28.01.2017 Views

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.

SHOW MORE
SHOW LESS

Create successful ePaper yourself

Turn your PDF publications into a flip-book with our unique Google optimized e-Paper software.

structural changes in the thylakoid <str<strong>on</strong>g>by</str<strong>on</strong>g> increasing<br />

degradati<strong>on</strong> <str<strong>on</strong>g>of</str<strong>on</strong>g> thylakoid proteins (Sigfridss<strong>on</strong>, 2004;<br />

Pastikka et al., 2001).<br />

Chlorophyll pigments <str<strong>on</strong>g>and</str<strong>on</strong>g> carotenoid biosynthesis<br />

As can be seen in fig. 2. , accumulati<strong>on</strong> <str<strong>on</strong>g>of</str<strong>on</strong>g> Zn, Pb<str<strong>on</strong>g>and</str<strong>on</strong>g><br />

Cd at high level in the substratum induced decreases<br />

in chlorophyll pigments <str<strong>on</strong>g>and</str<strong>on</strong>g> carotenoid c<strong>on</strong>tent in<br />

leaves. However, the biosynthesis <str<strong>on</strong>g>of</str<strong>on</strong>g> chlorophyll a,<br />

chlorophyll b, total chlorophyll as well as carotenoids<br />

was altered. This fact was in agreement with previous<br />

research in some other plant species such as Brassica<br />

juncea, Phaseolus vulgaris, Pisumsativum (Zengin<br />

<str<strong>on</strong>g>and</str<strong>on</strong>g> Munzuroglu, 2005; Hattab et al., 2009; Sinha<br />

<str<strong>on</strong>g>and</str<strong>on</strong>g> Shrivastave, 2012).<br />

Indeed, chlorophyllb biosynthesis was declined<br />

substantially in resp<strong>on</strong>se to <str<strong>on</strong>g>heavy</str<strong>on</strong>g> metal<br />

c<strong>on</strong>centrati<strong>on</strong> in substrata. A linear decrease was<br />

shown in c<strong>on</strong>taminated substrata JR <str<strong>on</strong>g>and</str<strong>on</strong>g> GH, which<br />

varied between 15.29% <str<strong>on</strong>g>and</str<strong>on</strong>g> 50.08%, when compared<br />

to the c<strong>on</strong>trol at the 4 th <str<strong>on</strong>g>and</str<strong>on</strong>g> the 6 th week after planting<br />

(Fig. 2.).<br />

Chlorophyll a c<strong>on</strong>centrati<strong>on</strong> is higher than that <str<strong>on</strong>g>of</str<strong>on</strong>g><br />

chlorophyll b. In fact, Chlorophyll a biosynthesis was<br />

more pr<strong>on</strong>ounced at the 4 th week <str<strong>on</strong>g>of</str<strong>on</strong>g> culture <str<strong>on</strong>g>and</str<strong>on</strong>g><br />

increased <str<strong>on</strong>g>by</str<strong>on</strong>g> 11.01%, 14.02% <str<strong>on</strong>g>and</str<strong>on</strong>g> 10.25% for plants<br />

<str<strong>on</strong>g>growing</str<strong>on</strong>g> in TU, JR <str<strong>on</strong>g>and</str<strong>on</strong>g> GH substrata, respectively<br />

when compared to values recorded at the 2 nd week.<br />

However a slight decrease was observed at the 6 th<br />

week <str<strong>on</strong>g>by</str<strong>on</strong>g> 15.15%, 15.77% <str<strong>on</strong>g>and</str<strong>on</strong>g> 12.65% for plants<br />

<str<strong>on</strong>g>growing</str<strong>on</strong>g> in TU, JR <str<strong>on</strong>g>and</str<strong>on</strong>g> GH substrata, respectively<br />

when compared to levels recorded at the 4 th week<br />

(Fig. 2.).<br />

Total chlorophyll c<strong>on</strong>tent in <str<strong>on</strong>g>Paulownia</str<strong>on</strong>g> leaves<br />

increased significantly at the 4 th week, when<br />

compared to levels recorded at the 2 nd week <str<strong>on</strong>g>of</str<strong>on</strong>g> culture<br />

<str<strong>on</strong>g>by</str<strong>on</strong>g> 11.5%, 16.92% <str<strong>on</strong>g>and</str<strong>on</strong>g> 10.81% for plants <str<strong>on</strong>g>growing</str<strong>on</strong>g> in<br />

TU, JR <str<strong>on</strong>g>and</str<strong>on</strong>g> GH substratum, respectively. However<br />

these levels decreased significantly at the 6 th week <str<strong>on</strong>g>by</str<strong>on</strong>g><br />

16.93%, 22.82% <str<strong>on</strong>g>and</str<strong>on</strong>g> 14.43% for plants <str<strong>on</strong>g>growing</str<strong>on</strong>g> in TU,<br />

JR <str<strong>on</strong>g>and</str<strong>on</strong>g> GH substrata, respectively when compared to<br />

values recorded at the 4 th week after planting (Fig. 2.).<br />

According to Mysliwa-Kurdziel <str<strong>on</strong>g>and</str<strong>on</strong>g> Strzalka (2002),<br />

<str<strong>on</strong>g>heavy</str<strong>on</strong>g> metal stress disturbs physiological metabolisms<br />

