LONGTERM MONITORING OF THE LOWER VOLGA VALLEY
Golub V.B. Longterm Monitoring of the Lower Volga Valley // Ecosystems: ecology and dynamics. No 2. 2024. P. 4-41. | Abstract | PDF | Reference
- Satellite image (Google.Earth, 2024) of an abandoned and overgrown with woody vegetation area in the irrigated arable land, west of the Volga River delta
- The bank of Akhtuba River, now used by people for recreation, in the middle of the Volga-Akhtuba floodplain, with plant communities of cl. Salicetea purpureae, August 2011 (photo by V.B. Golub)
- A meadow with a borehole, south of the Volga-Akhtuba floodplain, 08/12/2010 (photo by V.B. Golub)
- Schematic map of the Volga-Akhtuba floodplain. Legend: A, C, D, F, G – transects made by the Pre-Caspian Expedition of the Moscow State University; В, Е, Н – transects made by the All-Union Aerogeological Trust; numbers – stationary sample sites of the Yuzhgiprovodkhoz Institute and All-Union Aerogeological Trust
- Soil map (superimposed on the topographic map) of the sample site near the Semenovskiy strait, where relevés were carried out
- Satellite image (Google.Earth, 2024) of the sample sites near the Khora strait, Krugly Churakov Lake, the “Pastukhova Tonya” common, the Petropavlovka–Dosang transect, and the Astrakhan gas condensate complex (dotted line). The sample sites numbers correspond to those in Table 3
- Schematic map of the delta of the Volga River. Legend: I – group of transects in the eastern part of the delta; numbers – stationary sample sites of the Astrakhan State Pedagogical Institute, – dam of the water divider
- Algae on the meadow grass in the Volga River delta after a lasting flood, August 1979 (photo by V.B. Golub)
The construction of dams on rivers for hydropower, flood control, irrigation and water supply are a widespread phenomenon in the world. Natural complexes above the dams, which were created over thousands of years, are completely destroyed now. The reservoirs affect the regime of water flow in the river downstream of the dam, and these changes disrupt the functioning of natural ecosystems in the remaining areas of river floodplains.
The Volga River did not escape the fate of transformation. It was converted into a reservoir system by the late 1960s. Filling of the reservoirs with water destroyed all natural ecosystems in their beds. Howevr, there is an exception, the lowest section of the Volga River valley, about 500 km long from the Volgograd Hydroelectric Power Plant to the Caspian Sea. This area is known as the Volga-Akhtuba Floodplain and the Volga River Delta, and we call it the Lower Volga Valley. It’s watered through the special spring-summer water releases into the lower pool of the Volgograd Reservoir.
In the 1960s, a project was planned out to create the Nizhnevolzhskaya Hydroelectric Power Plant in the Volga-Akhtuba floodplain. According to one of its options, the entire floodplain was supposed to become the bottom of the new reservoir. To compensate for the losses in the local fishery industry, a water divider would be built. Its function was to redirect water during floods to the eastern part of the delta and create a favorable habitat for the spawning of semi-anadromous fish. Meanwhile, the western part of the delta was planned to be transformed into the intensively used irrigated agricultural plantations.
However, due to the loss of large areas of agricultural land the idea of the Nizhnevolzhskaya Power Plant was abandoned. Only some of the projects, such as the water divider and transformation of the wetlands and meadows in the western delta, were fulfilled. Then, in the late XX century, during the transition from a planned Soviet economy to a market system, both the divider and the irrigation systems were abandoned and destroyed.
The first goal of this study was to characterize the materials stored at the Institute of Ecology of the Volga River Basin in order to monitor the dynamics of plant cover and partly soil cover of the Lower Volga valley. This material is of a great value as it has 15,675 geobotanical relevés of sample plots made in the valley in 1924-2023. For about 10,000 of them, the exact geographical coordinates were obtained.
The second goal of the article was to briefly summarize the results of a long-term monitoring of vegetation dynamics in the valley. The main results (since the 1970s) of this monitoring are also presented below.
We discovered that even after exclusion of the western part of the delta, its natural vegetation was preserved in the remaining territory nonetheless, although in a modified form. We also found out that such determining factor as the hydrological regime of the Lower Volga valley is not the only one that affects the vegetation cover and its productivity. Other significant factors are, for example, peculiarities of economic land use and invasions of alien plant species.
