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International Journal of Advance Engineering and Research
Development
Volume 6, Issue 10, October -2019
@IJAERD-2019, All rights Reserved 22
Scientific Journal of Impact Factor (SJIF): 5.71
e-ISSN (O): 2348-4470
p-ISSN (P): 2348-6406
Remediation of heavy metals lead, cobalt and copper from industrail wastewater
by phytoremediation
Muhammad Asif, Salman Saeed2
, Rashid Rehan3
1
Civil Engineering Department, University of Engineering & Technology, Peshawar, Pakistan
2
National institute of Urban Infrastructure Planning, University of Engineering & Technology, Peshawar, Pakistan
3
Environmental Engineering Department, University of Engineering & Technology, Peshawar, Pakistan
Abstract: To fulfil human beings requirement number of industries increases day by day which play important role in
development of country but also causes environment pollution. Effluent of many industries contain heavy metals and
other contaminants. Industrial effluent usually used for agriculture purposes without treatment. Plants take these heavy
metals from industrial water and accumulate it in roots and Arial parts which become the part of animal and human
body through food chain causes various diseases. In this research work plants were grown using wastewater of industrial
effluents. Three sample of wastewater were made of various concentration level of lead, copper and cobalt. Typha
latifoliate was grown in controlled environment. Three sample of wastewater were used. Soil used in pots was of known
concentration of heavy metals. Using x-ray fluorescence spectrometry was used to find concentration of contaminants in
soil before and after plantation and atomic absorption spectrometry was used to find concentration of heavy metals in
industrial effluent. Wastewater of various concentration level was obtained by adding domestic water having no heavy
metals. Extraction percentage performed by plants in various lawn was found by analysis of soil before and after the
maturity of plants. soil which was irrigated by fully contaminated wastewater was remediated by 10%. Soil in which
plants were irrigated by diluted wastewater was remediated by 15 and 21% respectively for copper and cobalt. Plants
matured in seventy-five days in winter season.
Keywords: Heavy metals; industrial effluent; various concentration of contaminants; phytoremediation.
I. INTRODUCTION
Heavy metals found naturally and artificially. Artificially contributors of heavy metals to environment are industries,
agriculture, volcanic explosion, gasoline formation, sludge of sewage and extraction of Zinc and Copper (Cristaldi,
Oliveri, Hea, & Zuccarello, 2017; Hernberg, 2000; Kabata-pendias, 2004; Oosten & Maggio, 2014; Pacyna, Pacyna,
Steenhuisen, & Wilson, 2006; Sreeram & Ramasami, 2003; Tchounwou, Yedjou, Patlolla, & Sutton, 2014). Heavy
metals are mutagenic, carcinogenic, disturb metabolism, causes kidney failure, ammonia, fatigue, dizziness, short term
memory, renal failure, cardiovascular diseases, coordination problems, lung, throat, stomach cancer, neurotoxic,
hepatoxic, immunotoxin, rapid hair fall, kidney ,brain damage, severe anemia , intestinal irritation, disturbs cellular
processes such as ATP synthesis, oxidative phosphorylation ((Awofolu, 2005; Khan, Ahmad, & Rahman, 2007; Pabis et
al., 2018; Salem & Elfouly, n.d.; Tripathi et al., 2007). (Peng et al., 2018) used co-cropping to improve efficiency of
phytoremediation using (Trifolium repens, Artemisia selengensis, Houttuynia cordata and Medicago sativa) on purifying
wastewater contaminated by Vanadium, Chromium, Cadmium and Lead. The results exposed that reasonable cropping
pattern could expressively increase the efficiency of phytoremediation for wastewater. Phytoremediation use both woody
(Salix species, Populus species), Herb (Thalspi Caerulescens, Brassica Juncea). Herb and woody species have ability to
extract contaminants at root zone and transfer them to aerial parts of plants or stabilize them in root zone (Tahir, 2015).
