska E., Grzybkowska M., Dukowska M.

Acta Agrophysica

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2003

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tom 01

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nr 3[88]

17

What makes Chironomus more abundant above the bottom? Field experiments in mesocosms

63%

Kajak Z., Prus P.

International Journal of Ecohydrology and Hydrobiology

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2001

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tom 01

|

nr 4

In looking for factors affecting Chironomus plumosus (L.) abundance and its fluctuations − the comparison of its numbers has been done in the bottom (at 6 m depth) and in mesocosms trays with the same bottom sediment elevated 0.4-1.2 meter above the bottom. The experiment was carried out, in a shallow, strongly eutrophic, polymictic, lowland dam reservoir, where theabundance of Chironomus is among the highest in nature. The total abundance was on the average several times higher and more stable and larvae developed more quickly in trays over the bottom than in the same mud at the bottom. All this was probably due to better and more stable oxygen conditions above the bottom than at its very surface. Usually no differences in the abundance were found between levels 0.4, 0.8 and 1.2 m above the bottom, what indicates that conditions at all these levels were similar and different from those at the very bottom. The average density, and especially spring peak numbers in and above the bottom, were much higher in the year 1993 than in 1996 (the ratio of average numbers 1993/96 being similar 2.3 and 2.6 for the bottom and trays respectively). It was probably due to a higher food supply (mostly small diatoms) by rivers and also due to weaker spring water flow in 1993. The very strong decline from high spring peak numbers to summer minimum seems to result from interconnections between larvae and perhaps also increased fish pressure, after the spawning period.

18

Population of Yoldia eightsi [Bivalvia, Nuculanidae] in herve cove [Admiralty Bay, King George Island, Antarctic]

63%

Rozycki O.

Folia Universitatis Agriculturae Stetinensis. Piscaria

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2001

|

tom 28

19

Macrobenthos of productive carp ponds with different levels of intensification of second year carp rearing

51%

Zieba J., Szarowska M.

Acta Hydrobiologica

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1987

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tom 29

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nr 4

20

Molluscs of the Polish Baltic

51%

Piechocki A., Wawrzyniak-Wydrowska B.

Folia Malacologica

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2012

|

tom 20

|

nr 1

Ograniczanie wyników

A note on centrifugation for improving freshwater invertebrate sample conservation

Spatial changes in phytoplankton, zooplankton and macrobenthos communities in Drawa River

Species - area relationships for sandy beach macrobenthos in the context of intertidal width

Assemblages of Chironomidae larvae in the Hanczanska Bay [Lake Wigry]

Comparison of macroinvertebrate communities associated with various habitats in anthropogenic reservoirs

Links between biota and climate-related variables in the Baltic region using Lake Onega as an example

How lonely they are? A degree of isolation among macrozoobenthos species in the Marine Protected Area, the Bay of Puck, the Southern Baltic

Benthos and drift of invertebrates, particulary Chironomidae, in a selected cross-section profile of the River Widawka (Central Poland)

Ecohydrological conditions in two catchments in the Gorce Mountains: Jaszcze and Jamne streams - Western Polish Carpathians

Some features of the quantitative distribution of sipunculan worms (Sipuncula) in the Central and Southern Barents Sea