Journal of Environmental Treatment Techniques  
2019, Special Issue on Environment, Management and Economy, Pages: 993-998  
J. Environ. Treat. Tech.  
ISSN: 2309-1185  
Journal web link: http://www.jett.dormaj.com  
The Composition and Seasonal Dynamics of  
Planktonic Green Algae in the Mouth of the  
Kazanka River (Republic of Tatarstan)  
Liliya Yu. Khaliullina, Alina R. Fazlieva  
Institute of Fundamental Medicine and Biology, Kazan Federal University, Kazan, Russia  
Received: 05/08/2019  
Accepted: 20/11/2019  
Published: 20/12/2019  
Abstract  
The article presents the results of studies of the species composition and seasonal dynamics of planktonic green algae in the  
mouth of the Kazanka River in the city of Kazan in 2018. During the observation period, 51 taxa of green planktonic algae of  
Chlorophyceae and Trebouxiophyceae classes were found in the algoflora of the studied area, of which 53% of the species belong to  
the order Sphaeropleales spheroplei. The largest numbers of taxa belong to the families Hydrodictyaceae (13%), Scenedesmaceae  
(
23%), Selenastraceae (10%), Chlorellaceae (14%), Oocystaceae (10%), Chlamydomonadaceae (8%). The total number and biomass  
range from 1.6-18.8 million cells/liter and 1.2-9.9 mg/liter. Flagellate monadic algae dominate in phytoplankton, belonging to the  
order Chlamydomonadales Phacotus lenticularis, Pandorina morum, Chlamydomonas sp. sp., Carteria sp. sp. The species of the  
spheroplei genera Scenedesmus, Pediastrum, Coelastrum, Crucigenia, Actinastrum, Dictyosphaerium, Oocystis. Mass reproduction  
of these algae throughout the summer and autumn indicates the extreme pollution of the waters in this part of the Kazanka River.  
Based on the data obtained, an assessment was made of the ecological state of water in the considered section of the river. Water  
quality is assessed as β-mesosaprobic (1.6-2.5) and moderately polluted; quality class III. According to trophic indices, the water in  
the considered area for the observation period is mostly consistent with the hypereutrophic type.  
Keywords: Algocenosis, Phytoplankton, Algae, The river Kazanka  
1
currents belong to the hydrocarbonate - calcium class, in the  
1
Introduction  
lower reaches downstream the Derbyshki settlement - to the  
sulfate class and calcium group. The river is characterized by  
high salinity of water, which increases markedly from the  
upper reaches to the lower reaches of the river. The upper and  
middle sections of the river are mainly affected by  
agricultural runoff, due to which nutrients enter the river. In  
the lower reaches, man-made impact comes to the fore:  
sewage from industrial and municipal enterprises and storm  
sewage enrich the river with toxic compounds of organic and  
inorganic nature such as oil products, surfactants, phenols,  
heavy metals with multiple excesses of permissible  
concentrations. Mineral forms of phosphorus are constantly  
present in excess concentrations, which contribute to the  
processes of eutrophication of the river. The river water is  
highly polluted and is rated as “dirty” (quality grade 4).  
Decisions of the Council of Ministers of the TASSR No. 25  
Today, the problem of monitoring of the status of water  
bodies located within the city boundaries is of great  
relevance. Urban bodies of water, to which the lower part of  
the Kazanka River belongs, traditionally used as sources of  
fresh water, as well as for technical, recreational, and other  
purposes. The functioning of settlements, the gradual  
expansion of their borders leads to pollution of water bodies  
by urban, mainly domestic wastewater, in aerotechnogenic  
way and, as a result, disrupts the natural functioning of water  
ecosystems and turns them into anthropogenic ones (3).  
For the purpose of ecological monitoring of aquatic  
ecosystems, the study of phytoplankton is actively used,  
which, due to the structure and functional features,  
determines the state of aquatic ecosystems in general. The  
objective of this work is to assess the environmental status of  
the estuarine area of the Kazanka River by indicators of the  
structure of communities of planktonic green algae.  
(
(
dated 10.01.1978) and the Cabinet of Ministers No. 644  
dated 29.12.2005) assigned the Kazanka River the status of a  
nature monument of regional significance (4,5,10,13). As a  
measure of river protection, it is recommended to comply  
with the regime of protection of the territory of the natural  
monument, as well as the regime of use of water protection  
zones. The river has economic and educational significance.  
The Kazan  Arsk section is recommended for tourism (3).  
In 2018, during the growing season, studies were made of  
planktonic green algae in the mouth of the Kazanka River in  
the city of Kazan. Permanent observation stations were  
located in the riverbed of the Kazanka River (near the  
Kremlin transport dam). The layout of the sampling station is  
shown in Fig. 1.  
2
Materials and methods  
The Kazanka River is a typical lowland river with mixed  
food that originates on the western slopes of the Vyatka  
Slopes and, flowing in a southwestern direction, flows into  
the Volga River in the city of Kazan. The length of the river,  
according to various sources, ranges from 140 km to 172 km  
(
7,9,12). The lower course of the Kazanka River, being in a  
backwater zone by the waters of the Kuibyshev reservoir, has  
turned into a wide bay. Water masses in the upper and middle  
Corresponding author: Liliya Yu. Khaliullina, Kazan  
Federal University, Republic of Tatarstan. E-mail: Liliya-  
kh@yandex.ru.  
Samples were taken once every week. In total, between  
June and October 2018, 34 qualitative and quantitative  
993  
Journal of Environmental Treatment Techniques  
2019, Special Issue on Environment, Management and Economy, Pages: 993-998  
samples of algae were collected. Selection and office  
processing of phytoplankton samples were carried out  
according to standard methods (2, 6, 17, 18).  
Phytoplankton samples were collected from a depth of  
0
4
.5 - 2.5 m. All quantitative samples of 0.5L were fixed with  
0% formalin solution. The fixed samples were concentrated  
Phacotaceae  
Chlamydomonadaceae  
Volvocaceae  
2
4
by sedimentary method to 7-10 ml for qualitative and  
quantitative measurement of phytoplankton. Also, to thicken  
phytoplankton, a vacuum filter was used for hydrobiological  
studies in water PVF-35/NB. For concentration of  
phytoplankton, Vladipor membrane filters of the MFAS  OS  
2
Goniaceae  
1
Carteriaceae  
1
2 and MFAS  OS  3 type with pore sizes of 0.45