Plant species, soil nature, bioavailability, contaminants type play important role in efficiency of phytoremediation
(Sreelal & Jayanthi, 2017). In phytoremediation two type of plants are used known as hyper accumulator and low
accumulator plants. Hyper accumulator have ability and tolerance to more metals accumulation but having less biomass
production (Oosten & Maggio, 2014). Plants extraction efficiency for contaminants also depend on biomass production
of the pants, plants with high biomass production extract and accumulate more contaminants in roots and aerial parts
(Labelle et al., 2005; Rajakaruna, Tompkins, & Pavicevic, 2006; Sharma & Pandey, 2014) plants with high biomass need
number of harvesting, composting of biomass, biomass transportation. So, use of such plants increase the overall cost for
phytoremediation. (Lasat, 1999) show that phytoremediation is economical and environmentally friendly compared to
conventional techniques used for soil remediation from pollutants such as soil washing using solubilizing agents in water,
electrochemical separation, vitrification of polluted soil, excavation and confrontation of the soil in landfill. Various
research work show that engineered plant can improve efficiency of phytoremediation (Campos, Merino, Casado, Pacios,
& Gómez, 2008; Kawahigashi, 2009). Arundo donax L. was used for remediation of soil contaminated by cadmium
during hydroponics experiments and in in soil experiment. Bioaccumulation factor and translocation factor were greater
in case of hydroponics experiments (Sabeen et al., 2013). Effect of chemically aided soil on phytoremediation using
Typha latifolia and vetiver (Chrysopogon zizanioides) was studied by (Ko & Akoto, 2018). In this research work three
type soil was used each containing sixteen sample differ by ethylene di-aminete- traacetic acid (EDTA), aluminum
sulfate [Al2(SO4)3], and unchanged soil. Using tetramethylammonium (TMA) and dodecyl trimethylammonium
International Journal of Advance Engineering and Research Development (IJAERD)
Volume 6, Issue 10, October-2019, e-ISSN: 2348 - 4470, print-ISSN: 2348-6406
@IJAERD-2019, All rights Reserved 23
(DTMA) improved bentonites (T-Bents and D-Bents) as amendments was studied for Stabilization of Cu, Zn, Cd, Hg, Cr
and As in soil (Yu et al., 2017). Various research work show that engineered plant can improve efficiency of
phytoremediation (Campos et al., 2008; Kawahigashi, 2009). Arundo donax L. was used for remediation of soil
contaminated by cadmium during hydroponics experiments and in in soil experiment. Bioaccumulation factor and
translocation factor were greater in case of hydroponics experiments (Sabeen et al., 2013) Effect of chemically aided soil
on phytoremediation using Typha latifolia and vetiver (Chrysopogon zizanioides) was studied by (Ko & Akoto, 2018). In
this research work three type soil was used each containing sixteen sample differ by ethylene di-aminete- traacetic acid
(EDTA), aluminum sulfate [Al2(SO4)3], and unchanged soil. Using tetramethylammonium (TMA) and dodecyl
trimethylammonium (DTMA) improved bentonites (T-Bents and D-Bents) as amendments was studied for Stabilization
of Cu, Zn, Cd, Hg, Cr and As in soil (Yu et al., 2017).
II. Sample collection
Best result of laboratory is function of sample therefore sample was collected using all necessary precautions to get result
more accurate. Little error in sample making tends to error in whole results, as sample is representation of whole quantity
used in research work. Quantity of sample should be which can be easily handled.
The selection of sampling point’s location and the samples collection was carried out by following general principles.
 Sample was collected near effluent of industrial zone where effluent was well mixed by free falling from pipe
carrying industrial wastewater.
 All suspended material was removed such as wood particles, papers and plastic etc. All those particles whose
diameter is one-quarter inch is known as large particles; it effects the overall result of sample.
 The collection of proper samples was made as easy as possible such that sampling points was eagerly reachable,
proper equipment were at hand, safety precautions were followed.
following above principal, a sample point location was selected just outside the industrial area. Sample of waste water
was collected from effluent of Industrial Estate at two points shown in Figure 2; where effluent was well mixed,
accessible and sample handle easily. Sample is collected in water cane which was then mixed to form composite sample.
