Der Pharma Chemica
Journal for Medicinal Chemistry, Pharmaceutical Chemistry, Pharmaceutical Sciences and Computational Chemistry

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Research Article - Der Pharma Chemica ( 2018) Volume 10, Issue 3

Bio-monitoring of Metal Trace Elements by Epiphytic Lichen in the Bordj Bou Arreridj Area, East of Algeria

Fatima Adjiri1, Messaoud Ramdani1*, Takia lograda1 and Pierre Chalard2

1Laboratory of Natural Resource Valorisation, SNV Faculty, Setif 1 University, 19000 Setif, Algeria

2SIGMA Clermont, Campus des Cezeaux, CS 20265, 63178 Aubière cedex, France

*Corresponding Author:
Messaoud Ramdani
Laboratory of Natural Resource Valorisation, SNV Faculty
Setif 1 University
19000 Setif, Algeria

Abstract

The objective of this study is to use a bio-sensor in order to assess environmental by metal trace elements (MTE) contamination in the Bourdj Bou Arreridj region, East of Algeria. The sampling of biological material from 32 locations was performed using a natural bioaccumulators represented by a lichenic species; Xanthoria parietina. Samples were taken and ten heavy metals (Fe, Cd, Co, Cr, Cu, Mn, Ni, Pb, Sb and Zn) were selected for analysis. The metal content recorded in various sampled sites were found greatly fluctuating and exceeded standard values with the exception of Pb at the Kseur and Ghilassa locations. The level of Fe was very high in all sampled locations with an average of (43184.4 ± 16373.7 mg/kg). This important accumulation of MTE in thalli was correlated to road and rail traffic as well as to industrial activities. These results show the tolerance of X. parietina to metallic stresses and therefore its effectiveness as a bio-sensor in the bio-monitoring programs assessing air quality.

Keywords

trace elements, Bio-monitoring, Bio-accumulation, Xanthoria parietina, Bourdj Bou Arreridj, Algeria

Introduction

The level of urban air pollution is due to the intensive development of industry, road traffic, population density and urbanization, leading to the degradation of air quality [1,2]. Bio-monitoring of air quality is the use of responses, at all levels, of biological organisms to predict and reveal environmental alterations and to follow its evolution [3]. Bio-monitoring is a very effective operational tool [2,4-6]. It is a complementary method to the physico-chemical analyzes and highlights the impregnation of the environment by the Metallic Trace Elements (MTE) [7].

The MTE, known as heavy metals or toxic metals, are widely reputed pollutants emitted into the atmosphere by a large number of natural and anthropogenic sources [8-10]. Epiphytic cryptogams are gaining increasing importance in environmental bio-monitoring because they can absorb and accumulate elements in their systems [11,12].

Bio-indication studies involving lichens provide much information on the qualitative status of the environment and are useful for assessing the long-term effects of bio-monitoring programs [2]. Lichens are among the most commonly used cryptogamic organisms in the bio-monitoring of MTEs in air [2,13,14]. Foliaceous lichens are highly tolerant to metal trace elements and reflect the history of the environment [11,12,15]. Xanthoria parietina is the most widely used lichen in bio-monitoring studies [2,13,16-19].

The aim of this study is to assess MTE environmental contamination by drawing up a map of the distribution of pollution in the 32 municipalities of the Bordj Bou Arreridj province (BBA), East of Algeria, using the lichen X. parietina.

Materials and Methods

Sample collection

The foliaceous lichen X. parietina, widespread in the studied areas and widely used in similar studies in several countries, has been selected as a bio-accumulator [16]. Samples were collected in 34 locations spread throughout the BBA province (Figure 1).

derpharmachemica-Sampled-populations

Figure 1: Sampled populations of Xanthoria parietina

Samples were collected avoiding the usage of tools or containers which may contaminate them (We avoided steel tools or stainless steel containers whose walls contain pigments based on trace elements such as PVC). Each sampled site consists of an area of a maximum 100 m2, located near high traffic roads and secondary roads. The geographical coordinates of each sampled area were noted using a GPS (Table 1). The BBA province is characterized by a semi-arid continental climate, with hot dry summers and severe winters. Rainfall is inadequate and irregular both in time and space.

