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Investigation on the potential of sand filter as a pre-treatment of waste water was done in Kangar wet market, Perlis. Besides, the best composition of filter in order to treat wastewater based on BOD, COD, SS, AN, turbidity and pH levels are further examined. In this study, there are four types of sand filter composition which the medias consist of fine sand and coarse sand while the modified sand filter are consist of sand, course sand and activated carbon prepared from rice husk and coconut shells. After 10 weeks of treatment, the results show that the concentration of BOD, COD, SS, AN, turbidity and pH were reduced up to 86%, 84%, 63%, 88%, 73%, respectively while pH nearly to neutral with 6.83. Moreover, the result also revealed that the sand filter added with rice husk almost complied with Standard B of Malaysia Environmental Quality (Sewage) Regulations 2009 as well as gives the highest number of WQI with 36.81. Overall, WQI obtained in this study are ranged from 12.77 to 36.81.
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Study on Modified Sand Filtration Towards
Water Quality of Wet Market Waste Water
F.N.M. Saad1,*, M.N. Jamil1, Z.S.M. Odli1 , and T.N.T. Izhar1
1School of Environmental Engineering, Universiti Malaysia Perlis (UniMAP), Kompleks Pusat
Pengajian Jejawi 3, 02600 Arau, Perlis, Malaysia.
Abstract. Investigation on the potential of sand filter as a pre-treatment of
waste water was done in Kangar wet market, Perlis. Besides, the best
composition of filter in order to treat wastewater based on BOD, COD,
SS, AN, turbidity and pH levels are further examined. In this study, there
are four types of sand filter composition which the medias consist of fine
sand and coarse sand while the modified sand filter are consist of sand,
course sand and activated carbon prepared from rice husk and coconut
shells. After 10 weeks of treatment, the results show that the concentration
of BOD, COD, SS, AN, turbidity and pH were reduced up to 86%, 84%,
63%, 88%, 73%, respectively while pH nearly to neutral with 6.83.
Moreover, the result also revealed that the sand filter added with rice husk
almost complied with Standard B of Malaysia Environmental Quality
(Sewage) Regulations 2009 as well as gives the highest number of WQI
with 36.81. Overall, WQI obtained in this study are ranged from 12.77 to
36.81.
1 Introduction
Wet market is the place where people get raw materials such as fish, vegetables and
chicken. Waste water generated from this premise is from different sources and activities
such as cleaning of fish, vegetables and fruits as well as slaughtering poultry which used
huge water usage. Then, this waste water containing high organic and inorganic matters are
directly discharged into the drains without any treatment.
As said by Idris et al. [1], the wet market waste water usually contains two to three
times of organic matter and solids commonly found in residential waste water, thus waste
water, produce from market sources classified as “high intensity”. Discharged of untreated
waste water adds oxygen-demanding substances, nutrients and toxic elements into the
water, thus influencing the level of parameters such as BOD, COD and TSS in the receiving
water. This scenario in turn converts the streams to become unsuitable for aquatic flora and
fauna. Because of this effect, discharged of grey water into the steam need to be treated to
avoid or reduce that effect [1]. Therefore, an economical and easy to be used treatment
should be applied in the premise in order to treat the waste water generated from wet
market before it being released to receiving water.
* Corresponding author: farahnaemah@unimap.edu.my
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© The Authors, published by EDP Sciences. This is an open access article distributed under the terms of
the Creative
Commons Attribution License 4.0 (http://creativecommons.org/licenses/by/4.0/).
Sand filter is one of the oldest wastewater treatment technologies. It is also a biofilm
technology that has been used in waste water treatment due to its low cost and maintenance
and relatively high treatment efficiency. There have been several studies carried out and
reported relevant to the application of sand filter in treating waste water [2,3]. Results
showed that the sand filter may reduce the concentration of water quality such as BOD,
COD and SS. Therefore, this study is aimed to observe the potential of sand filter act as a
pre-treatment of wet market waste water as well as to compare the quality of waste water
produced from conventional sand filter with modified sand filter which added with
activated carbon based on BOD,COD, suspended solid, AN, turbidity and pH.
