Phytotoxicity and remediation of heavy metals by Alfalfa (Medicago sativa) in soil-vermicompost media.
The soil has been traditionally the site for disposal for most of the heavy metal wastes which needs to be treated. Unlike organic compounds, metals cannot be degraded (Salt et al., 1995) and their cleanup requires their immobilization and toxicity reduction or removal. Currently, conventional remediation methods of heavy metal contaminated soils include electrokinetical treatment, chemical oxidation or reduction, leaching, solidification, vitrification, excavation and off-site treatment. But a majority of these technologies are costly to implement and cause further disturbance to the already damaged environment (Bio-Wise, 2003). Furthermore, bare soil is more susceptible to wind erosion and spreading of contamination by airborne dust. In an attempt to overcome the aforementioned problems associated with more traditional remediation techniques, scientists and engineers have been investigating the ability of live plants and inactivated biomaterials as remediation alternatives (Peralta et al., 2001). The techniques that involve the use of living organisms include bioremediation, phytoextraction, phytovolatilization, phytostabilization, rhizofiltration and phytoremediation (Yang et al., 2005). Phytoremediation using trees provides a potential opportunity to extract or stabilize metals. Phytoextraction (uptake) involves the use of high yielding plants that readily transport targeted metals from soil to vegetation, allowing removal of metals by harvesting the plants, without damaging the soil or requiring its disposal to landfill. The process takes longer, but meanwhile allows greening of the land and harvested plants can be used as bioenergy crops. Some plants have developed the ability to remove ions selectively from the soil to regulate the uptake and distribution of metals in their tissues. Most metal uptake occurs in the root system, usually via absorption, where many mechanisms are available to prevent toxic effects due to the high concentration of metals in the soil and water (EPA, 1996). Phytoremediation can be used to remove not only metals (e.g. Ag, Cd, Co, Cr, Cu, Hg, Mn, Mo, Ni, Pb, Zn) but also radionuclides (e.g. ([sup.90]) Sr, ([sup.137]) Cs, ([sup.239]) Pu, ([sup.234]) U, ([sup.238]) U) and certain organic compounds (Andrade and Mahler., 2002).
Plants have shown the capacity to withstand relatively high concentration of contaminants without toxic effects. A wide range of plants can be useful in cleaning up toxins. Some of the species now being studied--or already in use--are mustards, alfalfa, vines, bamboo, cord grass and sunflowers. Some trees, including willows and poplars, also make good phytoremediators. The plant material may be used for non-food purposes; alternatively, it can be ashed followed by recycling of the metals or as disposal in a landfill (Angel and Linacre, 2005). Alfalfa has a number of characteristics that make it a prime candidate for mitigation of environmental contamination problems. This includes deep rooted (commonly 9-16 feet), an active rhizosphere and its ability to absorb water, nitrates and other heavy metals (Putam, 2001). In the present study we examine the potential of alfalfa plant for phytoremediation (uptake) of heavy metals. Medicago sativa (alfalfa) is a good source of plant tissues, because it has been found to tolerate heavy metals and grow well in contaminated soils (Baligar et al., 1993). Gardea-Torresdey et al. (2000) have shown that alfalfa is a potential source of biomaterials for the removal and recovery of heavy metal ions.
Phytoremediation is essentially an agronomic approach and its success depends ultimately on agronomic practices applied at the site (Chaney et al., 1999). Biological processes such as composting followed by vermicomposting to convert vegetable waste (as valuable nutrient source) in agriculturally useful organic fertilizer would be of great benefit. The composting followed by vermicomposting of vegetable waste with earthworm (Eisenia foetida) develops in to a natural fertilizer (Maharashtra Nature Park Bulletin, 2003). The vermicompost contain high nutrient value, increases fertility of soil and maintains soil health (Suthar et al., 2005). Application of compost and vermicompost in contaminated soil improves soil fertility and physical properties as well as helps in successful approach to phytoremediation which has been demonstrated by Zheljazkov and Warman (2004). It also enhances quality of growing plants and increased biomass which could suggest that more metal can be taken up from the contaminated growth media and the tolerance to the metal toxicity is improved (Tang et al., 2003). The use of vermicompost developed from vegetable waste by vermiculture biotechnology with soil would provide natural environment for phytoremediation (Elcock and Martens, 1995).
In the work presented we addressed the application of vermicompost developed from vegetable waste in soil contaminated with heavy metals for phytoremediation studies. The objectives of this study is to determine the effects of heavy metals on seed germination, plant growth, biomass and examine their uptake by alfalfa (Medicago sativa) in soil- vermicompost media.
Materials and mehtods
Soil Sampling, Processing and Characterization
Soil was collected from a depth of about 0-15 cm along the banks of Surya River, Palghar (located 100 km away from Mumbai). Stones and plant tissues were carefully removed from the soil prior to drying process under laboratory condition. The soil was screened through 2 mm stainless steel sieve and stored in a plastic bag at room temperature until use. Concentrations of Pb, Zn, Cu, Ni and Cd were measured by atomic absorption spectrophotometer (APHA, 1998). The physicochemical parameters were measured by standard methods(Table 1).
Soil texture was determined by the Bouyoucos hydrometer method. The moisture content of soil was calculated by the weight difference before and after drying at 105 [degrees]C to a constant weight. The pH and electrical conductivity (EC) were measured after 20 min of vigorous mixed samples at 1: 2.5:: Solid: deionized water ratio using digital meters [Elico, Model LI-120] with a combination pH electrode and a 1-cm platinum conductivity cell respectively. Total nitrogen and total phosphorus were determined according to the standard methods of the American Public Health Association (1998). Cation exchange capacity was determined after extraction with ammonium acetate at pH 7.0 and the organic carbon was determined by using Walkley-Black method (Jackson, 1973).