<str<strong>on</strong>g>and</str<strong>on</strong>g> affected primary <str<strong>on</strong>g>photosynthetic</str<strong>on</strong>g> parameters in<br />

higher plants. Indeed,Cd is reported to have negative<br />

effect <strong>on</strong> chlorophyll c<strong>on</strong>tent <str<strong>on</strong>g>by</str<strong>on</strong>g> reducti<strong>on</strong> <str<strong>on</strong>g>of</str<strong>on</strong>g> the<br />

energy c<strong>on</strong>sumpti<strong>on</strong> <str<strong>on</strong>g>by</str<strong>on</strong>g> Calvin’s cycle reacti<strong>on</strong>s<br />

(Stobart et al,. 1985) <str<strong>on</strong>g>and</str<strong>on</strong>g> a decrease in the net CO2<br />

assimilati<strong>on</strong> (Mysliwa-Kurdziel <str<strong>on</strong>g>and</str<strong>on</strong>g> Strzalka, 2002).<br />

Furthermore, Azzarello et al. (2012) reported that<br />

high Zn levels (above 1000 µM) affected chloroplasts,<br />

which are sensitive to oxidative stress. C<strong>on</strong>sequently,<br />

changes in cellular organizati<strong>on</strong> were detected, which<br />

affected negatively the photosynthesis <str<strong>on</strong>g>and</str<strong>on</strong>g> lead to<br />

depressed growth. Besides, Lei et al. (2012) noted<br />

that metal stress (Zn <str<strong>on</strong>g>and</str<strong>on</strong>g> Cd) imposed during the<br />

culture period <str<strong>on</strong>g>of</str<strong>on</strong>g> Seagrass thalassia hemprichii<br />

decreased biosynthesis <str<strong>on</strong>g>of</str<strong>on</strong>g> chlorophyll pigments. This<br />

is a c<strong>on</strong>sequence <str<strong>on</strong>g>of</str<strong>on</strong>g> the disorganizati<strong>on</strong> <str<strong>on</strong>g>and</str<strong>on</strong>g> the<br />

damage <str<strong>on</strong>g>of</str<strong>on</strong>g> chloroplasts, the disassembly <str<strong>on</strong>g>of</str<strong>on</strong>g> the<br />

thylakoids <str<strong>on</strong>g>and</str<strong>on</strong>g> a c<strong>on</strong>sequent decrease in nutrient<br />

absorpti<strong>on</strong> <str<strong>on</strong>g>by</str<strong>on</strong>g> plants.<br />

The highest carotenoid c<strong>on</strong>tent (564.14 µg g -1 DMW)<br />

was measured in the c<strong>on</strong>trol plants <str<strong>on</strong>g>and</str<strong>on</strong>g> these<br />

c<strong>on</strong>tents were found to be affected <str<strong>on</strong>g>by</str<strong>on</strong>g> the highest<br />

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> <str<strong>on</strong>g>and</str<strong>on</strong>g> the durati<strong>on</strong> <str<strong>on</strong>g>of</str<strong>on</strong>g> exposure to<br />

the stress. Indeed, at the 6 th week after planting,<br />

carotenoid c<strong>on</strong>tent decreased <str<strong>on</strong>g>by</str<strong>on</strong>g> 35.08%, 47.96% <str<strong>on</strong>g>and</str<strong>on</strong>g><br />

7.94% in TU, JR <str<strong>on</strong>g>and</str<strong>on</strong>g> GH substrata, respectively when<br />

compared to the levels measured at the 4 th week (Fig.<br />

.2).<br />

In fact, these substances are n<strong>on</strong>-enzymatic<br />

antioxidants, which play an important role in the<br />

protecti<strong>on</strong> <str<strong>on</strong>g>of</str<strong>on</strong>g> chlorophyll pigments (Sinha et al.,<br />

2010). Heavy metal stress decreased the carotenoid<br />

biosynthesis <str<strong>on</strong>g>and</str<strong>on</strong>g> lead to a reducti<strong>on</strong> in the protecti<strong>on</strong><br />

<str<strong>on</strong>g>of</str<strong>on</strong>g> photosystems II (PSII) against photo-oxidati<strong>on</strong>.<br />

C<strong>on</strong>clusi<strong>on</strong>s<br />

Overall results showed that the different parameters<br />

<str<strong>on</strong>g>of</str<strong>on</strong>g> growth (fresh <str<strong>on</strong>g>and</str<strong>on</strong>g> dry matter weight, leaf area,<br />

plant height) <str<strong>on</strong>g>of</str<strong>on</strong>g> <str<strong>on</strong>g>Paulownia</str<strong>on</strong>g> <str<strong>on</strong>g>tomentosa</str<strong>on</strong>g> plants <str<strong>on</strong>g>growing</str<strong>on</strong>g><br />

<strong>on</strong> <str<strong>on</strong>g>heavy</str<strong>on</strong>g> metal c<strong>on</strong>taminated Tunisian <strong>soils</strong> were<br />

declined. Additi<strong>on</strong>ally, a negative effect in<br />

Bahri et al.<br />

Page 40

Hooray! Your file is uploaded and ready to be published.

Saved successfully!

Ooh no, something went wrong!