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Biosynthesis of Ag-Cu-Al Nanoparticles for Efficient Adsorption of
Lead, Iron and Chromium from Industrial Wastewater
Godwin Effiong Ankwai
1*
, Alhaji Modu Kolo
2
, Auwal Adamu Mahmoud
2
, Istifanus Yarkasuwa Chindo
2
1
Department of Chemistry, University of Jos, P.M.B 2084, Jos, Plateau, Nigeria.
2
Department of Chemistry, Abubakar Tafawa Balewa University, Bauchi 740101, Nigeria.
*Corresponding Author
DOI: https://dx.doi.org/10.51584/IJRIAS.2025.101100039
Received: 16 November 2025; Accepted: 25 November 2025; Published: 09 December 2025
ABSTRACT
Lack of proper effluent disposal methods in industries has led to an exacerbation of the risk posed by heavy
metal contaminants present in industrial wastewater. Several approaches have been explored to mitigate these
harmful threats but, most of these approaches have several limitations such as, lacking selectivity, removing
essential ions along with heavy metals, high post-treatment cost and generating toxic byproducts which further
contaminates the environment. To address these difficulties, nanoparticles have recently been employed to
mitigate these limitations. Nanoparticles, owing to their minute size and large surface-to-volume ratio, exhibit
enhanced reactivity and adsorption capacities, making them exceptional contenders for heavy metal removal.
Furthermore, the synergistic effect of trimetallic nanoparticles has also increased its efficacy as an adsorbent.
This study efficiently biosynthesized silver-copper-aluminum trimetallic nanoparticles (Ag-Cu-Al NPs) using
aqueous leaves extract of Hierochloe odorata at room temperature. The synergistic effect of the three metals was
efficiently harnessed in conjunction with the biologically active components from Hierochloe odorata present in
the nanoparticles, to enhance the adsorption affinity of the nanoparticles towards available heavy metal ions
present in the wastewater. The biosynthesized Ag-Cu-Al NPs was first confirmed by an obvious color shift from
grey to olive green after adding the aqueous leaves extract to the trimetallic salt solution of silver nitrate, copper
chloride and aluminum oxide. UV-vis spectroscopy of the nanoparticles presented a distinct peak maximum at
405 nm. The possible secondary metabolites responsible for bio-reduction, capping and homogeneity of the
nanoparticles were assessed using FTIR. The crystalline nature and particle size of the NPs were investigated
using XRD. SEM-EDS analysis revealed the surface texture and constituent elements of the NPs. Adsorption
studies demonstrated that the biosynthesized Ag-Cu-Al nanoparticles acts as a highly efficient nano-adsorbent
for the removal of lead, iron and chromium from industrial wastewater.
Keywords: Nanoparticles, Wastewater, Heavy metals, Biosynthesis, Hierochloe odorata, Adsorption.
INTRODUCTION
Burgeoning industrialization and urbanization have resulted in considerable health concerns as a result of
indiscriminate wastewater discharge which introduces enormous amount of harmful heavy metals such as
mercury, iron, lead, cadmium, arsenic, copper, zinc and nickel into water bodies. These poisonous metals
constitute grave health challenges due to their toxic and carcinogenic effect [1]. The environmental impact of
heavy metals in wastewater is extreme, causing disruptions to the ecosystem and endangering biological
diversity. Heavy metals accrue in aquatic habitats through mining activities, industrial discharges and natural
occurrences like weathering of rocks leading to contamination of surface water, groundwater, and sediments,
where they exert toxic effects on flora and fauna. For instance, mercury bioaccumulates in fish through food
chains, reaching concentrations that harm predatory species and human consumers [2]. Heavy metals have also
been proven to degrade soil quality when contaminated wastewater is used for irrigation. Lead and cadmium
alter microbial communities essential for nutrient cycling, reducing the soils inherent fertility and agricultural
yields [3].
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Unlike other biodegradable contaminants, heavy metal’s non-biodegradable characteristics enhances their
doggedness and increased concentration in the environment. This often leads to extensive and indefinite heavy
metal pollution of the soil, water and the ecosystem [4]. When humans are exposed to heavy metals through
contaminated food and water it can lead to acute health challenges ranging from nervous disorders to cancer,
with susceptible groups like children and pregnant women facing increased risks [5]. In 2019, the World Health
Organization (WHO) reported that an estimated 1 million people were killed as a result of exposure to lead
exposure while approximately 140 million people from 70 countries have been exposed to arsenic contaminated
drinking water [6,7].
