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Growth performance, photosynthetic status and bioaccumulation of heavy metals by Paulownia tomentosa (Thunb.) Steud growing on contaminated soils

Abstract This work focuses on the study of the potential of a woody specie Paulownia tomentosa (Thunb.) Steud in the phytoremediation of soils polluted by heavy metals. Total metal concentrations in soil samples as well as their bioaccumulation in plant tissues were performed by Atomic Absorption Spectrometry. Bioaccumulation factors (BF) and translocation factors (TF) were calculated in order to determine the effectiveness of plants in removing heavy metals from soil. Results showed that heavy metals significantly affected the root biomass production compared to the leaf biomass and caused slight reductions in all growth parameters. However, the presence of high amounts of ETM in polluted substratum restricted the synthesis of chlorophyll pigments and lead to the deterioration of photosynthetic parameters. Zn, Pb and Cd were found in plant shoots and roots at different levels, between 5.083 and 205.33 mg kg-1 DMW for Zn, 23.22 and 50.13 mg kg-1 DM for Pb and between 0 and 3.88 mg kg-1 DMW for Cd. Translocation and bioaccumulation factors indicated that Paulownia tomentosa could be used in the phytoextraction of Zn and Pb.

Abstract
This work focuses on the study of the potential of a woody specie Paulownia tomentosa (Thunb.) Steud in the phytoremediation of soils polluted by heavy metals. Total metal concentrations in soil samples as well as their bioaccumulation in plant tissues were performed by Atomic Absorption Spectrometry. Bioaccumulation factors (BF) and translocation factors (TF) were calculated in order to determine the effectiveness of plants in removing
heavy metals from soil. Results showed that heavy metals significantly affected the root biomass production compared to the leaf biomass and caused slight reductions in all growth parameters. However, the presence of
high amounts of ETM in polluted substratum restricted the synthesis of chlorophyll pigments and lead to the deterioration of photosynthetic parameters. Zn, Pb and Cd were found in plant shoots and roots at different
levels, between 5.083 and 205.33 mg kg-1 DMW for Zn, 23.22 and 50.13 mg kg-1 DM for Pb and between 0 and 3.88 mg kg-1 DMW for Cd. Translocation and bioaccumulation factors indicated that Paulownia tomentosa could
be used in the phytoextraction of Zn and Pb.

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Introducti<strong>on</strong><br />

Heavy <str<strong>on</strong>g>metals</str<strong>on</strong>g>, such as zinc (Zn), lead (Pb), <str<strong>on</strong>g>and</str<strong>on</strong>g><br />

cadmium (Cd) are am<strong>on</strong>g the most comm<strong>on</strong><br />

pollutants found in both industrial <str<strong>on</strong>g>and</str<strong>on</strong>g> urban<br />

effluents <str<strong>on</strong>g>and</str<strong>on</strong>g> hence, pose a great potential threat to<br />

the envir<strong>on</strong>ment <str<strong>on</strong>g>and</str<strong>on</strong>g> human health.In fact, Zn is an<br />

essential element or micr<strong>on</strong>utrient for plants but can<br />

be highly toxic <str<strong>on</strong>g>and</str<strong>on</strong>g> impairs their growth when present<br />

at excessive c<strong>on</strong>centrati<strong>on</strong> (Ebbes <str<strong>on</strong>g>and</str<strong>on</strong>g> Kochian, 1997;<br />

Hansch<str<strong>on</strong>g>and</str<strong>on</strong>g> Mendel, 2009). In c<strong>on</strong>trast, Pb <str<strong>on</strong>g>and</str<strong>on</strong>g> Cd<br />

are c<strong>on</strong>sidered to have extremely toxic effect even at<br />

low c<strong>on</strong>centrati<strong>on</strong> (Willams et al., 2000).<br />

Heavy metal stress can exert a negative effect <strong>on</strong><br />

physiological functi<strong>on</strong>s within plants <str<strong>on</strong>g>by</str<strong>on</strong>g> inducing an<br />

oxidative stress, alter the membrane permeability <str<strong>on</strong>g>and</str<strong>on</strong>g><br />

impair the mineral nutriti<strong>on</strong> (Reddy et al., 2005).<br />

These effects lead to impairment <str<strong>on</strong>g>of</str<strong>on</strong>g> photosynthesis <str<strong>on</strong>g>by</str<strong>on</strong>g><br />

changing chloroplast ultrastructure <str<strong>on</strong>g>and</str<strong>on</strong>g> disassembly<br />

