Analysis of Phosphate, Nitrate and Macrozoobenthos Density in
Belawan River
Mayang Sari Yeanny
and Ternala Alexander Barus
Department of Biology, Universitas Sumatera Utara, Medan, Indonesia
Keywords: Phosphate, Nitrate, Macrozoobenthos, Belawan River
Abstract: The goals of this research was to identify Phosphate and Nitrate contents and also macrozoobenthos density
in Belawan River. Activities done by the community such as industries, PLTU, PDAM and aquaculture are
found in Belawan River area. This action produce waste straightly discharged into water river, emerging
several bad effect on water quality such as Phosphate, Nitrate, and Macrozoobenthos density. Retrieval of
data with Purposive Random Sampling with five analysis the location.The method used in this research was
included in the measurement of density (K), KR (relative density), and FR (frequency of attendance) of
Macrozoobenthos. Identification of Macrozoobenthos results obtained in the Belawan river was amounted
as nine genera. The lowest Marcozzoobenthos density was at the Station 5 (Scylla), Station 4 (Hirudo),
Station 2 (Microbachiumand Melanoides) and Station 1 (Melanoides) with a density of 3.703, and the
highest was instation 4 (Polymesodaerosa) with a density of 629.62. Based on phosphate concentrations, it
is included as hypertrophic (0.14-0.18 mg/l,). Based on nitrate concentration, it is included as eutrophicand
mesotrophic waters (1.18-7.57 mg/l).
1 INTRODUCTION
Activities done by the community such as industries,
PLTU, PDAM and aquaculture are found in the
Belawan River area. Waste produce from these
activities is straightly released into the river,
emerging in several bad effect on water qualityand
the contingency of the aquatic biota. The condition
of the Belawan river are based on its tributary, the
condition of the land and the watersit passes
through. (Yeanny, 2018).
Phosphate and nitrate are included as sources of
nutrients that are needed by aquatic biota for energy
sources by organisms. Organisms need nutrients in
the form of phosphate and nitrates. The forms of
sediment nutrients are divided into 3 forms that are
on the surface of sediments,in sediments and
dissolved in sedimentary pore water. Water biota
that really needs nitrate and phosphate, one of them
is Macrozoobenthos. Macrozoobenthos are live in
sediments, under water and sediment eater, which
has digging properties, in which this areas contain
high as in sediments that contain lots of nutrients
found in the river (Firmansyah, et al., 2016)
Analysis of phosphate, nitrate, and
macrozoobenthos density still has an adequate of
scientific data, meanwhile this scientific data is an
important issues in river management in water
analysis. Therefore, it is necessary to undergo an
analysis of phosphate, nitrate, and macrozoobenthos
density, to obtain scientific data, results that can be
used to assess the macrozoobenthos condition of in
the river.
This purpose of observing the results of the
analysis phosphate, nitrate countent and
macrozoobenthos in the Belawan River with an
approaches, that is (1) Macrozoobenthos analysis of
including ; K (density), KR (relative density) and
FR (frequency of attendance). (2) Describe the
relation between macrozoobenthos with phosphate
and nitrate.
2 RESEARCH METHODS
2.1 Materials and Methods
Sampling in March - September 2018. The stations
were determined based on the community activities
different. The sample was done with 3 repetition and
the sampling started from upstream to downstream of
Belawan river. The number of sampling site was five.
Yeanny, M. and Barus, T.
Analysis of Phosphate (PO4), Nitrate (NO3) Contents and Macrozoobenthos Density in Belawan River.
DOI: 10.5220/0010200300002775
In Proceedings of the 1st International MIPAnet Conference on Science and Mathematics (IMC-SciMath 2019), pages 431-434
ISBN: 978-989-758-556-2
Copyright
c
2022 by SCITEPRESS Science and Technology Publications, Lda. All rights reserved
431
Table 1.
Station
I
Deli Serdang District,
Salam Tani Village, Pancur
Batu Sub-district
Control No
activity/
Upstream
Station
II
Deli Serdang District
Sunggal kanan Village,
Sunggal Sub-district
Domestic
Habitation
Station
III
Deli Serdang District
Kampung Lalang Sunggal
Sub-district
Market,
Hotel
Station
IV
Deli Serdang District
Kelambir 5 Village,
Hamparan Perak Sub-
district
Paper
Industries,
Soy
Industries
Station
V
Medan Belawan City
Sicanang Village, Medan
Belawan Sub-district
Downstream
(estuary)
2.2 Phosphates and Nitrate Sampling
Phosphates and Nitrates measurement results data
can be seen in Table 2:
Table 2. Phosphates and Nitrates Parameters.
