Survey of lake flora and fauna as a basis for hydromelioration planning, enhancement of biological productivity, and waterbody restoration

Survey of lakes and other water bodies

Why a comprehensive waterbody survey is necessary

Survey of the lake's flora and fauna to evaluate cleanup and restoration efforts
Survey of the lake’s flora and fauna to evaluate cleanup and restoration efforts

Modern projects aimed at cleaning, restoring, and managing lakes, ponds, oxbow lakes, and other waterbodies require not only engineering solutions but also a deep understanding of the ecology of a specific aquatic system. Aquatic vegetation and lake fauna are not merely “sludge” or chaotic overgrowth but a well-organized natural system formed according to strict ecological patterns, reflecting the geological history and origin of the waterbody.

The species composition of plants and their depth distribution, the structure of bottom sediments, and the morphology of the shoreline directly determine:

  • Water transparency and hydrochemical parameters; certain aquatic plants and algae indicate the chemical composition of water and the degree of eutrophication.
  • The rate of sedimentation (siltation), which depends on the extent of overgrowth and the water exchange rate. The inflow of large amounts of suspended solids from wetlands—and especially from cultivated agricultural land, livestock farms, mining sites, and other human-disturbed biotopes—significantly accelerates siltation.
  • The level of eutrophication, i.e., the degree to which a waterbody is enriched with nutrients, primarily nitrogen and phosphorus compounds, and the intensity of biological production (algae, macrophytes, phytoplankton).
  • The oxygen regime at different depths.
  • Biological productivity; waterbodies may be used for fish farming, and such prospects are identified through targeted surveys.
  • Ecosystem resilience to anthropogenic pressure, which belongs to the field of ecological forecasting and requires long-term, multi-year observations.

For this reason, before works for cleaning the water area or bottom sediments, operating a waterbody for fishery or recreational purposes, or carrying out any construction near water, it is advisable—and in some cases mandatory—to conduct a comprehensive environmental survey involving hydrologists, biologists, and botanists.

Objectives of waterbody surveys

A survey of a lake or other waterbody – pond, oxbow lake, impoundment, river, or stream – may be conducted for the following purposes:

  1. Entomological surveys and implementation of measures to prevent outbreaks of Zika fever, West Nile fever, malaria, and other parasitic diseases.
  2. Determination of shoreline location (the boundary of the waterbody), as well as the boundaries of water protection zones and coastal protective belts.
  3. Assessment of hydrological and morphometric characteristics of the waterbody.
  4. Preparation of a hydrological report specifying morphometric parameters and describing the hydrological regime of the waterbody.

services for a comprehensive survey of a reservoir to determine measures for cleaning and environmental improvement of the reservoir

    An example of how to create a profile of the vegetation zones and soils of a lake

    An example of drow-up a lake profile with a description of facies – vegetation zones and underlying soils

    Example of a drow-up a lake profile with a description of facies—vegetation zones and underlying bottom sediments—based on a scientific monograph on the documentation of aquatic vegetation and sediments.

    Profile of aquatic vegetation and bottom sediments of a lake. Cross-section through Naroch Lake along the transect Stebenevo village – Nanosy village.

    No. Facies, m (distance) Bottom sediment characteristics Plant association
    1 0.0—0.7 Silty sand Sparganium–Elodea–Lemna association (24 species)
    2 0.7—1.0 Silty sand Phragmites–Chara–Potamogeton association (11 species)
    3 1.0—3.0 Silty sand Chara–Stratiotes association with Potamogeton (3 species)
    4 3.0—6.0 Silty sand Chara–Ceratophyllum association (4 species)
    5 6.0—8.0 Carbonate sapropel Ceratophyllum association (2 species)
    6 4.0—6.0 Carbonate sapropel Elodea–Ceratophyllum association (4 species)
    7 2.0—4.0 Sand with gravel Chara–Bryophyta association (4 species)
    8 4.0—6.0 Sand with gravel Chara–Ceratophyllum association (3 species)
    9 7.0—9.5 Carbonate sapropel Ceratophyllum association (2 species)
    10 6.0—8.0 Carbonate sapropel Chara association (2 species)
    11 5.0—6.0 Carbonate sapropel Elodea–Ceratophyllum association (4 species)
    12 2.0—5.0 Silty sand with shells Elodea–Chara association (3 species)
    13 0.6—2.0 Silty sand* Phragmites–Chara association (2 species)
    14 0.2—0.6 Sandy–gravel material* Potamogeton–Chara association