Code Locations Latitude North (N) Longitude East (E) Altitude (m)
1 El Main 36° 21' 59.907" 4° 43' 56.866" 983
2 Tassameurt 36° 15' 52.732" 4° 48' 11.329" 629
3 Tefreg 36° 18' 39.333" 4° 42' 30.243" 1131
4 Djaafra 36° 17' 33.561" 4° 39 42.894" 1335
5 Khelil 36° 10' 1.578" 5° 1' 25.946" 964
6 Bordj Zemoura 36° 15' 59.677" 4° 50' 21.156" 913
7 Ouled Dahmane 36° 13' 41.188" 4° 46' 50.138" 1250
8 Colla 36° 15' 32.299" 4° 39 43.326" 1250
9 Teniet En Nasr 36° 13' 34.759" 4° 35 21.930" 1250
10 Ouled Sidi Brahim 36° 13' 52.071" 4° 20 31.498" 580
11 Ain-Taghrout 36° 7' 31.180" 5° 4' 44.572" 907
12 Bir Kasdali 36° 9' 0.853" 5° 1' 16.698" 955
13 Sidi Embarek 36° 6' 13.896" 4° 54' 29.289" 1011
14 Hasnaoua 36° 8' 17.610" 4° 48' 13.622" 993
15 Medjana 36° 7' 55.621" 4° 40' 20.503" 1052
16 Mansoura 36° 4' 16.060" 4° 28 21.561" 807
17 El M'hir 36° 6' 57.042" 4° 23 2.713" 557
18 Haraza 36° 8' 20.085" 4° 12 52.610" 1201
19 Ben Daoud 36° 3' 59.274" 4° 8' 42.662" 1050
20 Tixter 36° 2' 49.300" 5° 5' 8.592" 947
21 Aïn Tesra 36° 2' 17.28" 5° 0' 75.81" 1039
22 El Ansseur 36° 1' 47.470" 4° 53' 80.124" 980
23 Bordj Bou Arreridj 36° 4' 22.548" 4° 41' 31.452" 901
24 El Achir 36°3' 10.771" 4° 37' 54.631" 967
25 Ras El Oued 35° 56' 58.912" 5° 2' 2.774" 1078
26 Belimour 35° 58' 40.738" 4° 52' 25.165" 937
27 El Hamadia 35° 58' 24.081" 4° 44' 29.356" 819
28 Ksour 36°59' 29.014" 4°30' 39.281" 1250
29 Ouled Brahem 35° 51' 53.737" 5° 4' 55.452" 1259
30 Bordj Ghédir 35° 55' 8.500" 4° 53' 22.47" 1387
31 Taglait 35° 50' 35.347" 4° 57' 10.404" 1434
32 Ghilassa 35° 51' 35.031" 4° 54' 39.110" 1171

Table 1: Geographic coordinates of the sampled areas

Samples treatment

Lichen samples were digested in the laboratory in aseptic conditions, using a mixture of HNO3/HF/H2O in Teflon containers [20,21]. A solution of our samples is prepared using the grinded solid material to which 10 ml of 40% Hydrofluoric Acid (HF) and 3 ml of 70% Perchloric Acid (HClO4) were added. Evaporation takes place on a hotplate at 160°C. After a quasi-total evaporation, 1 ml of 65% Nitric Acid (HNO3) and 10 ml of distilled water were added. The samples are then left for 30 min at 4°C in the refrigerator.

The dissolution of the residue is performed by placing the samples on a hotplate at 60°C for 1 h. The resulting mixture is transferred to a 100 ml flask for filtration, adjusting the volume with distilled water.

Analytical methods for ETM concentration measurements in lichens

The concentrations of the following elements; Fe, Cd, Co, Cu, Cr, Mn, Ni, Pb, Sb and Zn, were determined by Atomic Absorption Spectro-photometry with Flame (AASF). There are no established standards of trace elements concentration in lichens [22]. To interpret the results of each element studied we used as a standard reference, values of the European Commission BCR information CRM-482 (Table 2) [23].

MTE Symbols Certified values Uncertainty
Lead Pb 40.9 1.40
Copper Cu 7.03 0.19
Cadmium Cd 0.56 0.02
Zinc Zn 100.6 2.20
Nickel Ni 2.47 0.07
Chrome Cr 4.12 0.15
Cobalt Co 0.32 0.03
Iron Fe 804 160
Manganese Mn 33.0 0.50
Antimony Sb 0.35 0.09

Table 2: Certified CRM-482 values of trace elements (mg/kg) using AASF

Statistical analysis

Data were first subjected to Principal Components Analysis (PCA) to examine the relationship among the trace elements and the bio-accumulation by lichens, and also the relation between the presence of these elements and the pollution. Cluster analysis (UPGMA) was carried out on the original variables and on the Manhattan Distance Matrix to look for hierarchical associations among the elements and the locations. Statistical analyses were carried out using STATISTICA 10 software.

