View of Effect of Cadmium and Lead on Quantitative and Essential Oil Traits of Peppermint (Mentha piperita L.)

(1)

Effect of Cadmium and Lead on Quantitative and Essential Oil Traits of Peppermint ( Mentha piperita L.)

Shahram AMIRMORADI

¹*,

Parviz Rezvani MOGHADDAM

¹,

Alireza KOOCHEKI

¹,

Shahnaz DANESH

²,

Amir FOTOVAT

³

1Ferdowsi University of Mashhad, Faculty of Agriculture, Department of Agronomy, P.O. Box 91775-1163, Mashhad, Iran; [email protected] (*corresponding author), [email protected], [email protected]

2Ferdowsi University of Mashhad, Civil Engineering Department, P.O.Box 91775-1363, Mashhad, Iran; [email protected]

3Ferdowsi University of Mashhad, Faculty of Agriculture, Department of Soil Science, P.O. Box 91775-1163, Mashhad, Iran; [email protected]

Abstract

Cadmium (Cd) and lead (Pb) are particularly noteworthy metals that can pollute the air, soil and water contributing to serious environmental problems. Tests were done on concentrations of Pb and Cd; treatments tested in the experiment were as follows; Cd concentrations (10, 20, 40, 60, 80, 100 ppm) and concentrations of Pb (100, 300, 600, 900, 1200, 1500 ppm) and control. Tests were done on Mentha piperita L. in a greenhouse, arranged as a randomized complete block design with three replications. Rhizomes with uniform weight were planted in pots 30×50×35 cm. Plants were irrigated with Cd and Pb chloride after germination of all rhizomes.

Results demonstrated that with increasing concentrations of Cd and Pb there was a decrease in fresh and dry weights, main stem height, leaf area per plant, leaf number, number of nodes per main stem and essential oil of peppermint compared to the control. Fresh weights were decreased at 100 ppm of Cd and 1500 ppm of Pb, 18.16% and 24.55%, respectively compared to the control at the first harvest. At the second harvest, these decreases were 15.24% and 32.72%, respectively. At the highest concentrations of Cd and Pb, dry weight of peppermint was dropped 22.92% and 39.01% at the first harvest. For the second harvest, decreased dry weights were 25.88% and 26.77%

respectively. It seems that peppermint can tolerate waste water or soil polluted with medium range of Cd and Pb concentrations and the essential oil percentage was not affected by these concentrations.

Keywords: heavy metals, leaf area, medicinal plant

Introduction

In the last decade medicinal plants have become more widely used in medicine (Blumenthal, 1998) and industry (Lorenzi and Matos, 2002). Medicinal plants are currently important plants in ecological agriculture. Cultivation of these plants in polluted soil or soils irrigated with wastewater may contribute to the contamination of end products. Furthermore these polluted products are not safe for human consumption and may create serious health problems (Rai et al., 2004). Research has shown that some medicinal plants can be cultivated in soil contaminated with heavy metals without evidence of these hazardous elements in end products (Zhejazkov et al., 2008). Pepper- mint (Mentha piperita L.) is an aromatic plant from the family of Lamiaceae, which is a hybrid of Mentha aquatica L. and Mentha spicata L. This plant has traditionally been used in medicine (Blumenthal, 1998). Peppermint oil is rich in menthol, which is a great component in the manu- facturing of perfume and essence (Lorenzi and Matos, 2002). Peppermint cultivate in some Porivnce like Fars, Markazi, South Khorasan, North Khorasan, Kermanshah

province. Peppermint is cultivated in some parts of Iran as a medicinal plant for industrial purpose and fresh use.

Mostly Peppermint is cultivated by small holder farmers differed from year to year (100 to 1100 ha) and the cultivation area statistics is not clear. Industrialization has been the cause of much environmental pollution and one of the most significant pollutants is that of heavy metals.

Heavy metals can cause air, water and soil pollution and may create serious problems in the biosphere (Emese et al., 2009; Street et al., 2007). Heavy metals exist world- wide as their use is widespread in industry (Chen Wang and Wang, 2005; Singh et al., 2004). Irrigation of soil with waste-water polluted with heavy metals not only causes soil pollution, but may also affect food quality and security because of gradual accumulation of heavy metals (Muchuweti et al., 2006). Cd and Pb are more noteworthy than other heavy metals because they are more persistent in the environment (Pendey et al., 2007). Heavy met- als may accumulate in the food chain becoming hazardous for humans and livestock that are more sensitive than plants in terms of absorption of these elements (Liu et al., 2006). Toxic effects of heavy metals may cause damage to Received 11 August 2012; accepted 27 October 2012

(2)

and second harvests were carried out at the stage of 10 percent flowering. After every harvest, number of leaves per plant, main stem height, number of nodes per main stem, leaf area per plant and fresh weight of plants were measured. All plants were dried in shading for 72 hours and dry weights of plants were determined. Essential oil percentage was measured by clevenger with distilled water. In this method 30 grams of peppermint leaves were dried and soaked in 400 ml of distilled water and then were boiled in a round-bottom flask. After 120 min, heating was stopped and essential oil percentage was measured. (Croteau et al., 2006). Data were analyzed by MSTATC software. All means were compared with Duncan’s Multiple Range Test at 5 % level.