Industrial effluent from deserted mining sites and other industrial activities is usually characterized by various
heavy metals, Pb, Cu, Cd, Cr, Ni and Mn. These pollutants constitute a great risk to the biota, resulting in a range
of diseases and dysfunction. For example, exposure to lead (Pb) has been linked with cardiovascular issues,
kidney damage, hyperactivity, mental retardation, and dermatitis. Conversely, susceptiveness to Chromium has
been linked with the development of acute respiratory issues, skin disorders, kidney failure, and enfeebled
immune systems [8]. The acceptable concentration of lead (II) and Chromium (VI) ion in drinking water by
World Health Organization (WHO) is 0.05 mg/L [9]. Also, the presence of these contaminants can contribute to
the development of skin exfoliation, disruption of thyroid function, development of liver cirrhosis and
gastrointestinal issues such as death of organisms, stalled growth, diarrhea and reduced reproductive rate [10,
11]. Therefore, the need to immediately implement efficient treatment methods for industrial wastewater and
prevent its release into the environment and alleviate these detrimental consequences cannot be overemphasized.
Customary methods employed for heavy metal remediation from industrial wastewater, such as chemical
precipitation, coagulation-flocculation, ion exchange, membrane filtration, and reverse osmosis amongst others,
have limitations that hinders their effectiveness. These methods often lack selectivity, removing essential ions
along with heavy metals, high post-treatment cost and generating toxic byproducts like sludge [12]. For example,
coagulation-flocculation processes result in the generation of high quantities of chemical sludge and can leave
residual coagulant metals in the treated water among other [13]. Furthermore, conventional methods of heavy
metal treatment can be very expensive and difficult to scale-up for large-scale industrial effluent treatment
applications. For instance, graphene-based materials such as activated carbon are produced consequent upon
high heat and pressure requirements, which are energy consuming and expensive [2, 12]. To address these
difficulties, nanomaterial-based routes have emerged as encouraging solutions due to their distinct properties
and diverse applications in heavy metal remediation [14].
Nanoparticles, owing to their minute size and large surface-to-volume ratio, exhibit enhanced reactivity and
adsorption capacities, making them exceptional contenders for heavy metal removal [15]. Several research have
shown that nanomaterials as well possess notable redox and catalytic properties. Their large surface area provides
several active sites for interaction with heavy metal ions, expediting efficient adsorption and modification
processes. Additionally, the tunability of nanomaterials allows for the alteration of their properties to target
specific contaminants [16]. The tunability of these nanomaterials enhances their versatility in various
environmental conditions. The potential for functionalization with specific ligands or coatings further enhances
their astuteness and effectiveness in intricate environments. Nanoparticles are progressively traversed for
environmental cleanup and sustainable effluent treatment technologies [17].
There are various types of nanoparticles depending on their size, morphology and other characteristics.
Metallic oxide nanoparticles such as silicon oxide nanoparticles, zinc oxide, tungsten oxide, magnesium oxide
and titanium dioxide have been widely recognized for their potential in environmental remediation [18, 19].
Metallic nanoparticles have garnered significant attention among the numerous types of nanoparticles due to
their exceptional stability in thermal and biological processes, photochemical effective adsorption capabilities,
low toxicity and affordability [20]. When compared to monometallic nanoparticles, multi-metallic (trimetallic)
nanoparticles, composed of various metals, provide a unified system that can display unique features. They
exhibit enhanced catalytic activity and antibacterial effect, diversified shapes, high selective detection and
sensitivity, high level of stability, and chemical transformation [21]. These enhanced characteristics are
consequent upon the synergistic effects of the three metals that makes up the trimetallic nanoparticles [22].