III. Materials and Methodology
Materials used were pots, soil, plants, industrial wastewater, shed covered by plastic, water canes to collect sample, water
tank to make composite sample. Overall methodology is shown in Figure 1.
Figure 1: Over all methodology
Three lawns were made each lawn contain three flower pots shown in Figure 3. Shed was provided to protect from
surrounding environment interference such as extra contaminants or rain water shown in Figure 4. Concentration of
heavy metals in soil before and after maturity of plants were found using X-ray Fluorescence spectrometry shown in
Figure 5. Concentration of heavy metals in industrial wastewater was determined by using atomic absorption
International Journal of Advance Engineering and Research Development (IJAERD)
Volume 6, Issue 10, October-2019, e-ISSN: 2348 - 4470, print-ISSN: 2348-6406
@IJAERD-2019, All rights Reserved 24
spectrometry shown in Figure 6. Waste water of different concentration level of heavy metals was made by adding
domestic water in industrial wastewater in known amount. Three lawns were made labeled as Lawn X, Lawn Y and
Lawn Z. Lawn X and Lawn Y were irrigated by industrial wastewater which were diluted by domestic wastewater. Lawn
Z was irrigated by undiluted wastewater. In this research work amount of heavy metals extracted by plant was
determined by soil analysis before and after plantation in it. Soil used in pots shown in Figure 7 of known concentration
of heavy metals and wastewater used for irrigation also of known amount of heavy metals were used for plant growth. On
daily basis wastewater of different concentration level in known amount were provided to X, Y and Z lawn for seventy-
five days. After maturity plants are removed from pot carefully such that no soil wasted in which plantation were
completed shown in Figure 8. After mixing soil in each flower pot separately in X, Y and Z were analyzed in laboratory
using X-ray Fluorescence spectrometry. Amount of concentration removed from soil was calculated by following
formula.
Heavy metals in soil = Cs
Heavy metals in wastewater used for irrigation = Cw
Heavy metals extracted by plants= CE
Heavy metals in soil after plants growth C2=Cs + Cw - CE
Total dosage in of heavy metals in soil C1 = Cs + Cw
% Extraction by plants= 100= ×10……………………. (1)
Figure 2: Sample collection
Figure 3 plantation Figure 4 Shed to protect from rain
Figure 5: X-ray Fluorescence Spectrometry Figure 6: Atomic absorption spectrometry
Figure 7: Lawn preparation Figure 8: Plants harvesting
International Journal of Advance Engineering and Research Development (IJAERD)
Volume 6, Issue 10, October-2019, e-ISSN: 2348 - 4470, print-ISSN: 2348-6406
@IJAERD-2019, All rights Reserved 25
3.1. Results
After maturity of plants, plants were removed from soil in each pot. Soil of each flower pot was analyzed for heavy
metals using X-ray fluorescence spectrometry Using Formula 1 to calculate the amount of heavy metals remediated from
soil it was found that heavy metal lead was totally extracted by plant provided in form of waste water of different
concentration level. In case of soil which was irrigated by fully contaminated wastewater copper was remediated by 15%.
Copper while cobalt was remediated by 21%. Plants was grown for 75.
IV. FOOTNOTES
To know the efficiency of various plants species to extract heavy metals is very important because phytoremediation is
environmentally friendly process to remediate contaminants from soil and water, as soil and water is getting polluted due
to increase in population and industries. Following recommendations are made for future studies:
 More contamination levels.
