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International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395-0056
Volume: 10 Issue: 09 | Sep 2023 www.irjet.net p-ISSN: 2395-0072
© 2023, IRJET | Impact Factor value: 8.226 | ISO 9001:2008 Certified Journal | Page 684
Phytoremediation of Lead-Contaminated Shooting Range Soils using
Indian Mustard and Sunflower
Mohd Adnan1, Sukhwinderpal Singh2, Balihar Singh3
1M.Tech (Environmental Science and Engineering), GNDEC Ludhiana, Punjab, India
2Assistant Professor, Dept. of Civil Engineering, Guru Nanak Dev Engineering College, Ludhiana, Punjab, India
3Assistant Professor, Dept. of Civil Engineering, Guru Nanak Dev Engineering College, Ludhiana, Punjab, India
---------------------------------------------------------------------***---------------------------------------------------------------------
Abstract - Lead in the soil is a common problem that hurts
people and the environment. It gets into the soil from
manufacturing, past lead use, and throwing things away that
have lead in them. This is a big problem because lead can hurt
the land and get into our water. We need to come up with
good solutions to this problem. With phytoremediation, heavy
metals like lead can be taken out of contaminated soil. It uses
plants that can take in, move, and store heavy metals, which
makes the earth cleaner. We looked at two plants, Indian
mustard and sunflower, to see if they could remove lead from
shooting ranges. Both plants did a good job, but Indian
mustard did it better, cleaning up 67% of the lead while
sunflower only cleaned up 54%. So, Indian mustard and
sunflower are good choices for cleaning up lead at shooting
ranges. They can get rid of lead and improve the dirt. By using
plants' natural abilities, phytoremediation is a cheap and
long-lasting way to deal with lead pollution, protect the
environment, and help the land heal.
Key Words: Lead pollution, Phytoremediation, Indian
mustard, Sunflower, Shooting ranges
1.INTRODUCTION
Our lives depend on the delicatebalanceofourenvironment,
which includes the air we breathe, the water we drink, the
land we live on, and the ecosystems that keep life going.
Unfortunately, this balance is threatened by things that
people do, such as industrial processes, mining, and not
getting rid of lead-containing products properly. When
heavy metals like lead are in the environment, they pose a
major threat to both nature and human health.Heavymetals
are naturally occurring substances that can hurt the
environment and people's health if there are too many of
them. Some of the elements in this group are lead, mercury,
cadmium, arsenic, and chromium.Thewidespread releaseof
these toxic substances into theenvironment,whichiscaused
by both human activities and natural geological processes,
has made people very worried aboutthe badeffectstheywill
have.
1.1 Lead and its acceptable limit in soil
Metals like lead have been used by people for a very long
time. Pbstands for it, and its atomic number is 82. It's easy to
bend lead, which is a soft, grey metal that doesn't rust. It has
been used in many fields because of these qualities.Butusing
lead has hurt the earth and people's health in very bad ways.
When lead gets into the ground, it can hurt both people
and the environment. What the land is used for and the rules
set by different countries or groups determine how much
lead is allowed in the dirt. There was a lot of study that went
into making these rules. The Environmental Protection
Agency (EPA) in the US has set a lead limit of 400 parts per
million (ppm) in dirt near homes. This means that people
could get sick if they touch oreat things that grow in dirt that
has more lead than this amount. There should be no more
than 120 parts per million (ppm) of lead in the dirt in places
where people garden or farm. Lead from the earth can get
into plants, and then it could end up in the food we eat. When
you think about how much lead is allowed in dirt, keep in
mind that each country has its own rules. So, it's very
important to follow the laws and rules that apply to a place
when you're doing study or trying to clean up lead there.
1.2 Phytoremediation
Phytoremediation is the cleanup of contaminated soil,
water, and air using plants and the microbial communities
they are associated with. This method is natural, cheap, and
safe for the earth. It uses the natural abilities of some plant
species to absorb, change, or stabilise pollutants, which
lowers their levels in the environment.
Phytoremediation can be used to get rid of heavy metals,
organic pollution,radionuclides,andpesticides,amongother
things. Researchers have shown that phytoremediation
could be a useful way to clean up leadpollution. Plantswhich
are used for this research are IndianmustardandSunflower.