Results and discussion Fresh and dry weight

Results of analysis of variance indicated that vari- ous concentrations of Cd and Pb had significant impact (p≤0.01) at the first harvest (Tab. 1 and 2). Increasing doses of Cd caused a decrease of fresh weight. This decline was 18.16% at 100 ppm Cd and was 24.55% at 1500 ppm of Pb compared to the control. At the first harvest, dry weight declined by 25.88% at 100 ppm of Cd and decreased by 39.01% at the Pb concentration of 1500 ppm compared to the control (Tab. 2). Cd and Pb on fresh and dry weights of peppermint had significant impact at 5 (p≤0.05) and 1 percent (p≤0.01), respectively (Tab. 3). At the second harvest the highest doses of Cd and Pb caused decreases of fresh weight by 15.24% and 32.72% respectively compared to the control and decreases of dry weight by 22.93% and 26.77% respectively compared to the control, (Tab. 4). Another research tested the effect of PbNo₃ concentrations (0, 0.048, 0.48, 4.8 and 48 mM) on Vicia faba L. and reported that increasing Pb decreased fresh weight (Ahmed Kamel, 2008). Increasing doses of Cd (0, 2. 5, 5, 10, 20, 30, 30 mg/l, cdcl₂) caused a decline of dry weight of the aerial part of Matthiola chenopodiifolia L.

and all treatments showed significant difference compared to the control (Ghaderian and Jamali Hajiani, 2010). In- creasing Cd doses (0, 3, 6, 9, 12 mg/kg) on Vigna radiata L. decreased fresh and dry weights in all varieties, but varieties responded differently (Ghani, 2010). It was indicated that the impact of Cdcl₂ (0, 2, 6, 10 ppm) and Pbcl₂ (0, 50, 100, 500 ppm) had significant effects on dry weight of Mentha piperita L., Anethum graveolens L., Ocimum basi- licum L. (Zheljazkov et al., 2006). Incremental Cd doses (0, 0.01, 0.02, 0.05, 0.1 ppm) caused a decrease of root and shoot dry weights of Gossypium hirsutum L. (Aycicek et al., 2008). Tests were done on Thlaspi caerulescens L. treat- ed with Cd (2.5 mg/l) for 14 days. Results indicated that aerial dry weight and root dry weight decreased by 14%

and 28%, respectively (Wojcik et al., 2005). It was indi- cated that leaf dry weight of Arabidopsis halleril L. treated with 2.5 mg/l of Cd decreased by 26% compared to the human DNA, particularly in children (Baudouin, 2002).

For example toxicity from lead causes damage to the ner- vous system and consequently causes loss of intelligence and short-term memory, decreased learning ability and carcinogenic diseases (Soghian, 2009). Plants suitable for phytoremediation may be identified through investigation of germination parameters, plant growth and production under heavy metals contaminated media. It was reported that increasing amounts of certain heavy metals causes a decrease of germination and plant growth parameters in many plants (Jun et al., 2009; Marques et al., 2007; Sen- gar et al., 2008). Loss of plant biomass by increasing levels of Cd toxicity occurred because processes of chlorophyll synthesis and photosynthesis were inhibited (Padmaja, 1990). Scora and Chang (1997) reported that Mentha peperita L. planted in polluted soil contaminated with Cd at 0.12 to 6.1 ppm concentrations did not demonstrate al- tered biomass or essential oil components, but Zheljazkov and Nielsen (1996) indicated that with increasing Cd, Cu, Pb, Mn and Zn concentrations, fresh yield and essential oil yield decreased. Scavroni demonstrated that peppermint can be cultivated as a good phytoremediator in polluted soil as it was capable of developing without accumulation of these metals in its tissue (Scavroni et al., 2005). Zhel- jazkov et al. (2006) reported that with increasing con- centrations of Cd, Pb and Cu from 10 to 100 ppm, dry matter of peppermint, basil (Ocimum basilicum L.) and dill (Anethum graveolens L.) were not affected. The main goal of this study was investigation of Cd and Pb impact on fresh and dry weight, stem height, number of nodes in main stem, leaf area, number of leaf per plant and essential oil percent of peppermint.

Materials and methods

The experiment was done in the research greenhouse of the Agricultural Faculty of Ferdowsi University of Mash- had in 2011. Experimental treatments were Cd concentrations (10, 20, 40, 60, 80 and 100 ppm), Pb concentrations (300, 600, 900, 1200 and 1500 ppm) and control (Khorra- mi Vafa et al., 2012 a, b; Zheljazkov et al., 2006). The treatments were arranged basis on a randomized block design with three replications. Solutions were prepared with Cd and Pb cholride and distilled water was used as the control.

Peppermint was cultivated with uniform weight rhizomes harvested from the research farm of Ferdowsi University of Mashhad, Iran. Every rhizome had two buds and 6 rhizomes were planted in pots of dimensions 30×50×35 cm.

The soil of pots was brought from the farm of Ferdowsi University of Mashhad. Irrigation of pots with Cd and Pb solutions was done on the basis of field capacity when all rhizomes were germinated. Distilled water was used for the control. After irrigation with Cd and Pb solutions, all pots were irrigated with distilled water for subsequent ap- plications. Nitrogen, phosphorus and potassium fertilizers were applied according to results of the soil analysis. First

(3)

control (Cosio et al., 2004). Salsola kali L. was introduced as a tolerant plant Cd and it was reported that a dose of 5 mg/l of Cd caused a decrease in aerial dry weight of 31%

(Rosa et al., 2004). The effect of 5 mg/l of Cd on corn and pea affected dry weights of aerial parts by 81% and 41%, respectively (Lozano-Rodriguez et al., 1997). It seems reduction in fresh and dry weight of peppermint were due to decrease in photosynthesis and respiration (Moya et al., 1993), reducing carbohydrate metabolism (Wierzbicka, 1995) and probably chlorosis (Sanita di Toopi and Gob- brielli, 1999). Disturbance in water availability (Patra et al., 2004), inhibition of nutrient uptake (Sanita di Toppi and Gabrielli, 1999) and reduced synthesis of protein or degradation of it (Blaestrasse et al., 2003) are some of the other reasons for declining of fresh and dry weight of peppermint. Wierzbicka reported that Pb ions caused water deficit because they disrupted the water balance. (Wier- zbicka, 1995). Increasing doses of Pb (0, 10, 20, 30, 40 ppm) had significant negative effects on water availability.