 Effects of Seasonal Variations
 Different species
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International Journal of Advance Engineering and Research Development (IJAERD)
Volume 6, Issue 10, October-2019, e-ISSN: 2348 - 4470, print-ISSN: 2348-6406
@IJAERD-2019, All rights Reserved 26
21. Tahir, U. (2015). Phytoremediation : Potential flora for synthetic dyestuff metabolism. JOURNAL OF KING SAUD
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Remediation of heavy metals lead, cobalt and copper from industrail wastewater by phytoremediation

  • 1. International Journal of Advance Engineering and Research Development Volume 6, Issue 10, October -2019 @IJAERD-2019, All rights Reserved 22 Scientific Journal of Impact Factor (SJIF): 5.71 e-ISSN (O): 2348-4470 p-ISSN (P): 2348-6406 Remediation of heavy metals lead, cobalt and copper from industrail wastewater by phytoremediation Muhammad Asif, Salman Saeed2 , Rashid Rehan3 1 Civil Engineering Department, University of Engineering & Technology, Peshawar, Pakistan 2 National institute of Urban Infrastructure Planning, University of Engineering & Technology, Peshawar, Pakistan 3 Environmental Engineering Department, University of Engineering & Technology, Peshawar, Pakistan Abstract: To fulfil human beings requirement number of industries increases day by day which play important role in development of country but also causes environment pollution. Effluent of many industries contain heavy metals and other contaminants. Industrial effluent usually used for agriculture purposes without treatment. Plants take these heavy metals from industrial water and accumulate it in roots and Arial parts which become the part of animal and human body through food chain causes various diseases. In this research work plants were grown using wastewater of industrial effluents. Three sample of wastewater were made of various concentration level of lead, copper and cobalt. Typha latifoliate was grown in controlled environment. Three sample of wastewater were used. Soil used in pots was of known concentration of heavy metals. Using x-ray fluorescence spectrometry was used to find concentration of contaminants in soil before and after plantation and atomic absorption spectrometry was used to find concentration of heavy metals in industrial effluent. Wastewater of various concentration level was obtained by adding domestic water having no heavy metals. Extraction percentage performed by plants in various lawn was found by analysis of soil before and after the maturity of plants. soil which was irrigated by fully contaminated wastewater was remediated by 10%. Soil in which plants were irrigated by diluted wastewater was remediated by 15 and 21% respectively for copper and cobalt. Plants matured in seventy-five days in winter season. Keywords: Heavy metals; industrial effluent; various concentration of contaminants; phytoremediation. I. INTRODUCTION Heavy metals found naturally and artificially. Artificially contributors of heavy metals to environment are industries, agriculture, volcanic explosion, gasoline formation, sludge of sewage and extraction of Zinc and Copper (Cristaldi, Oliveri, Hea, & Zuccarello, 2017; Hernberg, 2000; Kabata-pendias, 2004; Oosten & Maggio, 2014; Pacyna, Pacyna, Steenhuisen, & Wilson, 2006; Sreeram & Ramasami, 2003; Tchounwou, Yedjou, Patlolla, & Sutton, 2014). Heavy metals are mutagenic, carcinogenic, disturb metabolism, causes kidney failure, ammonia, fatigue, dizziness, short term memory, renal failure, cardiovascular diseases, coordination problems, lung, throat, stomach cancer, neurotoxic, hepatoxic, immunotoxin, rapid hair fall, kidney ,brain damage, severe anemia , intestinal irritation, disturbs cellular processes such as ATP synthesis, oxidative phosphorylation ((Awofolu, 2005; Khan, Ahmad, & Rahman, 2007; Pabis et al., 2018; Salem & Elfouly, n.d.; Tripathi et al., 2007). (Peng et al., 2018) used co-cropping to improve efficiency of phytoremediation using (Trifolium repens, Artemisia selengensis, Houttuynia cordata and Medicago sativa) on purifying wastewater contaminated by Vanadium, Chromium, Cadmium and Lead. The results exposed