Advanced Techniques in Biology & Medicine

Advanced Techniques in Biology & Medicine
Open Access

ISSN: 2379-1764

Mini Review - (2017) Volume 5, Issue 3

Ecotoxicological Evaluation of Parallelomorphus laevigatus (Coleoptera, Carabidae) as a Useful Bioindicator of Soil Metal Pollution

Erminia Conti*
Department of Biological, Geological and Environmental Sciences, Catania University, Via Androne 81, 95124 Catania, Italy
*Corresponding Author: Erminia Conti, Department of Biological, Geological and Environmental Sciences, Catania University, Via Androne 81, 95124 Catania, Italy, Tel: 390957306019 Email:

Abstract

The importance of carabid beetles in environmental study is reported. Among this group P. laevigatus is a useful bio indicator of metal pollution. The burden of trace elements in animal tissue reflects the contamination level of investigated areas. The alteration of orientation performances by this species put the basis to consider orientation in space of P. laevigatus as a behavioral biomarker for exposure to trace metals contamination.

Keywords: Carabid beetles; Parallelomorphus laevigatus; Trace metals; Environmental assessment; Behavioral biomarker

Among soil invertebrates, the carabid beetles are predators considered useful ecological indicators [1-7]. This is because they play a key role in clarifying the route of contaminants in food webs; in fact, they are both predators of small invertebrates and prey for amphibians, reptiles, birds and small mammals [8].

This taxon is generally considered as poor accumulator of trace elements [9,10]; this is probably due to a series of detoxification enzymes [9,11] of which it is endowed. However, a few studies have shown that physiology of carabid beetles [5,11,12] as well as their susceptibility to additional stressors [13] can be affected by the accumulation of heavy metals.

Among these beetles, Parallelomorphus laevigatus (Fabricius) (homotypic synonym of Scarites (Parallelomorphus) laevigatus Fabricius, 1792) (Figure 1) did reserve a relative few interest from ecological point of view while has never been studied for an ecotoxicological analyses. It is a ground beetle widespread on the Atlantic coasts of the Mediterranean and Morocco and along the Mediterranean basin and the western coast of the Black Sea [14]. This species, living on sandy beaches, occurs in relatively dense populations in Sicily from April to October, while no specimens are visible during winter season. It has a highly precise orientation capacity; if it accidentally falls into the water, caused by waves or wind action (and this can occur whether by day or by night), it is able to float and swim on the sea surface using an effective swimming technique [15] and quickly lands by using a path perpendicular to the shoreline. During daytime, it uses the solar azimuth as an orientation cue (it carries out the chronometric compensation of the apparent motion of the sun using the photoperiod known as “Zeitgeber” [16]. Nocturnal tests have also discovered it has a lunar orientation [17] and is sensitive to the magnetic field [18].

advanced-techniqes-biology-Parallelomorphus-laevigatus

Figure 1: Parallelomorphus laevigatus.

P. laevigatus is particularly active on surface in the evening and in the night in summer [19] peaking after sunset. Conversely, it spends the daylight hours in an individual burrow in the sand near the shoreline. When active, the beetle uses its time hunting mainly Talitrus saltator [19,20].

The progressive depletion of the population size due to human impacts [21] and the narrow habitat have made this species an excellent ecological indicator for sandy coastal environments [22].

The presence of one of largest refining and petrochemicals industries in Western Europe and the Mount Etna (the tallest active volcano in Europe) in the southern part of the Ionian coast of Sicily stimulated to investigate on the bioaccumulation capacity of trace elements in this species. For this investigation, 16 target metals, 11 of which are essential elements for living organisms (Co, Cr, Cu, Fe, Mn, Mo, Ni, Se, Sn, V and Zn) and four of which are toxic (As, Cd, Hg and Pb) were analyzed in adult specimens from four Sicilian locality (Figure 2). The sites were selected according a gradient of trace metal pollution and considering the site D, Vendicari Nature Reserve, located approximately 40 km south of Syracuse, as site control. It has been recognized as a wetland of international importance under the Ramsar Convention of 1971.

advanced-techniqes-biology-Ionian-sandy-coast

Figure 2: Sampling sites on the Ionian sandy coast of Sicily: A (Simeto mouth); B (Agnone Bagni beach); C (Marina di Priolo); D (Vendicari beach).