High doses of Cd in plants may interfere in plant growth in different methods. Enzyme activity (Van Assche and Clijster, 1990), photosynthesis inhibition (Vassilev and Yordanov, 1997), stomal closure (Barcelo and Poschen- rieder, 1990) and inhibition of nutrients uptake are all possible effects on plant growth that may have occurred from Cd. Increasing doses of Cd (0, 10, 20, 50, 100 µm/l) caused decrease of root growth resulting in decreased nutrients and water uptake and reduced respiration (Chen et al., 2003). Protein synthesis was also affected by Cd. Pro- tein content of Cicer arietinum L. exposed to high doses of Cd, decreased by 38% percent compared to the control (Bavi et al., 2011). Reduction in protein content may have been due to reduced synthesis or degradation of protein (Blaestrasse et al., 2003). It was reported that a reduction of aerial parts of plants as a result of Cd may be because of reduced chlorophyll contents and photosynthesis type I activity (Shah et al., 2008). In some concentrations of Cd (10, 20, 40 ppm) or Pb (100, 300, 600, 900, 1200) fresh and dry weight of peppermint were not significant differences(Tab. 2) in the first and second harvest.

Some researchers reported that in hyper heavy metals accumulator plants, dry weight was increased more than control with increasing of heavy metal concentrations (Tang et al., 2009). On the basis of experiment of Tang et

al. (2009) with increment of Cd concentrations from 0 to 44 ppm dry weight of Arabis paniculata Franch increased and after 44 to 267 ppm decreased. In their research the dry weights in medium concentrations were not significant. In our study despite of declining of dry weight with increasing of Cd concentrations in medium doses, the differences between treatments in these concentrations were not significant.

Main stem height

Results demonstrated that tested treatments impacted significantly on main stem height at the first harvest (p≤0.05) (Tab. 1 and 3). Main stem height of peppermint at the highest doses of Cd and Pb decreased by 17.89%

and 3.69%, respectively compared to the control. At the second harvest this reduction was 3.05% and 3.6% from Cd and Pb, respectively. Another research reported effects of CuSO₄ and CdSO₄ (10 ^-6 and 10^-5) on Vicia faba L. to decrease main stem (Kasim, 2005). Increased Cd in the soil of 25 mg/kg caused plant height to decline in Solanum nigrum L. (Sun et al., 2008). It was reported that plant height of Anethum graveolens L. under concentrations of Cd (2, 6, 10 mg/l) and Pb (50, 100, 500 mg/l) decreased, but the height of Ocimum basilicum L. was not affected by Cd and Pb (Zheljazkov et al., 2006). A study on Cd doses (0, 1, 5, 10, 100, 500 ppm) on Lycopersicum sculen- tum Mill. indicated that a high level of Cd (100 and 500 ppm) caused a significant decrease in plant height (Singh et al., 2011). An increment of Cd concentration caused a reduction of plant height in corn especially at concentrations of 100 and 200 ppm (Mihalescu et al., 2010). In the afore-mentioned study, with an increased concentration of Cd, yellowness appeared in the aerial part of plants, especially in leaves, consequently leaves gradually dried. In two studies in hydroponic and pot cultivation on Vetiveria zi- zanioides L. using PbNo₃ doses both cultivation methods caused a decrease of root and shoot growth. This reduction was significant in hydroponic culture. Vetiveria ziza- nioides L. was introduced as a green phytoremediator and hyper-accumulator because traits of biomass, plant height and essential oil contents were not significantly affected by Pb (Rotkittikhun et al., 2010). A plant can be classed as a hyper accumulator if no reduction in plant biomass and height is recorded from cultivation in heavy metals con- Tab. 1. Analysis of variance (Mean square) of impact of Cd and Pb on fresh weight, dry matter, main stem height , leaf area per plant, number of leaf per plant, number of node in main stem, leaf essential oil in the first harvest of Mentha piperita L.

Degree of

freedom Fresh

weight Dry

weight Main

stem Leaf area Number of

leaf per plant Number of node

per main stem Leaf essential oil

Replication 2 170.459 77.98 52.88 25025.076 2046.015 16.157 0.54

Treatment 12 48.84 29.50 16.958 2768.415 148.527 1.448 0.031

Error 24 12.376** 6.425** 5.734** 822.668** 29.65** 0.459** 0.015**

Coefficient

variation(%) 5.60 8.59 7.35 8.62 6.25 5.32 5.11

*,**: Significant at 5 and 1% probability levels, respectively

(4)

Cd treatments 0, 10^-2, 10^-4, 10^-5,10^-8 m/l was reported by Siddhu and Khan (2012). Increasing Cd concentrations to above 10^-2m/l caused leaf twisting and leaf abscission that reduced leaf area. High doses of Cd in soil (100 and 500 µg/kg) caused a significant reduction in leaf area in tomato (Singh et al., 2011). This reduction in leaf area was due to reduced leaf area expansion and leaf senescence.

Other research reported a reduction in leaf area of tomato under CdNO₃ concentrations (150, 450, 900 mg/kg soil) compared to the control (Zhao et al., 2011). Increasing doses of Pb (0, 4, 6, 8 g/kg soil) and Cd (0, 150, 450, 900 g/kg soil) caused a decrease of leaf area of Phaseolus vul- garis L by 16.87%, 56.27%, 68.62% and 79.78% for Pb and 22.96%, 63.47% and 84.91% for Cd compared to the control (Bhardwaj et al., 2009). It seems that based on lit- eratures the reduction of leaf area of peppermint in our study was due to impact of Pb on hystological changes in leaves (Elzbieta and Miroslawa, 2005).

It was reported that there was a negative relation between the increment of Cd dose and specific leaf area (Barcelo et al., 1988 a). Reduction in turgor pressure of plant cells treated by Cd and reduction of cell wall elasticity caused the formation of small cells and fewer spaces between plant cells. Reduction of turgor pressure occurred from a disturbed water balance. Research reported that Cd impacted in terms of decreased water uptake, water translocation and respiration (Vassilev et al., 1997). Re- duction of water uptake in plants treated with Cd was due to reduced root growth. Hydraulic conductivity of water from roots to xylems depends on the degree of Cd stress and plant characteristics of bean, soybean and Acer pseu- doplatanus L. that decreased two to four times (Barcelo et al., 1988 b; Lamoreaux and Chaney, 1977; Marchiol et al., 1996).

