Seasonal and treatment-process variations in invertebrates in drinking water treatment plants

Zhiling Wu, Xianchun Tang, Hongbin Chen

PDF(702 KB)
PDF(702 KB)
Front. Environ. Sci. Eng. ›› 2021, Vol. 15 ›› Issue (4) : 62. DOI: 10.1007/s11783-020-1354-6
RESEARCH ARTICLE
RESEARCH ARTICLE

Seasonal and treatment-process variations in invertebrates in drinking water treatment plants

Author information +
History +

Highlights

• Seasonal and treatment-process variations in invertebrates in a DWTP were analyzed.

• The propagation and leakage of invertebrates in BAC filter were the most serious.

• Invertebrates can survive and reproduce in chlorine disinfected clear water tanks.

• Proportions of endogenous invertebrates increased along the treatment process.

Abstract

Problems associated with excessive propagation and leakage of invertebrates in drinking water have received increasing attention in recent years. We performed a monthly survey of invertebrate abundance and taxa in the effluent of each treatment stage in a drinking water treatment plant between May 2015 and April 2016 and analyzed seasonal and treatment-process variations in invertebrates. The results showed that invertebrate abundances in raw water, effluent of the biological activated carbon (BAC) filter, and finished water significantly correlated with water temperature, whereas no correlation was observed between water temperature and invertebrate abundance in the effluents of the sedimentation tank and sand filter. The dominant taxa in the effluent of each treatment stage were rotifers, nematodes, and crustaceans. The sedimentation tank could efficiently remove invertebrates with an annual average removal rate of 92%. The propagation and leakage of invertebrates occurred in the sand and BAC filters but more seriously in the latter. The average reproduction rate in the BAC filter was 268.8% with rotifers as the taxon that leaked the most. Invertebrate survival and reproduction were also observed in the chlorine-disinfected clean water reservoir with an average reproduction rate of 41.9%. Owing to differences in chlorine resistance, the reproduction ability of the dominant taxa was in the order nematodes>crustaceans>rotifers. The proportion of endogenous invertebrates gradually increased along the treatment process. The average proportion of endogenous invertebrates in the finished water was higher than 79.0%. Our findings suggested that waterworks should pay more attention to endogenous invertebrate growth.

Graphical abstract

Keywords

Invertebrates / Drinking water / Seasonal variations / Treatment process

Cite this article

Download citation ▾
Zhiling Wu, Xianchun Tang, Hongbin Chen. Seasonal and treatment-process variations in invertebrates in drinking water treatment plants. Front. Environ. Sci. Eng., 2021, 15(4): 62 https://doi.org/10.1007/s11783-020-1354-6