1.3 Objective of this research
Pollution from lead in shooting range soils is a big
problem for the environment and public health that could
get worse. To deal with this problem, phytoremediation, a
natural and environmentally friendly process, is becoming
more popular, especially for harmful heavy metals like lead.
In this study, the main goal is to find out how well Indian
mustard and sunflowerwork asphytoremediationspecies to
get rid of lead from shooting range soil.
International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395-0056
Volume: 10 Issue: 09 | Sep 2023 www.irjet.net p-ISSN: 2395-0072
© 2023, IRJET | Impact Factor value: 8.226 | ISO 9001:2008 Certified Journal | Page 685
2. Methodology
The flowchart shows the method used to examine the
efficacy of Indian mustard and sunflower in lead
phytoremediation in shooting range soil.
The following technique was used to achieve the research
objectives:
1. Reactor Model Setup: A glass jar measuring 56 cm in
length, 46 cm in width, and 28 cm in height was made to
represent the shooting range's soil conditions.Ononeside of
the pot, Indian mustard plants weregrown,andontheother,
sunflower plants were grown. The partswereclearlysplitup
so that they could be separated and watched properly.
2. Collection of contaminated soil:Knownsamplingmethods
were used to get soil samples from a number of locations on
the NCC shooting range site at Guru Nanak Dev Engineering
College in Ludhiana. Samples of 30 kg of polluted soil were
collected and put in clean containers with labels.
Fig 1: NCC shooting range site at Guru Nanak Dev
Engineering College in Ludhiana
3. Plant Development: To grow plants, 10 cm apart Indian
mustard (Brassica juncea) and sunflower (Helianthus
annuus) seeds were put in glass containers. The seeds
germinated normally, and the plants grew as planned. The
pots were put in a well-lit area with enough sunlight,andthe
temperature was adjusted to make sure the seeds would
germinate and grow well. Watering was done regularlywith
tap water that has been tested and found to be free of lead.
This kept the soil at the right level of moisture for plant
growth. Indian mustard grew best between 20°C and 25°C,
and it did better in full sun than in some shade.Itmadesense
to put Indian mustard in February and March because it
grows best when it is cool. It was best for sunflower seeds to
grow between 18°C and 24°C, and they needed to be in full
sun. When put in February and March, just before spring,
sunflowers did very well. Lead in the soil can hurt plants'
health and growth in a number of ways. Too much lead can
hurt plants by slowing their growth and making itharderfor
them to take in nutrients. It can also cause oxidative stress
and death in the leaves, which can be seen as chlorosis and
necrosis.
Fig 2: Reactor Model Setup
4. Reactor soil sample collection: Every five days for two
months, soil samples were taken from the Indian mustard
and sunflower parts of the glass container. To record
differences in space, samples of each piece were taken more
than once from different spots.
5. Sample analysis: The EPA 3050B method was used to get
the soil samples ready for testing. To get the heavy metals
out of the earth samples, strong nitric acid and hydrochloric
acid were used as digesting reagents. The samples were
heated in a device called a digestion unit, and digestion
vessels were used to make the processgomoresmoothly.An
AAS was used to test the digested soil samples. The AAS was
calibrated with heavy metal analysis calibration standards
that are widely used in business. The AAS readings were
used to figure out how much lead was in the soil samples.
6. Results: The results from the AAS analysis showed the
quantity of lead in the soil samples at different times. This
gave important information about how well
International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395-0056
Volume: 10 Issue: 09 | Sep 2023 www.irjet.net p-ISSN: 2395-0072
© 2023, IRJET | Impact Factor value: 8.226 | ISO 9001:2008 Certified Journal | Page 686
phytoremediation with Indian mustard and sunflower
worked. Throughout the study, careful records were kept of
samples being taken and of plants growth. During the
experiment, careful notes were taken on what was seen so
that any changes in the plants and soil could be found.
2.1 EPA-3050B method
Atomic absorption spectroscopy hasbeenusedtodetermine
the initial lead concentration using method epa-3050B acid
digestion of sediments, sludge, and soils.