The decline in leaf area of peppermint with increasing of Cd and Pb doses were probably due to reduction in cell taminated soil, these evaluations are important in terms of

defining a plant as tolerant to heavy metals (Yang et al., 2004). In these plants biomass did not reduce under the lowest doses of heavy metals to critical amounts but with an increment of heavy metals concentrations from critical and later doses, plant growth was inhibited. Inhibition of plant growth was observed as yellowness, reduction of stem height and plant biomass (Wei and Zhou, 2004). In this study the impact of Cd doses (0, 20, 40, 60, 80, 100 ppm) had no significant effect on peppermint at the first harvest (Tab. 2). Increasing concentrations of Pb from 0 to 1200 had no significant effect on peppermint at the first harvest, but with increasing concentrations of Cd from 1200 to 1500 ppm, plant height significantly decreased. Although, plant height reduced at different doses of Cd and Pb, differences between concentrations was not significant (Tab.

4). It seems increasing Cd and Pb concentrations gradually decreased growth of peppermint and decreased cell length which caused to decrease the plant height, as it was mentioned by other researchers. For instance it was reported that when heavy metals were transferred to the aerial parts of plants causing disturbance in cell metabolism and reducing plant height (Shanker et al., 2005). Reduction in growth may be due to loss of cell turgor and reduction in mitosis activity or inhibition of cell elongation. For example Cd in plant cells can influence cell walls specially the middle layer of a cell wall that causes an increasing in cell width instead of cell length (Hassan et al., 2006).

Leaf area per plant

Effects of Cd and Pb concentrations on leaf area of peppermint was significant at the first harvest (p≤0.01), but was not significant at the second harvest (Tab. 1 and 3). At the first harvest, leaf area decreased by 7.37% at 100 ppm of Cd and 22.21% at 1500 ppm Pb compared to the control (Tab. 2). Leaf area of Phaseolus mungo L. under

Tab. 2. Means of Cd and Pb effects on fresh weight(g), dry matter(g), main stem height(cm), leaf area per plant(cm²), number of leaf per plant, number of node in main stem, leaf essential oil(%) in the first harvest of Mentha piperita L.

Treatment Fresh

weight (g) Dry weight

(g) Main stem

height (cm) Leaf

area(cm²) Number of

per main stem Leaf essential oil (%)

Control 73.07 a 37.78 a 37.86 a 371.1 a 98.46 a 14.16 a 2.59 a

Cd-10 ppm 64.11 b 30.49 b 33.84 ab 368.1 a 94.49 ab 13.23 ab 2.46 ab

Cd-20 ppm 63.12 b 29.55 b 32.8 b 332.3 abcde 88.54 abcde 12.82 b 2.45 abc

Cd-40 ppm 62.45 b 29.25 b 32.46 b 338.9 abcde 86.55 bcde 12.69 b 2.43 abc

Cd-60 ppm 61.12 bc 28.62 b 31.76 b 309.6 bcde 82.58 cdef 12.41 bc 2.4 bc

Cd-80 ppm 60.46 bc 28.31 b 31.42 b 292.3 cde 80.59 def 12.28 bc 2.38 bc

Cd-100 ppm 59.80 bc 28.00 b 31.08 bc 286.5 e 78.61 ef 12.15 bc 2.38 bc

Pb-100 ppm 65.11 b 30.49 b 33.84 ab 365.9 a 94.49 ab 13.23 ab 2.35 ab

Pb-300 ppm 64.46 b 30.17 b 33.49 ab 355.0 ab 92.51 abc 13.09 ab 2.3 abc

Pb-600 ppm 63.78 b 29.87 b 33.15 b 346.5 abc 90.52 abcd 12.95 ab 2.3 abc

Pb-900 ppm 63.12 b 29.55 b 32.8 b 343.9 abcd 88.53 abcde 12.82 b 2.28 abc

Pb-1200 ppm 61.12 bc 28.62 b 31.76 b 322.2 abcde 82.58 cdef 12.41 bc 2.25 bc

Pb-1500 ppm 55.13 c 23.04 c 27.05 c 291.0 de 74.64 f 11.21 c 2.2 c

Means in treatments followed by similar letter are not significantly different at 5% probability level, using Duncan’s Multiple Range Test (DMRT)

(5)

cell walls (Barcelo et al., 1986). Vazquez (1989) reported that reduction of cell elasticity was due to decreased synthesis of cell wall components because of reduced function of Golgi apparatus.

Number of leaf per plant and number of node per main stemAt the first harvest, effects of Cd and Pb concentrations on number of leaves per plant and number of nodes per main stem (p≤0.01) were significant (Tab. 1). At the second harvest the impact of treatments on number of leaves per plant (p≤0.05) and on number of nodes per main stem (p≤0.05) was significant (Tab. 3). Number of leaves per plant decreased at 100 ppm of Cd and 1500 ppm of Pb 21.16% and 24.19% respectively compared to the control at the first harvest. The number of nodes per main stem declined at the highest doses of Cd and Pb 14.19% and 20.83%, respectively compared to the control at the first harvest (Tab. 3). Other research reported that increasing Pb doses (0, 5, 10, 15, 20, 25 µm/M) caused a decrease of leaf number in Thespesia populnea L. (Kabir et al., 2010). It was reported that incremental concentrations of Cd after 0.1 µm/M caused a reduction of leaf number in tomato.

For example 30 days after planting in a concentration of division, cell differentiation of cambium cells. Barcelo et

al. (1988 b) reported that water movement in bean was due to a reduction of vascular ray and vascular bundles caused by Cd induction and cell division, cell elongation and differentiation of cambium cells (Barcelo et al., 1988 b). These researches assumed that these events were due to hormonal disturbance but data was not shown in support of this assumption. Another reason for the reduction of water movement was due to the disturbance of vascular structures because of deposition of non-soluble phenolic compounds (Fuhrer, 1982) and lignin and sequestration of calcium oxalate (Van Balen et al., 1980). These events caused a reduction of water potential and consequently relative water content in leaves. Therefore, components of leaf water potential, treated by Cd decreased. Reduction of turgor pressure may be due to inappropriate osmotic adjustment because even this is a proper mechanism for stability of water balance in plants (Yancey et al., 1982).

