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Heavy metal accumulation and relation with soil contamination in Rubus ulmifolius growing in Esteiro de Estarreja, Portugal

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HEAVY METAL ACCUMULATION AND

RELATION WITH SOIL

CONTAMINATION IN RUBUS

ULMIFOLIUS

GROWING IN ESTEIRO

DE ESTARREJA, PORTUGAL

Ana P. G. C. Marques, Helena Moreira, António O. S. S. Rangel, Paula M. L. Castro

(2)

Enlargement of the data concerning plant species

valuable for phytoremediation

Investigation of Investigation of the potential for the potential for phytoremediation phytoremediation

Site-specific constraints can render the known- to-date species used for

phytoremediation inadequate phytoremediation phytoremediation of plants of plants indigenous to a indigenous to a historically HM historically HM contaminated contaminated site: Esteiro de site: Esteiro de Estarreja Estarreja

(3)

Discharge of solid residues in the surrounding area, with consequent contamination of the aquiferous;

High permeability of the soils

Conducting of the wastewaters of the factories into the stream nearby (“Esteiro de Estarreja”).

Levels of metals in the sediments of the stream remain above the limits established by EC Directive 86/278/EC

The contamination occurs mainly in the top 20 cm layer of the soil and near the former exit of wastewaters

(4)

General

view of the

view of the

stream

(5)

Z n

8 9 8 .9 (12 5 -3 6 2 0 )

P b

8 3 5 .4 (16- 3 7 4 0 )

A s

1 495 (4 5- 5620)

Fe

16.8

Cr

2 6. 0

Total metal (mg/ kg soil)

Cr

2 6. 0

N i

3 7. 3

Cu

0

(6)



Survey of the main

colonising species of

Esteiro de Estarreja

-Phragmites australis,

Rubus

ulmifolius

and

Solanum

nigrum

- and determination

of their Zn accumulation

(7)

Accumulation of Zn in the whole plant samples collected near the former wastewaters exit AMF colonisation of the roots of the plants collected near the former wastewaters exit

Pb Zn As S. nigrum 2,6 1130 5,4

R. ulmifolius 6,0 714 31,2

(8)

Solanum nigrum grown in Zn contaminated

matrices : effect of AMF on Zn accumulation

Survey of metal accumulation in plant species indigenous to Esteiro de Estarreja Zn, As, Pb and Ni accumulation in Rubus. ulmifolius EDDS and

EDTA-enhanced Zn accumulation by

Solanum nigrum

inoculated with AMF grown in contaminated soil ulmifolius growing in Esteiro de Estarreja Application of manure and compost to contaminated soils and its effect on Zn accumulation by

Solanum nigrum

(9)

Solanum nigrum grown in Zn contaminated

matrices : effect of AMF on Zn accumulation

Survey of metal accumulation in plant species indigenous to Esteiro de Estarreja

(10)

1450 mg Zn kg-1 (L)

Accumulation studies showed that increasing concentrations of

available zinc in the matrix induced increased metal accumulation in the tissues of this species the plant was able to grow with levels of available Zn

of 100 mg/kg dry soil

Main results

Main results

Enhanced accumulation levels were observed in all the sections of S.

nigrum plants inoculated with G. claroideum (83%) and G. intraradices (49%)

3240 mg Zn kg-1 (L)

(11)

Solanum nigrum grown in Zn contaminated

matrices : effect of AMF on Zn accumulation

Survey of metal accumulation in plant species indigenous to Esteiro de Estarreja

EDDS and EDTA-enhanced Zn

accumulation by

Solanum nigrum

inoculated with AMF grown in

(12)

When EDTA or EDDS were applied to the soil, AMF colonisation decreased and there was no effect of the selected AMF on Zn

accumulation by the plant

The Zn concentrations in water-extracts of the soils collected at the time of harvest were increased by the addition of EDTA or EDDS by up to 4.0- and

3.1-folds, respectively.  Higher metal mobility !!

