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Archive of SID
Journal of Chemical Health Risks 3(2): 53-58, 2013
ISSN:2251-6719
53
The Effects of Arbuscular Mycorrhizal Fungi on Nitrogen Concentration of
Berseem Clover in Contaminated Soil with Cadmium
H.Aram*
, A. Golchin
Soil Science Department, Zanjan University, Zanjan, Iran
)Received: 15 April 2013 Accepted: 20 May 2013)
Abstract: The effects of Arbuscular Mycorrhizal fungi on nitrogen concentration of berseem clover were
examined in contaminated soil with cadmium. Examined factors included: levels of arbuscular mycorrhizal
fungi inoculation (Glomus mosseae) (With and without inoculation), and different levels of soil contamination
by cadmium (0, 5, 10, 20, 40 and 80 mg.kg-1). The results showed that the effects of cadmium levels and
mycorrhiza fungi were significant on nitrogen concentration (P≤ 0.01). Arbuscular mycorrhizal fungi
increased nitrogen concentration in the root and aerial plant 30% and 40.3% respectively. Also cadmium in
concentration of 80 mg.kg-1
reduced nitrogen concentration in root and aerial plant 28.3% and 35%
respectively.
Keywords: Arbuscular mycorrhizal, cadmium, contaminated soil
INTRODUCTION
Soil contamination with heavy metals represents a
potential risk to the biosphere and leads to increase
concentration in the ground or surface water,
therefore metals mobility in soil have been
extensively studied in the last decade [1]. Toxic
heavy metal contaminations in soils and crop
plants have major importance due to their health
effects on humans and other animals [2]. Cadmium
is a heavy metal with a strong effect on crop
quality. Moreover, it is a very mobile element in
the environment. Plants can easily uptake
cadmium and transfer it to other organs [3].
Experiments on the effect of cadmium on contents
of macro elements in plants are scarce and
therefore the mechanism of its effect has not yet
been fully explained [4]. Contaminated soil can be
remediated by chemical, physical or biological
techniques [5]. Arbuscular mycorrhizae have been
observed to play a vital role in metal tolerance [6]
and accumulation [7]. Many workers have
reported enhancement of phosphate uptake and
growth of leguminous plants by vesicular
arbuscular mycorhizal fungi (AMF). It is well
documented that AM symbiosis can increase plant
growth and nutrient uptake, improve fruit quality
and enhance several abiotic stresses such as low
temperature stress, drought, salt stress [8]. The
effects of AM fungi on plant uptake of metals are
varied [9]. For example, some studies suggest that
high concentrations of heavy metals in soil may
significantly decrease root colonization by AM
fungi [10]. Heggo and his colleagues (1990) and
Hetrick his colleagues (1994) demonstrated that at
high soil heavy metal concentrations, arbuscular
mycorrhizal infection reduced the concentrations
of Zn, Cd and Mn in plant leaves [11, 12].
MATERIALS AND METHODS
The study in June of 2011 was performed the
Corresponding Author: H.Aram, MSc student, Soil Science Department, Zanjan University, Zanjan, Iran E-mail:
hashemaram2011@yahoo.com
www.SID.ir
Archive of SID
Journal of Chemical Health Risks 3(2): 53-58, 2013
ISSN:2251-6719
53
factorial experiment on based completely
randomize design (CRD) with three replications in
the greenhouse of Agriculture Faculty of
University of Zanjan. Examined factors include
levels of arbuscular mycorrhizal fungi inoculation
Glomus mosseae) (With and without
inoculation),and different levels of soil
contamination by cadmium (0, 5, 10, 20, 40 and 80
mg.kg-1). The soil prepared of arable land of depth
of 0-20 cm at University of Zanjan, after the
complete analysis of soil and obtains chemical and
physical properties in the laboratory, 6 kg of soil
were weight for each pot and then the soil was
contaminated. Cadmium sulfate salt used in this
experiment, for contaminate soil samples different
amounts of salts dissolved in were distilled water
and sprayed on the soil, weighed 150 grams to the
mycorrhizal fungi and mixed with the soil. After
mixing the soil with mycorrhizal fungi, the soil
was put in pots and then cultivated clover. After
the complete growth plant (70 days), Plant aerial
and roots were harvested. Data were analyzed by
SAS and MSTATC software, and obtained
variance analysis tables. Average comparison of
different treatments was conducted by Duncan
test. Charts were obtained by Excel 2010.