The vermicompost was produced from vegetable waste (cabbage, french bean, cauliflower, lady finger, spinach, carrot and raddish) collected from the vegetable market. In the process dry leaves, coconut fibers and fresh grasses having high lignin content were taken with the vegetable waste in appropriate quantity. About '/2 Kg of exotic varieties of earthworms (Eisenia foetida) was spread on bedding materials. Everyday, 200 to 300 gm of vegetable waste collected from market was supplied for a period of two and half months as a source of food for the earthworms. The physicochemical parameters were measured during vermicomposting as described in soil analysis. After two and half month, vermicompost was collected, air dried, sieved (2-mm) and a portion of it was taken for nutrient analysis in order to prove its potency as biofertilizer. The nutrients in dried sample of vermicompost was digested with concentrated nitric acid and 30% hydrogen peroxide and then determined by an atomic absorption spectrophotometer [AAS, Perkin Elmer] (APHA, 1998).
Green house pot culture experiments were conducted to study the effect of heavy metals viz Cd, Ni, Cu, Pb and Zn on seed germination, root growth, shoot growth and phytoremediation (uptake) by Alfalfa. The ratio 3:1 of alluvial soil and vermicompost were used as media. Nutrient and trace elements concentrations in the vermicompost are presented in table 2. This soil-vermicompost media was then amended with the heavy metals: Cd as Cd ([NO.sub.3]), 4[H.sub.2]O; Cu as CUS[O.sub.4]. 5[H.sub.2]O; Ni as Ni([NO.sub.3]).sub.2]; Pb as Pb ([NO.sub.3].sub.2], and Zn as Zn ([NO.sub.3]).sub.2]. 6[H.sub.2.O]. The concentrations of each heavy metal used in this study were 0, 5, 10, 20, 40 and 50 ppm. Alfalfa seeds were obtained from seed supplier Ratanshi Agro-Hortitech (Byculla, Mumbai). Seeds were immersed in 3% (v/v) of formaldehyde for 5 minutes and washed with distilled water several times to avoid fungal contamination. The soil- vermicompost media contaminated/amended with the heavy metal was used as potting media. To determine the effect of heavy metals; 10 seeds of uniform size were placed in every Petri dish (the lids were left on until 3 days after the germination) for study of seed germination. The Petri dish were kept in the dark and observed for germination. The seeds were considered germinated with the emergence of radicles. Small plastic pots/glasses were used for studying shoot and root growth. Ten plants were grown in 2 Kg capacity plastic pots for phytoremediation study. Soil-moisture content was adjusted regularly by weight to about 60% of water-holding capacity with deionized water.
To prevent loss of nutrients and trace elements out of the pots, plastic trays were placed under each pot and the leachets collected were put back in the respective pots. Each treatment of plant consisted of three replicate for statistical purpose. The seeds were set under 12/12 hrs light/dark cycle and temperatures of 30[degrees]C during the day and 27[degrees]C during the night. The average relative humidity was recorded to be 75%. The seedlings were harvested after two weeks; germination rate and shoot/root length were recorded. For the phytoremediation study plants were harvested after 10 weeks. The plants were then separated in to roots and shoots. The plant samples were washed with distilled water and dried in an oven at 70[degrees]C for 3 days and the dry weight of biomass was determined, after which these samples were stored in the brown paper bags. The samples were considered for analysis of metal content digested with concentrated nitric acid and 30% hydrogen peroxide and then the heavy metal content was determined by an atomic absorption spectrophotometer [AAS, Perkin Elmer] (APHA, 1998).
Each treatment for % seed germination, plant root/ shoot growth and uptake consisted of three replicate for statistical purpose. The data presented for each treatment in this study is represented as mean of samples with standard deviation (X [+ or -] S.D.) calculated by standard statistical methods (Mahajan, 1997).
The present research study has been carried out in glass house in pot culture experiments to study the uptake of heavy metals at various concentrations in soil -vermicompost media. The alfalfa plant was used for uptake of heavy metals. The soil and developed vermicompost were analyzed for physicochemical characteristic. The soil was amended with heavy metals (Pb, Zn, Cu, Ni and Cd) for phytoremediation. The results are presented below:
After selecting the probable site, soil was collected and subjected to extensive analysis of various physicochemical parameters, which influence root establishment in soil (Table 1). Soil, texture, which was found to be sandy loam, had profound effect upon the properties of soil including its water supplying power, rate of water intake, aeration, fertility and ease of tillage. The pH was 7.2, which lies within the recommended value for proper growth and efficient uptake of nutrients and compounds from soil. The percentage of organic matter and nitrogen were found to be 0.80 and 0.05 respectively. Macronutrients including metals were also present in substantial amount. Further to augment the existing native state of soil, it was spiked with vermicompost, which gives all the nutrients conducive to plant growth for phytoremediation studies. There was no history of heavy metal (Cd, Ni and Ph) contamination found in the soil collected.
The vermicompost developed was characterized and found to have high concentration of nutrients such as Ca, Zn, Cu, Mg, Fe and Mn (Table 2). This vermicompost developed by the vermiculture biotechnology was then used as a natural fertilizer for phytoremediation studies of heavy metals.
Effect of Heavy Metals on Seed Germination
The present research demonstrated a concentration dependent inhibition of the seed germination with regards to Alfalfa species (Table 3). The results of this study indicated that Cd, Ni and Pb at 5 ppm levels had very low toxic effects on seed germination while Copper at the same doses increased seed germination. At the 10 and 20 ppm concentrations of Cd, Ni and Pb reduced the seed germination while 5 and 10 ppm doses of Cu promoted seed germination. The seed germination inhibited at 40 and 50 ppm levels as compared to the control for all the four metals i.e. Cd, Ni, Pb and Cu. Delayed germination was also observed in all cases at higher i.e 40 and 50 ppm concentrations. However, in the same study Zinc (Zn) being the only metal which did not reduce the seed germination. The resulting rank order of toxicity for metals on seed germination was Cd > Cu > Ni > Pb >Zn. However, seed germination increased at all Zn concentrations.
