Figure 1

Figure 2

Figure 3

Figure 4

Figure 5

Figure 6

List of ciliate species encountered in Daya Bay
| Ciliate species | |||
|---|---|---|---|
| 1 | Amphorellopsis acuta | 22 | Tintinnopsis schotti |
| 2 | Codonellopsis morchella | 23 | Tintinnopsis tentaculata |
| 3 | Codonellopsis ostenfeldi | 24 | Tintinnopsis tubulosa |
| 4 | Dadayiella ganymedes | 25 | Tintinnopsis turgida |
| 5 | Eutintinnus fraknoii | 26 | Tintinnopsis vosmaeri |
| 6 | Eutintinnus stramentus | 27 | Wangiella dicollaria |
| 7 | Favella companula | 28 | Helicostomella longa |
| 8 | Leprotintinnus nordqvisti | 29 | Strombidium conicum |
| 9 | Leprotintinnus simplex | 30 | Strombidium globosaneum |
| 10 | Salpingacantha minutissima | 31 | Strombidium major |
| 11 | Metacylis tropica | 32 | Strombidium sp. |
| 12 | Metacylis oviformis | 33 | Spirotontonia turbinata |
| 13 | Stenosemella pacifica | 34 | Laboea strobila |
| 14 | Tintinnopsis minuta | 35 | Euplotes eurystomus |
| 15 | Tintinnopsis radix | 36 | Mesodinium rubrum |
| 16 | Tintinnopsis tocantinencis | 37 | Didinium nasufum |
| 17 | Tintinnopsis beroidea | 38 | Lacrymaria sp. |
| 18 | Tintinnopsis butschlii | 39 | Amphileptus sp. |
| 19 | Tintinnopsis corniger | 40 | Cyclidium sp. |
| 20 | Tintinnopsis digita | 41 | Prorodon sp. |
| 21 | Tintinnopsis nucula | ||
Dominant ciliate species in each season in Daya Bay (species dominance, Y ≥ 0_02)
| Dominant species | Y | |||
|---|---|---|---|---|
| Winter | Spring | Summer | Autumn | |
| Tintinnopsis minuta | 0.5716 | - | - | 0.0215 |
| Tintinnopsis beroidea | 0.0863 | - | - | - |
| Strombidium conicum | 0.0387 | 0.4583 | 0.0336 | 0.1792 |
| Strombidium globosaneum | 0.1165 | 0.0538 | 0.0413 | 0.1481 |
| Spirotontonia turbinata | - | 0.3678 | 0.0656 | 0.0443 |
| Laboea strobila | - | 0.0687 | - | - |
| Amphorellopsis acuta | - | - | 0.1321 | - |
| Eutintinnus stramentus | - | - | 0.0407 | - |
| Tintinnopsis tocantinencis | - | - | 0.0200 | 0.0447 |
| Tintinnopsis corniger | - | - | 0.0235 | - |
| Helicostomella longa | - | - | 0.3221 | - |
| Tintinnopsis nucula | - | - | - | 0.0937 |
| Wangiella dicollaria | - | - | - | 0.0507 |
| Mesodinium rubrum | - | - | - | 0.0948 |
Summary of results from biota-environment (BIOENV) analysis, with the top ten correlations corresponding to different variables (R is Spearman correlation coefficient)
| Rank | R | Environmental variables |
|---|---|---|
| 1 | 0.391 | Sal., pH |
| 2 | 0.388 | Sal., NO2-, NO3-, NH4+, PO43- |
| 3 | 0.387 | DO, NO2-, NO3-, NH4+, PO43- |
| 4 | 0.386 | Temp., Sal., pH |
| 5 | 0.386 | Temp., NO2-, NO3-, NH4+, PO43- |
| 6 | 0.386 | Sal., DO, NO2-, NO3-, PO43- |
| 7 | 0.384 | pH, NO2-, NO3-, NH4+, PO43- |
| 8 | 0.384 | Sal., pH, NO2-, NO3-, PO43- |
| 9 | 0.383 | Temp., Sal., NO2-, NO3-, PO43- |
| 10 | 0.383 | pH, DO, NO2-, NO3-, PO43- |
Correlation between environmental variables and ciliate abundance (N), the number of species (S) in four seasons in Daya Bay
| parameters | Winter | Spring | Summer | Autumn | ||||
|---|---|---|---|---|---|---|---|---|
| N | S | N | S | N | S | N | S | |
| Temp. | -0.448 | 0.088 | 0.374 | -0.181 | 0.282 | -0.751** | -0.470 | -0.083 |
| Sal. | -0.606* | 0.441 | -0.840** | -0.103 | 0.881** | -0.720** | 0.231 | 0.431 |
| pH | 0.748** | -0.537 | -0.448 | -0.061 | 0.342 | -0.241 | 0.309 | -0.169 |
| DO | 0.672* | -0.352 | -0.379 | -0.330 | 0.757** | -0.560 | -0.214 | -0.064 |
| NO2- | -0.469 | 0.454 | 0.331 | -0.088 | 0.772** | -0.549 | 0.499 | 0.395 |
| NO3- | -0.489 | 0.185 | 0.341 | -0.02 | -0.346 | 0.049 | -0.161 | -0.511 |
| NH4+ | -0.113 | 0.543 | 0.434 | -0.105 | -0.088 | 0.225 | 0.590* | 0.688* |
| DIN | -0.484 | 0.247 | 0.468 | -0.091 | 0.179 | -0.155 | 0.474 | 0.338 |
| PO43- | -0.329 | 0.693* | 0.547 | -0.165 | 0.677** | -0.278 | -0.423 | -0.794** |
| Chl a | 0.395 | 0.179 | 0.244 | 0.432 | 0.026 | 0.047 | -0.065 | -0.298 |
Environmental variables for Daya Bay water samplings in winter 2013, spring, summer and autumn 2014
| Parameters | Unit | Winter | Spring | Summer | Autumn |
|---|---|---|---|---|---|
| Temp. | °C | 16.93 | 24.73 | 27.75 | 24.89 |
| Sal. | PSU | 32.83 | 31.86 | 33.94 | 33.80 |
| pH | 8.27 | 8.31 | 8.07 | 8.20 | |
| DO | mg l-1 | 7.21 | 5.98 | 5.45 | 5.46 |
| NO2- | μmol l-1 | 0.39 | 0.27 | 0.63 | 0.20 |
| NO3- | 1.57 | 1.73 | 7.05 | 2.09 | |
| NH4+ | 1.53 | 1.74 | 3.12 | 1.78 | |
| DIN | 3.49 | 3.74 | 10.8 | 4.08 | |
| PO43- | 0.29 | 0.20 | 0.41 | 0.22 | |
| Chl a | μg l-1 | 1.78 | 2.07 | 3.92 | 2.48 |