1. To achieve equal particle size, the materials were sieved
with a USS #10 sieve. To avoid cross-contamination, all
homogenization equipment was cleaned in accordance with
the instructions.
Fig 3: Dry soil sample weighing 1 gm
2. Dry soil sample weighing 1 gm was added to a digestion
vessel.
3. 2.5 mL of concentrated nitric acid (HNO3) and 10 mL of
concentrated hydrochloric acid (HCl) were added to the
sample in the digestion vessel. The sample was refluxed for
15 minutes on a heating source with the vessel coveredwith
a watch glass or vapor recovery device.
Fig 4: Sample refluxed for 15 minutes
4. Whatman No. 41 filter paper was used to filter the
digestate. In a volumetric flask measuring 100 mL, the
filtrate was collected. The filter paper was washedoncewith
20 mL of hot reagent water and once with no more than 5
mL of hot (95°C) HCl while it was still inside the funnel. The
same 100-mL volumetric flask was used to collect the
washes.
5. The digesting vessel received the filter paper and residue
back. The vessel was then filled with 5 mL of concentrated
HCl and heated for 5°C at 95°C until the filter paper was
dissolved. The vessel's cover and sides were cleaned with
reagent water after being removed from the heating source.
The filtrate was collected in the same 100-mL volumetric
flask after the residue was filtered.
6. After allowing the filtrate to cool, it was dilutedinthe100-
mL volumetric flask to volume. Up to 10 mL of strong HCl
was added to the flask to dissolve any precipitates that may
have developed at the bottom. The solution was diluted to
volume with reagent water after the precipitate had been
dissolved.
Fig 5 : Final sample diluted in 100 ml volumetric flask
7. The digested and diluted soil sample solution was ready
for further investigation with Flame Atomic Absorption
Spectroscopy (FLAA).
3. Results and Discussion
The Guru Nanak Dev Engineering College's NCC shooting
range soil contains lead at a value of 1579 ppm, which
denotes a high degree of lead pollution.
International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395-0056
Volume: 10 Issue: 09 | Sep 2023 www.irjet.net p-ISSN: 2395-0072
© 2023, IRJET | Impact Factor value: 8.226 | ISO 9001:2008 Certified Journal | Page 687
Table -1: Concentration of Pb in soil before treatment
(mg/kg)
Heavy metals Concentration of
heavy metals in
soil (mg/kg)
Permissible
limits (mg/kg)
Lead 1579 400
Table -2: Results for removal of Pb by Indian mustard
Time (Days) Lead Concentration
(mg/kg)
Lead Removal (%)
0 1579 -
5 1530 3.11
10 1454 7.93
15 1347 14.71
20 1238 21.61
25 1099 30.43
30 975 38.23
35 885 43.97
40 811 48.65
45 728 53.92
50 668 57.68
55 606 61.63
60 515 67.4
Table -3: Results for removal of Pb by Sunflower
Time (Days) Lead Concentration
(mg/kg)
Lead Removal (%)
0 1579 -
5 1535 2.76
10 1497 5.20
15 1396 11.61
20 1325 16.11
25 1253 20.62
30 1167 26.12
35 1062 32.75
40 992 37.17
45 904 42.74
50 852 46.07
55 781 50.56
60 722 54.3
3.1 Discussion on results of lead removal
The outcomes forthe elimination ofPbbyIndianmustard
are shown in Table-2. The amountofleadinthesoilgradually
decreased as the number of days grew. The amount of lead
removed from the soil likewise increased over time,
demonstrating the efficiency of Indian mustard in doing so.
The lead concentration was 1579 mg/kg on day 0 of the
experiment, and there was no elimination. The lead
eliminationpercentagewas67.4%after60days,althoughthe
lead concentration dropped to 5,15 mg/kg.
The outcomes for the elimination of Pb by sunflower are
shown in Table-3. Like Indian mustard, the concentration of
lead reduced, and the percentage of lead removal rose over
time. Day 0 saw no elimination and a lead concentration of
1579 mg/kg. The lead levels dropped to 722 mg/kg after 60
days, yielding a lead elimination rate of 54.3%.