Effect of Heavy Metals on Root growth
Increase in the heavy metal concentration in the soil- vermicompost media caused root length decrease with stunt growth of roots (Table 3). The dose of 5ppm of Cd, Ni, Pb, Cu and Zn promoted the root growth of the plants as compared to the root growth of the control plants. The heavy metals Cu, Ni, Zn and Pb at 10 ppm level further increased the root growth over the control root size. However at the same dose Cd reduced the root size on comparison with the control root elongation. Cd, Ni, Cu and Pb demonstrated a concentration dependant inhibition of root growth at 20, 40 and 50 ppm dosages. All the Zn concentrations increased the root length than the control root length alfalfa plants. Root toxicity symptom included browning, reduced number of roots hair and growth. In comparison to the control treatment without heavy metals (Cd, Pb, Cu and Ni), Plant roots were healthy and normal. The color of the roots receiving higher heavy metals treatment (40 and 50 ppm) except Zn, changed gradually over time from creamy white color to dark brown, an indication of intense suberification. Plants treated at lower concentrations were not significantly affected by the metals. All Zinc, concentrations showed increase in root growth. Lateral roots were observed in almost all treated samples of Zn, Cd, Cu, Pb and Ni demonstrated concentration dependant inhibition of root growth at higher ppms.
Effect of Heavy Metals on Shoot Growth
The effects of heavy metals on the shoot growth are different from their effects on root growth (Table 3). The shoot length was found slightly reduced than the control alfalfa plants at the 5 ppm Cd dose. On the otherhand, the 5 ppm dose of Cu, Pb, Ni and Zn increased the shoot lengths as compared to the control treatment. These results indicate that low concentrations of Cd, Cu, Ni and Pb have micronutrient-like effects on the sorghum plants and all the plants appeared to be healthy. The heavy metals Cd, Ni and Pb at 10 and 20 ppm levels reduced the shoot growth; however, Cu at the same dose increased the shoot size. When the concentration of these above said four metals was increased to 40 and 50 ppm dose, the shoot size of the plants found a concentration dependant inhibition of shoot growth as compared to the control plants. All plants grown in the media contaminated with Zn showed increase in the shoot elongation than the plants grown in media without Zn contamination.
Effect of Heavy Metals on Plant Biomass
The biomass results after 10 weeks of experiments indicated that the mean plant biomass of alfalfa showed increasing tendency as the concentrations increased from 5 to 10 to 20 ppm for Cd, Cu and Ni (Table 4). Biomass decreased gradually as the concentration of Cd, Cu and Ni in the soil- vermicompost media increased to 40 and 50 ppm. The biomass yield affected by the higher ppm levels of Cd caused reduction in the plant biomass. Lead showed low effect on plant biomass. There was positive effect seen in all Zn concentrations and increase in biomass yield as compared to control ones.
Heavy Metal Uptake by Plant Tissue
The heavy metals concentration in the plant is affected by two factors that is the metal content supplied in the soil-vermicompost media and the plant tissue as well as by the interaction between these factors. The mean uptake of metals Cd, Ni, Pb, Cu and Zn by alfalfa increased as the concentrations of these metals in the soil vermicomposting media increased (Table 5). In plant, shoot and root were observed to have a characteristic uptake capacity for different metals. The heavy metals were untaken by the alfalfa plants in the following order: Zn> Cu>Cd>Ni>Pb.
Several researchers have demonstrated that earthworm castings (vermicompost) have excellent aeration, porosity, structure, drainage and moisture-holding capacity. The vermicompost is a rich source of beneficial microorganisms and nutrients (Paul, 2000) and is used as a soil conditioner or fertilizer (Hattenschwile and Gaser, 2005). Increase in crop yield, soil nutrients status and nutrients uptake was reported due to application of vermicompost (Singh and Sharma, 2003). Peng et al. (2005) and Yang et al. (2005) have reported that application of compost or manure can increase the bioavailability and in-plant mobility of copper. Significantly more copper was found in grains and straw of oat treated with vermicompost as compared with the application of mineral fertilizers. Experimental work has shown that earthworm activity enhances tree seedling growth associated with enhanced soil organic matter, improved nutrition (including [N0.sup.-.sub.3], [NH.sup.+.sub.4] and [Ca.sup.+.sub.2]) and increased mycorrhizal colonization (Welke and Parkinson, 2003). Yield of a tropical leguminous woody shrub, Leucaena leucocephala, in amended Pb-Zn mine tailings has been found to be increased by 10 to 30% in the presence of burrowing earthworms (Pheretima spp.) (Ma et al., 2003). The earthworms increased available forms of N and P in soil, increased metal bioavailability and raised metal uptake into plants by 16 to 53%. Some evidence indicates that earthworms increase metal bioavailability in relatively low-level metal-contaminated soils with higher organic matter contents. This agrees with results of experiments in which the addition of exogenous humic acid to soil has been shown to increase plant-available metals (Halim et al., 2003).
Effect of Heavy Metals on Seed Germination
The research demonstrated concentration dependent inhibition of the seed germination. Early growth period such as germination is more sensitive to heavy metal pollution. Generally the germination started after 24 hours of sowing and was more enhanced during early hours (before 72 hours after showing). Peralta et al. (2001) found that 20 and 40 ppm of Cu, Cd and Ni inhibited ability of seeds of Medicago sativa to germinate and grow in the contaminated medium, whereas Zn did not reduce the seed germination. Compared to the control, at and above 10 ppm Cr (VI) concentration, significant inhibitory effect on seedling growth of tested rice cultivars were detected by Xiong (1998). The experiment conducted by Peralta-Videa et al. (2004) showed that the susceptibility of living alfalfa plants to Cd, Cu and Zn was correlated to the age of the plants. He also reported that after four days germination, Cr, Cd, Ni, except Zn, had lethal effects on the alfalfa seedlings. The toxic effects of copper in plant cells appear to be largely attributable to competitive inhibition of essential ion pathways by copper and to the redox production of reactive oxygen species. Jonak et al. (2004) mentioned that an excess of copper ions activated four different mitogen-activated protein kinase (MAPK) pathways in alfalfa seedlings: SIMK, MMK2, MMK3 and SAMK. The same pathways appear to respond to cadmium, but with a greater time delay than with copper. They suggested that this may indicate the MAPK response is mediated by reactive oxygen species.
