Heavy Metal Removal Efficiency of Vetiver Grass from Contaminated Soil

DOI : 10.17577/IJERTCONV10IS06022

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Heavy Metal Removal Efficiency of Vetiver Grass from Contaminated Soil

Rinitha P

Dept. Of Civil Engineering

(APJ Abdul Kalam Technological University) College Of Engineering Thalassery (APJ Abdul Kalam

Technological University) Kannur, India

Anugraha A

Dept. Of Civil Engineering

(APJ Abdul Kalam Technological University) College Of Engineering Thalassery (APJ Abdul Kalam

Technological University) Kannur, India

Athira N

Dept. Of Civil Engineering

(APJ Abdul Kalam Technological University) College Of Engineering Thalassery (APJ Abdul Kalam

Technological University ) Kannur, India

Pranav P V

Dept. Of Civil Engineering

(APJ Abdul Kalam Technological University) College Of Engineering Thalassery (APJ Abdul Kalam

Technological University Kannur, India

Nakul A

Dept.Of Civil Engineering

(APJ Abdul Kalam Technological University)

College Of Engineering Thalassery (APJ Abdul Kalam Technological University) Kannur, India

Abstract Rapid population increase, along with rapid industrialization and agricultural practices, causes major environmental problems, such as the development and release of massive amounts of toxic waste into the soil environment. The two forms of soil contaminants are inorganic and organic pollutants. Inorganic pollutants, such as lead, arsenic, cadmium, copper, zinc, nickel, and mercury, are regularly introduced to the environment by the discharge of urban sewage sludge and industrial wastes onto agricultural soils. Concerns about the dangers of soil contamination to human health and the environment have driven substantial research into creative, cost-effective remediation techniques in recent years. Installing and operating chemical, physical, and microbiological procedures for treating contaminated soils, for example, is costly.

This project uses vetiver grass for the removal of heavy metals in soil. It has the ability to adapt and develop in a variety of habitats, as well as fast recovery from poor environmental conditions. It also has the ability to absorb a considerable amount of nitrogen, phosphorus, and dissolved heavy metals from the environment. Heavy metals are hazardous to soil biota because they interfere with critical microbial processes and reduce the number and activity of soil microorganisms. We chose biological approaches for eliminating these pollutants from soil in our experiment.

Heavy metal extraction from contaminated soils were the subjects of pot culture investigations. For the experiment, soil samples were collected from locations where heavy metal concentrations could be high. The tests last approximately three months.

Index TermsVetiver,heavy metal, Phytoremediation,

I.INTRODUCTION

A. Need of the study

Soil is an important component of the environment, as it plays a role in a variety of ecosystem services. However, inadequate land management practices have resulted in a fall in actual and/or potential soil productivity, posing a serious challenge to sustainable agriculture and environmental quality, putting many countries' food security at risk. Poor land management practices often result in soil erosion and agrochemical pollution as a result of agricultural activities, urban trash, and industrial operations, reducing the soil's ability for long-term food production and impacting plants, animals, and human lives.

Heavy metals and metalloids can accumulate in soils due to emissions from rapidly expanding industrial areas, mine tailings, disposal of high metal wastes, leaded gasoline and paints, fertilizer land application, animal manures, sewage sludge, pesticides, wastewater irrigation etc.. Heavy metals are an ill-defined set of inorganic chemical dangers, with lead (Pb), chromium (Cr), arsenic (As), zinc (Zn), cadmium (Cd), copper (Cu), mercury (Hg), and nickel being the most typically found in contaminated locations (Ni).Unlike organic pollutants, which are converted to carbon dioxide by microbial action, most metals do not undergo microbial or chemical degradation, and their total content in soils endures for a long period after their introduction. However, changes in their chemical forms (speciation) and bioavailability may occurToxic metals in soil can prevent organic pollutants from degrading properly. Heavy metal contamination of soil poses risks and hazards to humans and the ecosystem through direct ingestion or contact with contaminated soil, the food chain (soil-plant-human or soil-

plant-animal-human), drinking contaminated groundwater, reduction in food quality (safety and marketability) via phytotoxicity, reduction in land usability for agricultural production causing food insecurity, and land tenure issues. Vetiver grass is a tufted bunch grass that thrives in both tropical and temperate climates. Heavy metals don't bother vetiver grass. It could be used to fight pests biologically. When compared to other soil conservation technologies, the usage of vetiver grass has been viewed as a low-cost solution for soil and water conservation, stability and repair of polluted soils, and enhancement of water quality for irrigation applications.

II.METHODOLOGY

Firstly, we chose the subject that we needed for our research. We looked through numerous journals and devised a plan for what we needed to do. We then decided to apply a 2 stage procedure for checking the tolerance level of the plant against heavy metals in soil.Heavy metal- contaminated soils were collected from four different places in Kannur district. Soil samples weighing 5 kg were sampled from an E-waste disposal site in Anjarakandy, Kripesh textiles, a grain factory in Pappinisseri panchayath, Malabar dyeing industry and finishing mills ltd, a textile mill on Kakkad road, and an automobile workshop in Valapattanam.

fig.1 Vetiver planted in pots with soil sample.

The soil samples were taken and then placed in pots and a part of each sample was sent to a soil testing laboratory. The initial soil analysis, the one before planting the vetiver was done.The vetiver plants were planted then and were grown for about 90days. After 90 days the soil samples were again sent for analysis.

Test results at initial stage

Sample No

Zn(ppm)

Fe(ppm)

Cu(ppm)

Mn(ppm)

1

19.08

92.7

4.27

32.1

2

1.07

3.2

0.56

1.2

3

33.6

129

23.8

50.3

4

24.6

147

10.4

61.2

Sample 1 = e-waste anjarakandy Sample 2 = Kripesh textile factory Sample 3 = Malabar dying industry Sample 4 = valapattanm car scrap

REFERENCE

[1] Phytoremediation of cadmium and nickel using vetiveria zizanioides.H. Niknahad gharmakher, A. Esfandyari,HRezaei

[2] Joice K Joseph, Amrutha Haridasan , Karunakaran Akhildev and Pradeep Kumar AP (2017) , Applications of Vetiver Grass (Chrysopogonzizanioides) in Eco System Based Disaster Risk Reduction – Studies from Kerala State of India, Journal of Geography & Natural Disasters,(2017)

[3] Phytoremediation of soils polluted by heavy metals using vetiver grass and tall fescue. S.Ghadiria., M.H.Farpoora,M.Hejazi Mehrizia.

Desert 23-1(2018)123-132,http://ut.ac.ir

[4] Nor Azizi Yusoff, Mohamad Fazrin Mohamad Fauzi and FirdaursAbdullaha 2016) , The Study of Soil-Roots Strength Performance by Using Pennisetum Setaceum Grass ,The 3rd International Conference on Civil and Environmental Engineering for Sustainability,Vol. 47, 03021 (2016).

[5] Mohammmad S. Islam1, Md. Z. U. Arif2, Faria F. Badhon3, Soumik Mallick4, Tanzila Islam (2016) Investigation Of Vetiver Root Growth In Sandy Soil, Department of Civil Engineering, Bangladesh University of Engineering and Technology, Dhaka

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