Results

The concentrations of metal elements (Fe, Cd, Co, Cr, Cu, Mn, Ni, Pb, Sb and Zn) accumulated in the X. parietina were determined by Atomic Absorption Spectro-photometry with Flame (Table 3).

Stations Pb Mn Fe Cu Sb Cd Co Zn Ni Cr
1 El Main 110 800 65900 78 158 3 638.04 611.37 99.93 380.95
2 Tassameurt 120 1300 68500 80 194 3 658.15 348.55 77.16 321.09
3 Tefreg 96 800 46400 56 203 4 605.36 376.47 101.32 376.87
4 Djaafra 89 1300 72800 63 187 3 692.5 614.25 93.89 406.8
5 Khelil 133 500 36600 35 219 3 347.3 437.36 3.72 202.72
6 Bordj Zemoura 105 400 29000 51 163 3 416.84 323.88 42.3 274.83
7 Ouled Dahmane 111 400 45100 36 253 4 668.2 484.19 52.99 334.69
8 Colla 60 700 32900 33 185 3 674.91 433.4 98.07 387.76
9 Teniet En Nasr 81 500 47800 55 145 2 673.23 482.75 95.75 406.8
10 Ouled Sidi Brahim 110 1300 71400 68 167 3 714.29 514.28 105.51 395.92
11 Aïn Taghrout 206 500 40700 28 212 5 254.29 916.87 30.68 127.89
12 Bir Kasdali 114 300 36000 36 210 4 389.19 372.87 26.96 201.36
13 Sidi Embarek 115 1300 73000 67 162 3 579.39 497.7 46.01 293.88
14 Hasnaoua 136 800 48900 65 238 3 527.44 408.72 90.17 359.18
15 Medjana 173 700 46400 87 226 4 600.34 429.97 95.28 390.48
16 Mansoura 90 600 43800 52 183 3 581.06 469.96 123.63 434.01
17 El M'hir 96 500 46000 67 178 3 811.48 438.8 100.4 472.11
18 Haraza 93 400 50200 66 170 3 772.1 360.8 118.52 443.54
19 Ben Daoud 71 900 58000 33 186 3 814.83 570.66 133.4 428.57
20 Tixter 169 400 32800 24 243 5 283.62 983.52 16.27 144.22
21 Aïn Tesra 86 400 30100 43 164 3 434.44 471.04 7.44 229.93
22 El Ansseur 99 1100 63200 76 190 3 488.06 539.67 43.69 292.52
23 Bordj Bou Arreridj 68 400 17000 23 93 3 601.17 549.4 38.58 303.4
24 El Achir 120 600 40800 39 194 3 711.77 390.34 107.83 378.23
25 Ras El Oued 93 400 29500 23 175 4 297.86 431.96 3.3 161.9
26 Belimour 66 500 23500 38 182 3 633.01 347.65 54.38 303.4
27 El Hamadia 58 900 42100 37 174 3 572.69 480.41 88.31 348.3
28 Ksour 6 900 24200 27 226 3 591.12 451.23 95.75 386.39
29 Ouled Brahem 95 700 45100 51 190 3 380.81 364.77 4.65 165.99
30 Bordj Ghédir 91 500 37100 62 233 3 457.06 364.77 32.07 227.21
31 Taglait 67 400 30100 23 171 3 426.06 406.92 19.99 239.46
32 Ghilassa 23 300 7000 72 102 3 510.68 377.56 30.68 209.52
Average 98,4 671.9 43184.4 49.8 186.8 3.3 556.5 476.6 65 313.4
SD 39,5 312.4 16373.7 19.3 35.7 0.6 152.6 145.9 40.3 97.3
CV% 40,1 46,5 37,9 38,8 19,1 18,2 27,4 30,6 62,0 31,1
Min 6 300 7000 23 93 2 254.3 323.9 3.3 127.9
Max 206 1300 73000 87 253 5 814.8 983.52 133.4 472.1
Certified standard 40.9 33 804 7.03 0.35 0.6 0.32 100.6 2.47 4.12

Table 3: ETM concentrations in Xanthoria parietina (mg/kg dry weight)

The MTE concentrations in the 32 sampled sites are found highly variable. It is noted that the (Fe) concentrations are too high in the thalli. The high Fe rate hid the variability of the rest of the elements in the analysis (Figure 2a), this element was removed and a second analysis was performed to reveal the variability of the MTE in X. parietina (Figure 2b).

derpharmachemica-concentrations

Figure 2: Variability of MTE concentrations in X. parietina thalli

The Fe element exhibits the highest mean concentration in X. parietina samples with (43184.4 ± 16373.7 mg/kg), while Cd is the least abundant in the thalli (3.3 ± 0.6 mg/kg). The metals concentrations analyzed are distributed in the following order: Fe > Mn > Co > Zn > Cr > Sb > Pb > Ni > Cu > Cd. Fe showed the greatest variation followed by Mn (671.9 ± 312.4 mg/kg). Concentration levels of Co, Zn and Cr are relatively close and exceed standard values. The mean concentrations of Sb and Pb found in rural and urban communes are relatively similar (186.8 ± 35.7 mg/kg) and (98.4 ± 39.5 mg/kg), while concentrations of Ni and Cu are the lowest in order of appearance after the Cd.