Our investigation pointed out that animal tissue from control area had the highest values of As, Cd, Cr, Hg, Ni, Pb, Se and Sn, while Fe and Mn were at the lowest values; moreover, the concentration of Hg, Cd and Se in the tissues of P. laevigatus differed among the four sites.

Assessing the possible transfer of each metal through the food chain, we considered the metal burden in P. laevigatus (predator) and in its prey T. saltator. We can affirm that the concentration of As, Cr, Cu, Ni and Se in animal tissue differs in the beetles and in the sandhoppers according to their trophic role inside the ecological net. Differences in concentration for Cd, Co, Fe, Hg and V were correlated to both trophic level and sampling site, while Mn concentration differed among sites in a different way for the prey and predator. Moreover, the transfer trophic coefficient (TTC) (i.e., the ratio of the metal concentration in the beetles to that in their prey) is particularly high (approximately 5) for Hg.

On the best of my knowledge P. laevigatus is the first psammohalophilous species used for ecotoxicological purpose. An interesting first result of this survey is the confirmation of increasing Hg concentrations across the simplified trophic net of sandy beaches and the ability of this pollutant to biomagnificate.

Furthermore, based on the results obtained, the Ionian sandy coast of Sicily can be divided into a northern region (sites A and B), where there is the influence of Mount Etna, and a southern region (sites C and D), where there is the anthropogenic influence. Both conditions can cause metal pollution, however, of these two; the most dangerous seems to be the man-made one.

Many of trace metals measured (i.e., Fe, Mn, V, Zn and Cr) are present in lava soil and volcanic ash, causing sand contamination [23-29]. However, the long-term contribution of heavy metals to the environment by the volcano has allowed living organisms to adequately adapt.

The assessment of the southernmost area is very different. The high values of numerous trace metals detected in beetles right from the control site are mainly due to the emissions sources of the nearby industrial plants; but also the intense agricultural activity in nearby areas certainly contributes, at least for cadmium, very abundant in both prey and predators [30]. Particularly alarming is the very high concentration of Hg in insect tissues from this site; on the other hand, a huge burden of this dangerous metal has already been found in this southern area of eastern Sicily in previous research on both sediments and animal tissues [31-34]. Indeed, various authors (e.g. Sprovieri et al. [32], Di Leonardo et al. [33]) have considered this area to be a mercury point source for the entire Mediterranean Sea.

These first outcomes confirm the possibility to consider P. laevigatus as a useful bioindicator of trace metal contamination in sandy beaches. Further experiments on the alteration of orientation behavior strengthen this hypothesis. Indeed, an investigation on the influence of trace metals (namely Cu, Zn and Hg) intake on the spatial orientation performances of the carabid beetle Parallelomorphus laevigatus [35], showed alteration of the correct directional choices by this insect. Beetles performed a progressive and significant counterclockwise displacement of the angle of orientation and a corresponding progressive reduction in the precision in the directional choices. This recent study also allows considering the orientation in space of P. laevigatus as a behavioral biomarker for exposure to trace metals contamination.