It was reported that cell turgor in plant leaves treated by Cd had a lower threshold of relative water content compared to the control. The reason for this loss of water was reduced cell wall elasticity due to the decomposition of phenolic and cellulose compounds in cell walls and the re- placement of Cd with calcium in the middle lamella inside

Tab. 3. Analysis of variance (Mean square) of impact of Cd and Pb on fresh weight, dry matter, main stem height, leaf area per plant, number of leaf per plant, number of node in main stem, leaf essential oil in the first harvest of Mentha piperita L.

Degree of

freedom Fresh

weight Dry

weight Main stem

height Leaf area Number of leaf per plant Number of node

per main stem Leaf essential oil

Replication 2 121.70 17.55 83.28 5260.67 328.615 5.94 0.063

Treatment 12 28.49 8.72 27.24 640.53 41.07 1.26 0.01

Error 24 12.68* 2.69** 10.75* 366.00^ns 18.21* 0.42** 0.004**

Coefficient

variation(%) 9.58 9.58 8.79 10.75 10.05 8.81 6.28 5.04

*,**: Significant at 5 and 1% probability levels, respectively

Tab. 4. Means of cadmium and lead effects on fresh weight(g), dry matter(g), main stem height(cm), leaf area per plant(cm²), number of leaf per plant, number of node in main stem, leaf essential oil(%) in the first harvest of Mentha piperita L.

Treatment Fresh

weight (g) Dry weight

(g) Main stem

height (cm) Leaf area

(cm²) Number of

per main stem Leaf essential oil (%)

Control 43.02 a 23.64 a 39.78 a 231.3 a 57.33 a 12.18 a 1.27 ab

Cd-10 ppm 39.1 a 19.93 b 31.76 b 194.1 b 49.75 abc 10.53 b 1.29 a

Cd-20 ppm 37.83 a 19.11 b 30.30 b 190.4 b 48.83 bc 10.29 b 1.20 ab

Cd-40 ppm 37.55 a 18.59 b 29.74 b 199.2 ab 51.01 ab 10.15 b 1.21 ab

Cd-60 ppm 36.37 a 18.18 b 28.88 b 181.7 b 46.63 bc 9.96 b 1.18 ab

Cd-80 ppm 36.3 a 18.01 b 28.60 b 177.4 b 45.6 bc 9.88 b 1.16 b

Cd-100 ppm 36.46 a 18.22 b 28.5 b 183.0 b 46.96 bc 9.81 b 1.18 ab

Pb-100 ppm 38.65 a 19.04 b 31.00 b 199.6 ab 51.23 ab 10.66 b 1.25 ab

Pb-300 ppm 38.62 a 18.72 b 30.67 b 191.8 b 49.06 bc 10.53 b 1.22 ab

Pb-600 ppm 37.68 a 18.00 b 30.78 b 186.7 b 48.10 bc 10.38 b 1.24 ab

Pb-900 ppm 36.12 a 17.24 b 30.10 b 186.6 b 47.82 bc 10.41 b 1.23 ab

Pb-1200 ppm 36.72 a 16.95 b 28.96 b 179.2 b 45.98 bc 9.74 b 1.22 ab

Pb-1500 ppm 28.94 b 17.31 b 27.75 b 174.1 b 41.47 c 9.63 b 1.06 c

Means in treatments followed by similar letter are not significantly different at 5% probability level, using Duncan’s Multiple Range Test (DMRT)

(6)

mint decreased in plants cultivated in compost contaminated with heavy metals (Topalov and Zheljazkov, 1991).

It was demonstrated that terpenoids produced in epidermal glands in peppermint leaves consumed the carbon provided by photosynthesis (Croteau and Johnson, 1984).

Synthesis of peppermint essential oil in epidermal glands depends on providing the photosynthetic carbon and disturbance in carbon nutrition that can cause a reduction of essential oils (Srivastava et al., 1994). As it was mentioned in literature, it seems synthesis of essential oil of peppermint affected by high doses of Cd and Pb concentrations due to disturbing on carbon translocations and toxic effects of these heavy metals and consequently essential oil percent was reduced.

Conclusion

Increasing concentrations of Cd and Pb decreased fresh and dry weights of peppermint at the first and second harvest compared to the control. Main stem height reduced at the first harvest more than the second harvest. Impact of treatments on leaf area per plant was significant at the first harvest, but at the second harvest it was not significant. Effect of Cd and Pb concentrations on essential oil percentage was significant and increasing doses of Cd and Pb reduced essential oil percentages. Although fresh and dry weights and essential oil percentages decreased with increasing concentrations of Cd and Pb, means comparison indicated that differences between treatments were not significant. It seems that peppermint can be cultivated in conditions of polluted soil or wastewater polluted with Cd and Pb.

Acknowledgment

The authors acknowledge the financial support of the project by Ferdowsi University of Mashhad. We thank Mr.

Nejati for his providing valuable help during experiment.

References

Abdo FA, Nassar DMA, Gomaa EF, and Nassar RMA (2012).

Minimizing the harmful effects of cadmium on vegetative growth, leaf anatomy, yield and physiological characteristics of soybean plant [Glycine max (L.) Merrill] by foliar spray with active yeast extract or with garlic cloves extract. Re- search J of Agric and Biol Sci 8(1):24-35.

Ahmad Kamel H (2008). Lead accumulation and its effect on photosynthesis and free amino acids in Vicia faba grown hy- droponically. Aust J of Basic and App Sci 2(3):438-446.

Aycicek M, Ince M, Yaman M (2008). Effects of cadmium on the germination, early seedling growth and metal content of cotton (Gossypium hirsutum L.). Int J of Sci and Tech 3(1):1-11.