The three-dimensional spatial projection of the stations, based on the first three axes resulting from the ACP, shows the separation of populations into two more-or-less distinct groups, thus isolating three Ghilassa, Ain Taghroute and Tixter areas (Figure 3). The concentrations of ETMs found in the thalli at Ain Taghrout and Tixter are high and similar, especially Cd and Zn, exceeding standard values. On the other hand, at the Ghilassa station, the thalli accumulate low concentrations of MTE, while the Pb concentration is below the standard values (40.6 mg/kg).

derpharmachemica-projection-stations

Figure 3: Spatial projection of stations based on the first three axes from the ACP

The use of UPGMA, a statistical method based on the un-weighted pair average and the distance from city-block (Manhattan), reflects heterogeneity in metal accumulation in X. parietina thalli and confirms disaggregation of the studied sites into several clades (Figure 4).

derpharmachemica-heavy-metals

Figure 4: UPGMA based on the concentration of heavy metals

The first group is represented by the station of Ghilassa with a low ETM accumulation in the thalli, while the second group splits into two branches; The Sidi Embarek, Djaafra, Ouled Sidi Brahim, Tassameurt, El Anasseur, El Main and Ben Daoud stations with a very high Fe accumulation, exceeding standard values (804 mg/kg). The remaining sites form an amalgam representing the same groups as those coming from the ACP. Sites with high concentrations of Pb and Zn in the thalli are located close to high traffic road axes such as Ain Taghrout and Tixter and then decrease in low traffic stations.

Discussion

Assessment of levels of contamination in the BBA province for ten different metals showed Pb contamination values similar to those previously found in lichen thalli X. parietina in Italy [16], France [8,24], Turkey [25], and Poland [10]. Generally, high concentrations of Pb measured in thalli near roads are closely related to vehicle emissions and fuel combustion [18,25-32]. In addition, in the studied areas the observed high concentrations of Pb may be related to the increase in industrial activities [8-9,32], and the incineration of waste [24].

A low Pb accumulation in the southern mountainous sites (Kseur and Ghilassa) was observed with values between (6 and 23 mg/kg). However the concentration of Pb in northern mountainous sites was high due to a higher air humidity level as suggested by some authors [14,33].

The values of Zn in the thalli of X. parietina exceeded standard values. These high rates are due to traffic [18,29] and industrial activities [25,34]. The same Zn concentrations were observed in France [8,9,24] and Turkey [25]; In contrast, low concentrations were found in Italy [16], Turkey [29] and Poland [10].

Cd concentrations are high in thalli and similar to the results observed in France [8,9,24], Turkey [25] and in Algeria [35]. Road traffic and anthropogenic activities [25,36] contribute to the increase in Cd concentrations in the thalli of X. parietina [18,29,37]. The concentrations below standard values were observed in Italy [16] and Morocco [37].

The levels of Sb concentrations measured in the thalli of X. parietina are above standard values, whereas earlier studies in France [9,31] and Spain [38] showed that Sb concentrations in the thalli are below standard values (0.35 mg/kg). According to the authors of these studies, high Sb levels were attributed mainly to road traffic, waste incineration and the production of batteries [9,39]. Sb contamination spreads to rural areas where the maximum concentration is recorded in Ouled-Dahmane (253 mg/kg), and this high rate comes probably from sources outside the studied area, as reported by [31].

The levels of iron (Fe) in lichenic thalli are very high. The results obtained are similar to those recorded in other countries such as France [24], Turkey [25], and Poland [10]. On the other hand, the concentrations recorded in Portugal by [40] are lower than the standard values. The high rate of Fe in the studied sites has been linked to geographical factors [10,13,25,37]. The other explanation for the high level of Fe in the thalli is the accumulation of dust from anthropological activities [15,25,32,37,39,40-42].