Effect of Heavy Metals on Root growth
Increase in the heavy metal concentration in the soil- vermicompost media caused root length decrease with stunt growth of roots. One of the explanations for roots to be more responsive to toxic metals in environment might be that roots were the specialized absorptive organs so that they were affected earlier and subjected to accumulation of more heavy metals than any of the other organs This could also be the main reason that root length was usually used as a measure for determining heavy metal- tolerant ability of plant (Xiong 1998). According to Chaignon and Hinsinger (2003), higher concentrations of Copper can inhibit root growth before shoot growth and can accumulate in the roots without any significant increase in its content of the aerial parts. Heavy metals are found to be more toxic for root growth because they accumulate on root and retard cell division and cell elongation. Gyawali and Lekhak, (2006) mentioned that the order of metal toxicity to new root primordia in Salix viminalis is Cd>Cr>Pb, whereas root length was more affected by Cr than by other heavy metals studied.
Effect of Heavy Metals on Shoot Growth
The results indicate that low concentrations of Cd, Cu, Ni and Pb have micronutrient-like effects on the alfalfa plants. Ormrod et al. (1986) investigated that Nickel caused stunted and deformed growth of shoot with symptoms of chlorosis. Statistically significant differences (P<0.05) between the shoot length of the control treatment plants and the length of plants of alfalfa grown in the presence of the heavy metal mixture was reported by Peralta- Videa et al. (2006). When Cr was added at 2, 10 and 25 ppm to nutrient solutions in sand cultures in oats (Avena sativa L.), Gyawali and Lekhak, (2006) noted that the 11%, 22% and 41% reduction in plant height, respectively, over control. Generally, it was seen that degrees of inhibition of shoot and root growth started from 10 ppm concentration. In this respect Peralta- Videa et al. (2004) reported that that Cd affected young plants more than old plants of P. coccineus. and Cd applied to the younger plants caused a stronger reduction in growth parameters such as leaf area and fresh weight accumulation and reduce shoot growth by reducing the chlorophyll content and the activity of photosystem I.
Effect of Heavy Metals on Plant Biomass
The biomass yield affected by the higher concentrations of metals and caused reduction in the plant biomass. Higher doses of heavy metal can affect physiology, reduced plant growth and dry biomass yield (Grifferty and Barrington, 2000). Nwosu, et al. (1995) mentioned that the mean plant biomass decreased in both lettuce and radish, as the concentration of Cd and Pb in soil increased. Grifferty and Barrington (2000) showed that the increased Zn concentration from 25 to 50 mg/kg had a significantly positive effect on dry biomass yield. Higher levels of organic matter (882.30g kg-') and nutrients content in the compost had beneficial influence on soil chemical and biochemical properties and plant growth, thus increasing biomass yields (Yang et al., 2005). The plant biomass may be incinerated either to reduce volume, recover energy, disposed offusing appropriate techniques or recycled to recover valuable metals (Angel and Linacre, 2005). The alfalfa produced greater biomass which result in a higher concentrations uptake of metals was reported by Pivetz, (2001). The phytotoxicity of cadmium on growth and dry matter production of a number of cultivated plants have been determined by Gondek and Filipek-Mazur (2003). Corn, alfalfa and sorghum were found to be effective due to their fast growth rate and large amount of biomass produced.
Heavy Metal Uptake by Plant Tissue
The mean uptake of metals Cd, Ni, Pb, Cu and Zn by alfalfa increased as the concentrations of these metals in the soil- vermicomposting media increased. Laboratory experiments have determined that alfalfa possesses the ability to bind various heavy metal ions. Alfalfa shoot biomass has demonstrated the ability to bind an appreciable amount of copper, nickel, cadmium, chromium, lead and zinc from aqueous solutions (Tiemann et al., 1998). In addition, alfalfa biomass is also able to reduce the oxidation state of other metals such as Cr and An (GardeaTorresdey et al., 2000). Increased in lead uptake by alfalfa (Medicago sativa) using EDTA and a plant growth promoter was reported by Lopez et al. (2005). The roots preferentially explored metals in the contaminated area. The large surface area of roots and their intensive penetration of soil, may reduce leaching, runoff and erosion via stabilization of soil, offer advantages for phytoremediation. Most crop species tend to accumulate Cd at the highest concentrations in the root tissue, followed by leaves, then by seeds or storage organs. Several studies have demonstrated that the metal concentration in the plant tissue is a function of the heavy metals content in the growing environment (Cui et al., 2004; Grifferty and Barrington, 2000).
Plants use photosynthetic energy to extract ions from the soil and concentrate them in their biomass, according to nutritional requirements (Kramer and Chardonnens, 2001). The essential elements (Cu and Zn) are required in low concentrations and hence are known as trace elements or micronutrients, whereas nonessential elements (Cd, Ni and Ph) are phytotoxic (Gerard et al., 2000). Zn is relatively mobile in soils and is the most abundant metal in root and shoot of contaminated plants as it is in soils. This metal is necessary as a minor nutrient and it is known that plants have special zinc transporters to absorb this metal (Zhu et al., 1999). However, an excessive accumulation of this element in living tissues leads to toxicity symptoms. The phytoavailable Lead is usually very low due to its strong association with organic matter, Fe-Mn oxides, clays and precipitation as carbonates, hydroxides and phosphates (Shen et al., 2002). An ultrastructural study using transmission electron microscopy revealed the retention of unchelated Pb mainly in cell wall of roots, particularly around intercellular spaces (W enger et al., 2003).
Cadmium also is considered to be mobile in soils but is present in much smaller concentrations than Zn (Zhu et al., 1999). Moreover, many studies have demonstrated that Cd taken up by plants accumulates at higher concentrations in the roots than in the leaves (Boominathan and Doran, 2003). Alloway (1995) mentioned that Alyssum species which are naturally adapted to serpentine soils can accumulate over 2% Ni. The uptake by some plants has been confirmed for Cd (up to 0.2% Cd in shoot dry biomass), Ni (up to 3.8% Ni in shoot dry biomass) and Zn (up to 4% Zn in shoot dry biomass) by Kramer and Chardonnens, (2001). The application of peat and manure in contaminated soil increased Cu, Zn and Ni accumulation by wheat (Schmidt, 2003).