Main results

Main results

A chelate-enhanced phytoextraction strategy using S. nigrum and EDDS or EDTA still appears as time consuming and risky concerning

contamination dispersion

The accumulation of Zn in all plant tissues generally increased with the addition of both chelating agents application of EDTA would reduce the number of crops to achieve soil clean-up from 23 to 13

(13)

Solanum nigrum grown in Zn contaminated

matrices : effect of AMF on Zn accumulation

Survey of metal accumulation in plant species indigenous to Esteiro de Estarreja

Application of manure and compost to

contaminated soils and its effect on Zn accumulation by

Solanum nigrum

(14)

The establishment of S. nigrum in combination with OM

amendments provided a reduction in the quantity of Zn leached of ca. 70 to 80%  reduction of metal dissemination

When manure or compost were applied to the soil, AMF

colonisation decreased and there was no effect of the selected AMF on Zn accumulation by the plant

Main results

Main results

The addition of manure resulted in a reduction in Zn accumulation

Phytostabilisation employing

Phytostabilisation employing S. nigrum

S. nigrum

and manure appears thus

and manure appears thus

as a realistic scenario for the remediation of Zn contaminated soils

as a realistic scenario for the remediation of Zn contaminated soils

The addition of manure resulted in a reduction in Zn accumulation in S. nigrum of up to 80% (reduction promoted by compost addition

(15)

Survey of metal accumulation in plant species indigenous to Esteiro de Estarreja Zn, As, Pb and Ni accumulation in Rubus. ulmifolius ulmifolius growing in Esteiro de Estarreja

(16)

AMF colonisation of the roots of the plant samples collected along the banks of the stream

Accumulation of metals in the roots, stems and leaves of the plant

samples collected along the banks of the stream (4 spots separated 20 m from each other)

stream stream

Levels of metals in soils

collected along the banks of the stream (4 spots

separated 20 m from each other) R1 R2 R3 R4 20 m 20 m 20 m 20 m right bank stream wastewaters conduct R1 R1 R2R2 R3R3 R4R4 20 m 20 m 20 m 20 m20 m 20 m20 m right bank stream wastewaters conduct

(17)

Collection site pH Water content (%) Organic content (%) N (mg kg-1) P (mg kg-1) R1 7.13 ± 0.4 1.46 ± 0.09 10.1 ± 0.2 3513 ± 4 201 ± 8 R2 6.49 ± 0.1 1.4 ± 0.1 8.4 ± 0.3 1596 ± 10 282 ± 4

Results: Soil caractheristics

Results: Soil caractheristics

R2 6.49 ± 0.1 1.4 ± 0.1 8.4 ± 0.3 1596 ± 10 282 ± 4 R3 6.33± 0.2 1.6 ± 0.1 7.9 ± 0.3 3359 ± 5 255 ± 8 R4 7.14 ± 0.1 1.60 ± 0.09 9.5 ± 0.2 1118 ± 13 44 ± 4

(18)

Collection site

Metal (mg kg-1dry soil)

As Pb Ni Zn Total EDTA extract Total EDTA extract Total EDTA extract Total EDTA extract R1 3078 ± 117 43 ± 2 1400 ± 9 204 ± 5 96 ± 5 2.23 ± 0.05 957 ± 74 87 ± 2 R2 952 ± 13 26 ± 3 371 ± 1 67 ± 10 135 ± 10 9 ± 1 715 ± 47 71 ± 2 R3 1180 ± 24 8.7 ± 02 611 ± 7 77 ± 3 63 ± 2 2.01 ± 0.05 853 ± 13 42 ± 2 R4 1126 ± 27 20 ± 3 540 ± 9 83 ± 9 105 ± 3 3.7 ± 0.4 713 ± 55 35 ± 2

Results: Soil total and available metal levels

Results: Soil total and available metal levels

Total metal levels higher than those

proposed as normal in soils 2 to 100 mg Ni kg-1 2 to 300 mg Pb kg-1 0.1 to 40 mg As kg-1 70 a 400 mg Zn kg-1

Levels of EDTA extractable Pb, As, Ni and Zn representing up to 13, 0.7, 2.4 and 10 % of the total metal contents

(19)

100 200 300 400 500 600 Z n ( m g k g -1 d ry w e ig h t) root stem leaves

Results: Zn accumulation by

Results: Zn accumulation by Rubus ulmifolius

Rubus ulmifolius

0 100 R1 R3 R5 R7 Sampling locations Z n ( m g k g

Zn in the roots generally above the normal levels (10 to 100 mg kg-1 )

(20)

400 600 800 1000 1200 1400 1600 1800 A s ( m g k g -1 d ry w e ig h t) roots stems leaves

Results: As accumulation by

Results: As accumulation by Rubus ulmifolius

Rubus ulmifolius

0 200

R1 R2 R3 R4

Sampling locations

As in the roots generally above the normal levels (5 mg kg-1 )

(21)