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Different synthesis methods have been investigated for the synthesis of trimetallic nanomaterials but, the
biogenic synthesis route has proven to be most affordable and environmentally friendly. This method involves
the reduction of metal ions by biological entities to form nanoparticles. Distinct plants, microbes, and
compostable wastes have been employed as starting materials in the synthesis of these nanoparticles via this
route. Green plant constituents can be employed in this synthesis method due to phytochemicals present in plants,
which serves as reductant, organic ligands, and stabilizers due to the presence of biologically active compounds
such as hydroxylated polyphenols, isoprenoids, enzymes, and other free radical scavengers [23]. One of such
plants that have been used in the synthesis of trimetallic nanoparticles is Hierochloe odorata. Hierochloe odorata
(Also known as sweet grass) is an aromatic herb native to North America. It is used ceremonially through burning
the dried and braided grass stems for an incense or smudge. Its distinctive sweet scent is associated to the
presence of some natural aromatic organic chemical and is also rich in antioxidant [24].
This work aimed to investigate the biogenic synthesis of Ag-Cu-Al trimetallic nanoparticles using aqueous leaves
extracts of Hierochloe odorata, characterization of the biosynthesized trimetallic nanoparticles using
spectroscopic and microscopic techniques, and to investigate its possible application in the removal of heavy
metals Lead (Pb), Iron (Fe) and Chromium (Cr) from simulated wastewater solution. The aqueous leaves extract
of the plant used serves as reductant, organic ligands, and stabilizers due to the presence of diverse secondary
metabolites present in the extract. There has been no previous report of the use of biosynthesized AgCu-Al
trimetallic nanoparticles in heavy metal removal hence, this study intends to harness the synergistic effect of the
trimetallic nanoparticles coupled with the biologically active components from Hierochloe odorata present in
the nanoparticles in order to enhance the adsorption affinity of the nanoparticles towards available heavy metal
ions present in the aqueous solution of the wastewater [25, 26].
MATERIALS AND METHODS
Materials and Chemicals
The plant materials used was Hierochloe odorata leaves collected from the Federal College of Forestry Jos,
Nigeria and identified by a plant taxonomist. The chemicals used were analytical grade copper (II) chloride
(CuCl
2
), silver nitrate (AgNO
3
), aluminum oxide (Al
2
O
3
), Iron (II) Chloride (FeCl₂), Potassium dichromate
(KCr₂O₇), Lead acetate (Pb(C₂H₃O₂)₂), and obtained from Thermo Fisher Scientific Pittsburgh, PA, United
States of America. The chemical compounds and substances were used as received without further refinement
or alteration.
METHODS
Preparation of Aqueous leaves extract of Hierochloe odorata
Accurately weighed 10 grammes of fresh Hierochloe odorata leaves was washed with running tap water and
rinsed with distilled water for removal of dust particles. Subsequently, the leaves were cut into pieces, weighed
and transferred into a 500 mL beaker containing 100 mL of distilled water and then placed on a hotplate for 15
minutes at 30
o
C after which it was allowed to cool and then filtered using Whatman filter paper No. 1.
The filtrate was then kept for subsequent use.
Preparation of 0.1 M AgNO
3
, CuCl
2,
and Al
2
O
3
Salt Solutions
Exactly 1.70 g, 1.34 g and 1.02 g of silver nitrate, copper (II) chloride and aluminum oxide salts respectively
were weighed and transferred into three beakers containing 100 mL each of demineralized water. The resultant
mix were properly agitated to ensure the salt dissolves properly after which the salt solutions were mixed together
to obtain a homogenous mixture. The prepared salt solutions were then stored for subsequent use 2.2.3
Biosynthesis of Ag-Cu-Al Trimetallic Nanoparticles
Ag-Cu-Al trimetallic nanoparticles was successfully biosynthesized by bio-reducing the stock solution of silver,
copper and aluminum salts concurrently with the aqueous leaves extract. 30 mL of the leaf extract was added to
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150 mL of 0.1 M AgNO
3
-CuCl
2
-Al
2
O
3
stock solution (50 ml of each salt solution) in dropwise manner with
continuous stirring on a magnetic stirrer. After a little while, a colour change was observed indicating the
formation of the trimetallic nanoparticles. The nanoparticles formed was centrifuged at 3000 rpm for 15 minutes,
after which it was washed with distilled water and allowed to dry at room temperature. It was then set aside for
onward use.