Organic matter in soil could effectively increase the activity of metals in soil and improve metal mobility and distribution in soil. The application of natural fertilizer (compost and vermicompost) in soils has helped in increase in metal mobility through the formation of soluble metal-organic complexes (Yang et al., 2005). In addition, exudation of organic compounds by plant roots, such as organic acids, influence ion solubility and uptake (Klassen et al., 2000) through their effects on microbial activity, rhizosphere physical properties and root-growth dynamics (Yang et al., 2005). The higher concentrations uptake of heavy metals (Cu, Zn, Fe, Al and Mn) by alfalfa (Medicago sativa) was reported by Rehab et al. (2002).
This research work deals with phytoremediation of heavy metals by Alfalfa in the soil- vermicompost media. Medicago sativa (alfalfa) is a good source of plant tissues, because it has been found to tolerate heavy metals and grow well in contaminated soils. The phytoremediation techniques for the heavy metal management proves to be very effective as its cost is approximately one tenth that of conventional soil cleansing procedures and in some cases, the plant material can be further utilized to recoup the cost of the operation or even turn a profit. Another advantage of phytoremediation is that it leaves the soil fertile and has less adverse environmental effects as compared to conventional procedures. The low-doses of heavy metals applied stimulated the root and shoot elongation of Alfalfa plants. At higher concentrations i.e. 40 and 50 ppm of Cd, Cu, Ni and Pb reduced the ability to germinate. However the plants were able to germinate and grow efficiently at any Zn concentration evaluated in this study. The study shows that heavy metals were efficiently uptaken at all concentrations using vermicompost media and the uptake was increased along the increasing concentrations in soil. Alfalfa is a very fast-growing, deep rooted with a high biomass producing plant and maybe used for energy production and metal-enriched biomass can be harvested using standard agricultural methods and smelted to recover the metals. The present technology will help to remediate the higher concentrations of metals by the application of vermicompost as a natural fertilizer in soil. This technology will be applicable at the site to remediate the heavy metals. Thus, an increase in the plant resistance to heavy metal toxicity (Zn, Pb and Cd) seems possible by means of addition of nutrient (vermicompost) supply.
The authors are grateful to the University of Mumbai for providing financial assistance to C.D. Jadia.
Chhotu D. Jadia and M.H. Fulekar, Phytotoxicity and Remediation of Heavy Metals by Alfalfa (Medicago sativa) in Soil-vermicompost Media, Adv. in Nat. Appl. Sci., 2(3): 141-151, 2008
Adriano, D.C., 2001. Trace elements in terrestrial environments; Biochemistry, bioavailability and risks of metals. Springer-Verlag, New York.
Alloway, B.J., 1995. Soil processes and the behaviour of heavy metals. pp.11-37. In. B.J. Alloway (ed.) Heavy metals in soils. Blackie Academic and Professional, London.
American Public Health Association (APHA), Standard methods for the examination of water and waste water, 20th ed. Washington D.C., U.S.A, 1998.
Andrade, J.C.M. and C.F. Mahler, 2002. Soil Phytoremediation. In 4th International Conference on Engineering Geotechnology. Rio de Janeiro, Brazil.
Angel, J.S., N.A. Linacre, 2005. Metal phytoextraction-A survey of potential risks. International Journal of Phytoremediation. (7): 241-254.
Baligar, V.C., T.A. Campbell and R.J. Wright, 1993. Differential responses of alfalfa clones to aluminum-toxic acid soil, J. Plant Nutrition. (16): 219-233.
BIO-WISE, 2003. Contaminated Land Remediation: A Review of Biological Technology, London, DTI.
Boominathan, R. and P.M. Doran, 2003. Cadmium tolerance antioxidative defenses hyperaccumulator, Thlaspi caerulescens. Biotechnology and Bioengineering, (83): 158-167.
Chaignon, V. and P. Hinsinger, 2003. A biotest for evaluating copper bioavailability to plants in a contaminated soil. J. Environ. Qual., (32): 824-833.
Chaney, R.L., Y.M. Li, J.S. Angle, A.J.M. Baker, R.D. Reeves, S.L. Brown, F.A. Homer, M. Malik and M. Chin, 1999. Improving metal hyperaccumulators wild plants to develop commercial phytoextraction systems: Approaches and progress. In Phytoremediation of Contaminated Soil and Water, eds N Terry, GS Bahuelos, CRC Press, Boca Raton, FL
Cui, Y., Q. Wang and P. Christie, 2004. Effect of elemental Sulphur on uptake of Cadmium, Zinc and Sulphur by oilseed Rape growing in soil contaminated with Zinc and Cadmium. Communications in Soil Science and Plant Analysis, (35): 2905-2916.
Elcock, G. and J. Martens, 1995. Composting with red wiggler worms, City farmer, Canada, 1.
EPA, 1996. Phytoremediation Resource Guide U.S. Washington, DC: Environmental Protection Agency Office of Solid Waste and Emergency Response Technology.
Fargasova, A., 1994. Effect of Pb, Cd, Hg, As and Cr on germination and root growth of Sinapis alba seeds, Bull. Environ. Contam. Toxicol., (52): 452-456.
Gardea-Torresdey, J.L., K.J. Tiemann, G. Gamez, K. Dokken, I.M. Cano-Aguilera, M.W. Renner and L.R. Furenlid, 2000. Reduction and accumulation of gold (III) by Medicago sativa alfalfa biomass: X-ray Absorption Spectroscopy, pH and temperature dependence. Environ. Sci. Technol., (34): 4392-4396.
Gerard, E., G. Echevarria, T. Sterckeman and J.L. Morel, 2000. Cadmium availability to three plant species varying in cadmium accumulation pattern. J. Environ. Qual., (29): 1117-1123.
Gondek, K. and B. Filipek-Mazur, 2003. Biomass yields of shoots and roots of plants cultivated in soil amended by vermicomposts based on tannery sludge and content of heavy metals in plant issues. Soil Environ, 49(9): 402-409.
Grifferty, A. and S. Barrington, 2000. Zinc uptake by young wheat plants under two transpiration regimes. J. Environ. Qual., (29): 443-446.