2 Materials and methods
2.1 Sampling location and activity
Kangar wet market (6˚26’11”N 100˚11’33”E) was chosen as sampling location. Grab water
sample was collected at the final discharge of the wet market during peak hour of wet
market operation before being transfered to the laboratory for further study.
2.2 Preparation of activated carbon
Coconut shell was taken from the local shop selling coconut milk while the rice husk was
collected from local rice mill. Both materials were washed with distilled water to remove
impurities before being dried in the oven. Then, both coconut shell and rice husk were
burned in the furnace at 300˚C for 2 hours before being ground and sieved according to the
desired size.
2.3 Preparation of sand filter
The sand filtrations were constructed in the transparent plastic columns. The dimension of
each plastic column is 260 mm of height, 80 mm for top diameter and 24 mm for bottom
diameter. A hole was created at the bottom of the plastic column which acts as a channel
for effluent water sample.
Fine sand, coarse sand, as well as rice husk and coconut shell act as activated carbon,
with their effective size of 0.06 mm, 2.00 mm, and 0.08 mm, respectively were used in this
study. All these materials were washed by using distilled water to remove impurities and
dried before being filled up in the plastic column. Plastic net was used to avoid the material
from wash out.
There were four types of sand filtrations used in this study. There were sand filtration
consist only fine and course sand, sand filtration with additional of rice husk, sand filtration
with additional of coconut shell and sand filtration with additional of rice husk and coconut
shell. The schematic diagram of all sand filters used in this study is shown in Fig. 1.
2.4 Experimental study
5 L of water sample was pumped into each of the sand filter. The flow rate for all filters
was 0.13 L/ min. Then, the effluent of each sand filter was collected for further analysis. In
this study, six parameters were chosen based on water quality index (WQI). The parameters
are BOD, COD, SS, ammoniacal nitrogen, pH and turbidity. All procedures of experiments
were according to American Public Health Association (APHA) [4].
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Fig. 1. Schematic diagram of (a) sand filtration, (b) sand filtration with coconut shell, (c) sand
filtration with rice husk and (d) sand filtration with rice husk and coconut shell.
3 Results and discussion
The wet market waste water was collected at the final discharge of the premise before it
being treated with the four types of sand filtrations. Then, the filtered waste water were
analysed based on six parameters and compared with the Standard B of Malaysia
Environmental Quality (Sewage) Regulations 2009 [5]. The WQI of each effluent of sand
filtration is also calculated.
The concentrations of BOD, COD, SS and AN recorded by the effluent of wet market
before and after being treated by four types of sand filters is shown in Fig. 2. The results of
these parameters are then compared with the Malaysia’s regulation.
The result shows that high BOD level is detected before the treatment is applied with
137.07 mg/L while the lowest is recorded from the sand filter added with rice husk which is
18.97 mg/L. This indicates that more than 80% of organic matter is removed. Besides that,
the result also shows that only two types of sand filters are comply with the Standard B (50
mg/L) which are sand filter added with rice husk and sand filter added with both activated
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carbons. This suggests that the addition of activated carbon in the sand filter composition
may reduce the pollutant in the water sample.
High BOD level in water sample has course a threat to the aquatic environment since it
reduces the dissolved oxygen concentration to the levels that affect aquatic organisms [6].
This is due to the fact that oxygen is used by microorganisms to oxidize the organic matter
to stable inorganic form [7].
137.03
79.77
62.88
18.97
42.21
350.27
186.8
162.4
54.8
116.2
126.4 127.4
75.2
46.8
85.6
45.81
26.01
10.96 5.68
8.47
Before treatment Sand filtration Sand filtration
with coconu t
shell
Sand filtration
with rice husk
Sand filtration
with co conut
shell and rice
husk
Concentration (mg/L)
Sampl e
BOD COD SS AN
Fig. 2. Concentration of BOD, COD, SS and AN recorded by the wet market waste water before and
after treatment with sand filters.
