- Open Access
Toxicity characteristics of sewage treatment effluents and potential contribution of micropollutant residuals
© The Author(s) 2017
- Received: 29 September 2017
- Accepted: 10 November 2017
- Published: 25 November 2017
A typical sewage treatment plant is designed for organic and nutrient removal from municipal sewage water and not targeted to eliminate micropollutants such as pesticides, pharmaceuticals, and nano-sized metals which become a big concern for sustainable human and ecological system and are mainly discharged from sewage treatment plant. Therefore, despite contaminant removal by wastewater treatment processes, there are still remaining environmental risks by untreated pollutants in STP (sewage treatment plant) effluents. This study performed aquatic toxicity tests of raw wastewater and treated effluents in two sewage treatment plants to evaluate toxicity reduction by wastewater treatment process and analyze concentration of contaminants to reveal potential toxic factors in STP effluents.
Water samples were collected from each treatment steps of two STPs, and acute and chronic toxicity tests were conducted following USEPA (United States Environmental Protection Agency) and OECD (Organization for Economic Cooperation and Development) guidelines. Endpoints were immobility for mortality and reproduction effect for estrogenicity.
Acute EC50s (median effective concentration) of influents for Seungki (SK) and Jungnang (JN) STPs are 54.13 ± 32.64% and 30.38 ± 24.96%, respectively, and reduced to 96.49 ± 7.84% and 100%. Acute toxicity reduction was clearly correlated with SS (suspended solids) concentration because of filter feeding characteristics of test organisms. Chronic toxicity tests revealed that lethal effect was reduced and low concentration of influents showed higher number of neonates. However, toxicity reduction was not related to nutrient removal. Fecundity effect positively increased in treated wastewater compared to that in raw wastewater, and no significant differences were observed compared to the control group in JN final effluent implying potential effects of estrogenic compounds in the STP effluents.
Conventional wastewater treatment process reduced some organics and nutritional compounds from wastewater, and it results in toxicity reduction in lethal effect and positive reproductive effect but not showing correlation. Unknown estrogenic compounds could be a reason causing the increase of brood size. This study suggests that pharmaceutical residues and nanoparticles in STP effluents are one of the major micropollutants and underline as one of estrogenic effect factors.
- Toxicity reduction
- Wastewater treatment
A typical sewage treatment plant (STP) is limited for organic and nutrient removal from municipal sewage water. Suspended solids (SS) are also one of the main targets to remove from wastewater. STP processes generally consist of primary settlement process for SS removal and biological treatment process for nutrient such as nitrogen and phosphorus removal. Biological treatment, which is called as the secondary treatment process, includes aerobic, anaerobic, and anoxic processes. Thus, it is expected that other micropollutants such as pharmaceuticals, personal health care products, and detergents are retained at the effluent stream which are subsequently released to the aquatic environment (Fent et al. 2006).
Environmental levels of pharmaceuticals varied from ppbs to ppts according to its media and discharge patterns (Vieno et al. 2005; Loraine and Pettigrove 2006) and their usage pattern (Balakrishna et al. 2017). Carbamazepine, an antidepressant drug, is one of the most detectable pharmaceuticals because of its persistency in the environment even though metformin showed the highest concentration of 8100 ng/L (Kot-Wasik et al. 2016). Pharmaceutical residues in the aquatic environment have been a big concern in terms of its consistent discharge from sewage but it is also considered nontoxic because of relatively low environmental levels and nonsevere acute toxicity resulting in a low risk to humans and aquatic animals.
Nanoparticles are also one of the major micropollutants which should be issued for human health and water environment. Nanomaterials are defined as less than 100 nm of their size and are well known as they show different physicochemical characteristics according to size. Drastically increased usage in the industry resulted in more detection in the environment. Health effects on human and the ecosystem have been studied but some toxicologists doubt its ecological effect because of its size distribution in the environment. Titanium oxides and zinc oxide are one of high-ranked compounds among industrial nanomaterials in terms of annual usage in Korea (Kim et al. 2014), and relevant detections have been reported as they are used for mainly consumer products which finally flows into water environment though STP effluent (Gottschalk et al. 2013). Like pharmaceuticals, ENM (engineered nanomaterials) were measured in the level of ppbs and ppts.
The main objective of this study is to investigate toxicity reduction by performing WET (whole effluent toxicity) tests on raw wastewater, treatment process effluents, and final effluents of sewage treatment plants. In addition, factors which could influence toxic effect in the effluent were studied by contaminant and nutrient removal analysis and by literature reviews.