According to the findings, both Indian mustard and
sunflower have the capacitytosuccessfullyremoveleadfrom
the soil. However, during the testing period, Indian mustard
outperformed sunflower in terms of lead elimination. The
unique traits and mechanisms of each plant species can be
used to explain this variation in lead removal effectiveness.
Indian mustard is renowned for its great resistance to heavy
metals, including lead, as well as its capacity to ingest and
store these pollutants in its tissues. Although effective at
removing lead, sunflowers may have a marginally reduced
efficiency because of their unique physiological and
biochemical properties. The results of this study support the
potential use of phytoremediation for the elimination of lead
in shooting range environments utilizingIndianmustardand
sunflower. Indian mustard might be a better choice for
locations with higher lead contamination levels due to its
higher lead removal percentage. To fully comprehend the
underlying principles and enhance the phytoremediation
procedure for optimal lead removal effectiveness, more
research is nevertheless required.
Overall, the findings show how effective Indian mustard and
sunflower are in phytoremediation methods, providing a
long-term and environmentally safe solution to the problem
of lead contamination in shooting range soils.
International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395-0056
Volume: 10 Issue: 09 | Sep 2023 www.irjet.net p-ISSN: 2395-0072
© 2023, IRJET | Impact Factor value: 8.226 | ISO 9001:2008 Certified Journal | Page 688
Fig 6: Bar graph showing removal efficiency between
Indian mustard and Sunflower
Fig 7: Line chart showing removal efficiency between
Indian mustard and Sunflower
4. CONCLUSIONS
In the realm of phytoremediation research focused on
tackling lead contamination in shooting range soils, both
Indian mustard and sunflowers have emerged as promising
candidates. The conclusive findings of this study highlight
the effectiveness of both plant species in the removal of lead
from polluted soil. Notably, Indian mustard exhibited a
higher lead removal rate at 67.4%, outperforming
sunflowers, which removed 54.3% of the lead. These results
underscore the potential of Indianmustardandsunfloweras
valuable tools in the remediation of lead-contaminated soil,
not only within shooting ranges but also in addressing
similar pollution challenges in various other settings.
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International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395-0056
Volume: 10 Issue: 09 | Sep 2023 www.irjet.net p-ISSN: 2395-0072
© 2023, IRJET | Impact Factor value: 8.226 | ISO 9001:2008 Certified Journal | Page 689
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BIOGRAPHIES
MOHD ADNAN
M.Tech (Environmental Science
and Engineering), GNDEC
Ludhiana, Punjab, India
International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395-0056
Volume: 10 Issue: 09 | Sep 2023 www.irjet.net p-ISSN: 2395-0072
© 2023, IRJET | Impact Factor value: 8.226 | ISO 9001:2008 Certified Journal | Page 690
SUKHWINDERPAL SINGH
Assistant Professor, Dept. of Civil
Engineering, Guru Nanak Dev
Engineering College, Ludhiana,
Punjab, India
BALIHAR SINGH
Assistant Professor, Dept. of Civil
Engineering, Guru Nanak Dev
Engineering College, Ludhiana,
Punjab, India

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Phytoremediation of Lead-Contaminated Shooting Range Soils using Indian Mustard and Sunflower

  • 1. International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395-0056 Volume: 10 Issue: 09 | Sep 2023 www.irjet.net p-ISSN: 2395-0072 © 2023, IRJET | Impact Factor value: 8.226 | ISO 9001:2008 Certified Journal | Page 684 Phytoremediation of Lead-Contaminated Shooting Range Soils using Indian Mustard and Sunflower Mohd Adnan1, Sukhwinderpal Singh2, Balihar Singh3 1M.Tech (Environmental Science and Engineering), GNDEC Ludhiana, Punjab, India 2Assistant Professor, Dept. of Civil Engineering, Guru Nanak Dev Engineering College, Ludhiana, Punjab, India 3Assistant Professor, Dept. of Civil Engineering, Guru Nanak Dev Engineering College, Ludhiana, Punjab, India ---------------------------------------------------------------------***--------------------------------------------------------------------- Abstract - Lead in the soil is a common problem that