No. Parameter Tools Measurment
Location
1 Phosphate Atomic
Absorption
Spectrofotometer
(AAS)/Ascorbic
Acid
Laboratory
2 Nitrate Atomic
Absorption
Spectrofotometer
(AAS)/Screening
Laboratory
2.3 Macrozoobenthos Sample
Collection
The selected sample locations five (5) which
provided Macrozoobenthos samples were based on
the local community activities from upstream to
downstream. The data collecting method used was
Purposive random sampling. This method used to
collect the macrozoobenthos samples. Afterward,
Suber net was used to collect the sample on each
sampling point. The collected macrozoobenthos
samples were put in a bottle and preserved using 4%
formalin. In the laboratory, the samples were
preserved with 70% alcohol. Identification was done
using identification book; Streble and Krauter
(1988), Oennak (1978), Edmonson (1953).
2.4 Data Analysis
Water quality analysis using standard method
APHA, (2005) and macrozoobenthos analysis as
follows :
(1) Density (K)
(1)
K = density
a = the number of macrozoobenthos
b = area of plots
(2) Relative Density (KR)
(2)
ni= the number of ind of a kind
ΣN = total of all individuals
(3) Frequency of Attendance (FK)
(3)
FK = 0-25 (Very Rarely)
25-50 (Rarely)
50-75 (Many)
>75 (Very much
3 RESULTS AND DISCUSSIONS
3.1 Phosphate and Nitrate Contents
Analysis
Analysis of phosphate and nitrate contents on Table
3 below provided data based on Phosphate and
Nitrate measurements in Belawan River:
Table 3. The Value Phosphate and Nitrate Contents in the
Belawan river.
No Parameter Station
1 2 3 4 5
1 Phosphate
(PO
4
)
0.15 0.14 0.17 0.18 0.16
2 Nitrate
(NO
3
)
1.18 0.53 4.41 7.57 3.45
b
a
K
%100x
N
ni
KR
10
0
plots ofnumber Total
typeaby occupied is plots ofnumber The
xFK
IMC-SciMath 2019 - The International MIPAnet Conference on Science and Mathematics (IMC-SciMath)
432
Belawan river phosphateis at the station IV had
the highest value (0.18 mg/l) while station II resulted
as the lowest one (0.14 mg/l). Stated in MENLH No.
51 of 2004 the maximum phosphate concentration of
phospat for marinelife is 0.015, has exceeded the
Belawan river quality standard.
T Phosphate content in the river, namely the
range between > 0.13 (hypertrophic) 0.04 to 0.13
(eutrophic) 0.015 to 0.04 (mesotrophic) < 0.015
(oligotrophic) (Hakanson 2006). Furthermore, fresh
water was ranged from > 0.06 (hypertrophic), 0.025
to 0.06 (eutrophic), 0.008 to 0.025 (mesotrophic)
and < 0.008 (oligotrophic). Belawan river phosphate
concentration was included as hypertrophic.
According to Joshimura (1966) in Hartoko (2010)
phosphate content was presented in Table 4.
Belawan river phosphate content was ranged from
0.14 to 0.18 (very good fertility).
Table 4. Phosphate based on fertility levelsin water
Aquatic Fertility Phosphate
Low 0.000
0.020 mg/l
Adequate 0.021
0.050 mg/l
Goo
d
0.051
0.100 mg/l
Very Goo
d
0.101
0.200 mg/l
Excellen
t
0.201 mg/l or more
The Belawan river nitrate concentrations was ranged
from 1.18 to 7.57 (station II had the lowest value
and the highest was at station IV). It has passed the
enviromental quality standart ( MENLH of 2004 No.
51 attachment III that nitrate 0.008). Nitrate
contentis presented in Table 5 according
Vollenweider (1969) in Effendi (2003)
Table 5. Nitrate based on fertilitylevelsin water.
Category
N
itrate Conten
t
Oligotrophic 0-1 mg/l
Mesotrophic 1-5 mg/l
Eutrophic 5-50 mg/l
Nitrate levels based on fertility levels (Table 5) in
The Belawan river, are namely 1.18-7.57 mg/l
(eutrophic and mesotrophic). This was in accordance
with Wetzal (2001), eutrophic waters have level
ranging from 5-50 mg/l, mesotrophic (1-5 mg/l)
and oligotrophic (0-1 mg/l). Belawan river is
categorized aseutrophic and mesotrophic waters.
3.2 Analysis of Density (K), Relative
Density (KR) and Frequency of
Attendance (FK) Macrozoobenthos
in Belawan River.
Analysis of Density (K), Relative Density (KR) and
Frequency of Attendance (FK) Macrozoobenthos in
Belawan River are presented in Table 6 and 7.
Table 6. Analysis of Density (K) (ind/m2), KR (Relative Density) (%) and FR (Frequency of Attendance) (%)
Macrozoobenthos at Station I and II in Belawan River.
