Journal of Environmental Treatment Techniques
2020, Volume 8, Issue 1, Pages: 429-436
new concrete projects [8]. Yap et al. showed that using
recycled coarse aggregates (RCA) decreased compressive
strength of the porous concrete [9].
samples, 85, 43 and 76% for samples containing vermiculite
and 78, 45 and 84% for samples containing quartz,
respectively [22].
Using porous concrete in large cities and developed
countries is a proper method to reduce runoff and prevent
urban stormwater events. Adding inexpensive minerals to
porous concrete that has a low specific weight and the ability
to adsorb contamination, can reduce the volume and improve
the quality of runoff. In the present study, in addition to
adding 0, 10 and 20% fine-grains, different percentages of
mineral adsorbents such as zeolite, perlite, pumice and
LECA were added to the mixing design. Mechanical
characteristics of porous concrete such as compressive
strength, permeability coefficient and porosity, which are
important factors in the urban roads, were investigated.
Using the results of mechanical characteristics for each
percentage of fine grains, 3 samples that had better
performance in terms of compressive strength were selected
for quality tests. The COD, BOD, TSS, EC parameters,
percentage of NaCl and turbidity of selected samples were
calculated.
Figure 1: Blocks of porous concrete
It is important to use filters to improve water quality by
replacing appropriate materials that can reduce water
pollution. Some minerals such as zeolite, fly ash, iron slag,
perlite, LECA, pumice, vermiculite, silica and quartz have
been used in previous studies to reduce contamination in
addition to the cost-effective adsorption of contaminants [10,
2 Material and Methods
1.2 Concrete and mixing design
To prepare the mixing design for porous concrete, ACI
211.3R standard was used to determine the mixing ratios of
zero-slump concrete [23]. The aggregate and cement values
were selected to be 1400 and 330 kg/m3, respectively. In
order to increase the strength of concrete against sulfate
environments, type 5 cement was used. The water to cement
ratio was fixed to 0.38 for all samples. Four different
percentages of the zeolite, perlite, pumice and LECA
adsorbents (0, 5, 10 and 15% w/w), with 0.6 to 1.2 mm
average diameter, and three different percentages of fine-
grains (0, 10, 20) (0, 140 and 280 kg/m3, respectively) with
size of 2.36 to 4.75 mm, were tested. Figure 2 shows the four
adsorbents. Figure 3 presents granulometric curves of the
aggregates and additives. For each sample, three replicates
were considered to ensure the desired accuracy. The
adsorbents were saturated before mixing. Chemical
characteristics of the adsorbents are shown in Table 1. Each
mixing design was encoded using type of adsorbent in it.
Letter C is used for control sample, and letters Z, Pe, Pu and
L are used for samples containing Zeolite, Perlite, Pumice
and LECA, respectively. The percentage of adsorbents and
fine-grains is mentioned after the sample’s letter. The first
number after the letter is percentage of the adsorbent and the
second number is percentage of the fine grains. For example,
Z15-10 is porous concrete sample containing 15% zeolite
and 10% fine-grains.
1
1, 12, 13]. Using these mineral adsorbents in porous
concrete, that is applicable to urban roads, is important
because in addition to preventing the urban storm-runoff,
they can have positive effects on the improvement of runoff
quality.
Tsai et al. used silica to eliminate color from aqueous
solution [14]. Al-Anber found that bentonite and quartz
could remove Fe(II) from wastewater [15]. Körlü et al. used
waste pumice stones to reduce the BOD and COD
concentration [16]. Verbinnen et al. indicated that perlite-
supported magnetite is suitable for treating real wastewaters
by eliminating several oxyanions simultaneously from the
considered industrial wastewater [17].
Zhang et al. showed that porous concrete containing
pumice was able to reduce COD and BOD up to 60% [18].
Abedi Kupai et al. succeeded in reducing COD, turbidity,
TSS and lead (Pb) concentration by adding iron slag to
porous concrete and using sand filter. Contaminants
concentrations were measured before and after passing the
samples through the filter. Results showed that COD,
turbidity, lead (2 mg/l), lead (5 mg/l) and TSS were
decreased by 11, 38, 44, 42 and 53% and for samples
containing iron slag these parameters were decreased by 43,
9
1, 91, 95 and 70%, respectively [19].
Ong et al. used fly-ash, iron-slag, and limestone powder
1.2 Porosity test
in porous concrete to improve urban runoff quality [20].
Shabalala et al. eliminated some of the heavy metals from
aqueous solution using porous concrete containing fly-ash
Porosity was measured in cubic samples (10×10×10 cm)
using the ASTM C1754 standard [24]. Samples were placed
in a 105 °C oven for 24 hours. Then, the samples were
weighed to get their dry weight. Then, they were immersed
in water and their buoyant weight was measured by an
Archimedes scale. Porosity of each sample was calculated
by the following equation:
[21]. Azad et al. by using vermiculite and quartz in porous
concrete, managed to reduce TSS, COD and turbidity.
Results showed that by adding 30% adsorbents to porous
concrete, the quality parameters such as TSS, COD and
turbidity were reduced by 45, 14 and 54% for control
4
30