hurts people and the environment. It gets into the soil from manufacturing, past lead use, and throwing things away that have lead in them. This is a big problem because lead can hurt the land and get into our water. We need to come up with good solutions to this problem. With phytoremediation, heavy metals like lead can be taken out of contaminated soil. It uses plants that can take in, move, and store heavy metals, which makes the earth cleaner. We looked at two plants, Indian mustard and sunflower, to see if they could remove lead from shooting ranges. Both plants did a good job, but Indian mustard did it better, cleaning up 67% of the lead while sunflower only cleaned up 54%. So, Indian mustard and sunflower are good choices for cleaning up lead at shooting ranges. They can get rid of lead and improve the dirt. By using plants' natural abilities, phytoremediation is a cheap and long-lasting way to deal with lead pollution, protect the environment, and help the land heal. Key Words: Lead pollution, Phytoremediation, Indian mustard, Sunflower, Shooting ranges 1.INTRODUCTION Our lives depend on the delicatebalanceofourenvironment, which includes the air we breathe, the water we drink, the land we live on, and the ecosystems that keep life going. Unfortunately, this balance is threatened by things that people do, such as industrial processes, mining, and not getting rid of lead-containing products properly. When heavy metals like lead are in the environment, they pose a major threat to both nature and human health.Heavymetals are naturally occurring substances that can hurt the environment and people's health if there are too many of them. Some of the elements in this group are lead, mercury, cadmium, arsenic, and chromium.Thewidespread releaseof these toxic substances into theenvironment,whichiscaused by both human activities and natural geological processes, has made people very worried aboutthe badeffectstheywill have. 1.1 Lead and its acceptable limit in soil Metals like lead have been used by people for a very long time. Pbstands for it, and its atomic number is 82. It's easy to bend lead, which is a soft, grey metal that doesn't rust. It has been used in many fields because of these qualities.Butusing lead has hurt the earth and people's health in very bad ways. When lead gets into the ground, it can hurt both people and the environment. What the land is used for and the rules set by different countries or groups determine how much lead is allowed in the dirt. There was a lot of study that went into making these rules. The Environmental Protection Agency (EPA) in the US has set a lead limit of 400 parts per million (ppm) in dirt near homes. This means that people could get sick if they touch oreat things that grow in dirt that has more lead than this amount. There should be no more than 120 parts per million (ppm) of lead in the dirt in places where people garden or farm. Lead from the earth can get into plants, and then it could end up in the food we eat. When you think about how much lead is allowed in dirt, keep in mind that each country has its own rules. So, it's very important to follow the laws and rules that apply to a place when you're doing study or trying to clean up lead there. 1.2 Phytoremediation Phytoremediation is the cleanup of contaminated soil, water, and air using plants and the microbial communities they are associated with. This method is natural, cheap, and safe for the earth. It uses the natural abilities of some plant species to absorb, change, or stabilise pollutants, which lowers their levels in the environment. Phytoremediation can be used to get rid of heavy metals, organic pollution,radionuclides,andpesticides,amongother things. Researchers have shown that phytoremediation could be a useful way to clean up leadpollution. Plantswhich are used for this research are IndianmustardandSunflower. 1.3 Objective of this research Pollution from lead in shooting range soils is a big problem for the environment and public health that could get worse. To deal with this problem, phytoremediation, a natural and environmentally friendly process, is becoming more popular, especially for harmful heavy metals like lead. In this study, the main goal is to find out how well Indian mustard and sunflowerwork asphytoremediationspecies to get rid of lead from shooting range soil.