Gyawali, R. and H.D. Lekhak, July 2006. Chromium tolerance of rice (Oryza sativa L.) cultivars from Kathmandu valley, Nepal. Scientific World. 4: 4.
Halim, M., P. Conte and A. Piccolo, 2003. Potential availability of heavy metals to phytoextraction from contaminated soils induced by exogenous humic substances, Chemosphere, (52): 265.
Hattenschwile, S. and P. Gaser, 2005. Soil animals after plant litter diversity effects on decomposition. PNAS. 102: 1519-1524.
Jackson, M.L., 1973. Soil chemical analysis, Prentice Hall of India, New Delhi publication.
Jonak, C., H. Nakagami and H. Hirt, 2004. Heavy metal stress. activation of distinct mitogen-activated protein kinase pathways by copper and cadmium. Plant Physiology, (136): 3276-3283.
Klassen, S.P., J.E. McLean, P.R. Grossel and R.C. Sims, 2000. Fate and behavior of lead in soils planted with metalresistant species (River birch and smallwing sedge). J.Environ. Qual., (29): 1826-1834.
Kramer, U. and A.N. Chardonnens, 2001. The use of transgenic plants in the bioremediation of soils contaminated with trace elements. Appl. Microbiol Biotechnol., (55): 661-672.
Lasat, M.M., 2002. Phytoextraction of toxic metals: A review of biological mechanisms, J. Environ. Qual., (31): 109-120.
Life Extention, 2003. Heavy Metal Toxicity. http://www.lef.org/protocols/prtcl-156.shtml
Lopez, M.L., J.R. Peralta-Videa, T. Benitez and J.L. Gardea-Torresdey, 2005. Enhancement of lead uptake by alfalfa (Medicago sativa) using EDTA and a plant growth promoter. Chemosphere, 61(4): 595-8.
Maharashtra Nature Park Societys, Dharavi, Mumbai Bulletin, (2003).
Ma, Y., N.M. Dickinson and M.H. Wong, 2003. Interactions between earthworms, trees, soil nutrition and metal mobility in amended Pb/Zn mine tailings from Guangdong, China, Soil Biol. Biochem., (35): 1369.
Mahajan, B.K., 1997. Methods in Biostatistics for medical students and research workers, 6th ed. New Delhi: Jaypee Brothers.
Nwosu, J.U., A.K. Harding and G. Linder, 1995. Cadmium and lead uptake by edible crops grown in a silt loam soil. Bull. Environ. Contam. Toxicol., (54): 570-578.
Ormrod, D.P., J.C. Hale and O.B. Allen, 1986. Joint action of particulate fall-out Nickel and rooting medium Nickel on Soybean plants. Environmental Pollution., (41): 277-291.
Paul, F.H., 2000. Earthworms. p. C77-C85. In Malolme Sumner (ed.) Hand book of soil science. CRC Press.
Peralta, J.R., J.L. Gardea-Torresdey, K.J. Tiemann, E. Gomez, S. Arteaga, E. Rascons and J.G. Parsons, 2001. Uptake and effects of five heavy metals on seed germination and growth in Alfalfa (Medicago sativa L.). Bull. Environ. Contam. Toicology, pp: 727-734.
Peralta-Videa, J.R., G. de la Rosa, J.H. Gonzalez and J.L. Gardea-Torresdey, 2004. Effects of the growth stage on the heavy metal tolerance of alfalfa plants. Advances in Environmental Research, (8): 679-685.
Peralta-Videa, J.R., J.L. Gardea-Torresdey, E. Gomez, K.J. Tiemann, J.G. Parsons and G. Carrillo, July, 2006. Effect of mixed cadmium, copper, nickel and zinc at different pHs upon alfalfa growth and heavy metal uptake. Scientific World, 4: 4.
Peng, H.Y., X.E. Yang, L.Y. Jiang and Z.L. He, 2005. Copper phytoavailability and uptake by Elsholtzia splendens from contaminated soil as acted by soil amendments. Journal of Environmental Science and Health Part A-Toxic/Hazardous Substances and Environmental Engineering, (40): 839-856.
Pivetz, B.E., 2001. Phytoremediation of contaminated soil and ground water at hazardous waste sites. United States Environmental Protection Agency, 1-35.
Putnam, D., 2001. Sustaining the soil for future generations (Alfalfa), California Alfalfa and Forage Association.http://alfalfa.ucdavis.edu and http://www.mother.com/-cafa/
Rehab, F.B., D. Prevost and R.D. Tyagi, 2002. Growth of alfalfa in sludge-amended soils and inoculated with rhizobia produced in sludge. J. Environ. Qual., (31): 1339-1348.
Roy, S., S. Labelle, P. Mehta, A. Mihoc, N. Fortin, C. Masson, R. Leblanc, G. Chateauneuf, C. Sura, C. Gallipeau, C. Olsen, S. Delisle, M. Labrecque and C.W. Greer, 2005. Phytoremediation of heavy metal and PAH-contaminated brownfield sites. Plant and soil. (272): 277-290.
Salt, D.E., M. Blaylock, N.P.B.A. Kumar, V. Dushenkov, B.D. Ensley, 1. Chet and 1. Raskin, 1995. Phytoremediation: a novel strategy for the removal of toxic metals from the environment using plants. Biotechnology, 13: 468-474.
Schmidt, U., 2003. Enhancing Phytoextraction: The effects of chemical soil manipulation on mobility, plant accumulation and leaching of heavy metals, J. Environ. Qual., (32): 1939-1954.
Shen, Z.G., X.D. Li, C.C. Wang, H.M. Chen and H. Chua, 2002. Lead phytoextraction from contaminated soil with high-biomass plant species. J. Environ. Qual., (31): 1893-1900.
Singh, A. and S. Sharma, 2003. Effect of microbial inocula on mixed solid waste composting, vermicomposting and plant response. Compost Science & Utilization. (11): 190-199.
Suthar, S.S., J. Watts, M. Sandhu, S. Rana, A. Kanwal, D. Gupta and M.S. Meena, 2005. Vermicomposting of kitchen waste by using Eisenia foetida (SAVIGNY). Asian jr. of Microbiol. Biotech. Env. Sc., (7): 541-544.