Table 1: Chemical and physical analysis of soil
Soil depth
cm
EC dsm-1
PH Soil texture N % P
(ppm)
K
(ppm)
Cd
(ppm)
Fe
(ppm)
Mn
(ppm)
0-20 2.3 7.27 Sandy loam o.19 21 224 1.2 0.4 1.4
RESULT AND DISCUSSION
Effect of cadmium levels on nitrogenconcentration
According to analysis of variance table 2, the
effect of cadmium levels and mycorrhiza fungi on
nitrogen concentration was significant (P≤ 0.01).
With increasing cadmium concentrations in soil,
nitrogen concentration reduced in root and aerial
plant (Figure1). 80 mg.kg-1
Cadmium
concentrations reduced nitrogen concentration in
root and aerial plant 28.3 and 35% respectively.
Table 2: Analysis of variance the traits measured
Variation Resource Degree of Freedom Nitrogen Root Nitrogen Aerial
Cadmium 5 1.567** 0.908**
Mycorrhiza 1 11.156** 6.079**
Cadmium× Mycorrhiza 5 0.176* 0.083*
Error 24 0.047 .027
Coefficient of Variation (%) - 6.56 5.37
**: significant p<0.01 *: significant p<0.05
www.SID.ir
Archive of SID
Journal of Chemical Health Risks 3(2): 53-58, 2013
ISSN:2251-6719
53
Figure 1: Effect of levels cadmium on nitrogen concentration
External mycelium of AM fungi provides a wider
exploration zone [13]. thus providing access to
greater volume of heavy metals present in the
rhizosphere. Also AM symbiosis can establish
extra radical mycelia, which disperses outside the
roots to have access to a greater quantity of water
and soil minerals for the host plants [14].
Effect of mycorrhiza fungi on nitrogen
concentration
According to analysis of variance table 2, the
effects of mycorrhiza fungi on nitrogen
concentration were significant (P≤ 0.01). 80
mg.kg-1
cadmium, reduced nitrogen concentration
in root and aerial plant by 30% and 40.3%,
respectively in compared to control
Figure 2: Effect of mycorrhiza fungi on nitrogen concentration
Zandavalli and his colleagues (2004) studied
Araucaria angustifolia inoculated with Glomus
clarum, found that the biomass and nitrogen
content of A. angustifolia forming AM increased
significantly [15]. AM fungi, as endomycorrhiza,
functions mainly to regulate nutrients (trace metals
included) assimilation and sequester noxious metal
translocation from mycorrhizal root to the shoot,
so that the associated plant can grow better [16].
Ghazala (2005) reported that nutrient uptake of
mycorrhizal plants was higher when compared
with non-mycorrhizal one [17].
REFERENCES
1. Aydinalp C., 2010. The status of some selected
heavy metals in roadside soils of Bursa province,
www.SID.ir
Archive of SID
Journal of Chemical Health Risks 3(2): 53-58, 2013
ISSN:2251-6719
58
Turkey, Environmental Engineering and
Management Journal, 9, 559-563.
2. Farmer A., Farmer A., 2000. AM Concentration
of cadmium, lead and zinc in livestock feed and
organs around a metal production center in eastern
Kazakhstan. Science of the Total Environment.
257:53_60.
3. Kabata-pendias A., pendias H., 2001. Trace
elements in soils and plants. crc press, bocaraton,
fl (3rd edition), pp 413.
4. Ciecko Z., Kalembasa S., Wyszkowski M.,
Rolka E., 2004. Effect of Soil Contamination by
Cadmium on Potassium Uptake by Plants. Polish
Journal of Environmental Studies Vol. 13, No. 3 ,
333-337.
5. Mceldowney S., Hardman D.J., Waite S., 1993.
Treatment Technologies. In McEldowney, S.,
Hardman, J., Waite, S. (Eds.), Pollution Ecology
and Biotreatment Technologies. Longman,
Singapore Publishers, Singapore.
6. Del Val C., Barea J.M., Azcon-Aguilar C.,
1999. Assessing the tolerance of heavy metals of
arbuscular mycorrhizal fungi isolated from
sewage-sludge contaminated soils. Applied Soil
Ecology 11: 261-269.
7. Jamal, A., Ayub, N., Usman, M., Khan, A.G.
2002. Arbuscular mycorrhizal fungi enhance zinc
and nickel uptake from contaminated soil by soya
bean and lentil. International. Journal of
Phytoremediation 4:205-221.