Azmat R, Haider S, Hajra N, Farha A (2009). A viable alterna- tive mechanism in adapting the plants to heavy metal envi- 10 µm/M leaf number reduced by 31.5% compared to the

control (Jing et al., 2005). It was reported that with an increment of Cd doses (0, 10^-10, 10^-8, 10^-5, 10^-2 m) leaf number and leaf area of bean decreased (Siddhu and Khan, 2012). It seems absorption and translocations of Cd and Pb in aerial parts of a plant can disturb the cell metabolism in the stem and that will decrease plant height and number of nodes per plant (Shanker et al., 2005). Reductions in plant growth may be due to loss of cell turgor and mitosis activity or cell expansion and elongation. These Cd can inhibit the elongation of plant cells by means of re- placement Cd instead of Ca in cell walls that increases cell width instead of cell length (Hassan et al., 2006). These events may affect the nodes of a stem. It was reported that an incremental dose of Cd reduced plant height, number of leaves and dry weight of tomato (El-Gamal and Ham- mad, 2003). The reason for this may be the reduction of water uptake, reduction of synthesis of photosynthetic pigments, carbohydrates and soluble sugars. Increment of Cd doses reduced growth and leaf number in soybean, and the maximum reduction of leaf number was 44.4% at 200 ppm of Cd (Abdo et al., 2012). Fouda and Arafa (2002) also reported that high doses of Cd reduced plant height, leaf number and leaf area of soybean. An increment of Pb caused water stress and consequently reduced the leaf area, photosynthesis, dry weight and plant height and number of nodes in soybean (Azmat et al., 2009).

Essential oil percentage

Impact of Cd and Pb concentrations on leaf essential oil of peppermint was significant (p≤0.01) at the first and second harvests (Tab. 1 and 3). At the first harvest, essential oil percentage was decreased by 8.10% and 15.05% at the 100 ppm of Cd and 1500 ppm, respectively compared to the control. This reduction was 7.08% and 16.53% at the second harvest compared to the control (Tab. 2 and 4).

It was reported that the impact of Cd concentrations (2, 6, 10 mg/l) and Pb concentrations (50, 100, 500 mg/l) on essential oil of peppermint was not significant but decreased essential oil percentages of dill and basil (Zheljazkov et al., 2006). The impact of chromium on hypericin content in Hypericum perforatum L. was not significant (Tirillini et al., 2006). Using the compost consists of Cu (311 mg/kg), Pb (223 mg/kg), Mo (17 mg/kg) and Zn (767 mg/kg) decreased essential oil content of basil, but the essential oil was free of heavy metals (Zheljazkov and Philip, 2003). It was reported that leaf essential oil content of Lavandula vera D. C. was not affected by heavy metals (Zheljazkov and Nielsen, 1993). Essential oil of peppermint extracted from leaves and stems may depend on dry matter, which is produced by leaves and stems. More essential oil yield depends on more dry matter of the aerial parts of plants (Czepak, 1998). Although it was indicated that there was no difference between essential oil yields of peppermint cultivated in polluted soil to heavy metals and the control (Scora and Chang, 1997). Essential oil yield of pepper-

(7)

bioaccumulation of toxic metals in vegetables. Community.

Soil Sci. Plant Anal 40:285-293.

Fouda RA, Arafa AA (2002). Alleviation of cadmium toxicity on soybean, Glycine max (L.) Merr. by inoculation with bra- dyrhizobium and vesicular-arbuscular mycorrhizae or kine- tin. J Agric Sci Mansoura Univ 27(11):7385-7403.

Fuhrer J (1982). Ethylene biosynthesis and cadmium toxicity in leaf tissue of beans (Phaseolus vulgaris L.). Plant Physiol 70:162-167.

Ghaderian SM, Jamali Hajiani N (2010). Tolerance, uptake and accumulation of cadmium in Matthiola chenopodiifolia Fisch and C. A. Mey (Brassicaceae). J of Plant Biol 6:87-98.

Ghani A (2010). Effect of cadmium toxicity on the growth and yield components of mungbean [Vigna radiata (L.) Wilc- zek]. World Appl Sci (Special Issue of Biotech and Genetic Engin) 8:26-29.

Hassan MJ, Zhu Z, Ahmad B, Mahmood Q (2006). Influence of cadmium toxicity on rice genotypes as affected by zinc, sulfur and nitrogen fertilizers. Casp J Environ Sci 4(1):1-8.

Jing D, Fei-bo WU, Guo-ping Zh (2005). Effect of cadmium on growth and photosynthesis of tomato seedlings. J of Zheji- ang Univ Sci 6(10):974-980.

Jun R, Ling T, Guanghua Z (2009). Effects of chromium on seed gemination, root elongation and coleoptile growth in six pulses. Int J Environ Sci Tech 6:571-578.

Kabir M, Iqbal MZ, Shafiq M, Farooqi ZR (2010). Effects of lead on seedling growth of Thespesia populnea L. Plant Soil Environ 56 (4):194-199.

Kasim WA (2005). The correlation between physiological and structural alterations induced by copper and cadmium stress in broad beans (Vicia faba L.). Egypt J of Biol 7:20-32.

Lamoreaux R, Chaney W (1977). Growth and water movement in silver maple seedlings affected by cadmium. J Environ Qual 6(2):201-204.

Khorrami Vafa M, Shokri K, Sayyadian K, Rejali F (2012 a).

The Combined Effects of Sulfur, Thiobacilli and Mycorrizal Fungi on Lead Uptake by Mentha × Piperita). American J Sci Res pp. 84-91.

Khorrami Vafa M, Shokri K, Sayyadian K, Rejali F (2012 b).

Contribution of microbial associations to the cadmium uptake by peppermint (Mentha piperita). Ann of Biol Res 3(5):2325-2329.

Lorenzi H, Matos FJA (2002). Plantas medicinais no Brasil:

nativas e exóticas cultivadas. Nova Odessa: Instituto Plan- tarum, 544 p.

Lozano-Rodriguez E, Hernandez LE, Bonay P, Carpena-Ruiz RO (1997). Distribution of cadmium in shoot and root tis- sues of maize and pea plants: physiological disturbances. J Exp Bot 48(306):123-128.