    * Sandy deposits at a depth of 8–10 cm are underlain by carbonate sapropel.

    Principles of lake and shoreline surveying

    typical flora and fauna of a lake in the middle zone of the continental climate zoneA comprehensive waterbody survey includes:

    • analysis of the water area and bottom profile;
    • description of the shoreline, boundaries of the waterbody, water protection zones, and coastal protective belts;
    • study of flora, algae, and macrophytes;
    • description of fauna and aquatic organisms (hydrobionts);
    • assessment of the degree of anthropogenic impact.

    The nature of anthropogenic pressure—agriculture, urban development, recreation, discharges, and surface runoff—directly determines the scope and type of biological reclamation measures required for the waterbody and adjacent areas.

    Special attention is given to surveys of waterbodies located within protected areas such as parks, nature reserves, and wildlife sanctuaries. Protected waterbodies with restricted public access require special procedures and permits for survey work. The main research methods—hydrochemical analysis and studies of flora and fauna—generally do not significantly affect protection regimes but must be carried out by specialists with appropriate qualifications.

    In cases of near-complete degradation of a waterbody—total siltation, overgrowth, and a sharp reduction in open-water area—the primary task becomes mechanical removal of vegetation and bottom sediments. In all other situations—where the ecosystem is preserved, or in cases of construction, landscaping, or fisheries use—scientific investigation is fundamentally necessary.

    Macrophytes as the ecological foundation of a lake

    Higher aquatic vegetation includes macrophytes—large aquatic plants, including flowering plants and some large algae, inhabiting the littoral zone and the bottom of waterbodies.

    Macrophytes:

    • absorb nutrients entering from the catchment;
    • reduce the intensity of algal blooms;
    • stabilize bottom sediments;
    • form natural biological filters;
    • provide shelter and spawning grounds for fish;
    • create habitats for plankton, larvae, and microorganisms.

    As plants die off, they form silt and sapropel, which act as accumulators of organic matter and contribute to the fertility of bottom sediments.

    Facies and zonation of aquatic vegetation

    Aquatic plants in a lake do not grow randomly but form belts parallel to the shoreline. These zones are referred to as facies—areas characterized by a homogeneous composition of macrophytes and a specific type of bottom substrate. The term is borrowed from geology and ecology and reflects the structural organization of the landscape.

    The distribution of facies is determined by:

    • water depth;
    • transparency and chemical composition of water;
    • type of bottom sediments;
    • wave exposure;
    • shape and origin of the lake (glacial, karst, etc.).

    Most glacial lakes exhibit well-defined vegetation and substrate belts, allowing the creation of profile maps and analysis of waterbody development dynamics.

    Main belts of aquatic vegetation

    1. Littoral Wetland Zone

    A shallow zone at the water’s edge with sweet flag (Acorus), sedges (Carex), marsh marigold (Caltha), arrowhead (Sagittaria), and buttercups (Ranunculus). This zone is the first to receive surface runoff and plays a key role in biological water purification.

    1. Emergent and Semi-Submerged Plants

    Located at depths of up to 1–2 m. Reeds dominate on sandy substrates, while bulrush and sweet grass prevail on silty soils. This belt forms a “second shoreline” and protects the water area from wave action.

    1. Floating-Leaved Plants

    Water lilies (Nymphaea), yellow water lily (Nuphar), floating pondweeds (Potamogeton spp.), and duckweed (Lemna). These plants create calm zones and serve as indicators of a healthy waterbody. Many species are legally protected.