COD is the amount of oxygen required to chemically oxidize organic and inorganic
matter. COD gives an estimation of the amount of organic and inorganic matter present. In
Fig. 2, it shows that high level of COD recorded before the water sample is treated with
350.27 mg/L. On the other hand, all the water samples that gone through the treatments
have shown a good finding where the COD concentrations recorded are lower than the
Standard B (200 mg/L), ranging from 54.8 to 186.8 mg/L. This indicates that all types of
sand filtrations tested in this study have a potential in removing organic and inorganic
matters in the water sample with the higest percentage reduction of 84%.
Further analysis was carried out by examined the level of suspended solids in the water
sample before and after the treatment with sand filters. According to Standard B of
Malaysia Environmental Quality (Sewage) Regulations 2009, the limits of SS is not more
than 100 mg/L. Refering to the Fig. 2, the results show that the water samples are high with
SS before the treatment as well as treated with the sand filter. However, the SS
concentrations recorded by sand filtrations added with activated carbon have reduced the
pollutants in the effluent with the lowest concentration of 46.8 mg/L, indicating of more
than 60% reduction. Excessive SS in the water sample may cause the recieving water to
lose its stability in suppoting the diversity of aquatic life. It will abdsorb heat from the sun
thus increase the water temperature and lower the levels of dissolved oxygen [8].
The concentrations of AN in the water sample before and after the treatment are shown
in Fig. 2. The result shows that the level of AN are ranging from 5.68 mg/L up to 45.81
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mg/L with the lowest and the highest AN concentrations are recorded by sand filter added
with rice husk and before the water sample is treated, respectively. Although high
percentage reduction is recorded with 87.6%, this concentrations are still not comply with
the limit set up by the Malaysian law which is 5 mg/L. AN is very soluble in the water.
High level of AN contributes to oxygen demand and nutrient loading of the water bodies,
promoting toxic algal blooms and leading to a destablised aquatic ecosystem [9].
The pH of the water sample is recorded in the study before and after sand filter
treatment is shown in Fig. 3. The result shows that the highest pH is 6.83 which recorded
by sand filtration while the lowest is recorded by sand filtration added with both activated
carbons with 6.38. Overall, it reveals that the water sample is slightly acidic. Based on the
Standard B of Malaysia Environmental Quality (Sewage) Regulations 2009, all the water
samples are comply with the limit (5.5-9.0). According to Morrison et al. [10], high pH
values could alter the toxicity of other pollutants while low pH values may affect aquatic
life and impair recreational uses of water.
6.64
6.83
6.63
6.45
6.38
6.1
6.2
6.3
6.4
6.5
6.6
6.7
6.8
6.9
Before
treatment
Sand filtration Sand filtration
with co conut
shell
Sand filtration
w ith ric e h usk
Sand filtration
with co conut
shell and rice
husk
pH
Sampl e
Fig. 3. pH of the water sample before and after treatment with four types of sand filters.
Fig. 4 shows the level of turbidity of the water samples recorded during the study
period. It shows that high turbidity is recorded before the sample is treated with 41.68 NTU
while the lowest is recorded by sand filter added with rice husk which recorded 11.12 NTU.
Generally, all the effluents collected from sand filters are low which is less than 16 NTU,
showing that more than 70% are reduced. As said by Ntengwe [11], turbidity is caused by
the presence of suspended matter, organic particles, plankton and other microscopic
organisms.
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41.68
15.5 13.06 11.12 12.49
0
5
10
15
20
25
30
35
40
45
Before
treatment
Sand filtration Sand filtration
with co conut
shell
Sand filtration
with rice husk
Sand filtration
with co conut
shell and rice
husk
Uni t (NTU)
Sample
Fig. 4. The turbidity of water sample before and after sand filters treatment.
Water quality index of the water samples are also calculated in this study. Fig. 5 lists the
WQI recorded by water samples before and after sand filters treatment. Overall, the result
shows that only sand filtrations with rice husk falls in Class IV (31.0-51.9) which is
suitable for irrigation purpose only while others fall in Class V (less than 31.0) which is not
suitable for any activities. High WQI recorded by sand filter added with rice husk may be
due the pores produced during activation that trapped more pollutants of the water thus
filtered more efficiently. According to Kalderis et al. [12], the relative surface area (SBET)
for rice husk was up to 750 m2/g while for coconut shell, the relative surface area was 546
m2/g [13]. Hence, it gives a better result compared to the other samples.