Characterization
The biosynthesized trimetallic nanoparticles was put through certain spectroscopic and microscopic
characterization methods to determine the size, morphology and composition of the biosynthesized
nanoparticles. UV-Visible spectroscopic measurements of the biosynthesized nanoparticles were analyzed using
the T70 PG InstrumentsUV- Spectrophotometer. The possible secondary metabolites present in the plant extract
responsible for the bio-reduction of the trimetallic salt solution were determined using FTIR spectrophotometer
(Cary 630 Agilent Technologies). SEM–EDS analysis was recorded using Quanta 250 FEG instrument to
investigate the surface morphology and elemental composition of the nanoparticles. The crystal lattice and size
distribution of the biosynthesized nanoparticles was analyzed using X-ray diffraction (XRD Empyrean Malvern
Panalytical diffractometer).
Applications
Heavy Metal Adsorption Studies
Exactly 1.27 g, 2.94 g and 3.25 g of FeCl₂, K₂Cr₂O₇, and Pb(C₂H₃O₂)₂ respectively were weighed and transferred
into separate beakers containing 100 ml each of deionized water in order to prepare 0.1 M solutions of the various
metal salts. Adsorption studies were carried out by mixing 2, 4, 6, 8 and 10 mg of biosynthesized silver-copper-
aluminum trimetallic nanoparticles (Al-Ag-Cu TMNPs) with 5 ml each of 0.1 M FeCl₂, K₂Cr₂O₇ and
Pb(C₂H₃O₂)₂ Solutions (Simulated waste water). The solutions were then placed in an ultrasonic bath to ensure
that the nanoparticles dissolved properly in the test solution.
Atomic Absorption spectrophotometer (AAS) was used to analyze the concentration of the metal ion present in
the simulated waste water, with and without the biosynthesized trimetallic nanoparticles. The amount of metal
ion absorbed by the adsorbent (nanoparticles) was evaluated and percentage removal calculated as;
% Removal = [(C₀ – Cₑ) / C₀] × 100………………………………………………………. .(1)
Where Co and Ce are the initial and final concentration of the pollutant (simulated waste water)
RESULTS AND DISCUSSION
Optical Properties
Plate 1: Hierochloe odorata leaves extract (A), Ag-Cu-Al trimetallic salt solution (B), Ag-Cu-Al nanoparticle
solution (C)
One unique attribute of nanoparticles is their opto-electronic properties. The opto-electronic property of the
trimetallic salt solution of Ag-Cu-Al, Hierochloe odorata leaf extracts and the trimetallic nanoparticles of Ag-
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Cu-Al are shown on plate 1. After addition of 30 ml of aqueous leaf extract of Hierochloe odorata the colour of
the 150 mL of the 0.1 M trimetallic salt solution of Ag-Cu-Al changed from grey to olive green indicating the
formation of Ag-Cu-Al trimetallic nanoparticles. The excitation of the surface plasmon resonance action in the
nanoparticles is responsible for the colour variations. The size and shape of metal surface plasmon oscillation,
as well as their optical properties are well understood.
UV-Visible Spectroscopy Analysis
More information about the biosynthesized Ag-Cu-Al trimetallic nanoparticles was obtained through the use of
Ultraviolet-visible spectroscopy, which aided in observing the bio-reduction of hydrated metal ions on addition
of the aqueous leaves extract (figure 1). In the absorption spectrum of Ag-Cu-Al trimetallic nanoparticle, the
characteristic surface plasmon resonance (SPR) is observed with an absorbance of approximately 400-407 nm
with peak maximum of 405 nm, which can be attributed to the presence of Ag-Cu-Al trimetallic nanoparticles.
The nearly ordered structure of the collective electron oscillation suggest that the nanoparticles are not evenly
spread and homogenous. This heterogeneity of the nanoparticles is responsible for the extensive absorption band.
The size, shape and stabilizing agent of nanoparticles influence the location of the SPR band.