8. Miransari M., 2010. Contribution of arbuscular
mycorrhizal symbiosis to plant growth under
different types of soil stress. Plant Biology.
12:563- 569.
9. Shen H., Peter C., Li X., 2006. Uptake of zinc,
cadmium and phosphorus by arbuscular
mycorrhizal maize (Zea mays L.) from a low
available phosphorus calcareous soil spiked with
zinc and cadmium. Environmental Geochemistry
and Health. 28:111–119.
10. Gildon A., Tinker P. B., 1983. Interactions of
vesicular-arbuscular mycorrhizal infection and
heavy metals in plants. I. The effects of heavy
metals on the development of vesicular–
arbuscular mycorrhizas. New Phytologist. 95,
247–261.
11. Heggo A., Angle J. S., Chaney R. L., 1990.
Effects of vesicularar buscular mycorrhizal fungi
on heavy metal uptake by soybeans. Soil Biology
& Biochemistry. 22, 865–869.
12. Hetrick B. A. D., Wilson G. W. T., Figge D. A.
H., 1994. The influence of mycorrhizal symbiosis
and fertilizer amendments on establishment of
vegetation in heavy-metal mine spoil.
Environmental Pollution. 86, 171–179.
13. Malcova R.,Vosatka M., Gryndler M., 2003.
Effects of inoculation with Glomus intraradices on
lead uptake by Zea mays L. and Agrostis
capillaries L. Applied Soil Ecology 23:55-67.
14. Wu Q. S., Li G. H., Zou Y.N., 2011. Roles of
arbuscular mycorrhizal fungi on growth and
nutrient acquisition of peach (prunus persica l.
batsch) seedlings. The Journal of Animal & Plant
Sciences, 21(4): 746-750.
15. Zandavalli R.B., Dillenburg L.R, Souza P.V.,
2004. Growth responses of Araucaria angustifolia
(Araucariaceae) to inoculation with the
mycorrhizal fungus Glomus clarum. Applied Soil
Ecology, 25: 245–255.
16. Khan A. G., 2005. Role of soil microbes in
the rhizospheres of plants growing on trace metal
contaminated soils in phytoremediation. J Trace
Elem Med Biol 18:355–364.
17. Ghazala N., 2005. Role of symbiotic soil fungi
in controlling roadside erosion and in the
establishment of plant communities.
www.SID.ir

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The Effects of Arbuscular Mycorrhizal Fungi on Nitrogen Concentration of Berseem Clover in Contaminated Soil with Cadmium

  • 1. Archive of SID Journal of Chemical Health Risks 3(2): 53-58, 2013 ISSN:2251-6719 53 The Effects of Arbuscular Mycorrhizal Fungi on Nitrogen Concentration of Berseem Clover in Contaminated Soil with Cadmium H.Aram* , A. Golchin Soil Science Department, Zanjan University, Zanjan, Iran )Received: 15 April 2013 Accepted: 20 May 2013) Abstract: The effects of Arbuscular Mycorrhizal fungi on nitrogen concentration of berseem clover were examined in contaminated soil with cadmium. Examined factors included: levels of arbuscular mycorrhizal fungi inoculation (Glomus mosseae) (With and without inoculation), and different levels of soil contamination by cadmium (0, 5, 10, 20, 40 and 80 mg.kg-1). The results showed that the effects of cadmium levels and mycorrhiza fungi were significant on nitrogen concentration (P≤ 0.01). Arbuscular mycorrhizal fungi increased nitrogen concentration in the root and aerial plant 30% and 40.3% respectively. Also cadmium in concentration of 80 mg.kg-1 reduced nitrogen concentration in root and aerial plant 28.3% and 35% respectively. Keywords: Arbuscular mycorrhizal, cadmium, contaminated soil INTRODUCTION Soil contamination with heavy metals represents a potential risk to the biosphere and leads to increase concentration in the ground or surface water, therefore metals mobility in soil have been extensively studied in the last decade [1]. Toxic heavy metal contaminations in soils and crop plants have major importance due to their health effects on humans and other animals [2]. Cadmium is a heavy metal with a strong effect on crop quality. Moreover, it is a very mobile element in the environment. Plants can easily uptake cadmium and transfer it to other organs [3]. Experiments on the effect of cadmium on contents of macro elements in plants are scarce and therefore the mechanism of its effect has not yet been fully explained [4]. Contaminated soil can be remediated by chemical, physical or biological