<str<strong>on</strong>g>of</str<strong>on</strong>g> the thylakoids <str<strong>on</strong>g>and</str<strong>on</strong>g> hence, the inhibiti<strong>on</strong> <str<strong>on</strong>g>of</str<strong>on</strong>g><br />

<str<strong>on</strong>g>photosynthetic</str<strong>on</strong>g> pigments biosynthesis (Azzarello et<br />

al., 2012; Vassilev et al., 2011). It results a visual<br />

toxicity symptoms in higher plants like growth<br />

inhibiti<strong>on</strong>, chlorosis, browning <str<strong>on</strong>g>of</str<strong>on</strong>g> roots, senescence<br />

<str<strong>on</strong>g>and</str<strong>on</strong>g> death <str<strong>on</strong>g>of</str<strong>on</strong>g> plants (Ebbs <str<strong>on</strong>g>and</str<strong>on</strong>g> Kochian, 1997).<br />

Accordingly, several processes such as physical,<br />

thermal <str<strong>on</strong>g>and</str<strong>on</strong>g> chemical treatments have developed in<br />

order to remediate the soil c<strong>on</strong>taminated with <str<strong>on</strong>g>heavy</str<strong>on</strong>g><br />

<str<strong>on</strong>g>metals</str<strong>on</strong>g>. However, these technologies are costly <str<strong>on</strong>g>and</str<strong>on</strong>g><br />

damage the soil structure <str<strong>on</strong>g>and</str<strong>on</strong>g> fertility (Sim<strong>on</strong>not <str<strong>on</strong>g>and</str<strong>on</strong>g><br />

Cruz, 2008).<br />

Thus, phytoremediati<strong>on</strong> has been proposed as an<br />

envir<strong>on</strong>ment friendly <str<strong>on</strong>g>and</str<strong>on</strong>g> cost-effective alternative<br />

for removing <str<strong>on</strong>g>metals</str<strong>on</strong>g> <str<strong>on</strong>g>and</str<strong>on</strong>g> remediating c<strong>on</strong>taminated<br />

<strong>soils</strong> through plants. It includes two main techniques<br />

namely the phytoextracti<strong>on</strong> which is based <strong>on</strong> the use<br />

<str<strong>on</strong>g>of</str<strong>on</strong>g> hyperaccumulating plants able to c<strong>on</strong>centrate<br />

pollutants in their aerial parts destined for harvest<br />

<str<strong>on</strong>g>and</str<strong>on</strong>g> phytostabilizati<strong>on</strong> which uses plants that can<br />

reduce the mobility <str<strong>on</strong>g>and</str<strong>on</strong>g> bioavailability <str<strong>on</strong>g>of</str<strong>on</strong>g> <str<strong>on</strong>g>metals</str<strong>on</strong>g> in<br />

their rhizosphere (Gisbert et al., 2003).<br />

high biomass, have a rapid growth <str<strong>on</strong>g>and</str<strong>on</strong>g> have the<br />

potential to tolerate <str<strong>on</strong>g>and</str<strong>on</strong>g> accumulate high amounts <str<strong>on</strong>g>of</str<strong>on</strong>g><br />

<str<strong>on</strong>g>heavy</str<strong>on</strong>g> <str<strong>on</strong>g>metals</str<strong>on</strong>g> into their aboveground biomass<br />

(Chaney et al., 1997). Thus, woody species are<br />

c<strong>on</strong>sidered to be a good c<str<strong>on</strong>g>and</str<strong>on</strong>g>idate for this purpose,<br />

since the most hyperaccumulator are herbaceous<br />

species, which are slow-<str<strong>on</strong>g>growing</str<strong>on</strong>g>, produce low<br />

biomass <str<strong>on</strong>g>and</str<strong>on</strong>g> have shallow root systems (Pulford <str<strong>on</strong>g>and</str<strong>on</strong>g><br />