Figure 1: Ultraviolet-Visible Spectrum of Ag-Cu-Al trimetallic nanoparticle
Fourier Transform Infra-Red Spectroscopy Analysis
Figure 2 shows the FTIR spectra of Hierochloe odorata aqueous leaf extract mediated synthesized AgCu-Al
trimetallic nanoparticles. It shows the distinct absorption bands for the functional groups responsible for the
reduction of the trimetallic ions. Spectral peaks were obtained at 3317, 2938, 2080, 1735, 1367, 1217 and 1033
cm
-1
. The spectral lines at 3317 cm
-1
corresponds to secondary amine (N-H), C-H medium stretching for alkane
is responsible for the bonds found 2938 cm
-1
. The 2080 cm
-1
stems from C=C stretch for alkenes, 1735 cm
-1
. IR
band is associated with C=O stretching for esters. 1367 cm
-1
is strong band for N=O stretching for nitro
compounds While 1217 cm
-1
is attributed for C-O stretch for esters and 1033 cm
-1
is for C-C bending stretch for
alkanes. Hierochloe odorata leaves extract is rich in secondary metabolites such as polyphenols, alkaloids and
hydrates of carbon, saponins and flavonoids which are rich in free radical scavengers efficient in contributing
atoms of hydrogen and protein components that are capable of attaching themselves with metallic ions and
efficient in reducing metal ions of silver, copper and aluminum and also serve as stabilizers to the synthesized
nanoparticles [27].
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Figure 2: Comparative FTIR spectra of Ag-Cu-Al nanoparticles
XRD Analysis
The X-ray diffraction pattern is used to determine the size, shape, fragment examination and specification of the
sample. The location of the peaks obtained from spectral markings also gives details about the magnitude and
shape of the crystal. The medium size of the Ag-Cu-Al nanoparticles was calculated using the DebyeScherrer
equation;
𝐷=
where; D, is the size of the crystal, k = constant (0.94), ƛ = wavelength of incident rays βcoon the crystal
(1.5418 Ǻ), β= is the width at half maxima at (111) reflection at Bragg’s angle 2θ, while θ is the Bragg angle.
From the XRD patterns of the biosynthesized Ag-Cu-Al nanoparticles as depicted in Figure 3, it is clear that the
diffraction pattern of the trimetallic nanoparticles were essentially crystalline as observed with the sharp peaks.
Predicted Bragg peaks observed at 38.47°, 44.67°, 47.12° and 65.23° corresponds to the (111), (200) and (220)
standard face centered cubic structures of silver which establishes the presence of silver oxide in the sample [28,
29]. Diffraction peaks were also observed for copper oxide at 28.85° and 33.26°, aluminum oxide at 57.75° and
58.60° brought about by the oxidation of copper and aluminum particles respectively [30]. The average particle
size of the biosynthesized Ag-Cu-Al trimetallic nanoparticles was computed from table 1 to be 35.92 nm. The
values of the crystal planes of the biosynthesized Ag-Cu-Al nanoparticle observed were consistent with the
standard powder and diffraction card of Joint Committee on Powder Diffraction Standards (JCPDS) which
revealed that the trimetallic Ag-Cu-AL nanoparticles exhibits a Face center cubic crystal. Other diffraction
peaks observed in the spectrum might be from some biomolecules or proteins within the plant extract [31].
Figure 3: Xray Diffraction spectrum of Ag-Cu-Al nanoparticles
10
20
30
40
50
60
70
−5
0
5
10
15
20
25
30
35
40
ϴ
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Table 1: Particle size of Ag-Cu-Al Trimetallic nanoparticles
Table: XRD Peak Parameters
Position (nm)
Height (Abs)
FWHM (radians)
d-Spacing (Å)
Particle Size (nm)
15.195
6.103
0.725
0.173
9.275
19.157
8.234
0.636
0.137
21.977
29.781
9.890
0.720
0.317
32.955
33.292
15.106
0.210
0.278
39.677
38.789
23.207
0.265
0.387
45.012
45.016
11.026
0.425
0.167
51.072
47.129
11.221
0.328
0.241
55.596
57.321
4.476
0.352
0.195
63.047
65.230
9.652
0.346
0.268
67.786
SEM-EDS Analysis
This characterization method was used to determine the surface configuration of the Ag-Cu-Al nanoparticles as
depicted in plate 2 below. The surface conformation revealed an irregular crystalline structure which is
synonymous of metallic nanocomposites due to the strong intermolecular contact imposed by the high surface
energy. It also reveals the complexity of the particle size to be closely packed and also the cylindrical nature of
the nanoparticles. The image also shows a coarseness which might be ascribed to organic molecules present in
the leaf extract that are bounded to the Ag-Cu-Al nanoparticles. The EDS also revealed the elemental
composition of the nanoparticles with silver which is easily displaced and hence more active and having the
highest composition thereby forming the outer shell while aluminum forms the inner core shell.