Liu W-X, Li H-H, Li S-R, Wang Y-W (2006). Heavy metal accumulation of edible vegetables cultivated in agricultural soil in the suburb of Zhengzhou city, People’s Republic of China. Bullt of Environ Cont Toxic 76:163-170.

ronment. Pak J of Bot 41(6):2729-2738.

Barcelo J, Pochenrieder Ch, Andreu I (1986). Cadmium-induced decrease of water stress resistance in bush bean plants (Phaseolus vulgaris L. cv. ‘Contender’). I. Effects of cd on water potential, relative water content and cell wall elasticity. J of Plant Physiol 125:17-25.

Barcelo J, Poschenrieder C (1990). Plant water relations as affected by heavy metal stress: a review. J of Plant Nut 13:1- 37.

Barcelo J, Vazquez M, Poschenrieder Ch (1988 a). Cadmium- indused structural and ultrastuctural changes in the vascural system of bush bean stems. Botanica Acta 101:254-261.

Baudouin C, Charveron M, Tarrouse R, Gall Y (2002). En- vironmental pollutants and skin cancer. Cell Biol Toxic 18:341-348.

Bavi Kh, Kholdebarin B, Moradshahi A (2011). Effect of cadmium on growth, protein content and peroxidase activity in pea plants. Pak J Bot 43(3):1467-1470.

Bhardwaj P, Ashish K, Prasadi P (2009). Effect of enhanced lead and cadmium in soil on physiological and biochemical attri- butes of Phaseolus vulgaris L. Nature and Sci 7(8).

Blaestrasse KB, Benavides MP, Gallego SM, Tomaro ML (2003).

Effect of cadmium stress on nitrogen metabolism in nodules and roots of soybean plants. Funct Plant Biol 30: 57-64.

Blumenthal M (1998). The complete german commission monographs: therapeutic guide to herbal medicines. Austin:

American Botanical Council.

Chen YX, He YF, Luo YM, Yu YL, Lin Q, Wong MH (2003).

Physiological mechanism of plant roots exposed to cadmium. Chemos 50:789-793.

Chen Y, Wang C, Wang Z (2005). Residues and source identifi- cation of persistent organic pollutants in farmland soils irrigated by effluents from biological treatment plants. Environ Int 31:778-783.

Cosio C, Martinoia E, Keller C (2004). Hyperaccumulation of cadmium and zinc in Thlaspi caerulescens and Arabidopsis halleri at the leaf cellular level. Plant Physiol 134:716-725.

Croteau R, Johnson MA (1984). Biosynthesis of terpenoids in glandular trichomes. Chem of Plant Trichomes, 133-185 p.

Croteau R, Burbott AJ, Lommis WD (2006). Biosynthesis of mono and sesquiterpenes in peppermint. Phytochem 71:2937-2948.

Czepak MP (1998). Produção de óleo bruto e mentol cristal- izável em oito freqüências de colheita da menta (Menta ar- vensis L.). Sci Botucatu, 53-80 p.

El-Gamal SM, Hammad SAR (2003). Counteracting the del- eterious effects of lead and cadmium on tomato plants by using yeast, garlic and eucalyptus extracts. Minufiya J Agri Res 28(3):737-755.

Elzbieta WC, Chwil M (2005). Lead-induced histological and ultra structural changes in the leaves of soyben (Glycine max (L) Mee.). Soil Sci Plant Nut 51:203-212.

Emese S, Rita A, Katalin G, Gabriella MG (2009). Change of

(8)

(2008). Effect of lead on seed germination, seedling growth, chlorophyll content and nitrate reductase activity in mung bean (Vigna radiate L.). Res J of Phytochem 2:61-68.

Shah FR, Ahmad N, Masood KR, Zahid DM (2008). The influence of cadmium and chromium on the biomass production of shisham (Dalbergia sissoo ROXB.) seedlings. Pak J of Bot 40(4):1341-1348.

Shanker AK, Cervantes C, Loza-Tavera H, Avudainayagam S (2005). Chromium toxicity in plants. Environ Int 31:63- 68.

Siddhu G, Ali khan MA (2012). Effects of cadmium on growth and metabolism of Phaseolus mungo. J of Environ Biol 33:173-179.

Singh S, Singh A, Bahadur R (2011). Effect of cadmium on germination and seedling growth of tomato (Lycopersicum esculentum Mill). Plant Arch 11(2):859-862.

Singh KP, Mohan D, Sinha S, Dalwani R (2004). Impact assess- ment of treated/untreated wastewater toxicants discharged by sewage treatment plants on health, agricultural, and environmental quality in the wastewater disposal area. Chemos 55:227-255.

Soghian S, Sinert R (2009). Toxicity, heavy metals. http://

emedicine.medscape.com/article/8149 60-Overview.

Srivastava NK, Luthra R (1994). Relationship between photosynthetic carbon metabolism and essential oil biogenesis in peppermint under Mn stress. J Exp Botany 45:1127-1132.

Sun Y, Zhou Q, Diao Ch (2008). Effects of cadmium and arsenic on growth and metal accumulation of Cd-hyperaccumulator Solanum nigrum L. Bioresource Techn 99:1103-1110.

Street RA, Kulkarni MG, Stirk WA, Southway C, Staden J (2007). Toxicity of metal elements on germination and seedling growth of widely used medicinal plants belonging to Hyacinthaceae. Bull Environ Cont Toxic 79:371-376.

Tirillini B, Ricci A, Pintore G, Chessa M, Sighinolfi S (2006).

Induction of hypericins in hypericum perforatum in response to chromium. Fitoterapia 77:164-70.

Topalov V, Zhelyazkov V (1991). Effect of harvesting on the yield of fresh material, essential oil, and planting material from Mentha piperita L. and Mentha arvensis L. Herba.

Hung 50:60-67.

Van Assche F, Clijsters H (1990). Effects of heavy metals on enzyme activity in plants. Plant Cell Environ 13:195-206.