that reasonable cropping pattern could expressively increase the efficiency of phytoremediation for wastewater. Phytoremediation use both woody (Salix species, Populus species), Herb (Thalspi Caerulescens, Brassica Juncea). Herb and woody species have ability to extract contaminants at root zone and transfer them to aerial parts of plants or stabilize them in root zone (Tahir, 2015). Plant species, soil nature, bioavailability, contaminants type play important role in efficiency of phytoremediation (Sreelal & Jayanthi, 2017). In phytoremediation two type of plants are used known as hyper accumulator and low accumulator plants. Hyper accumulator have ability and tolerance to more metals accumulation but having less biomass production (Oosten & Maggio, 2014). Plants extraction efficiency for contaminants also depend on biomass production of the pants, plants with high biomass production extract and accumulate more contaminants in roots and aerial parts (Labelle et al., 2005; Rajakaruna, Tompkins, & Pavicevic, 2006; Sharma & Pandey, 2014) plants with high biomass need number of harvesting, composting of biomass, biomass transportation. So, use of such plants increase the overall cost for phytoremediation. (Lasat, 1999) show that phytoremediation is economical and environmentally friendly compared to conventional techniques used for soil remediation from pollutants such as soil washing using solubilizing agents in water, electrochemical separation, vitrification of polluted soil, excavation and confrontation of the soil in landfill. Various research work show that engineered plant can improve efficiency of phytoremediation (Campos, Merino, Casado, Pacios, & Gómez, 2008; Kawahigashi, 2009). Arundo donax L. was used for remediation of soil contaminated by cadmium during hydroponics experiments and in in soil experiment. Bioaccumulation factor and translocation factor were greater in case of hydroponics experiments (Sabeen et al., 2013). Effect of chemically aided soil on phytoremediation using Typha latifolia and vetiver (Chrysopogon zizanioides) was studied by (Ko & Akoto, 2018). In this research work three type soil was used each containing sixteen sample differ by ethylene di-aminete- traacetic acid (EDTA), aluminum sulfate [Al2(SO4)3], and unchanged soil. Using tetramethylammonium (TMA) and dodecyl trimethylammonium
  • 2. International Journal of Advance Engineering and Research Development (IJAERD) Volume 6, Issue 10, October-2019, e-ISSN: 2348 - 4470, print-ISSN: 2348-6406 @IJAERD-2019, All rights Reserved 23 (DTMA) improved bentonites (T-Bents and D-Bents) as amendments was studied for Stabilization of Cu, Zn, Cd, Hg, Cr and As in soil (Yu et al., 2017). Various research work show that engineered plant can improve efficiency of phytoremediation (Campos et al., 2008; Kawahigashi, 2009). Arundo donax L. was used for remediation of soil contaminated by cadmium during hydroponics experiments and in in soil experiment. Bioaccumulation factor and translocation factor were greater in case of hydroponics experiments (Sabeen et al., 2013) Effect of chemically aided soil on phytoremediation using Typha latifolia and vetiver (Chrysopogon zizanioides) was studied by (Ko & Akoto, 2018). In this research work three type soil was used each containing sixteen sample differ by ethylene di-aminete- traacetic acid (EDTA), aluminum sulfate [Al2(SO4)3], and unchanged soil. Using tetramethylammonium (TMA) and dodecyl trimethylammonium (DTMA) improved bentonites (T-Bents and D-Bents) as amendments was studied for Stabilization of Cu, Zn, Cd, Hg, Cr and As in soil (Yu et al., 2017). II. Sample collection Best result of laboratory is function of sample therefore sample was collected using all necessary precautions to get result more accurate. Little error in sample making tends to error in whole results, as sample is representation of whole quantity used in research work. Quantity of sample should be which can be easily handled. The selection of sampling point’s location and the samples collection was carried out by following general principles.  Sample was collected near effluent of industrial zone where effluent was well mixed by free falling from pipe carrying industrial wastewater.  