Plate 2: SEM-EDS images of Ag-Cu-Al nanoparticles
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Adsorption studies of Ag-Cu-Al Trimetallic Nanoparticles
Adsorption has been proven to be one of the most widely applied techniques in wastewater treatment due to its
simplicity, cost-effectiveness, and high efficiency in removing heavy metals and other toxic contaminants from
aqueous media [32]. Unlike precipitation, ion exchange, or membrane filtration, adsorption does not generate
excessive secondary pollutants, making it an environmentally sustainable approach for water purification. The
technique relies on the interaction between the adsorbate molecules or ions and the active sites available on the
surface of the adsorbent material [33]
Metallic nanoparticles such as Ag–CuAl trimetallic nanoparticles present a promising adsorbent candidate for
the removal of these heavy metals due to their synergistic properties of high stability, antimicrobial activity, and
enhanced surface functionality [34]. The presence of silver contributes a high surface area and energy, copper
enhances electron transfer and adsorption kinetics, while aluminum improves stability and provides additional
active sites for complexation [35]. Investigating the adsorption behavior of Pb, Fe and Cr ions using
biosynthesized Ag–CuAl trimetallic nanoparticles will provide valuable insights into their adsorption capacity,
efficiency, and underlying mechanisms, ultimately establishing their potential application in wastewater
treatment. The results of the adsorption studies conducted for the removal of Lead (Pb), Iron (Fe) and chromium
(Cr) from waste water using biosynthesized Ag-Cu-Al Trimetallic nanoparticles as adsorbent are presented
below;
Table 2. Results of Adsorption studies of Al-Cu-Ag Trimetallic nanoparticles on Lead (Pb)
Ag-Cu-Al Concentration (ppm)
Pb Concentration (mg/L)
% Removal
Blank
16.39 ±0.008
0
50
9.098 ±0.002
44.52
100
8.979 ±0.004
45.25
150
5.925 ±0.002
63.87
200
1.207 ±0.005
92.64
250
1.067 ±0.009
93.49
The results in table 2 shows a progressive decrease in lead (Pb) concentration with increasing concentrations of
AgCuAl nanoparticles with optimum percentage removal of 93.49 % obtained at 250 ppm. A positive
correlation between adsorbent concentration and removal efficiency was observed and is a well-established
principle in adsorption science, as a higher mass of adsorbent provides a greater surface area and more active
sites for metal ion binding [36].
The exceptionally high efficiencies (above 93 %) at higher concentrations highlight the strong adsorption affinity
and capacity of the synthesized trimetallic nanoparticles for lead ions. The high effectiveness for lead (Pb²⁺)
removal is typical of nanoscale adsorbents, which exhibit strong complexation with heavy metal cations [37].
This performance is attributed to the high surface area and the synergistic effects of the Ag-Cu-Al composition,
which provide abundant active sites for metal ion binding. The organic capping agents from the Hierochloe
odorata aqueous leaf extract containing phenolic and carboxyl groups, further enhance this capacity by
facilitating metal ion complexation [38]. Although some variability in measurement precision was observed, the
steady and sizeable decline in residual lead concentration across all concentration confirms the reliability and
effectiveness of the treatment method for lead-contaminated wastewater.
Table 3. Results of Adsorption Studies of Al-Cu-Ag Trimetallic nanoparticles on Iron (Fe)
Ag-Cu-Al Concentration (ppm)
Pb Concentration (mg/L)
% Removal
Blank
19.343 ±0.001
0
50
8.220 ±0.007
57.51
100
6.841 ±0.005
64.64
150
4.173 ±0.001
78.43
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200
1.984 ±0.004
89.74
250
1.046 ±0.006
94.59
The results in table 3 shows a progressive decrease in iron (Fe) concentration with increasing concentrations of
AgCuAl nanoparticles. It also reveals a clear increasing trend in removal efficiency, rising from 57.51% in
50-ppm to 94.59 % in 250-ppm. The exceptionally high efficiencies at higher dosages highlight the strong
adsorption affinity of the synthesized nanoparticles for iron ions. The high removal capacity for iron is consistent
with literature showing that metal oxide-based nanomaterials, particularly those containing aluminum, exhibit
high affinity for Fe ions through surface complexation and electrostatic interactions [39]. This performance is
attributed to the synergistic effects of the Ag-Cu-Al composition. The presence of aluminum is particularly
strategic, as it provides hydroxyl groups that facilitate ligand exchange and binding of iron species [40].