Van Balen E, Geijn VD, Desmet G (1980). Autoradiographic evidence for the incorporation of cadmium into calcium oxalate crystals. Z Pflanzenphysiol 97:123-133.

Vassilev A, Yordanov I, Tesonev T (1997). Effects of Cd²⁺ on the physiological state and photosynthetic activity of young barley plants. Photosynthetica 34(2):293-302.

Vassilev A, Yordanov I (1997). Reductive analysis of factors lim- iting growth of cadmium-treated plants: A Rev: Bulg J Plant Physiol 23(3-4):114-133.

Vazquez M, Poschenrieder Ch, Barcelo J (1989). Pulvinus struc- ture and leaf abscission in cadmium-treated bean plants Marchiol L, Leita L, Martin M, Peterssotti A, Zerbi G (1996).

Physiological responses of two soybean cultivars to cadmium. J Environ Qual 25:562-566.

Marques PGC, Rangel OSS, Castro ML (2007). Effect of arsenic, lead and znic on seed germination and plant growth in black nightshade (Solanum nigrum L.) vs. clover (Trifolium incarnatum L.). Fresenius Eviron Bullt 16:896-903.

Mihalescu LA, Mare-Rosca OE, Marian M, Bildar CF (2010).

Research on the growth intensity of the Zea mays L. plant- lets aerial parts under cadmium treatment. Analele Universi- tatii din Oradea, Fascicula Biologie, 147-151 p.

Moya JL, Ros R, Picazo I (1993). Influence of cadmium and nickel on growth, net photosynthesis and carbohydrate distribution in rice plants. Photosynt Res 36:75-80.

Muchuweti M, Birkett J W, Chinyanga E, Zvauya R, Scrimshaw M D, Lester JN (2006). Heavy metal content of vegetables irrigated with mixture of wastewater and sewage sludge in Zimbabwe: implications for human health. Agri, Ecos and Environ 112:41-48.

Padmaja K, Parsad DK, Parsad AR (1990). Inhibition of chlorophyll synthesis in Phaseolus vulgaris L. seedlings by cadmium acetate. Photosynthetica 24:399-404.

Pendey SK (2007) Gupta and A.K. Mukharjee: Impact of cadmium and lead on Catharanthus roseus- A phytoremediation study. J Environ Biol 28:655-662.

Patra M, Bhowmik N, Bandopadhyay B, Sharma A (2004).

Comparison of mercury, lead and arsenic with respect to genotoxic effects on plant systems and the development of genetic tolerance. Environ Exp Bot 52:199-223.

Rai V, Vaypayee P, Singh SN, Mehrotra S (2004) Effect of chromium accumulation on photosynthetic pigments, oxidative stress defense system, nitrate reduction, proline level and eugenol content of Ocimum tenuiflorum. Plant Sci 167:1159-1164.

Rosa G, Peralta-Videa JR, Montes M, Parsons JG, Cano-Agu- ilera I, Gardea-Torresdey JL (2004). Cadmium uptake and translocation in tumbleweed (Salsola kali), a potential Cd- hyperaccumulator desert plant species: ICP/OES and XAS studies. Chemos 55:1159-1168.

Rotkittikhun P, Kruatrachue M, Pokethitiyook P, Baker AJM (2010). Tolerance and accumulation of lead in Vetiveria zi- zanioides and its effect on oil production. J of Environ Biol 31:329-334.

Sanita di Toppi L, Gabbrielli R (1999). Response to cadmium in higher plants. Environ Exp Bot 41:105-130.

Scavroni J, Sivia Fernandes Boaro C, Ortiz Mayo Marques M, Cesar Ferreira L (2005). Yield and composition of the essential oil of Mentha piperita L. (Lamiaceae) grown with biosolid. Braz J Plant Physiol 17(4):345-352.

Scora RW, Chang AC (1997). Essential oil quality and heavy metal concentrations of peppermint grown on a municipal sludge-amended soil. J of Environ Qual 26(4):975-979.

Sengar RS, Gautam M, Garg SK, Chaudhary R, Sengar K

(9)

Zhao S, Ye X, Zheng J (2011). Lead-induced changes in plant morphology, cell ultrastructure, growth and yields of toma- to. Afric J of Biot 10(50):10116-10124.

Zheljazkov VD, Craker LE, Xing B (2006). Effects of Cd, Pb, and Cu on growth and essential oil contents in dill, peppermint, and basil Environ and Exp Bot 58:9-16.

Zheljazkov VD, Nielsen NE (1993). Studies on the effect of heavy metals (Cd, Pb, Cu, Mn, Zn and Fe) upon the growth, productivity and quality of lavander (Lavandula vera D. C.) Production. A paper presented at the 24^th international sym- posium on essential oils. Berlin. J Essential Oil Res.

Zheljazkov VD, Nielson NE (1996). Effect of heavy metals on peppermint and cornmint. Plant Soil 178:59-66.

Zheljazkov VD, Philip R (2003). Source-separated municipal solid waste compost application to swiss chard and basil.

Heavy metals in the environment. technical report.

(Phaseolus vulgaris L.). Can J Bot 67:2756-2764.

Wei SH, Zhou QX (2004). Discussion on basic principles and strengthening measures for phytoremediation of soils contaminated by heavy metals. Chin J of Ecol 23:65-72 (in Chi- nese).

Wierzbicka M (1995). How lead loses its toxicity to plant. Act Soc Bot Pol 64:81-90.

Wojcik M, Vangronsveld J, Tukiendorf A (2005) Cadmium tolerance in Thlaspi caerulescens: Growth parameters, metal accumulation and phytochelatin synthesis in response to cadmium. Environ and Exp Bot 53:151-161.

Yancey P, Clark M, Hand S, Bowlus R, Somero G (1982). Liv- ing with water stress: evolution of osmolyte systems. Sci 217:1212-1222.

Yang XE, Long XX, Ye HB, He ZL, Calvert DV, Stoffella PJ (2004). Cadmium tolerance and hyperaccumulation in a new zn hyperaccumulating plant species (Sedum alfrdii Hance). Plant and Soil 259:181-189.