techniques [5]. Arbuscular mycorrhizae have been observed to play a vital role in metal tolerance [6] and accumulation [7]. Many workers have reported enhancement of phosphate uptake and growth of leguminous plants by vesicular arbuscular mycorhizal fungi (AMF). It is well documented that AM symbiosis can increase plant growth and nutrient uptake, improve fruit quality and enhance several abiotic stresses such as low temperature stress, drought, salt stress [8]. The effects of AM fungi on plant uptake of metals are varied [9]. For example, some studies suggest that high concentrations of heavy metals in soil may significantly decrease root colonization by AM fungi [10]. Heggo and his colleagues (1990) and Hetrick his colleagues (1994) demonstrated that at high soil heavy metal concentrations, arbuscular mycorrhizal infection reduced the concentrations of Zn, Cd and Mn in plant leaves [11, 12]. MATERIALS AND METHODS The study in June of 2011 was performed the Corresponding Author: H.Aram, MSc student, Soil Science Department, Zanjan University, Zanjan, Iran E-mail: hashemaram2011@yahoo.com www.SID.ir
  • 2. Archive of SID Journal of Chemical Health Risks 3(2): 53-58, 2013 ISSN:2251-6719 53 factorial experiment on based completely randomize design (CRD) with three replications in the greenhouse of Agriculture Faculty of University of Zanjan. Examined factors include levels of arbuscular mycorrhizal fungi inoculation Glomus mosseae) (With and without inoculation),and different levels of soil contamination by cadmium (0, 5, 10, 20, 40 and 80 mg.kg-1). The soil prepared of arable land of depth of 0-20 cm at University of Zanjan, after the complete analysis of soil and obtains chemical and physical properties in the laboratory, 6 kg of soil were weight for each pot and then the soil was contaminated. Cadmium sulfate salt used in this experiment, for contaminate soil samples different amounts of salts dissolved in were distilled water and sprayed on the soil, weighed 150 grams to the mycorrhizal fungi and mixed with the soil. After mixing the soil with mycorrhizal fungi, the soil was put in pots and then cultivated clover. After the complete growth plant (70 days), Plant aerial and roots were harvested. Data were analyzed by SAS and MSTATC software, and obtained variance analysis tables. Average comparison of different treatments was conducted by Duncan test. Charts were obtained by Excel 2010. Table 1: Chemical and physical analysis of soil Soil depth cm EC dsm-1 PH Soil texture N % P (ppm) K (ppm) Cd (ppm) Fe (ppm) Mn (ppm) 0-20 2.3 7.27 Sandy loam o.19 21 224 1.2 0.4 1.4 RESULT AND DISCUSSION Effect of cadmium levels on nitrogenconcentration According to analysis of variance table 2, the effect of cadmium levels and mycorrhiza fungi on nitrogen concentration was significant (P≤ 0.01). With increasing cadmium concentrations in soil, nitrogen concentration reduced in root and aerial plant (Figure1). 80 mg.kg-1 Cadmium concentrations reduced nitrogen concentration in root and aerial plant 28.3 and 35% respectively. Table 2: Analysis of variance the traits measured Variation Resource Degree of Freedom Nitrogen Root Nitrogen Aerial Cadmium 5 1.567** 0.908** Mycorrhiza 1 11.156** 6.079** Cadmium× Mycorrhiza 5 0.176* 0.083* Error 24 0.047 .027 Coefficient of Variation (%) - 6.56 5.37 **: significant p<0.01 *: significant p<0.05 www.SID.ir
  • 3. Archive of SID Journal of Chemical Health Risks 3(2): 53-58, 2013 ISSN:2251-6719 53 Figure 1: Effect of levels cadmium on nitrogen concentration External mycelium of AM fungi provides a wider exploration zone [13]. thus providing access to greater volume of heavy metals present in the rhizosphere. Also AM symbiosis can establish extra radical mycelia, which disperses outside the roots to have access to a greater quantity of water and soil minerals for the host plants [14]. Effect of mycorrhiza fungi on nitrogen concentration According to analysis of variance table 2, the effects of mycorrhiza fungi on nitrogen concentration were significant (P≤ 0.01). 