The results of the Cu analysis show that the levels accumulated in the thalli are high and exceed standard values. The same remarks were observed in X. parietina, in France [9,24] and in Poland [10]. The highest Cu contamination was observed especially in rural communities, while the lowest contamination levels were observed in high industrial stations. The high level of Cu in rural communes is probably due to the usage of pesticides and fertilizers that can be sources of copper emission [2,9,16,25]. The presence of Cu in the thalli sampled in urban sites is due to road and rail traffic, as well as to metallurgical activity [9,10].

The concentrations of Mn recorded in the thalli of X. parietina are almost identical to those reported in France [9,24] and Turkey [25]. Approximately 50% of Mn in the air is of natural origin [10,24,37] and to this natural source can be added an anthropic source such as the usage of fertilizers due to agricultural activities [39].

Ni levels are high and there is a gradient of concentration of this element from west to east. The same observations are cited in literature in Italy [16], Turkey [25], France [9,24] and Poland [10]. Nickel pollution is linked to emissions from the metallurgical industry and combustion processes [10,18].

Chromium concentrations in the studied areas are above standard values (4.12 mg/kg) and the same results were observed in other regions such as France [9] and Italy [18,43].

The highest accumulation of Cr was observed in western sites; which then drops in eastern sites with a minimal concentration recorded at Ain Taghrout (127.89 mg/kg). Vehicle emissions and industrial activities can be important sources of air pollution by Ni and Cr [38].

High concentrations of Co in the thalli of X. parietina were observed at all studied locations. Dust from quarrying and building materials can be the main reason for these high concentrations [31] however, the metal industry may be an important source of cobalt [25] as lichenic thalli may accumulate more atmospheric elements when exposed for longer periods of time [29,33].

The classification of the elements by cluster analysis revealed two main clusters of elements with similar affinities or characteristics (Figure 5). Cluster 1, included Pb, Cd, Zn and Sb, three out of the four elements of this group (Pb, Cd and Sb) showed constant or decreased alteration loads in the present study, while Zn showed a high percentage contamination it the studied areas.

derpharmachemica-Cluster-dendrogram

Figure 5: Cluster dendrogram of the elements in X. parietina

A relationship between Cd and Zn is rather common in lichens [16,44-45]. It may be due to anthropogenic sources or metabolic interactions, since these two elements are essential for lichen metabolism [46]. The correlation between Pb and Zn indicates some affinity with atmospheric particles [31,47].

A common feature between Cd and Zn, including the fact that they accumulate in lichen cells [48] and plant emissions are the results of indirect sources of Cd and Zn [25,29]. According to [18], the found concentrations of Zn, Pb and Cd in sites which are far from sources of pollution are related to the usage of fertilizers and pesticides that are characteristic of the region.

Zn is generally related to the association of Pb and Cd elements. This phenomenon is ubiquitous in nature and its distribution in the atmosphere does not locate the source of the contamination [18]. More than 2% of Zn derives from vehicular traffic and of road dust; it is a component found in leaded and lead-free gasoline [10,37,49], confirming the significant accumulation of Zinc in thalli of lichen collected near the roads of the BBA region. 95% of Pb in plants is of atmospheric origin [10] and combustion of fuels remains the main sources of this toxic element in the environment even in mountainous areas [30].

The Sb is an element highly related to Pb in several industrial uses, because it increases the hardness of this element [9,18]. The high coupling of Cd, Zn and Pb and their correlation with Sb also indicate their common sources in traffic activities along road axes [25]. These elements appear in vehicle components and lubricants [39], confirming that the contamination of the BBA region by these elements is of anthropogenic source.

The cluster 2 included Mn, Fe, Cu, Co, Ni and Cr, these relationships are in line with the results of other similar studies [16,50]. All these elements substantially accumulate by particulate entrapment [32,33,51]. Further, the relationship of the two terrigenous macro-elements (Mn and Fe) with Ni and Cr confirmed the presence of anthropogenic influence on their distribution in lichen material. This suggested that trapped soil particulate in lichen thalli was a highly variable contribution which did not closely reflect the element concentrations in the atmosphere, but depended rather on environmental sources [15,51].

Conclusion

The results of the present survey showed that the mean concentration of all ten elements in X. parietina thalli, with the exception of Cd, are included between middle to high naturality classes. Multivariate analyses allowed us to find the main correlations among the groups of element taken into account in the present study. The changes in the concentrations of the MTE, contained in the thalli, can provide useful information on the long-term assessment of air pollution and to monitor the progress of the contamination phenomenon in the time. It is important to focus on the possibility of monitoring a large study area completely lacking an instrumental network for detecting this kind of anthropogenic impact. This confirms that lichen bio-monitoring can be useful in risk assessment for human health and it can be a powerful tool for administrators involved in environmental planning.

References

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