Test organisms and culturing conditions
Daphnia magna cultures were held in 3-L beakers containing moderately hard water (80–100 mg/L as CaCO3) prepared following the US EPA Guideline (USEPA 2002). Cultures were maintained in a growth chamber at 21 ± 1 °C and 16-h light: 8-h dark photoperiod was employed. The media were renewed every 2 days, and the daphnids were fed daily with 5 ml YCT (Yeast:Ceropyll®:Tetramin®) and 3 ml living Chlorella (1 × 107 cells/ml). Water qualities of the culture media were maintained as follows: pH, 7.4~7.8; hardness, 80~100 mg/L as CaCO3; and alkalinity, 57~64 mg/L as CaCO3.
Acute and chronic toxicity tests
Acute toxicity tests (48 h) were conducted using the grab samples with concentration range of 6.25, 12.5, 25, 50, and 100 vol% in accordance with the recommended procedure outlined in US EPA WET test (USEPA 2002). The immobility of test organisms was measured for endpoint. Standard reference tests were performed twice a month using sodium chloride as the test chemical to compare sensitivity of the test organisms over time.
Chronic toxicity tests (21 days) were conducted using the same range of concentration as mentioned under OECD TG (test guideline) 211 (OECD 2008). Ten neonates for each concentration were randomly selected and placed individually in 40-ml test solution of ten replicates. The test solutions were renewed every other day, and daphnids were fed with 150 μl YCT and 100 μl live Chlorella algae daily. The endpoints observed include molting, mortality, brood size, and number of brood and sex ratio of offspring. All experiments were carried out in the growth chamber at 21 ± 1 °C and a 16-h light:8-h dark photoperiod.
Analytical methods and data analyses
Measurement of the water quality parameters were done as follows: suspended solids (SS)—gravimetric methods, ammonia (NH4-N) and phosphate (PO4-P)—Branne + Luebbe Automatic Analyzer 3 with digital colorimeter, and NO3-N and NO2-N—Ion chromatography (Dionex ICS-100).
In statistical analysis, median effective concentration(EC50) for acute toxicity results and 25% inhibitory concentration(IC25) for chronic reproductive results were calculated using probit analysis, Spearman-Karber and trimmed Spearman-Karber methods with ToxStat (Ver 3.5, West Inc., Cheyenne, WY, USA). Statistically significant differences in toxicity were determined using ANOVA test with SPSS (Ver. 10.0). Nominal concentrations were used throughout the course of the study.
Characteristics of wastewater
Water quality parameters obtained from the grab samples collected from Seungki and Jungnang STPs
Water quality parameter
Seungki Sewage Treatment Plant
Jungnang Water Reclamation Center
8.1 ± 0.1
8.1 ± 0.2
7.9 ± 0.7
7.9 ± 0.3
7.9 ± 0.2
7.8 ± 0.2
7.8 ± 0.1
6.1 ± 2.2
6.2 ± 2.6
8.2 ± 1.0
7.2 ± 1.0
7.5 ± 1.6
8.5 ± 0.1
8.7 ± 0.1
68.3 ± 3.5
54.7 ± 6.4
29.3 ± 4.2
161.7 ± 26.2
41.3 ± 4.7
2.8 ± 0.4
1.9 ± 0.4
Alkalinity (mg/L CaCO3)
154.1 ± 27.2
178.6 ± 70.4
99.4 ± 16.3
118.1 ± 1.8
126.4 ± 3.0
57.5 ± 9.4
59.1 ± 6.2
Hardness (mg/L CaCO3)
201.7 ± 20.2
226.7 ± 25.2
170 ± 20
116.7 ± 28.9
126.7 ± 15.3
106.7 ± 5.8
105 ± 5
26.0 ± 1.4
21.7 ± 0.2
9.2 ± 0.2
21.7 ± 0.3
21.0 ± 0.2
1.7 ± 0.0
1.2 ± 0.8
16.1 ± 2.1
12.7 ± 1.1
8.6 ± 1.8
14.1 ± 1.0
13.8 ± 1.7
9.4 ± 1.4
6.4 ± 1.6
2.5 ± 0.0
1.9 ± 0.8
1.8 ± 0.6
3.2 ± 0.4
2.7 ± 0.7
1.7 ± 0.1
1.1 ± 0.1
3.9 ± 0.0
2.8 ± 0.1
0.9 ± 0.0
3.3 ± 0.0
1.9 ± 0.0
1.4 ± 0.1
0.60 ± 0.0
Acute toxicity test results
It is generally assumed that the dissolved fraction of a toxic substance in surface water is mainly responsible for the toxicity to aquatic organisms. However, toxic compounds are often adsorbed or chemically bound to suspended particles in the water column, depending on the physico-chemical conditions. Daphnia magna are filter-feeding organisms, and contaminated particles might end up in the gastrointestinal tract and exert toxic effects (Weltens et al. 2000). In this study, an average 19.6% suspended solids (SS) reduction was observed in SK PE while a more effective decline was measured in JN PE with 74.44% average SS reduction. Although a secondary precipitation and sedimentation tank was employed after biological treatment in SK STP, final effluent SS were still moderately high with an average of 29.33 mg/L. In contrast, disk filtration treatment employed in JN STP proved to be effective in decreasing the SS of the wastewater to 2.83 ± 0.35 mg/L.
