| Literature DB >> 35419189 |
Asus Maizar Suryanto Hertika1, Diana Arfiati1, Evellin Dewi Lusiana1, Renanda B D S Putra2.
Abstract
Background: Contamination of freshwater ecosystems has become a major issue as it threatens public water sources as well as aquatic life. It is important to predict changes in organism health, given a known number of environmental factors and pollutant concentrations, in order to better manage contaminants through biomarker analysis. This study aims to examine the ecosystem health of the Brantas River based on its environmental condition and the hematology profile of Gambusia affinis fish present in the river. This species was chosen because of its wide distribution along the Brantas River, and because it is very tolerant, adaptable, highly abundant, and easy to catch.Entities:
Keywords: biomarker; blood parameter; ecosystem health; river pollution; water quality
Mesh:
Substances:
Year: 2021 PMID: 35419189 PMCID: PMC8978147 DOI: 10.12688/f1000research.74117.2
Source DB: PubMed Journal: F1000Res ISSN: 2046-1402
Figure 1. Sampling locations in the Brantas River watershed.
Methods and instruments used for water quality evaluation.
| Parameter | Unit | Method/Instrument |
|---|---|---|
| Temperature | °C | Lutron PDO-520 |
| pH | - | pH meter |
| Dissolved Oxygen (DO) | mg/L | Lutron PDO-520 |
| Biological Oxygen Demand (BOD) | mg/L | Winkler method
|
| Ammonia (NH 3) | mg/L | Spectrophotometer Genesys 10S UV-Vis |
| Phenol | mg/L | 4-Aminoantipyrine method
|
Physicochemical water quality factor in Brantas River.
| Site | Temperature (°C) | pH | DO (mg/L) | BOD (mg/L) | Ammonia (mg/L) | Phenol (mg/L) |
|---|---|---|---|---|---|---|
| Batu | 23.52 ± 0.34 g | 7.48 ± 0.08 ab | 7.91 ± 0.25 a | 8.17 ± 0.90 g | 0.45 ± 0.07 f | 0.65 ± 0.05 c |
| Malang | 27.10 ± 1.01 f | 7.38 ± 0.10 abc | 6.46 ± 0.27 cd | 10.34 ± 0.60 f | 0.61 ± 0.04 e | 0.77 ± 0.04 bc |
| Jombang | 29.37 ± 1.10 abc | 7.29 ± 0.07 bcd | 6.38 ± 0.05 cd | 11.94 ± 0.74 e | 0.66 ± 0.04 de | 0.71 ± 0.06 bc |
| Kediri1 | 28.44 ± 0.59 cde | 6.87 ± 0.15 f | 6.59 ± 0.22 c | 12.41 ± 0.96 de | 0.73 ± 0.03 bcd | 0.80 ± 0.04 b |
| Kediri 2 | 30.22 ± 0.13 a | 7.42 ± 0.10 abc | 7.46 ± 0.07 b | 13.33 ± 0.09 cd | 0.78 ± 0.04 bc | 0.77 ± 0.05 bc |
| Tulungagung 1 | 30.16 ± 0.34 ab | 7.49 ± 0.05 a | 7.32 ± 0.07 b | 13.96 ± 0.32 bc | 0.79 ± 0.03 b | 0.76 ± 0.04 bc |
| Tulungagung 2 | 27.87 ± 0.15 ef | 7.26 ± 0.16 cd | 6.50 ± 0.34 cd | 14.22 ± 0.32 bc | 0.68 ± 0.07 cde | 0.72 ± 0.07 bc |
| Blitar | 28.19 ± 0.31 def | 7.42 ± 0.13 abc | 7.10 ± 0.29 b | 14.23 ± 0.13 bc | 0.49 ± 0.03 f | 0.70 ± 0.04 bc |
| Mojokerto | 29.08 ± 0.74 bcd | 7.17 ± 0.10 de | 6.12 ± 0.28 d | 18.40 ± 0.85 a | 1.11 ± 0.20 a | 1.14 ± 0.24 a |
| Surabaya | 29.73 ± 0.29 ab | 6.98 ± 0.12 ef | 6.68 ± 0.41 c | 14.77 ± 0.27 b | 0.66 ± 0.05 de | 0.77 ± 0.04 bc |
Figure 2. Boxplot of Gambusia affinis’ hematology profile which caught in study area (a) Erythrocyte; (b) Leucocyte; (c) Micronuclei.
Figure 3. Scatter plot and Pearson correlation analysis between erythrocyte and water quality parameters.
DO = dissolved oxygen; BOD = biological oxygen demand.
Figure 4. Scatter plot and Pearson correlation analysis between leucocyte and water quality parameters.
DO = dissolved oxygen; BOD = biological oxygen demand.
Figure 5. Scatter plot and Pearson correlation analysis between micronuclei and water quality parameters.
DO = dissolved oxygen; BOD = biological oxygen demand.