Genera Station I Station II
K (ind/m
2
) KR (%) FK (%) K (ind/m
2
)KR (%) FK (%)
Hirudo - - - - - -
Baetidae 25.92 25.92 66.67 - - -
Polymesodaerosa
Paguroide
Scylla
Macrobrachium 3.703 2.22 33.33
Fillopaludinajavanica
Melanoides 3.703 3.70 33.33 3.703 2.22 33.33
Gerrisremigis 70.37 70.37 100 159.25 95.55 100
Total 99.993 100 166.656 100
Analysis of Phosphate (PO4), Nitrate (NO3) Contents and Macrozoobenthos Density in Belawan River
433
Table 7. Analysis of Density (K) (ind/m
2
), KR (Relative Density) (%) and FR (Frequency of Attendance) (%)
Macrozoobenthos at Station III, IV and V in Belawan River
Genera Station III `Station IV Station V
K
(ind/m
2
)
KR
(%)
FK
(%)
K
(ind/m
2
)
KR
(%)
FK
(%)
K
(ind/m
2
)
KR
(%)
FK
(%)
Hirudo - - - 3.703 0.57 33.33 - - -
Baetidae - - - - - - - - -
Polymesodaerosa - - - 629.62 98.26 100 - - -
Paguroide - - - - - - 140.74 97.43 100
Scylla - - - - - - 3.703 2.5 33.33
Macrobrachium - - - - - - - - -
Fillopaludinajavanica 18.51 100 66.67 - - - - - -
Melanoides - - - 7.407 1.15 33.33 - - -
Gerrisremigis - - - - - - - - -
Total 18.51 100 66.67 640.73 100 144.443 100
Based on Table 6 and 7, The lowest
Macrozoobenthos density was at the Station 5
(Scylla), Station 4 (Hirudo), Station 2
(Microbachiumand Melanoides) and Station 1
(Melanoides) with a density of 3.703, and the
highest was in station 4 (Polymesodaerosa) with a
density of 629.62.
4 CONCLUSION
Analysis of phosphate (PO
4
), nitrate (NO
3
) contents,
macrozoobenthos density, with the conclusion that
phosphate was ranged from 0.14 -0.18 mg/l
(hypertrophic). Nitrate was ranged from 1.18-7.57
mg/l (eutrophic and mesotrophic). Macrozoobenthos
obtained amounted as 9 general. The lowest
Macrozoobenthos density was at the Station 5
(Scylla), Station 4 (Hirudo), Station 2
(Microbachiumand Melanoides) and Station 1
(Melanoides) with a density of 3.703, and the
highest was in station 4 (Polymesodaerosa) with a
density of 629.62.
ACKNOWLEDGEMENT
The authors of this research uttered gratitude for all
stakeholder who assisted this research. This research
is funded by no PNBP USU research program in the
fiscal year of 2018.
REFERENCES
[APHA] American Public Health Association. 2005.
Standard Methods For the Examination of Water and
Wastewater. Amer. Publ. 17th Edition. New York
Health Association.
Decree of the Minister of Environment (MENLH) No. 51
of 2004.Appendix III. About Sea Water Quality
Standards for Marine Biota
Edmonson W.T. 1963. Fresh Water Biology.Second
Edition.Jhon Willey & Sons, inc., New York.pp.274-
285.
Effendi, H. 2003.Review of Water Quality for Management
of Aquatic Resources and
Environment.CetakanKelima. Yogjakarta :Kanisius.
Firmansyah, N, Ihsan Y.N, Permatasari L, 2016.
Dynamics of Nutrients with Macrozoobenthos
Distribution in the SegaraAnakan Laguna.Journal
of Marine Fisheries Vol. VII No. 2.
Hartoko, A. 2010.Oceanography and Fisheries Resources
- Marine in Indonesia.Undip Press, Semarang
Håkanson, L. 2006, A dynamic model for suspended
particulate matter (SPM) in rivers. Global Ecology
and Biogeography, 15: 93–107. doi:
10.1111/j.1466-822X.2006
Pennak R.W. 1978. Fresh-water Invertebrates of the
United States.2nd Edition. New York: John Wiley &
Sons.
Streble H, and Krauter, D (1988) Das
LebenimWassertropfen: Mikroflora und Mikrofauna
des Sṻβwassers.EinBestimmungsbuch. Franckh-
KosmosVerlag GmbH, Stuttgart.
Wetzel, R.G. 2001. Limnology; lake and River Ecosystem
3rd ed. Academic Press New York 1006 pp.
Yeanny, M.S. 2018. Phytoplankton community as
bioindicator of fertility in belawan river. IOP
Conference Series: Earth and Environmental
Science 130 (1), 0120030
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