  • 2. International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395-0056 Volume: 10 Issue: 09 | Sep 2023 www.irjet.net p-ISSN: 2395-0072 © 2023, IRJET | Impact Factor value: 8.226 | ISO 9001:2008 Certified Journal | Page 685 2. Methodology The flowchart shows the method used to examine the efficacy of Indian mustard and sunflower in lead phytoremediation in shooting range soil. The following technique was used to achieve the research objectives: 1. Reactor Model Setup: A glass jar measuring 56 cm in length, 46 cm in width, and 28 cm in height was made to represent the shooting range's soil conditions.Ononeside of the pot, Indian mustard plants weregrown,andontheother, sunflower plants were grown. The partswereclearlysplitup so that they could be separated and watched properly. 2. Collection of contaminated soil:Knownsamplingmethods were used to get soil samples from a number of locations on the NCC shooting range site at Guru Nanak Dev Engineering College in Ludhiana. Samples of 30 kg of polluted soil were collected and put in clean containers with labels. Fig 1: NCC shooting range site at Guru Nanak Dev Engineering College in Ludhiana 3. Plant Development: To grow plants, 10 cm apart Indian mustard (Brassica juncea) and sunflower (Helianthus annuus) seeds were put in glass containers. The seeds germinated normally, and the plants grew as planned. The pots were put in a well-lit area with enough sunlight,andthe temperature was adjusted to make sure the seeds would germinate and grow well. Watering was done regularlywith tap water that has been tested and found to be free of lead. This kept the soil at the right level of moisture for plant growth. Indian mustard grew best between 20°C and 25°C, and it did better in full sun than in some shade.Itmadesense to put Indian mustard in February and March because it grows best when it is cool. It was best for sunflower seeds to grow between 18°C and 24°C, and they needed to be in full sun. When put in February and March, just before spring, sunflowers did very well. Lead in the soil can hurt plants' health and growth in a number of ways. Too much lead can hurt plants by slowing their growth and making itharderfor them to take in nutrients. It can also cause oxidative stress and death in the leaves, which can be seen as chlorosis and necrosis. Fig 2: Reactor Model Setup 4. Reactor soil sample collection: Every five days for two months, soil samples were taken from the Indian mustard and sunflower parts of the glass container. To record differences in space, samples of each piece were taken more than once from different spots. 5. Sample analysis: The EPA 3050B method was used to get the soil samples ready for testing. To get the heavy metals out of the earth samples, strong nitric acid and hydrochloric acid were used as digesting reagents. The samples were heated in a device called a digestion unit, and digestion vessels were used to make the processgomoresmoothly.An AAS was used to test the digested soil samples. The AAS was calibrated with heavy metal analysis calibration standards that are widely used in business. The AAS readings were used to figure out how much lead was in the soil samples. 6. Results: The results from the AAS analysis showed the quantity of lead in the soil samples at different times. This gave important information about how well
  • 3. International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395-0056 Volume: 10 Issue: 09 | Sep 2023 www.irjet.net p-ISSN: 2395-0072 © 2023, IRJET | Impact Factor value: 8.226 | ISO 9001:2008 Certified Journal | Page 686 phytoremediation with Indian mustard and sunflower worked. Throughout the study, careful records were kept of samples being taken and of plants growth. During the experiment, careful notes were taken on what was seen so that any changes in the plants and soil could be found. 2.1 EPA-3050B method Atomic absorption spectroscopy hasbeenusedtodetermine the initial lead concentration using method epa-3050B acid digestion of sediments, sludge, and soils. 1. To achieve equal particle size, the materials were sieved with a USS #10 sieve. To avoid cross-contamination, all homogenization equipment was cleaned in accordance with the instructions. Fig 3: Dry soil sample weighing 1 gm 2. Dry soil sample weighing 1 gm was added to a digestion vessel. 3. 2.5 mL of concentrated nitric acid (HNO3) and 10 mL of concentrated hydrochloric acid (HCl) were added to the sample in the digestion vessel. The sample was refluxed for 15 minutes on a heating source with the vessel coveredwith a watch glass or vapor recovery device. Fig 4: Sample refluxed for 15 minutes 4. Whatman No. 41 filter paper was used to filter the digestate. In a volumetric flask measuring 100 mL, the filtrate was collected. The filter paper was washedoncewith 20 mL of hot reagent water and once with no more than 5 mL of hot (95°C) HCl while it was still inside the funnel. The same 100-mL volumetric flask was used to collect the washes. 5. The digesting vessel received the filter paper and residue back. The vessel was then filled with 5 mL of concentrated HCl and heated for 5°C at 95°C until the filter paper was dissolved. The vessel's cover and sides were cleaned with reagent water after being removed from the heating source. The filtrate was collected in the same 100-mL volumetric flask after the residue was filtered. 6. After allowing the filtrate to cool, it was dilutedinthe100- mL volumetric flask to volume. Up to 10 mL of strong HCl was added to the flask to dissolve any precipitates that may have developed at the bottom. The solution was diluted to volume with reagent water after the precipitate had been dissolved. Fig 5 : Final sample diluted in 100 ml volumetric flask 7. The digested and diluted soil sample solution was ready for further investigation with Flame Atomic Absorption Spectroscopy (FLAA). 3. Results and Discussion The Guru Nanak Dev Engineering College's NCC shooting range soil contains lead at a value of 1579 ppm, which denotes a high degree of lead pollution.