Chronic toxicity tests
Raw wastewater and primary treatment effluents of JN STP exhibited mortality at low effective concentrations (EC50) of 8.94 ± 0.50% and 18.19 ± 0.77%, respectively. On the other hand, SK STP raw wastewater and primary treatment effluent EC50s were identical to each other with values at 18.75%. From the acute toxicity results, it was surmised that suspended solids in the water column may have highly contributed to the mortality of the Daphnia magna. Chronic exposure to suspended solids alone has been reported to induce detrimental and stimulate sublethal effects to daphnids as in their fecundity, growth, and juvenile survival at concentrations of 50 and 100 μg/L (Kirk 1992; Kirk and Gilbert 1990; Arruda et al. 1983; McCabe and O’Brien 1983). The result supports the previous study with the significant difference (p < 0.05) of the EC50s of the SK and JN STPs’ raw wastewater at SS values of 68.3 ± 3.5 mg/L and 161.7 ± 26.2 mg/L, respectively. Significant reduction of the toxicity was noted with JN STP effluent after the primary treatment with EC50 improvement from 8.94 ± 0.50% to 18.19 ± 0.77%. Additionally, disk filtration effluent of JN STP did not exert mortality to the daphnids (data not shown). In contrast, no improvement on the EC50 was observed in SK STP effluent because suspended solids content in the effluent remained relatively high at 54.7 ± 6.4 mg/L.
Besides mortality, average lifespan reflects the overall health and fitness of the test organisms during the 21-day chronic exposure. Effluents from JN STP exhibited substantially truncated average daphnid lifespan, particularly those tested in raw wastewater at 8.34 days and primary treatment effluent at 11.14 days. Conversely, disk filtration and ozonation effluents influenced protracted average lifespan on the test organisms with values 20.80 and 20.78 days, respectively.
As the scope of this study did not include toxicity identification evaluation, we can only attribute the sublethal effects of the sample effluents on the fecundity of the Daphnia magna on suspended materials and particle-bound organic chemicals such as EDCs, PPCPs, and pesticides. One possible effect of contaminated particles on particle-feeding organism like daphnids is a drastic reduction in food intake causing serious chronic effects on the population level. It has been shown many times that toxic products reduce food uptake in daphnids. Moreover, contaminated food particles affect food uptake even more than dissolve contaminants (Allen et al. 1995). The consequences to population growth of mortality during acute tests are commonly acknowledged, even though the relationship between survival and population growth is not a simple function (Caswell, 1989). Both field observations and laboratory studies have demonstrated that suspended materials can have deleterious effects on planktonic species including cladocerans (Bridges et al. 1996). For SK FE, JN DSE and JN FE where none or positive effects on daphnid fecundity were observed can be accredited to be result of ingestion of fine-grained sediment particles with nutritive values as shown in previous study (Dillon 1993; Ankley et al. 1994).
Sun et al. (2008) evaluated the estrogenic activities of the wastewater effluent samples and reported that since some estrogenic substances such as estradiol, bisphenol, and nonylphenol were discharged in conjugated forms, the microbial activity could deconjugate and reactivate them during the early steps of treatment. Hence, there are higher population densities for raw wastewater and primary treatment for both SK and JN STPs. Secondary treatment has been considered as one of the most effective treatment of processes to reduce the estrogenic activity in wastewater (Kirk et al. 2000; Leush et al. 2006). However, still some estrogenic compounds such as estrone showed only 6.3% of removal efficiency and implied high ecological risk (Belhaj et al. 2016). In addition, estrone in effluent showed higher level than in raw wastewater (Mailler et al. 2015; Belhaj et al. 2015), and pharmaceutical residues showed large variation of its removal efficiencies (Yang et al. 2017).
In this study, acute and chronic toxicity tests were successfully employed for the evaluation of the reduction of toxicity of sewage water effluents for two sewage treatment plants in SK STP, Incheon and JN STP, Seoul, Korea. Acute and chronic lethal effect decreased depending on SS removal by wastewater treatment process. As estrogenid effect, fecundity of daphnids was significantly increased in the influent and primary effluents implying presence/attribution of endocrine disrupting chemicals which controls reproduction and embryogenesis in mysid crustaceans. Pharmaceutical residues and nanoparticles in the effluents could be suggested as possible sources for estrogenic effect referring to previous study. However to identify and clarify the potential role of micropollutants on reproduction, further toxicity evaluation is needed.
This research was supported by the Academic research fund of Hoseo university in 2014(Project number: 2014-0442).
This study was funded by the Hoseo University research program (2014-0442).
Availability of data and materials
DMF conducted toxicity tests and statistical analysis. YK designed the study, drafted and revised manuscript. Both authors read and approved the final manuscript.
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