12.77
15.85
21.44
36.81
24.03
0 102030
40
Before treatment
Sand filtration
Sand filtration with coconut shell
Sand filtration with rice husk
Sand filtration with coconut shell and rice husk
WQI
Sampl e
Fig. 5. Water quality index of wet market waste water before and after treatment with four types of
sand filters.
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4 Conclusions
This study shows that wet market waste water is high with BOD, COD, AN and SS which
exceed the limit that set up by Malaysia authority. Therefore, four types of sand filters are
constructed in order to treat the waste water produced. There are four types of sand filters
examined in this study which one is conventional sand filter while the rest is added with
activated carbon. Based on laboratory tests, the modified sand filter that added with rice
husk is better than sand filtration added with coconut shell or a combination of both
activated carbon. The results show that better performance in eliminating the concentration
of the parameters tested is by sand filters added with rice husk where most results are
comply to Standard B of Malaysia Environmental Quality (Sewage) Regulations 2009 such
as the concentration of BOD, COD, SS, and pH. Besides that, this study also reveals that
sand filtration added with activated carbon shows a potential in eliminating the
concentration of some parameters compared to the conventional sand filters. Therefore, the
addition of activated carbon in the filter can be one of the alternative for the treatment of
waste water wet market.
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... Khalaphallah, (2012) ; Wurochekke et al., (2016) ; Saad et al., (2016) , reported that sand filtration using activated carbon is the best method and reduces COD and BOD 5 when the wastewater flows over it. BOD 5 and COD of both filter columns were meeting the ( USEPA, 2005 ) standards for reuse of all selected non-portable uses. ...
... Filter column B was more efficient in the removal of turbidity than filter column A, because of the adsorptive properties (active sites) of GAC that would attract the turbidity in wastewater. ( Khalaphallah, 2012 ;Saad et al., 2016 ) reported that sand filtration using activated carbon can reduce turbidity when the wastewater passes through it. The turbidity of the filtration system after treatment was within the allowable standards, (USEPA, 1992) ( ≤ 5) for reuse of selected non-potable uses except in column A at 36 h which showed a value of 7.3 that was beyond the reuse standards. ...
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Reclaimed water from wastewater has become a prominent water source option to manage water scarcity. This study explores the potential of coconut husk biomass, a common waste material in Ghana, as a valuable low-cost resource for greywater treatment. Engineered column treatment was applied to investigate the influence of pyrolysis and biochar properties of coconut husk biomass waste on greywater treatment. Coconut husk biomass waste was pyrolyzed at 600°C and characterized using SEM, FTIR, and XRD. Three engineered columns with 1) raw coconut husk powder (RCHP), 2) charred coconut husk powder (CCHP), and 3) sand-gravel filters (control setup) were used. A hydrostatic head of greywater with a throughput of 8.0 ml/min and a hydraulic retention time of 45 min was maintained for engineered columns. The SEM image suggested an increased surface area and pores due to the pyrolysis of the husk biomass. RCHP and CCHP contributed to 63% and 95% turbidity removal, respectively. Experimental results showed high removal efficiencies of 71% COD for CCHP. The nitrate removal efficiency of 78.93%, 88.38%, and 28.65% was observed for RCHP, CCHP, and control respectively. The log removal of faecal coliform by CCHP was two orders of magnitude higher than RCHP. Faecal and total coliform removal was 2.87 log units for CCHP. Significant differences were observed between CCHP and RCHP, p < 0.05 for electrical conductivity and total dissolved solids of effluents. CCHP showed a promising potential for greywater treatment. Pyrolyzed coconut husk powder is a promising adsorbent applicable to greywater treatment.