All suspended material was removed such as wood particles, papers and plastic etc. All those particles whose diameter is one-quarter inch is known as large particles; it effects the overall result of sample.  The collection of proper samples was made as easy as possible such that sampling points was eagerly reachable, proper equipment were at hand, safety precautions were followed. following above principal, a sample point location was selected just outside the industrial area. Sample of waste water was collected from effluent of Industrial Estate at two points shown in Figure 2; where effluent was well mixed, accessible and sample handle easily. Sample is collected in water cane which was then mixed to form composite sample. III. Materials and Methodology Materials used were pots, soil, plants, industrial wastewater, shed covered by plastic, water canes to collect sample, water tank to make composite sample. Overall methodology is shown in Figure 1. Figure 1: Over all methodology Three lawns were made each lawn contain three flower pots shown in Figure 3. Shed was provided to protect from surrounding environment interference such as extra contaminants or rain water shown in Figure 4. Concentration of heavy metals in soil before and after maturity of plants were found using X-ray Fluorescence spectrometry shown in Figure 5. Concentration of heavy metals in industrial wastewater was determined by using atomic absorption
  • 3. International Journal of Advance Engineering and Research Development (IJAERD) Volume 6, Issue 10, October-2019, e-ISSN: 2348 - 4470, print-ISSN: 2348-6406 @IJAERD-2019, All rights Reserved 24 spectrometry shown in Figure 6. Waste water of different concentration level of heavy metals was made by adding domestic water in industrial wastewater in known amount. Three lawns were made labeled as Lawn X, Lawn Y and Lawn Z. Lawn X and Lawn Y were irrigated by industrial wastewater which were diluted by domestic wastewater. Lawn Z was irrigated by undiluted wastewater. In this research work amount of heavy metals extracted by plant was determined by soil analysis before and after plantation in it. Soil used in pots shown in Figure 7 of known concentration of heavy metals and wastewater used for irrigation also of known amount of heavy metals were used for plant growth. On daily basis wastewater of different concentration level in known amount were provided to X, Y and Z lawn for seventy- five days. After maturity plants are removed from pot carefully such that no soil wasted in which plantation were completed shown in Figure 8. After mixing soil in each flower pot separately in X, Y and Z were analyzed in laboratory using X-ray Fluorescence spectrometry. Amount of concentration removed from soil was calculated by following formula. Heavy metals in soil = Cs Heavy metals in wastewater used for irrigation = Cw Heavy metals extracted by plants= CE Heavy metals in soil after plants growth C2=Cs + Cw - CE Total dosage in of heavy metals in soil C1 = Cs + Cw % Extraction by plants= 100= ×10……………………. (1) Figure 2: Sample collection Figure 3 plantation Figure 4 Shed to protect from rain Figure 5: X-ray Fluorescence Spectrometry Figure 6: Atomic absorption spectrometry Figure 7: Lawn preparation Figure 8: Plants harvesting
  • 4. International Journal of Advance Engineering and Research Development (IJAERD) Volume 6, Issue 10, October-2019, e-ISSN: 2348 - 4470, print-ISSN: 2348-6406 @IJAERD-2019, All rights Reserved 25 3.1. Results After maturity of plants, plants were removed from soil in each pot. Soil of each flower pot was analyzed for heavy metals using X-ray fluorescence spectrometry Using Formula 1 to calculate the amount of heavy metals remediated from soil it was found that heavy metal lead was totally extracted by plant provided in form of waste water of different concentration level. In case of soil which was irrigated by fully contaminated wastewater copper was remediated by 15%. Copper while cobalt was remediated by 21%. Plants was grown for 75. IV. FOOTNOTES To know the efficiency of various plants species to extract heavy metals is very important because phytoremediation is environmentally friendly process to remediate contaminants from soil and water, as soil and water is getting polluted due to increase in population and industries. Following recommendations are made for future studies:  More contamination levels.  