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Table 1
All taxonomic and functional groups composition across the Lake Fuxian during our study period.
| Species | Taxonomic group | Functional group | Habitat characteristics |
|---|---|---|---|
|
Chlorococcum Fries Kirchneriella contorta (Schm.) Bohl. Nephrocytium agardhianum Näg. Selenastrum Reinsch Dictyosphaerium Näg. Quadrigula chodatii (Tan-Ful) G. M. Smith Oocystis elliptica W. West Oocystis lacustis Chod. |
Chlorophyta | F | Clear, deeply mixed meso-eutrophic lakes |
|
Pleodorina californica Shaw Eudorina elegans Ehr. |
Chlorophyta | G | Stagnating water columns in small eutrophic lakes, reservoirs and stable phases in larger river-fed basins |
|
Coelastrum microporum Näg. Coelastrum reticulatum (Dang.) Senn. Golenkinia Chod. Actinastrum Lag. Chodatella longiseta Lemm. Tetraedron minimum (A. Br.) Hansg. Tetraedron trilobulatum (Reinscch.) Hansg. Scenedesmus bijuba (Turp.) Lag. Scenedesmus brasiliensis Bohl. Scenedesmus obliquus (Turp.) Kütz. Scenedesmus quadricauda (Turp.) Bréb. Scenedesmus Mey. Crucigenia Morr. |
Chlorophyta | J | Shallow, mixed, highly enriched regions |
|
Pteromonas Sel. Chlamydomonas Ehr. |
Chlorophyta | X2 | Shallow, meso-eutrophic regions |
| Chroomonas acuta Uterm. | Cryptophyta | ||
|
Chlorella Beij. Schroederia robusta Korsch. Schroederia spiralis (Printz) Korsch. Ankistrodesmus angustus Bern. Ankistrodesmus acicularis (A. Br.) Korsch. Ankistrodesmus falcatus (Cord.) Ralfs |
Chlorophyta | X1 | Eutrophic and hypertrophic regions |
| Mougeotia Ag. | Chlorophyta | T | Persistently mixed layers, in which light is increasingly the limiting constraint and thus optically deep, mixed environments including clear epilimnia of deep lakes in summer |
|
Melosira granulata (Ehr.) Ralfs Fragilaria Lyngby. |
Bacillariophyta | P | Eutrophic thermocline |
|
Closterium gracile Bréb. Staurastrum gracile Ralfs |
Chlorophyta | ||
|
Nitzschia Hass. Navicula Bory, Achnanthes Bory. Gomphonema Ag. Cocconeis Ehr. Frustulia Ag. Cymbella perpusilla Cl. Cymbella tumida (Greg.) Cl. |
Bacillariophyta | MP | Frequently stirred up, inorganically turbid shallow lakes |
| Ulothrix Kütz. | Chlorophyta | ||
| Synedra acus Kütz | Bacillariophyta | D | Shallow, turbid regions including rivers |
| Cyclotella Kütz. | Bacillariophyta | C | Eutrophic small- and medium-sized lakes |
|
Aphanizomenon flos-aquae (L.) Ralfs. Aphanizomenon Morr. Anabaena azotica Ley Anabaena osicellariordes Bory. |
Cyanophyta | H1 | Eutrophic, both stratified and shallow lakes |
|
Merismopedia Mey. Chroococcus Näg. |
Cyanophyta | Lo | Deep or shallow, oliotrophic or eutrophic, medium to large lakes |
|
Peridinium gutwinskii Ehr. Peridinium volzii Lemm. Peridinium pusillum (Pen.) Lemm. Ceratium hirundinella (Müll.) Schr. |
Pyrrophyta | ||
|
Phormidium Kütz. Pseudoanabaena |
Cyanophyta | S1 | Turbid mixed environments (shade-adapted cyanoprokaryotes) |
| Microcystis Kütz. | Cyanophyta | M | Eutrophic to hypereutrophic, small to medium lakes |
|
Cryptomons ovata Ehr. Cryptomonas erosa Ehr. |
Cryptophyta | Y | This codon, mostly including large cryptomonads but also small dinoflagellates, refers to a wide range of habitats, which reflect the ability of its representative species to live in almost all lentic ecosystems when grazing pressure is low |
| Dinobryon Ehr. | Chrysophyta | E | Usually small, shallow, base-poor lakes or heterotrophic ponds |
| Phacus Duj. | Euglenophyta | W1 | Ponds, even temporary, rich in organic matter from husbandry or sewages |
| Trachelomonas Ehr. Em. Defl. | Euglenophyta | W2 | Mesoeutrophic ponds, even temporary, shallow lakes |
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