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... The sand filter can decrease the amount of total suspended solids, 5-day biochemical oxygen demand (BOD), and total phosphorus (62-99%) (Bosak et al. 2016). A 10-week sand filter treatment can reportedly reduce biochemical oxygen demand (BOD), chemical oxygen demand (COD), suspended solids (SS), ammoniacal nitrogen (AN), and turbidity of water samples by up to 86%, 84%, 63%, 88%, and 73%, respectively (Saad et al. 2016). ...
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Fresh markets or wet markets function as important places for exchanging food stuffs and meeting of local people in many emerging economies. Through many activities in fresh markets, solid waste is substantially generated and becomes a main environmental issue. In Ubon Ratchathani, Thailand, solid waste in fresh markets emerges as an environmental issue with potentials to be improved. Selecting two fresh markets with different ownerships in Ubon Ratchathani, the concepts of waste hierarchy and triad-network model were applied to study and compare ways to improve solid waste management systems. Through focus group discussions and semi-structured interviews, this research reveals that solid waste managements of the two markets are centrally organized by the owners with the emphasis on tidiness with little involvements from other actors. To improve waste managements, moving beyond legal requirements and engaging relevant actors are essential. It is also found that different ownership (public vs. private) affects how fresh markets can organize improvement strategies.
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Fresh Market Wastewater (FMWW) is rich with high amounts of suspended solids, organic and inorganic compounds, nutrients, gases and some elements which come from fish entrails and seafood preparation sales, meat cutting, poultry slaughtering, fruits and vegetables sales. The excess of these parameters are harmful to the aquatic life since the FMWW is usually discharged into the drainage systems without any treatment or partial treatment. The FMWW technologies are developed due to some technical factors influencing the designation and construction. There are several projects of fresh market treatment technologies used on site area in small scale which could be replicated to other fresh market, and some case study have been tested in laboratory batch experiments. All the projects exhibited an efficiency to reduce critical parameters in FMWW and give positive impacts to the locals and responsible parties.
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The qualities of the treated final effluents of a wastewater treatment plant located in a rural community of the Eastern Cape province of South Africa were assessed over the duration of 12 months. Parameters measured include pH, temperature, electrical conductivity, salinity, turbidity, total dissolved solid, dissolved oxygen, chemical oxygen demand , nitrate, nitrite and orthophosphate levels and these were simultaneously monitored in the treated final effluents and the receiving watersheds using standard methods. Unacceptably, high levels of the assayed parameters were observed in many cases for chemical oxygen demand (7.5-248.5 mg/L), nitrate (1.82-13.14 mg/L), nitrite (0.09-1.3 mg/L), orthophosphate (0.07-4.81 mg/L), dissolved oxygen (4.15-11.22 mg/L) and turbidity (3.68-159.06 NTU) during the study period and are severally outside the compliance levels of the South African guidelines and World Health Organization tolerance limits for effluents intended for discharge through public sewers into receiving watersheds. The study has revealed that there was an adverse impact on the physico-chemical characteristics of the receiving watershed as a result of the discharge of inadequately treated effluents from the wastewater treatment facility. This poses a health risk to several rural communities which rely on the receiving water bodies primarily as their sources of domestic water. There is need for the intervention of appropriate regulatory agencies to ensure production of high quality treated final effluents by wastewater treatment facilities in rural communities of South Africa.
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The production of activated carbon from bagasse and rice husk by a single-stage chemical activation method in short retention times (30-60min) was examined in this study. The raw materials were subjected to a chemical pretreatment and were fed to the reactor in the form of a paste (75% moisture). Chemicals examined were ZnCl2, NaOH and H3PO4, for temperatures of 600, 700 and 800 degrees C. Of the three chemical reagents under evaluation only ZnCl2 produced activated carbons with high surface areas. BET surface areas for rice husk were up to 750m2/g for 1:1 ZnCl2:rice husk ratio. BET surface areas for bagasse were up to 674m2/g for 0.75:1 ZnCl2:bagasse ratio. Results were compared to regular two-stage physical activation methods.
  • F W Ntengwe
F.W. Ntengwe, Phys. Chem. Earth, 31, 832 (2006)
The first attempt of chicken wastewater treatment using sand filtration
  • R Seswoya
  • A M M Daud
  • Z M Ali
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