Furthermore, the organic capping agents from the Hierochloe odorata aqueous leaf extract provide additional
functional groups (e.g., carboxyl, phenolic) that enhance adsorption through complexation and hydrogen
bonding [38]. The consistent and substantial decline in residual iron concentration confirms the effectiveness of
the nanoparticles for iron-contaminated wastewater treatment.
Table 4: Results for Adsorption studies of Al-Cu-Ag Trimetallic nanoparticles on Chromium (Cr)
Ag-Cu-Al Concentration (ppm)
Pb Concentration (mg/L)
% Removal
Blank
13.05 ±0.009
0
50
9.097 ±0.005
30.04
100
7.114 ±0.007
45.29
150
6.863 ±0.003
47.22
200
6.612 ±0.006
52.23
250
4.876 ±0.002
62.50
From the results obtained, a progressive decrease in chromium (Cr) concentration with increasing concentrations
of Ag–Cu–Al nanoparticles were observed as shown in table 4. Removal efficiencies were observed to
progressively increase from 30.04 % at 50-ppm, to 62.50% for 250-ppm. This positive correlation between
adsorbent dosage and removal percentage is a well-established principle in adsorption science, as increased
nanoparticle mass provides a greater abundance of active surface sites for metal binding [41]. The measurable
efficiencies confirm the adsorption capability of the synthesized nanoparticles for chromium ions.
However, the overall lower and gradual increase in removal efficiency, compared to lead and iron, suggests a
weaker affinity or less optimal adsorption conditions for chromium species. This is likely because chromium
(VI) primarily exists as oxyanions (e.g., HCrO₄⁻, CrO₄²⁻) in aqueous solutions, which can experience electrostatic
repulsion with the potentially negatively charged surface of the nanoparticles at neutral pH [41]. The organic
capping agents from the H. odorata extract may also be more effective at complexing cationic metals like Pb²
and Fthan anionic chromium species [38]. The consistent reduction in residual concentration, nonetheless,
confirms the effectiveness of the Ag-Cu-Al nanoparticles for chromium uptake, indicating that mechanisms such
as reduction or electrostatic attraction despite repulsion may be contributing to the removal process [42].
CONCLUSION
This study successfully demonstrated the biogenic synthesis of silver-copper-aluminum (Ag-Cu-Al) trimetallic
nanoparticles (TMNPs) using aqueous leaf extract of Hierochloe odorata and evaluated its efficacy in adsorbing
heavy metals from wastewater. The biosynthesis and properties of the nanoparticles were confirmed using UV-
Vis spectroscopy, FTIR, XRD, and SEM-EDS techniques, which verified its crystalline nature, irregular coarse
surface conformation, elemental composition, and cylindrical morphology. Adsorption studies demonstrated that
the biosynthesized Ag-Cu-Al nanoparticles acts as a highly effective nano-adsorbent for the removal of heavy
metals from aqueous solution. This is attributed to the synergistic effect of the three metals coupled with the
organic capping agent present the nanoparticles which enhances active sites for complexation. The results
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showed that the removal efficiency increased significantly with higher adsorbent (nanoparticle) dosage. The
nanoparticles exhibited a strong and preferential affinity for different metals, with the maximum removal
efficiencies recorded at 94.59% for Iron, 93.49% for Lead, and 62.50% for Chromium. This establishes
Hierochloe odorata-mediated synthesized Ag-Cu-Al trimetallic nanoparticles as a promising, environmentally
friendly, and efficient material for wastewater remediation, particularly for the extraction of toxic heavy metals
like lead, iron and chromium from contaminated environments. The eco-friendly synthesis route employed and
the minute (nanosized) quantity of the trimetallic nanoparticles used in heavy metal remediation from wastewater
in this study can help in allaying/reducing the concerns of toxicity and long-term effects of nanoparticles on the
environment
Conflict Of Interests
Authors have declared that no conflict of interest exist.
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