Tang, S., L. Xi, Zheng and H. Li, 2003. Response to elevated CO, of Indian Mustard and Sunflower growing on copper contaminated soil, Bull. Environ. Contam. Toxicol., (71): 988-997.
Tiemann, K.J., J.L. Gardea-Torresdey, G. Gamez and K. Dokken, 1998. Interference studies for multimetal binding by Medicago sativa (Alfalfa). Department of Chemistry and Environmental Sciences and Engineering, University of Texas. Proceedings of the 1998 Conference on Hazardous Waste Research 63.
Welke, S.E. and D. Parkinson, 2003. Effect of Aporrectodea trapezoides activity on seedling growth of Pseudotsuga menziesii, nutrient dynamics and microbial activity in different forest soils, Forest Ecol. Manage., 173, 169.
Wenger, K., S.K. Gupta, G. Furrer and R. Schulin, 2003. The role of Nitrilotriacetate in Copper uptake by Tobacco. J. Environ. Qual., (32): 1669-1676.
Xiong, Z.T., 1998. Lead uptake and effects on seed germination and plant growth in a Pb hyperaccumulator Brassica pekinensis Rupr. Bull. Environ. Contam. Toxicol., (6): 258-291.
Yang, X.E., H.Y. Peng and L.Y. Jiang, 2005. Phytoremediation of Copper from contaminated soil by Elsholtzia splendens as affected by EDTA, citric acid and compost. International Journal of Phytoremediation, (7): 69-83.
Zheljazkov, V.D. and P.R. Warman, 2004. Application of high- Cu compost to Dill and Peppermint. J. Agric. Food Chem., (52): 2615-2622.
Zhu, D., A.P. Schwab and M.K Banks, 1999. Heavy metal leaching from mine Tailings as affected by plants. J. Environ. Qual., (28): 1727-1732.
Corresponding Author: M.H. Fulekar, Environmental Biotechnology Laboratory, Department of Life Sciences, University of Mumbai, Santacruz (E), Mumbai -400 098, Mumbai, India. E.mail: firstname.lastname@example.org
Chhotu D. Jadia and M.H. Fulekar
Environmental Biotechnology Laboratory, Department of Life Sciences, University of Mumbai, Santacruz (E), Mumbai -400 098, Mumbai, India.
Table 1: Physicochemical properties of experimental Soil. ([dagger]) Soil parameters Values S.D. Clay % 25.9 [+ or -] 1.8 Silt % 21.7 [+ or -] 2.5 Sand % 50.4 [+ or -] 2.8 pH 7.2 [+ or -] 0.1 Organic matter % 0.80 [+ or -] 0.045 Nitrogen % 0.05 [+ or -] 0.02 C EC * c mol/ 100 gm soil 11.27 [+ or -] 0.76 EC ([double dagger]) d[S.sup.-1] 1.1 [+ or -] 0.1 Potassium mg/kg 22.73 [+ or -] 2.63 WHC ** % 62 [+ or -] 4.0 Moisture Content % 34 [+ or -] 1.8 Heavy metal ppm Cu 3.6 [+ or -] 0.5 Cd ND Ni ND Ph ND Zn 12 [+ or -] 1.5 ([dagger]) Values are averages of three replicates [+ or -] S.D. * Cation exchange capacity ([double dagger]) Electrical conductivity. ** Water Holding Capacity Table 2: Chemical and Nutrient Status of Vermicompost. ([dagger]) Parameters Values S.D. pH 6.8 [+ or -] 0.173 EC ([double dagger]) dS [m.sup.-1] 10.55 [+ or -] 0.01 Total C % 13.5 [+ or -] 0.7 Total N % 1.33 [+ or -] 0.015 Available P % 0.47 [+ or -] 0.09 Sodium mg /100gm 354.68 [+ or -] 9.44 Magnesium mg/100gm 832.48 [+ or -] 22.48 Iron mg/100gm 746.26 [+ or -] 23.39 Zinc mg/100gm 16.19 [+ or -] 0.55 Manganese mg/100gm 53.86 [+ or -] 2.84 Copper mg/100gm 5.16 [+ or -] 0.36 ([dagger]) Values are averages of three replicates [+ or -] S.D. ([double dagger]) Electrical conductivity. Table 3: Seed germination. root and shoot length of alfalfa (Medicago sativa). after two weeks of exposure to heavy metals. ([dagger]) Dose Germination Metal (ppm) rate (%) Root length (cm) Shoot length (cm) Cd 0 80 [+ or -] 4 4.9 [+ or -] 0.8 5.5 [+ or -] 0.6 5 77 [+ or -] 5 5.5 [+ or -] 0.8 5.3 [+ or -] 0.6 10 70 [+ or -] 4 4.5 [+ or -] 0.9 4.7 [+ or -] 0.5 20 65 [+ or -] 5 3.9 [+ or -] 0.7 3.8 [+ or -] 0.4 40 57 [+ or -] 7 3.4 [+ or -] 0.3 4.1 [+ or -] 0.5 50 49 [+ or -] 7 2.9 [+ or -] 0.4 3.6 [+ or -] 0.5 Cu 5 83 [+ or -] 7 5.1 [+ or -] 0.55 5.7 [+ or -] 0.38 10 85 [+ or -] 6 5.6 [+ or -] 0.48 6.7 [+ or -] 0.77 20 72 [+ or -] 7 6.5 [+ or -] 0.34 7.8 [+ or -] 0.89 40 60 [+ or -] 4 4.1 [+ or -] 0.54 4.7 [+ or -] 0.44 50 58 [+ or -] 6 3.8 [+ or -] 0.82 4 [+ or -] 0.79 Ni 5 79 [+ or -] 7 5.2 [+ or -] 0.52 5.7 [+ or -] 0.76 10 75 [+ or -] 4 5.4 [+ or -] 0.56 5.2 [+ or -] 0.9 20 70 [+ or -] 8 4.8 [+ or -] 0.64 5 [+ or -] 0.8 40 64 [+ or -] 5 4.5 [+ or -] 0.55 4.7 [+ or -] 0.54 50 60 [+ or -] 7 4.1 [+ or -] 0.4 4.5 [+ or -] 0.5 Ph 5 79 [+ or -] 8 5 [+ or -] 0.4 5.9 [+ or -] 0.97 10 77 [+ or -] 5 5.3 [+ or -] 0.55 5.3 [+ or -] 0.27 20 74 [+ or -] 6 4.7 [+ or -] 0.59 5 [+ or -] 0.64 40 66 [+ or -] 5 4.3 [+ or -] 0.25 4.9 [+ or -] 0.64 50 63 [+ or -] 3 4 [+ or -] 0.38 4.7 [+ or -] 0.58 Zn 5 81 [+ or -] 5 5.1 [+ or -] 0.73 5.6 [+ or -] 0.48 10 83 [+ or -] 6 5.4 [+ or -] 0.27 6.8 [+ or -] 0.82 20 88 [+ or -] 5 6.1 [+ or -] 0.28 7.2 [+ or -] 0.68 40 91 [+ or -] 5 6.8 [+ or -] 0.54 7.7 [+ or -] 0.78 50 95 [+ or -] 3 7.5 [+ or -] 0.67 8.2 [+ or -] 0.55 Table 4: Biomass of alfalfa after 10 weeks of growth in heavy metals enriched soil-vermicompost media. ([dagger]) Dose Metal (ppm) Root Dry Weight (g) Shoot Dry Weight (g) Cd 0 0.530 [+ or -] 0.051 0.789 [+ or -] 0.097 5 0.545 [+ or -] 0.035 0.802 [+ or -] 0.089 10 0.578 [+ or -] 0.039 0.862 [+ or -] 0.029 20 0.421 [+ or -] 0.070 0.605 [+ or -] 0.03 40 0.340 [+ or -] 0.035 0.478 [+ or -] 0.046 50 0.285 [+ or -] 0.027 0.361 [+ or -] 0.021 Cu 5 0.571 [+ or -] 0.029 0.816 [+ or -] 0.045 10 0.672 [+ or -] 0.02 1.05 [+ or -] 0.05 20 0.500 [+ or -] 0.029 0.74 [+ or -] 0.05 40 0.455 [+ or -] 0.027 0.621 [+ or -] 0.028 50 0.352 [+ or -] 0.017 0.487 [+ or -] 0.036 Ni 5 0.58 [+ or -] 0.012 0.802 [+ or -] 0.039 10 0.68 [+ or -] 0.029 0.892 [+ or -] 0.031 20 0.516 [+ or -] 0.008 0.77 [+ or -] 0.06 40 0.489 [+ or -] 0.032 0.675 [+ or -] 0.036 50 0.417 [+ or -] 0.043 0.562 [+ or -] 0.041 Pb 5 0.535 [+ or -] 0.033 0.795 [+ or -] 0.054 10 0.503 [+ or -] 0.015 0.776 [+ or -] 0.045 20 0.583 [+ or -] 0.032 0.805 [+ or -] 0.036 40 0.623 [+ or -] 0.028 0.835 [+ or -] 0.054 50 0.515 [+ or -] 0.026 0.700 [+ or -] 0.041 Zn 5 0.58 [+ or -] 0.019 0.862 [+ or -] 0.049 10 0.625 [+ or -] 0.035 0.987 [+ or -] 0.048 20 0.705 [+ or -] 0.014 0.95 [+ or -] 0.031 40 0.892 [+ or -] 0.051 1.17 [+ or -] 0.19 50 0.962 [+ or -] 0.047 1.32 [+ or -] 0.19 ([dagger]) Values are averages of three replicates [+ or -] S.D. Table 5: Metal concentration in roots and shoots and uptake (compared to control treatment). ([dagger]) Metal Dose (ppm) uptake Metal (ppm) Roots shoots Cd 5 0.732 [+ or -] 0.05 0.152 [+ or -] 0.014 10 0.817 [+ or -] 0.033 0.198 [+ or -] 0.014 20 2.032 [+ or -] 0.093 0.652 [+ or -] 0.031 40 3.816 [+ or -] 0.116 1.557 [+ or -] 0.056 50 5.928 [+ or -] 0.136 2.715 [+ or -] 0.075 Cu 5 1.302 [+ or -] 0.087 2.710 [+ or -] 0.17 10 1.850 [+ or -] 0.19 3.620 [+ or -] 0.022 20 2.380 [+ or -] 0.19 5.460 [+ or -] 0.25 40 3.690 [+ or -] 0.18 7.800 [+ or -] 0.2 50 5.380 [+ or -] 0.12 9.750 [+ or -] 0.24 Ni 5 1.108 [+ or -] 0.012 0.473 [+ or -] 0.012 10 1.595 [+ or -] 0.094 0.708 [+ or -] 0.007 20 3.625 [+ or -] 0.109 0.834 [+ or -] 0.015 40 5.216 [+ or -] 0.095 1.102 [+ or -] 0.093 50 5.905 [+ or -] 0.034 1.575 [+ or -] 0.074 Pb 5 0.417 [+ or -] 0.033 0.098 [+ or -] 0.019 10 0.789 [+ or -] 0.027 0.175 [+ or-] 0.023 20 1.780 [+ or -] 0.082 0.334 [+ or -] 0.028 40 2.701 [+ or -] 0.08 0.452 [+ or -] 0.026 50 3.890 [+ or -] 0.18 0.614 [+ or -] 0.078 Zn 5 1.500 [+ or -] 0.03 3.500 [+ or -] 0.05 10 2.170 [+ or -] 0.09 4.010 [+ or -] 0.17 20 2.950 [+ or -] 0.15 8.230 [+ or -] 0.08 40 5.610 [+ or -] 0.12 10.760 [+ or -] 0.15 50 7.120 [+ or -] 0.11 11.37 [+ or -] 0.17 ([dagger]) Values are averages of three replicates [+ or -] S.D.
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|Title Annotation:||Original Article|
|Author:||Jadia, Chhotu D.; Fulekar, M.H.|
|Publication:||Advances in Natural and Applied Sciences|
|Date:||Sep 1, 2008|
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