References

  1. den Boer PJ (1977) Dispersal power and survival. Misc Pap Agricultural Wagon 14: 1-190.
  2. Brandmayr P, Zetto T, Pizzolotto R (2005) Carbide beetles for environmental assessment and conservation of biodiversity. APAT, Manuals and Guidelines, pp: 1-240.
  3. Butovsky RO (1997) Heavy metals and carabids (Coleoptera, Carabidae). Agrohimija 11: 78-86.
  4. Butovsky RO, Verhoef SC, Zaitsev AS, van Straalen NM (1999) Heavy metals in different invertebrate groups as related to soil contamination. In: Butovsky RO, Van Straalen NM (Edr.) Pollution-induced changes in soil invertebrate foodwebs. Vrije Universiteit, Amsterdam.
  5. Lagisz M, Laskowski R (2008) Evidence for between-generation effects in carabids exposed to heavy metals pollution. Ecotoxicology 17: 59-66.
  6. Schirmel J, Mantrilla-Conteras J, Gauger D, Blindow I (2015) Carabid beetles as indicators for shrub encroachment in dry grasslands. Ecol Indic 49: 76-82.
  7. Simon E, Harangi S, Baranyai E, Braun M, Fabian I, et al. (2016) Distribution of toxic elements between biotic and abiotic components of terrestrial ecosystem along an urbanization gradient: Soil, leaf litter and ground beetles. Ecol Indic 60: 258-264.
  8. Butovsky RO (2011) Heavy metals in carabids (Coleoptera, Carabidae). ZooKeys 100: 215-222.
  9. Kramarz P (1999) Dynamics of accumulation and decontamination of cadmium and zinc in carnivorous invertebrates. 1. The ground beetle Poecilus cupreus L. Bull Environ Contam Toxicol 63: 531-537.
  10. Heikins A, Peijnenburg WJGM, Hendriks AJ (2001) Bioaccumulation of heavy metals in terrestrial invertebrates. Environ Pollut 113: 385-393.
  11. Stone D, Jepson P, Laskowski R (2002) Trends in detoxification enzymes and heavy metal accumulation in ground beetles (Coleoptera: Carabidae) inhabiting a gradient of pollution. Comp Biochem Physiol C 132: 105-112.
  12. Lagisz M, Kramarz P, Niklińska M (2005) Metal kinetics and respiration rates in F1 generation of carabid beetles (Pterostichus oblongopunctatus F.) originating from metal-contaminated and reference areas. Arch Environ Contam Toxicol 48: 484-489.
  13. Stone D, Jepson P, Kramarz P, Laskowski R (2001) Time to death response in carabid beetles exposed to multiple stressors along a gradient of heavy metal pollution. Environ Pollut 113: 239-244.
  14. Magistretti M (1963) Coleoptera and Carabidae Cicindelidae Apennines Alnwick. Mem Mus Nat St Verona 11: 225-311.
  15. Caltabiano AM, Costa G, Petralia A (1981) Research on insect locomotion. V. Swimming in some species of carbide beetles. Animalia 8: 105-114.
  16. Costa G, Leonardi ME, Petralia A (1982) Research on the orientation of Scarites laevigatus F. (Coleoptera, Carabidae). II. The time direction of time. Animalia 9: 321-343.
  17. Costa G, Leonardi ME, Petralia A (1983) Research on the orientation of Scarites laevigatus F. (Coleoptera, Carabidae). V. Orientation on full moon nights. Animalia 10: 343-357.
  18. Conti E (1994) Orientation in the absence of visual references in psamophilic insects. Ph.D. thesis. Catania Univ, Italy.
  19. Caltabiano AM, Caruso S, Costa G, Di Franco F, Leonardi, ME, et al. (1984) Eco-ethological research on the fauna of the Simeto oceans fauna protection oasis (CT). I. Behavioral Biology of Scarites laevigatus F. (Coleoptera, Carabidae). Boll Acc Gioenia Sci Nat 17: 25-41.
  20. Alicata P, Caruso D, Costa G, Marcellino I, Motta S, et al. (1982) Eco-ethological studies on arthropods of the coastal dunes of Portopalo (Syracuse, Sicily). Quotations on the structure of terrestrial zoocenesis. C.N.R. Rome. 3. Mediterranean environments. I. The sandy shores, pp: 159-183.