Effects of Seasonal Variations  Different species REFERENCES 1. Awofolu, O. R. (2005). A SURVEY OF TRACE METALS IN VEGETATION , SOIL AND LOWER ANIMAL ALONG SOME SELECTED MAJOR ROADS IN METROPOLITAN CITY OF LAGOS. 431–447. https://doi.org/10.1007/s10661-005-4440-0 2. Campos, V. M., Merino, I., Casado, R., Pacios, L. F., & Gómez, L. (2008). Review . Phytoremediation of organic pollutants 1. 6, 38–47. 3. Cristaldi, A., Oliveri, G., Hea, E., & Zuccarello, P. (2017). Environmental Technology & Innovation Phytoremediation of contaminated soils by heavy metals and PAHs . A brief review. Environmental Technology & Innovation, 8, 309–326. https://doi.org/10.1016/j.eti.2017.08.002 4. Hernberg, S. (2000). Lead Poisoning in a Historical Perspective. 254(February), 244–254. 5. Kabata-pendias, A. (2004). Soil – plant transfer of trace elements — an environmental issue. 122, 143–149. https://doi.org/10.1016/j.geoderma.2004.01.004 6. Kawahigashi, H. (2009). Transgenic plants for phytoremediation of herbicides. 225–230. https://doi.org/10.1016/j.copbio.2009.01.010 7. Khan, M. A., Ahmad, I., & Rahman, I. (2007). Effect of Environmental Pollution on Heavy Metals Content of Withania somnifera. 339–343. 8. Ko, A., & Akoto, R. (2018). Ecotoxicology and Environmental Safety Assisted phytoremediation of heavy metal contaminated soil from a mined site with Typha latifolia and Chrysopogon zizanioides. 148(November 2017), 97– 104. https://doi.org/10.1016/j.ecoenv.2017.10.014 9. Labelle, S., Mehta, P., Mihoc, A., Fortin, N., Cha, G., Sura, C., … Greer, C. W. (2005). Phytoremediation of heavy metal and PAH-contaminated brownfield sites. 277–278. https://doi.org/10.1007/s11104-004-5295-9 10. Lasat, M. M. (1999). Phytoextraction of Metals from Contaminated Soil : A Review of Plant / Soil / Metal Interaction and Assessment of Pertinent Agronomic Issues. 2. 11. Oosten, M. J. Van, & Maggio, A. (2014). Functional biology of halophytes in the phytoremediation of heavy metal contaminated soils. Elsevier B.V. https://doi.org/10.1016/j.envexpbot.2014.11.010 12. Pabis, K., Gundacker, C., Giacconi, R., Basso, A., Costarelli, L., Piacenza, F., … Malavolta, M. (2018). Chemosphere Zinc supplementation can reduce accumulation of cadmium in aged metallothionein transgenic mice. Chemosphere, 211, 855–860. https://doi.org/10.1016/j.chemosphere.2018.08.017 13. Pacyna, E. G., Pacyna, J. M., Steenhuisen, F., & Wilson, S. (2006). Global anthropogenic mercury emission inventory for 2000. 40, 4048–4063. https://doi.org/10.1016/j.atmosenv.2006.03.041 14. Peng, L., Liu, P., Feng, X., Wang, Z., Cheng, T., Liang, Y., … Shi, Z. (2018). ScienceDirect Kinetics of heavy metal adsorption and desorption in soil : Developing a unified model based on chemical speciation. Geochimica et Cosmochimica Acta, 224, 282–300. https://doi.org/10.1016/j.gca.2018.01.014 15. Rajakaruna, N., Tompkins, K. M., & Pavicevic, P. G. (2006). PHYTOREMEDIATION : AN AFFORDABLE GREEN TECHNOLOGY FOR THE CLEAN-UP OF METAL-CONTAMINATED SITES IN SRI LANKA. 35(1), 25–39. 16. Sabeen, M., Mahmood, Q., Irshad, M., Fareed, I., Khan, A., Ullah, F., … Tabassum, S. (2013). Cadmium Phytoremediation by Arundo donax L . from Contaminated Soil and Water. 2013. 17. Salem, H. M., & Elfouly, A. A. (n.d.). Minerals Reconnaissance at Saint Catherine Area , Southern Central Sinai , Egypt and their Environmental Impacts on Human Health a b. 586–598. 18. Sharma, P., & Pandey, S. (2014). Status of Phytoremediation in World Scenario. 2(4), 178–191. https://doi.org/10.12691/ijebb-2-4-5 19. Sreelal, G., & Jayanthi, R. (2017). REVIEW ON PHYTOREMEDIATION TECHNOLOGY FOR REMOVAL OF SOIL CONTAMINANT. 14(1), 127–130. 20. Sreeram, K. J., & Ramasami, T. (2003). Sustaining tanning process through conser v ation , reco v ery and better utilization of chromium. 38.
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