References

[1]
Adam K, Heath R G M, Steynberg M C (1998). Invertebrates as biomonitors of sand-filter efficiency. Water S.A., 24(1): 43–48
[2]
Bichai F, Barbeau B, Dullemont Y, Hijnen W (2010). Role of predation by zooplankton in transport and fate of protozoan (oo)cysts in granular activated carbon filtration. Water Research, 44(4): 1072–1081
CrossRef Google scholar
[3]
Bichai F, Barbeau B, Payment P (2009). Protection against UV disinfection of E. coli, bacteria and B. subtilis, spores ingested by C. elegans, nematodes. Water Research, 43(14): 3397–3406
CrossRef Google scholar
[4]
Bichai F, Dullemont Y, Hijnen W, Barbeau B (2014). Predation and transport of persistent pathogens in GAC and slow sand filters: A threat to drinking water safety? Water Research, 64: 296–308
CrossRef Google scholar
[5]
Bichai F, Payment P, Barbeau B (2008). Protection of waterborne pathogens by higher organisms in drinking water: A review. Canadian Journal of Microbiology, 54(7): 509–524
CrossRef Google scholar
[6]
Chen Y Q, Zhang J S, Liu L J, You Z L, Zhou L, Liu Q (2005). Infestation and key control of Chironamid Midge in water supply. Shenzhen Science & Technology, (zl):293–297
[7]
da Costa J B, Rodgher S, Daniel L A, Espindola E L G (2014). Toxicity on aquatic organisms exposed to secondary effluent disinfected with chlorine, peracetic acid, ozone and UV radiation. Ecotoxicology (London, England), 23(9): 1803–1813
CrossRef Google scholar
[8]
Han J, Jeon B, Futatsugi N, Park H (2013). The effect of alum coagulation for in-lake treatment of toxic Microcystis and other cyanobacteria related organisms in microcosm experiments. Ecotoxicology and Environmental Safety, 96: 17–23
CrossRef Google scholar
[9]
Kâ S, Pagano M, Bâ N, Bouvy M, Leboulanger C, Arfi R, Thiaw O T, Ndour E H M, Corbin D, Defaye D, Cuoc C, Kouassi E (2006). Zooplankton distribution related to environmental factors and phytoplankton in a shallow tropical lake (Lake Guiers, Senegal, West Africa). International Review of Hydrobiology, 91(5): 389–405
CrossRef Google scholar
[10]
Li J Y, Duan D (2012). Research on the leakage and control of micro-animals in the O3-BAC treatment processes. Water & Wastewater Engineering, 38(9): 165–168
[11]
Lin T, Chen W, Zhang J S (2012). Optimization and mechanism of copepod zooplankton inactivation using ozone oxidation in drinking water treatment. Journal of Water Supply: Research & Technology- Aqua, 61(6): 342–351
CrossRef Google scholar
[12]
Liu D M, Cui F Y, Wu Y Q, Lin T, Zhang M, Yu M X (2007). Removal of cyclops in pre-oxidizing cooperation water treatment process. Journal of Zhejiang University. Science A, 8(11): 1826–1830
CrossRef Google scholar
[13]
Locas A, Barbeau B, Gauthier V (2007). Nematodes as a source of total coliforms in a distribution system. Canadian Journal of Microbiology, 53(5): 580–585
CrossRef Google scholar
[14]
Nie X B, Li Z H, Long Y N, He P P, Xu C (2017). Chlorine inactivation of Tubifex tubifex in drinking water and the synergistic effect of sequential inactivation with UV irradiation and chlorine. Chemosphere, 177: 7–14
CrossRef Google scholar
[15]
Qi W, Li W, Zhang J, Wu X, Zhang J, Zhang W (2019). Effect of biological activated carbon filter depth and backwashing process on transformation of biofilm community. Frontiers of Environmental Science & Engineering, 13(1): 15
CrossRef Google scholar
[16]
Schreiber H, Schoenen D, Traunspurger W (1997). Invertebrate colonization of granular activated carbon filters. Water Research, 31(4): 743–748
CrossRef Google scholar
[17]
Shaddock B (2005). An Evaluation of Invertebrate Dynamics in a Drinking Water Distribution System: A South African Perspective. Magister Scientiae in Zoology in the Faculty Science at the Rand Afrikaas University. Zoology
[18]
Stefanidis K, Papastergiadou E (2010). Influence of hydrophyte abundance on the spatial distribution of zooplankton in selected lakes in Greece. Hydrobiologia, 656(1): 55–65
CrossRef Google scholar
[19]
Tan Q, Li W, Zhang J, Zhou W, Chen J, Li Y, Ma J (2019). Presence, dissemination and removal of antibiotic resistant bacteria and antibiotic resistance genes in urban drinking water system: A review. Frontiers of Environmental Science & Engineering, 13(3): 36
CrossRef Google scholar
[20]
van Lieverloo J H, Bosboom D W, Bakker G L, Brouwer A J, Voogt R, De Roos J E M (2004). Sampling and quantifying invertebrates from drinking water distribution mains. Water Research, 38(5): 1101–1112
CrossRef Google scholar
[21]
Wahl D H, Goodrich J, Nannini M A, Dettmers J M, Soluk D A (2008). Exploring riverine zooplankton in three habitats of the Illinois River ecosystem: Where do they come from? Limnology and Oceanography, 53(6): 2583–2593
CrossRef Google scholar
[22]
Wang Q, You W, Li X W, Yang Y F, Liu L J (2014). Seasonal changes in the invertebrate community of granular activated carbon filters and control technologies. Water Research, 51: 216–227
CrossRef Google scholar
[23]
Weeks M A, Leadbeater B S C, Callow M E, Bale J S, Barrie Holden J (2007). Effects of backwashing on the prosobranch snail Potamopyrgus jenkinsi Smith in granular activated carbon(GAC) absorbers. Water Research, 41(12): 2690–2696
CrossRef Google scholar
[24]
Wei W Z, Chen R M, Wang L F, Fu L X (2017). Spatial distribution of crustacean zooplankton in a large river-connected lake related to trophic status and fish. Journal of Limnology, 76(3): 546–554
CrossRef Google scholar
[25]
Wu Z L, Chen H B (2018). Comparison of invertebrate removal by traditional-BAC and pre-BAC treatment processes: verification in a full-scale drinking water treatment plant. Water Science and Technology: Water Supply, 18(4): 1261–1269
CrossRef Google scholar
[26]
Wu Z L, Cheng Y, Chen T H, Tang X C, Chen H B (2018). Inactivation efficiency of sodium hypochlorite on rotifers and rotifer eggs. Desalination and Water Treatment, 115: 145–152
CrossRef Google scholar
[27]
Wu Z L, Tang X C, Chen H B (2017a). Influence of the type of activated carbon on invertebrate leakage in biological activated carbon filter. Desalination and Water Treatment, 94: 40–46
CrossRef Google scholar
[28]
Wu Z L, Zhu J, Tang X C, Chen H B (2017b). Synergistic effect of chlorination and sand filtration for efficient elimination of invertebrate leakage in BAC filter. Desalination and Water Treatment, 79: 235–242
CrossRef Google scholar
[29]
Xu B J (2000). Water Treatment Theory. Beijing: China Architecture & Building Press
[30]
Yin W C, Zhang J S, Liu L J, Zhao Y, Li T, Lin C (2012). Removal efficiency of invertebrates in the filtrate of biologically activated carbon filter with sand bed. Journal of Water Supply: Research & Technology- Aqua, 61(4): 228–239
CrossRef Google scholar
[31]
Zhang R (2015). The clean water reservoir’s cleaning process and technical emphases. Shanxi Science and Technology, 30(2): 158–159 (in Chinese)
[32]
Zhu J (2014). Study on the migration, leakage and control of invertebrates in purification processes with polluted raw water. Dissertation for Doctor’s Degree. Shanghai: Tongji University(in Chinese)
[33]
Zhu J, Chen H B, Chen C, Dai X H (2014). Study on the migration and inactivation of invertebrates in the advanced treatment process in waterworks. Fresenius Environmental Bulletin, 23(6): 1314–1321
[34]
Zhu J, Tang X C, Wu Z L, Chen H B (2018). Migration and Control of Invertebrates in waterworks with advanced treatment. Journal of Environmental Engineering, 144(7): 04018043

Acknowledgements

This work was supported by the National Five-year Water Special Project (No. 2017ZX07207004). We acknowledge the support of the waterworks that participated in this investigation. We would like to thank the anonymous reviewers for their helpful comments.

RIGHTS & PERMISSIONS

2020 Higher Education Press
AI Summary AI Mindmap
PDF(702 KB)

Accesses

Citations

Detail

Sections
Recommended

/