  21. Conti E, Costa G, Petralia A, Russo C, Zolfino G (2004) Presence monitoring of Scarites (Parallelomorphus) laevigatus (Coleoptera, Carabidae) in relation to the anthropic impact along some sandy beaches. In: MWWD Collection. Catania 1: 1-7.
  22. Zanella L, Uliana M, Scarton F, Barbieri F, Ratti E (2009) Environmental assessment of some Venetian areniles with dune formation through the specialized coleotterofauna (Insecta, Coleoptera). Boll Mus Civ St Nat Venice 60: 41-88.
  23. Taylor HE, Lichte FG (1980) Chemical composition of Mount St. Helens volcanic ash. Geophys. Res Lett 7: 949-953.
  24. Okamoto T, Kamiyama K, Wachi K (1997) Background levels of heavy metals in Kanagawa prefecture farm soils impacted by volcanic ash from Mt. Fuji. Plant nutrition for sustainable food production and environment. Dev Plant Soil Sci 78: 553-554.
  25. Cimino G, Toscano G (1998). Dissolution of trace metals from lava ash: Influence on the composition of rainwater in the Mount Etna volcanic area. Environ Pollut 99: 389-393.
  26. Toscano G, Caristi C, Cimino G (2008) Sorption of heavy metal from aqueous solution by volcanic ash. C R Chim 11: 765-771.
  27. Ochota P, Prokopowicz A, Kośmider L, Choina M, Stebel A, et al. (2012) Heavy metals in moss samples exposed to the atmospheric dust after eruption of Eyjafjallajökull volcano. Med Srod 15: 21-26.
  28. Baturin GN, Dubinchuk VT, Minnewit TM (2013) Species of graphite, phosphorus and some heavy metals in volcanic ashes. Dokl Earth Sci 451: 770-774.
  29. Orecchio S, Amorello D, Barreca S, Pettignano A (2016) Speciation of vanadium in urban, industrial and volcanic soils by a modified Tessier method. Environ Sci Process Impacts 18: 323-329.
  30. Conti E, Dattilo S, Costa G, Puglisi C (2016) Bioaccumulation of trace elements in the sand hopper Talitrus saltator (Montagu) from the Ionian sandy coasts of Sicily. Ecotoxicol Environ Saf 129: 57-65.
  31. Ausili A, Gabellini M, Cammarata G, Fattorini D, Debenedetti M, et al. (2008) Ecotoxicological and human health risk in a petrochemical district of southern Italy. Mar Environ Res 66: 215-217.
  32. Sprovieri M, Oliveri E, Di Leonardo R, Romano E, Ausili A, et al. (2011) The key role played by the Augusta basin (southern Italy) in the mercury contamination of the Mediterranean Sea J Environ Monit 13: 1753-1760.
  33. Di Leonardo R, Mazzola A, Tramati CD, Vaccaro A, Vizzini S (2014) Highly contaminated areas as sources of pollution for adjoining ecosystems: the case of Augusta Bay (Central Mediterranean). Mar Pollut Bull 89: 417-426.
  34. Longo G, Trovato M, Mazzei V, Ferrante M, Oliveri Conti G (2013) Ligia italica (Isopoda, Oniscidea) as bioindicator of mercury pollution of marine rocky coasts. PLoS ONE 8: 1-10.
  35. Conti E, Dattilo S, Costa G, Puglisi C (2017) Orientation behavior is a good biomarker for trace metal contamination in Parallelomorphus laevigatus (Coleoptera, Carabidae). Environ Sci Pollut Res, pp: 1-9.
Citation: Conti E (2017) Ecotoxicological Evaluation of Parallelomorphus laevigatus (Coleoptera, Carabidae) as a Useful Bioindicator of Soil Metal Pollution. Adv Tech Biol Med 5:228.

Copyright: © 2017 Conti E. This is an open-access article distributed under the terms of the Creative Commons Attribution License, which permits unrestricted use, distribution, and reproduction in any medium, provided the original author and source are credited.
Top