    1. Fully Submerged Plants

    Pondweeds, Elodea, hornwort (Ceratophyllum), water milfoil (Myriophyllum), and charophyte algae. In clear waterbodies, these plants may grow at depths of up to 7–8 m.

    Relationship between vegetation and bottom sediments

    The type of bottom substrate directly determines the structure of plant communities:

    • sand and gravel — vegetation-poor areas;
    • silty substrates — the most productive zones;
    • carbonate silts — areas dominated by charophyte algae;
    • peat substrates — weakly overgrown areas.

    This explains the differences between lakes that may appear similar at first glance.

    Flora, fauna of a water bodies and biological productivity

    The study of macrophytes is inseparable from the assessment of fauna. Plant communities form the food base, shelters, and spawning grounds for fish and invertebrates.

    Of particular importance are:

    • mollusks (e.g., freshwater pearl mussels), which are indicators of waterbody health;
    • invertebrates, forming the foundation of aquatic food webs;
    • fish, which regulate insect populations, including mosquitoes.

    Under conditions of global warming, entomological analysis and the development of anti-epidemic measures (West Nile fever, malaria, Zika virus, etc.) become mandatory components of waterbody surveys, especially in southern, subtropical, and sharply continental regions.

    Lake overgrowth and the role of humans

    Overgrowth of waterbodies is a natural process that unfolds over thousands of years:

    • oligotrophic lakes;
    • mesotrophic lakes;
    • eutrophic lakes;
    • paludifying (bog-forming) stages.

    Anthropogenic impact dramatically accelerates these stages. Understanding the current developmental stage of a waterbody allows for the selection of appropriate and environmentally safe intervention methods. Waterbody restoration may involve sediment removal and bottom deepening, or may be limited to the removal of debris and woody or plant residues.

    Substantiation of hydromelioration and cleaning measures

    Based on comprehensive surveys, recommendations and action plans are developed, including:

    • selective bottom cleaning;
    • regulation of macrophyte vegetation;
    • strengthening of water protection zone functions;
    • reduction of nutrient (biogenic) inflow;
    • biological and, where disease vectors are detected, chemical control of insect populations;
    • enhancement of fisheries and recreational value of the waterbody.

    Waterbody cleaning is viewed not as a one-time action but as part of an integrated system of reducing anthropogenic pressure and implementing ecological management.

    Aquatic vegetation and fauna are key indicators of lake condition. A well-designed survey not only enables effective cleaning but also extends the lifespan of a waterbody, increases its productivity, and preserves natural balance.

    Our services in water bodies surveys

    We provide comprehensive waterbody surveys, prepare reports and recommendations, and develop solutions for cleaning, reclamation, and environmental support.

    Cost of waterbody surveys

    The cost of surveying a waterbody—lake, river, oxbow lake, or impoundment—is determined by the scope of work specified in the contract or technical assignment.

    The cost of an on-site waterbody survey may include:

    • geodetic and bathymetric surveying;
    • express diagnostics of water and sediment parameters and laboratory analysis costs;
    • work of biologists, entomologists, and botanists involved in surveying flora and fauna, including laboratory analyses;
    • ichthyological studies involving specialists, determination of species composition and health indicators of fish fauna;
    • entomological monitoring of blood-feeding mosquitoes Aedes aegypti and Aedes albopictus, as well as assessment of Culex spp. populations (common house mosquitoes), whose breeding sites are located in populated areas;
    • shoreline surveys with vegetation characterization, preparation of dendrological plans, and tree inventory records;
    • on-site delineation of water protection zone boundaries and surveys conducted in accordance with the technical assignment;
    • travel expenses, transportation of equipment and instruments;
    • preparation of maps, reports, registers, and project documentation, where such follow-up work is envisaged.

    Contact us to arrange a waterbody survey.
    Contact us if waterbody cleaning and restoration are required.