The Volga-Akhtuba floodplain underwent xerophytization and synanthropization of its vegetation cover which is especially noticeable in its northern part. Meanwhile, in its western part, where the irrigation systems were destroyed, large areas turned into fallow lands with specific type of vegetation.
Most importantly, its eastern part has transformed differently compared to the floodplain. There, the vegetation changed greatly between the 1980s and the early XXI century; reed and cattail thickets spread over large territories, and the area of halophytic phytocenoses decreased sharply. The main reasons for this were the increase in water flow of the Volga River at the end of the 1970s, and the cessation of hay harvesting for farm animals and reed for industrial use. Some recent changes towards xerophytization in the delta occurred only on the slopes of the Baer hillocks where the representation of xerophytic plant communities has increased, while the communities has spread down the slopes, which can be explained by climate aridization.
In conclusion, the author would like to emphasize that it is necessary to organize constant observations of the aforementioned phenomena and processes taking place in the region. This is important to justify and make management decisions on the conservation of biodiversity and biological productivity of ecosystems in the Lower Volga valley.
Keywords: Volga-Akhtuba floodplain, Volga River delta, regulation of water flow, stationary observation sites, lower pools of the hydroelectric system, reduction in flow volume, water factor, vegetation, xerophytization, anthropogenic factors, Volgograd reservoir, reed thickets, fires, soil desalinization, climate aridization.
DOI: 10.24412/2542-2006-2024-2-4-41
EDN: FRALCL
BLACK KITE (MILVUS MIGRANS (Boddaert, 1783)) BREEDING ECOLOGY IN THE NORTH OF MOSCOW REGION
Vartanyants O.A., Sharikov A.V., Volkov S.V., Karvovsky D.A., Ivanov M.N. Black kite (Milvus migrans (Boddaert, 1783)) Breeding Ecology in the North of Moscow Region // Ecosystems: ecology and dynamics. No 2. 2024. P. 42-56. | Abstract | PDF | Reference
- Nest of a black kite in a black alder forest (photo by O.A.Vartanyants)
- Ringing of a black kite chick (photo by A.V.Sharikov)
- Black kite chicks in the nest (camera trap photo by M.N.Ivanov)
- O.A. Vartanyants with a ringed chick of a black kite (photo by E.Y.Lobischeva)
- R.Kh. Ataullin climbing up to the nest of a black kite (photo by E.M.Shishkina)
- Bedding inside the nest of a black kite (photo by M.N.Ivanov)
- Ringed chicks of a black kite in the nest (photo by M.N.Ivanov)
- Black alder forest (photo by O.A.Vartanyants)
The black kite (Milvus migrans (Boddaert, 1783)) is a species of birds of prey that is poorly studied in the European part of Russia and Eastern Europe. Therefore, in this work we analyze the long-term observations of black kites in the north of Moscow Region, and present the results of an analysis of the species’ phenology and nesting.
We discovered that black kites arrive at the study area from the 5th to the 17th of April, and leave from the 17th of August to the 7th of September. There is a connection between arrival and departure dates, as well as between them and some abiotic parameters. We found the nests of black kites in the tree species that were predominant in the study area. Each clutch had an average of 2 eggs; egg and chick mortality were 3.3%, which is less than that in other parts of the species’ range. In 2022, we discovered an aggregation of 7 nests of black kites in the area of 210 ha.
Keywords: black kite, (Milvus migrans (Boddaert, 1783)), breeding ecology, Moscow Region.
Acknowledgments. We would like to thank every biologist and volunteer of the Crane Homeland Nature Reserve for a long-term contribution of their observations to the Books of Facts of the reserve. The recent field data would have not been possible to collect without the help of students and postgraduate students of the Moscow Pedagogical State University and A.N. Severtsov Institute of Ecology and Evolution of RAS. We would also like to thank O.S. Grinchenko, the Chairman of the Moscow Branch of BirdsRussia, for the opportunity to conduct our research on the base of the Ecological Education Center “Dmitrovka Biostation”, and T.S. Massalskaya for assistance in statistical processing of our data.