  • 4. International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395-0056 Volume: 10 Issue: 09 | Sep 2023 www.irjet.net p-ISSN: 2395-0072 © 2023, IRJET | Impact Factor value: 8.226 | ISO 9001:2008 Certified Journal | Page 687 Table -1: Concentration of Pb in soil before treatment (mg/kg) Heavy metals Concentration of heavy metals in soil (mg/kg) Permissible limits (mg/kg) Lead 1579 400 Table -2: Results for removal of Pb by Indian mustard Time (Days) Lead Concentration (mg/kg) Lead Removal (%) 0 1579 - 5 1530 3.11 10 1454 7.93 15 1347 14.71 20 1238 21.61 25 1099 30.43 30 975 38.23 35 885 43.97 40 811 48.65 45 728 53.92 50 668 57.68 55 606 61.63 60 515 67.4 Table -3: Results for removal of Pb by Sunflower Time (Days) Lead Concentration (mg/kg) Lead Removal (%) 0 1579 - 5 1535 2.76 10 1497 5.20 15 1396 11.61 20 1325 16.11 25 1253 20.62 30 1167 26.12 35 1062 32.75 40 992 37.17 45 904 42.74 50 852 46.07 55 781 50.56 60 722 54.3 3.1 Discussion on results of lead removal The outcomes forthe elimination ofPbbyIndianmustard are shown in Table-2. The amountofleadinthesoilgradually decreased as the number of days grew. The amount of lead removed from the soil likewise increased over time, demonstrating the efficiency of Indian mustard in doing so. The lead concentration was 1579 mg/kg on day 0 of the experiment, and there was no elimination. The lead eliminationpercentagewas67.4%after60days,althoughthe lead concentration dropped to 5,15 mg/kg. The outcomes for the elimination of Pb by sunflower are shown in Table-3. Like Indian mustard, the concentration of lead reduced, and the percentage of lead removal rose over time. Day 0 saw no elimination and a lead concentration of 1579 mg/kg. The lead levels dropped to 722 mg/kg after 60 days, yielding a lead elimination rate of 54.3%. According to the findings, both Indian mustard and sunflower have the capacitytosuccessfullyremoveleadfrom the soil. However, during the testing period, Indian mustard outperformed sunflower in terms of lead elimination. The unique traits and mechanisms of each plant species can be used to explain this variation in lead removal effectiveness. Indian mustard is renowned for its great resistance to heavy metals, including lead, as well as its capacity to ingest and store these pollutants in its tissues. Although effective at removing lead, sunflowers may have a marginally reduced efficiency because of their unique physiological and biochemical properties. The results of this study support the potential use of phytoremediation for the elimination of lead in shooting range environments utilizingIndianmustardand sunflower. Indian mustard might be a better choice for locations with higher lead contamination levels due to its higher lead removal percentage. To fully comprehend the underlying principles and enhance the phytoremediation procedure for optimal lead removal effectiveness, more research is nevertheless required. Overall, the findings show how effective Indian mustard and sunflower are in phytoremediation methods, providing a long-term and environmentally safe solution to the problem of lead contamination in shooting range soils.