80 mg.kg-1 cadmium, reduced nitrogen concentration in root and aerial plant by 30% and 40.3%, respectively in compared to control Figure 2: Effect of mycorrhiza fungi on nitrogen concentration Zandavalli and his colleagues (2004) studied Araucaria angustifolia inoculated with Glomus clarum, found that the biomass and nitrogen content of A. angustifolia forming AM increased significantly [15]. AM fungi, as endomycorrhiza, functions mainly to regulate nutrients (trace metals included) assimilation and sequester noxious metal translocation from mycorrhizal root to the shoot, so that the associated plant can grow better [16]. Ghazala (2005) reported that nutrient uptake of mycorrhizal plants was higher when compared with non-mycorrhizal one [17]. REFERENCES 1. Aydinalp C., 2010. The status of some selected heavy metals in roadside soils of Bursa province, www.SID.ir
  • 4. Archive of SID Journal of Chemical Health Risks 3(2): 53-58, 2013 ISSN:2251-6719 58 Turkey, Environmental Engineering and Management Journal, 9, 559-563. 2. Farmer A., Farmer A., 2000. AM Concentration of cadmium, lead and zinc in livestock feed and organs around a metal production center in eastern Kazakhstan. Science of the Total Environment. 257:53_60. 3. Kabata-pendias A., pendias H., 2001. Trace elements in soils and plants. crc press, bocaraton, fl (3rd edition), pp 413. 4. Ciecko Z., Kalembasa S., Wyszkowski M., Rolka E., 2004. Effect of Soil Contamination by Cadmium on Potassium Uptake by Plants. Polish Journal of Environmental Studies Vol. 13, No. 3 , 333-337. 5. Mceldowney S., Hardman D.J., Waite S., 1993. Treatment Technologies. In McEldowney, S., Hardman, J., Waite, S. (Eds.), Pollution Ecology and Biotreatment Technologies. Longman, Singapore Publishers, Singapore. 6. Del Val C., Barea J.M., Azcon-Aguilar C., 1999. Assessing the tolerance of heavy metals of arbuscular mycorrhizal fungi isolated from sewage-sludge contaminated soils. Applied Soil Ecology 11: 261-269. 7. Jamal, A., Ayub, N., Usman, M., Khan, A.G. 2002. Arbuscular mycorrhizal fungi enhance zinc and nickel uptake from contaminated soil by soya bean and lentil. International. Journal of Phytoremediation 4:205-221. 8. Miransari M., 2010. Contribution of arbuscular mycorrhizal symbiosis to plant growth under different types of soil stress. Plant Biology. 12:563- 569. 9. Shen H., Peter C., Li X., 2006. Uptake of zinc, cadmium and phosphorus by arbuscular mycorrhizal maize (Zea mays L.) from a low available phosphorus calcareous soil spiked with zinc and cadmium. Environmental Geochemistry and Health. 28:111–119. 10. Gildon A., Tinker P. B., 1983. Interactions of vesicular-arbuscular mycorrhizal infection and heavy metals in plants. I. The effects of heavy metals on the development of vesicular– arbuscular mycorrhizas. New Phytologist. 95, 247–261. 11. Heggo A., Angle J. S., Chaney R. L., 1990. Effects of vesicularar buscular mycorrhizal fungi on heavy metal uptake by soybeans. Soil Biology & Biochemistry. 22, 865–869. 12. Hetrick B. A. D., Wilson G. W. T., Figge D. A. H., 1994. The influence of mycorrhizal symbiosis and fertilizer amendments on establishment of vegetation in heavy-metal mine spoil. Environmental Pollution. 86, 171–179. 13. Malcova R.,Vosatka M., Gryndler M., 2003. Effects of inoculation with Glomus intraradices on lead uptake by Zea mays L. and Agrostis capillaries L. Applied Soil Ecology 23:55-67. 14. Wu Q. S., Li G. H., Zou Y.N., 2011. Roles of arbuscular mycorrhizal fungi on growth and nutrient acquisition of peach (prunus persica l. batsch) seedlings. The Journal of Animal & Plant Sciences, 21(4): 746-750. 15. Zandavalli R.B., Dillenburg L.R, Souza P.V., 2004. Growth responses of Araucaria angustifolia (Araucariaceae) to inoculation with the mycorrhizal fungus Glomus clarum. Applied Soil Ecology, 25: 245–255. 16. Khan A. G., 2005. Role of soil microbes in the rhizospheres of plants growing on trace metal contaminated soils in phytoremediation. J Trace Elem Med Biol 18:355–364. 17. Ghazala N., 2005. Role of symbiotic soil fungi in controlling roadside erosion and in the establishment of plant communities. www.SID.ir