Wats<strong>on</strong>, 2003).<br />

<str<strong>on</strong>g>Paulownia</str<strong>on</strong>g> <str<strong>on</strong>g>tomentosa</str<strong>on</strong>g> (<str<strong>on</strong>g>Thunb</str<strong>on</strong>g>.) <str<strong>on</strong>g>Steud</str<strong>on</strong>g> is a tree species<br />

bel<strong>on</strong>ging to the genus <str<strong>on</strong>g>Paulownia</str<strong>on</strong>g> which included the<br />

woody species. These lasts are known <str<strong>on</strong>g>and</str<strong>on</strong>g> proved for<br />

their effectiveness in phytoremediati<strong>on</strong> purposes due<br />

to their rapid growth, a massive producti<strong>on</strong> <str<strong>on</strong>g>of</str<strong>on</strong>g><br />

biomass, a deep root system <str<strong>on</strong>g>and</str<strong>on</strong>g> an elevated tolerance<br />

to high levels <str<strong>on</strong>g>of</str<strong>on</strong>g> <str<strong>on</strong>g>heavy</str<strong>on</strong>g> <str<strong>on</strong>g>metals</str<strong>on</strong>g> in soil (Wang et al.,<br />

2010; Doumett et al., 2010).<br />

Therefore, the present study was designed to assess<br />

growth <str<strong>on</strong>g>performance</str<strong>on</strong>g>, <str<strong>on</strong>g>photosynthetic</str<strong>on</strong>g> <str<strong>on</strong>g>status</str<strong>on</strong>g> <str<strong>on</strong>g>and</str<strong>on</strong>g><br />

<str<strong>on</strong>g>bioaccumulati<strong>on</strong></str<strong>on</strong>g> <str<strong>on</strong>g>of</str<strong>on</strong>g> Zn, Pb <str<strong>on</strong>g>and</str<strong>on</strong>g> Cd <str<strong>on</strong>g>of</str<strong>on</strong>g> <str<strong>on</strong>g>Paulownia</str<strong>on</strong>g><br />

Tomentosa <str<strong>on</strong>g>growing</str<strong>on</strong>g> <strong>on</strong> <str<strong>on</strong>g>heavy</str<strong>on</strong>g> metal c<strong>on</strong>taminated<br />

Tunisian <strong>soils</strong>.<br />

Materials <str<strong>on</strong>g>and</str<strong>on</strong>g> methods<br />

Plant material <str<strong>on</strong>g>and</str<strong>on</strong>g> growth c<strong>on</strong>diti<strong>on</strong>s<br />

<str<strong>on</strong>g>Paulownia</str<strong>on</strong>g> <str<strong>on</strong>g>tomentosa</str<strong>on</strong>g> plantlets derived from<br />

micropropagati<strong>on</strong> were cultivated in plastic pots filled<br />

with Zn, Pb <str<strong>on</strong>g>and</str<strong>on</strong>g> Cd naturally rich substrata provided<br />

from two Tunisian mines, namely Jebel Ressas (JR)<br />

(36°61' N;10°32' E; 97m above sea level) <str<strong>on</strong>g>and</str<strong>on</strong>g> Ghezala<br />

(GH) (37°5’ N; 9°32’ E; 30 m above sea level),<br />

whereas the c<strong>on</strong>trol <strong>on</strong>e (TU) was collected from the<br />

experimental plot <str<strong>on</strong>g>of</str<strong>on</strong>g> the Nati<strong>on</strong>al Agr<strong>on</strong>omic Institute<br />

<str<strong>on</strong>g>of</str<strong>on</strong>g> Tunisia (INAT) (36°51' N; 10°11' E; 10 m above sea<br />

level).The pot-cultures were placed under glass house<br />

supplied with natural sunlight (photoperiod varying<br />

from 13 to 16 h) from May, 1 st to 30 th June, 2012. The<br />

glass house temperatures varied from 17°C to 29°C,<br />

whereas the relative humidity ranged between 43%<br />

<str<strong>on</strong>g>and</str<strong>on</strong>g> 67%. Pots were irrigated daily with distilled water<br />

to maintain vigorous plant growth.<br />

Suitable plants for phytoremediati<strong>on</strong> must produce<br />

The experiment was c<strong>on</strong>ducted at the Horticulture<br />

Bahri et al.<br />

Page 33

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