400 600 800 1000 1200 1400 P b ( m g k g -1 d ry w e ig h t) roots stems leaves

Results: Pb accumulation by

Results: Pb accumulation by Rubus ulmifolius

Rubus ulmifolius

0 200

R1 R2 R3 R4

Sampling locations

Pb in the roots generally above the normal levels (0.1 to 5 mg kg-1 )

(22)

20 40 60 80 100 120 140 160 N i (m g k g -1 d ry w e ig h t)

Results: Ni accumulation by

Results: Ni accumulation by Rubus ulmifolius

Rubus ulmifolius

0 20

R1 R2 R3 R4

Sam pling locations

Ni in the roots generally above the normal levels (1 to 10 mg kg-1 )

(23)

R. ulmifolius tolerant to Zn, As, Pb and Ni

Metal exclusion strategy from stems and reproductive tissue retaining the metal in the roots

Resistance of R. ulmifolius to the metals can be achieved by an avoidance mechanism such as

Results: metal accumulation

Results: metal accumulation

metal in the roots

R. ulmifolius never accumulated more than 1000 mg kg-1 of any of the metals in the aboveground tissues, a criteria indicated for As, Pb or Ni

hyperaccumulators or 10000 mg kg-1 in the case of Zn

mechanism such as the precipitation and association with cell walls or

detoxification in vacuoles

(24)

Soil: Generally, strong positive correlations between total Zn, As, Pb and Ni

concentrations and the metal levels in the available fraction Levels of available Zn, As, Pb and Ni are positively related with

Results: Soil total

Results: Soil total--available metal relations

available metal relations

related with total metal in the soil

Total As vs. EDTA extractable As  0.77 Total Pb vs. EDTA extractable Pb  0.96 Total Nis vs. EDTA extractable Ni  0.85 Total Zn vs. EDTA extractable Zn  0.85

(25)

Results: Soil

Results: Soil –

– plant relations

plant relations

Soil-Plant: Positive correlations between the level of all metals in the soil and Zn, Pb and As accumulation in the roots of R.

ulmifolius

Zn, As, Pb and Ni in the soil are positively related with the metal uptake at the root level

Total As vs. EDTA extractable As  0.71 Total Pb vs. EDTA extractable Pb  0.61

No AMF were detected in the roots of R. ulmifolius for any collection site sampling at different seasons would be necessary to confirm

Total Pb vs. EDTA extractable Pb  0.61 Total Nis vs. EDTA extractable Ni  0.67 Total Zn vs. EDTA extractable Zn  0.85

(26)

0 0,5 1 1,5 2 2,5 R1 R2 R3 R4 B C F As Pb Ni Zn 0,2

Higher BCF

values were

registered for the

roots of R.

ulmifolius

- in

some of these

cases values

Results: Soil

Results: Soil –

– plant relations

plant relations















 Bioconcentration factors

Bioconcentration factors

roots stems 0 0,1 R1 R2 R3 R4 B C F 0 0,1 0,2 0,3 R1 R2 R3 R4 sampling location B C F

cases values

higher than 1

were observed

soil the in ion concentrat metal tion plant a in ion concentrat metal BCF sec leaves

(27)

R. ulmifolius established successfully on this metal polluted soil

Metals were retained in the belowground sections, as shown by the metal accumulation patterns and BCF values

This species presents significant biomass production in the field

R. ulmifolius is well disseminated throughout the region and easy to propagate

Rubus ulmifolius

has desirable properties to be used in

phytostabilisation approaches.

(28)

Solanum nigrum grown in Zn contaminated matrices :

effect of AMF on Zn accumulation

Survey of metal accumulation in plant species indigenous to Esteiro de Estarreja

Future work: To survey

Future work:

Investigation of the effects of bacteria isolated from HM contaminated sites on S. nigrum growth and Zn and Cd accumulation

Evaluation of the potential of the combination of AMF and bacteria with S. nigrum for the phytoremediation of HM contaminated soils

Assessment of the efficacy of the tested associations under field conditions

To survey other HM contaminated sites for indigenous flora, bacteria and AMF

(29)

Aknowledgments

Aknowledgments

The authors wish to thank Câmara Municipal de

Estarreja for the provision of access to the site.

This work was supported by Fundação para a

Ciência e a Tecnologia and Fundo Social

Europeu (III Quadro Comunitário de apoio),

Europeu (III Quadro Comunitário de apoio),

research grant of Ana Marques

(SFRH/BPD/34585/2007 ).

This work was funded by Project MICOMETA

-POCI/AMB/60131/2004 (Fundação para a

(30)

Thank you for

Thank you for

your attention!

your attention!

your attention!

your attention!

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