The effect of physicochemical parameters on the abundance of zooplankton of River Adada, Enugu, Nigeria

Because of the pivotal role of zooplankton in most aquatic ecosystems; there is constant need to explore the effect of stressors (such as physicochemical properties of freshwater) on their abundance. We documented the effect of temperature, pH, turbidity, dissolved oxygen (DO), nitrate (NO3-), and p...

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Main Authors: Nkiruka F. Oparaku, Felix A. Andong, Ijem A. Nnachi, Elijah S. Okwuonu, James C. Ezeukwu, Joseph C. Ndefo
Format: Article
Language:English
Published: Taylor & Francis Group 2022-12-01
Series:Journal of Freshwater Ecology
Subjects:
Online Access:http://dx.doi.org/10.1080/02705060.2021.2011793
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author Nkiruka F. Oparaku
Felix A. Andong
Ijem A. Nnachi
Elijah S. Okwuonu
James C. Ezeukwu
Joseph C. Ndefo
author_facet Nkiruka F. Oparaku
Felix A. Andong
Ijem A. Nnachi
Elijah S. Okwuonu
James C. Ezeukwu
Joseph C. Ndefo
author_sort Nkiruka F. Oparaku
collection DOAJ
description Because of the pivotal role of zooplankton in most aquatic ecosystems; there is constant need to explore the effect of stressors (such as physicochemical properties of freshwater) on their abundance. We documented the effect of temperature, pH, turbidity, dissolved oxygen (DO), nitrate (NO3-), and phosphate (PO4³-) on the abundance of zooplankton of the River Adada, Nigeria. Using a manual pump, zooplankton were collected from three strategic stations from January to April (dry season) and June to September (rainy season). A total of 2,219 (dry = 945; rainy = 1,274) zooplankton occurred in the following descending order of abundance: copepods < rotifers < cladocerans < ostracods < insect larva. Whereas based on species number, cladocerans (n = 10) < copepods (n = 8) < rotifers (n = 7) < insect larva (n = 4) < ostracods (n = 2) occurred in this descending order. The downstream (station C) had more zooplankton (dry = 427; rainy = 391), followed by the mid-stream (station B; dry = 216; rainy = 591) and upstream (station A; dry = 302; rainy = 292). There was also a significant (P < 0.05) joint interactive effect of thermal condition on turbidity, pH, DO, PO4³- and NO3- to influence zooplankton abundance. Indicating that temperature is an important factor determining the assemblage of zooplankton in freshwater. Nevertheless, to assure an accurate evaluation of the effect of physicochemical parameters on zooplankton abundance in freshwater, future studies should include extended study periods and make use of more sophisticated trapping technique that would ensure the collection of a larger sample size with more species of zooplankton.
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spelling doaj.art-3877bcfd07be49bea62d7b83c2b886c92022-12-21T19:29:22ZengTaylor & Francis GroupJournal of Freshwater Ecology0270-50602156-69412022-12-01371335610.1080/02705060.2021.20117932011793The effect of physicochemical parameters on the abundance of zooplankton of River Adada, Enugu, NigeriaNkiruka F. Oparaku0Felix A. Andong1Ijem A. NnachiElijah S. OkwuonuJames C. EzeukwuJoseph C. Ndefo2Department of Zoology and Environmental Biology, University of NigeriaDepartment of Zoology and Environmental Biology, University of NigeriaDepartment of Science Laboratory Technology, University of NigeriaBecause of the pivotal role of zooplankton in most aquatic ecosystems; there is constant need to explore the effect of stressors (such as physicochemical properties of freshwater) on their abundance. We documented the effect of temperature, pH, turbidity, dissolved oxygen (DO), nitrate (NO3-), and phosphate (PO4³-) on the abundance of zooplankton of the River Adada, Nigeria. Using a manual pump, zooplankton were collected from three strategic stations from January to April (dry season) and June to September (rainy season). A total of 2,219 (dry = 945; rainy = 1,274) zooplankton occurred in the following descending order of abundance: copepods < rotifers < cladocerans < ostracods < insect larva. Whereas based on species number, cladocerans (n = 10) < copepods (n = 8) < rotifers (n = 7) < insect larva (n = 4) < ostracods (n = 2) occurred in this descending order. The downstream (station C) had more zooplankton (dry = 427; rainy = 391), followed by the mid-stream (station B; dry = 216; rainy = 591) and upstream (station A; dry = 302; rainy = 292). There was also a significant (P < 0.05) joint interactive effect of thermal condition on turbidity, pH, DO, PO4³- and NO3- to influence zooplankton abundance. Indicating that temperature is an important factor determining the assemblage of zooplankton in freshwater. Nevertheless, to assure an accurate evaluation of the effect of physicochemical parameters on zooplankton abundance in freshwater, future studies should include extended study periods and make use of more sophisticated trapping technique that would ensure the collection of a larger sample size with more species of zooplankton.http://dx.doi.org/10.1080/02705060.2021.2011793seasonscopepodsphysicochemical propertiesfreshwaterriver adada
spellingShingle Nkiruka F. Oparaku
Felix A. Andong
Ijem A. Nnachi
Elijah S. Okwuonu
James C. Ezeukwu
Joseph C. Ndefo
The effect of physicochemical parameters on the abundance of zooplankton of River Adada, Enugu, Nigeria
Journal of Freshwater Ecology
seasons
copepods
physicochemical properties
freshwater
river adada
title The effect of physicochemical parameters on the abundance of zooplankton of River Adada, Enugu, Nigeria
title_full The effect of physicochemical parameters on the abundance of zooplankton of River Adada, Enugu, Nigeria
title_fullStr The effect of physicochemical parameters on the abundance of zooplankton of River Adada, Enugu, Nigeria
title_full_unstemmed The effect of physicochemical parameters on the abundance of zooplankton of River Adada, Enugu, Nigeria
title_short The effect of physicochemical parameters on the abundance of zooplankton of River Adada, Enugu, Nigeria
title_sort effect of physicochemical parameters on the abundance of zooplankton of river adada enugu nigeria
topic seasons
copepods
physicochemical properties
freshwater
river adada
url http://dx.doi.org/10.1080/02705060.2021.2011793
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