  • 5. International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395-0056 Volume: 10 Issue: 09 | Sep 2023 www.irjet.net p-ISSN: 2395-0072 © 2023, IRJET | Impact Factor value: 8.226 | ISO 9001:2008 Certified Journal | Page 688 Fig 6: Bar graph showing removal efficiency between Indian mustard and Sunflower Fig 7: Line chart showing removal efficiency between Indian mustard and Sunflower 4. CONCLUSIONS In the realm of phytoremediation research focused on tackling lead contamination in shooting range soils, both Indian mustard and sunflowers have emerged as promising candidates. The conclusive findings of this study highlight the effectiveness of both plant species in the removal of lead from polluted soil. Notably, Indian mustard exhibited a higher lead removal rate at 67.4%, outperforming sunflowers, which removed 54.3% of the lead. These results underscore the potential of Indianmustardandsunfloweras valuable tools in the remediation of lead-contaminated soil, not only within shooting ranges but also in addressing similar pollution challenges in various other settings. REFERENCES [1] Alaboudi, K. A., Ahmed, B., & Brodie, G. (2018). Phytoremediation of Pb and Cd contaminated soils by using sunflower (Helianthus annuus) plant. Annals of agricultural sciences, 63(1), 123-127. [2] Angelova, V. R., Perifanova-Nemska, M. N., Uzunova,G.P., Ivanov, K. I., & Lee, H. Q. (2016). Potential of sunflower (Helianthus annuus L.) for phytoremediation of soils contaminated with heavy metals. World J. Sci. Eng. Technol, 10(9), 1-8. [3] Ashraf, S., Ali, Q., Zahir, Z. A., Ashraf, S., & Asghar, H. N. (2019). Phytoremediation:Environmentallysustainableway for reclamation of heavy metal polluted soils. Ecotoxicology and environmental safety, 174, 714-727. D. L., Pilon-Smits, E. A., & Mackey, B. (2005). Field trial of transgenic Indian mustard plants shows enhanced phytoremediation of selenium- contaminated sediment. Environmental science & technology, 39(6), 1771-1777. [5] Chandra, R., & Kumar, V. (2017). Phytoremediation: a green sustainable technology for industrial waste management. In Phytoremediation of environmental pollutants (pp. 1-42). CRC Press. [6] Chen, M., Daroub, S. H., Ma, L. Q., Harris, W. G., & Cao, X. (2002). Characterization of lead in soils of a rifle/pistol shooting range in central Florida, USA. Soil and Sediment Contamination, 11(1), 1-17. [7] Chrastný, V., Komárek, M., & Hájek, T. (2010). Lead contamination of an agricultural soil in the vicinity of a shooting range. Environmental Monitoring and Assessment, 162, 37-46. [8] Dinake, P., Kelebemang, R., Sehube, N., Kamwi, O., & Laetsang, M. (2018). Quantitative assessment of environmental risk from lead pollution of shooting range soils. Chemical Speciation & Bioavailability, 30(1), 76-85. [9] Goswami, S., & Das, S. (2015). A study on cadmium phytoremediation potential of Indian mustard, Brassica juncea. International journal of phytoremediation, 17(6), 583-588. [10] Hosseini, S. S., Lakzian, A., Halajnia, A., & Razavi, B. S. (2021). Optimization of EDTA and citric acid for risk assessment in the remediation of lead contaminated soil. Rhizosphere, 17, 100277. [11] Hou, D. (Ed.). (2019). Sustainable remediation of contaminated soil and groundwater: materials, processes, and assessment. Butterworth-Heinemann. [12] Jadia, C. D., & Fulekar, M. H. (2008). Phytoremediation: The application of vermicompost to remove zinc, cadmium, copper, nickel and lead by sunflower plant. Environmental Engineering & Management Journal (EEMJ), 7(5). [13] Jiao, F., Shi, X. R., Han, F. P., & Yuan, Z. Y. (2016). Increasing aridity, temperature, and soil pH induce soil CNP imbalance in grasslands. Scientific reports, 6(1), 19601.
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  • 7. International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395-0056 Volume: 10 Issue: 09 | Sep 2023 www.irjet.net p-ISSN: 2395-0072 © 2023, IRJET | Impact Factor value: 8.226 | ISO 9001:2008 Certified Journal | Page 690 SUKHWINDERPAL SINGH Assistant Professor, Dept. of Civil Engineering, Guru Nanak Dev Engineering College, Ludhiana, Punjab, India BALIHAR SINGH Assistant Professor, Dept. of Civil Engineering, Guru Nanak Dev Engineering College, Ludhiana, Punjab, India