DOI: 10.24412/2542-2006-2024-2-42-56
EDN: SQHBBJ
CHIRONOMIDS (DIPTERA, CHIRONOMIDAE) OF HIGHLY MINERALIZED RIVERS OF THE ELTON LAKE REGION, RUSSIA: TAXONOMIC COMPOSITION, ECOLOGICAL FEATURES
Zinchenko T.D., Golovatyuk L.V., Morov V.P. Chironomids (Diptera, Chironomidae) of Highly Mineralized Rivers of the Elton Lake Region, Russia: Taxonomic Composition, Ecological Features // Ecosystems: ecology and dynamics. No 2. 2024. P. 57-107. | Abstract | PDF | Reference
- Marsh sandpiper (Tringa stagnatilis) – one of the main consumers of Chironomidae larvae in river estuaries. Estuary of the Khara River, August 2007 (photo by V.P.Churbanov)
- Estuary of the Chernavka River is a habitat of many Cricotopus salinophilus and Сhironomus salinarius larvae, August 2014 (photo by T.D.Zinchenko)
- Expedition to the Elton Region, “Holodny Klyuch” sanctuary, April 2008. Expedition members: graduate student V.P. Churbanov, ans researchers of the Institute of the Ecology of the Volga River Basin of the Russian Academy of Sciences L.V. Golovatyuk, L.M. Taranova, T.D. Zinchenko (photo by T.V.Popchenko)
- Hydrochemical and hydrobiological researches in the middle reaches of the Khara River, August 2013 (photo by T.D.Zinchenko)
- Graduate student Vladimir Churbanov during an expedition, sampling the Chironomidae larvae in a stream flowing into the Khara River, April 2008 (photo by T.D.Zinchenko)
- Lake Elton Region, estuary of the Khara River at sunrise, August 2006 (photo by T.D.Zinchenko)
- Members of the expedition after the storm, May 2011 (photo by E.V. Koltunov)
- Expedition members dining in an improvised tent after the storm and a successful acquisition of samples, May 2011 (photo by N.C. Pashinin)
In this article we discuss the analysis results of the data from our long-term studies (2006-2019) of chironomids (Diptera, Chironomidae) that were part of bottom communities of 7 small but highly mineralized rivers, the tributaries of hyperhaline Lake Elton in Volgograd Region (N49° 13′, E46° 40′).
We collected data on species composition and quantitative development of macrozoobenthos communities were and registered 25 species and larval forms of chironomids from 4 subfamilies: Chironominae – 14 species (10 from Chironomini, 4 from Tanytarsini), Orthocladiinae – 9 species, Tanypodinae – 2 species. The structure of chironomids’ communities depends on the physical and chemical characteristics of biotopes, as well as water salinity, and is determined by the trophic indicators of the rivers (Zinchenko, Shitikov et al., 2014). The quantitative development and biodiversity of chironomids’ larvae significantly correlate with environmental conditions and physicochemical characteristics of bottom substrates and water masses.
We determined certain environmental factors, such as total salinity, ionic composition, pH, oxygen concentration, temperature and biotope diversity, that can cause changes in chironomids’ cenosis. Additionally, we provide values of abundance and biomass, and frequencies of species occurrence in rivers of different salinity under the influence of abiotic factors. We also present ecological and faunistic characteristics of chironomids as part of bottom communities of highly mineralized rivers of the Lake Elton region.
Keywords: highly mineralized rivers, chironomids, taxonomic composition, ecological features, mineralization, abiotic factors, tributaries of the Lake Elton.
Acknowledgements. The authors would like to thank Dr. Makarchenko E.V., Dr. Zorina O.V. (Federal Scientific Center for Biodiversity of the Far Eastern Branch of the Russian Academy of Sciences, Vladivostok), Dr. Krasheninnikov A.B. (Perm State National Research University) for the identification of some chironomids, and the staff of the Eltonsky Nature Park for help in making it possible to collect the field material.
Funding. This work was carried out as part of the state task “Changes, Sustainability and Conservation of Biological Diversity under the Global Climate Change and Intensive Anthropogenic Load on the Ecosystems of the Volga River Basin”, registration No. 1021060107212-5-1.6.20; 1.6.19; and with financial support from the Russian Foundation for Basic Research (17-04-00135).
DOI: 10.24412/2542-2006-2024-2-57-107
EDN: WTCQJU