Earthworm coelomocytes as nanoscavenger of ZnO NPs.

Earthworms can 'biotransform' or 'biodegrade' chemical contaminants, rendering them harmless in their bodies, and can bioaccumulate them in their tissues. They 'absorb' the dissolved chemicals through their moist 'body wall' due to the interstitial water and also ingest by 'mouth' while soil passes through the gut. Since the advent of the nanotechnology era, the environmental sink has been continuously receiving engineered nanomaterials as well as their derivatives. Our current understanding of the potential impact of nanomaterials and their natural scavenger is limited. In the present investigation, we studied the cellular uptake of ZnO nanoparticles (NPs) by coelomocytes especially by chloragocytes of Eisenia fetida and their role as nanoscavenger. Results from exposure to 100- and 50-nm ZnO NPs indicate that coelomocytes of the earthworm E. fetida show no significant DNA damage at a dose lower than 3 mg/l and have the potential ability to uptake ZnO NPs from the soil ecosystem and transform them into microparticles.

Background

The coelomic fluid, haemolymph and blood in some phyla (Nemertea, Annelida) of invertebrates play a crucial role in physiological processes, viz., transportation of nutrients, metabolic intermediates and end products, respiratory gases and signalling molecules. These body fluids have a defined composition, containing characteristic cell types which take part in blood coagulation, wound healing and immune response. The cells of invertebrate body fluids are analogous in function with vertebrate blood cells. Therefore, we need to understand the influence of nanoparticles (NPs) and their cytotoxicity and genotoxicity.

In this context, some earlier studies suggested the contribution of coelomocytes to homeostatic regulation, e.g. in blood coagulation immune reactions and in regeneration of lost body parts. Annelids are the first animals in the phylogenetic tree in which not only the cellular but also the humoral immune response is developed. During the cellular immune response, coelomocytes play a role in phagocytosis, inflammatory processes, graft rejection and coagulation of coelomic fluid. During the humoral immune response, they secrete lysozyme, agglutinin, peroxidase, phenoloxidases and antimicrobial factors (fetidin, lysenin, eiseniapore, coelomic cytolytic factor). Cytotoxic molecules may increase the intracellular calcium concentration in target cells, which participate in exocytosis, enzyme function, regulation of gene expression, cell proliferation and apoptosis; therefore, chloragocytes can induce and influence important physiological processes by these signal molecules [1]. Thus, they play a remarkable role in the function of the earthworm immune system and are involved in phagocytosis and the release of lytic factors which are characteristics of innate immunity [2].

Earthworms have pores that connect the coelomic cavity to the exterior, through which cells are extruded following stress. These cells are considered as immune cells (type of leucocytes) that have long been considered to constitute the major innate immune defense system of annelids [3,4]. Coelomocytes from various sources have shown to be capable of phagocytosis and thus perform functions of macrophages. These have natural killer cell features, mediate lytic reactions against several targets and also secrete antimicrobial peptides [5-9]. Valembois et al. [10] classified coelomocytes into three major categories: acidophils, basophils and chloragocytes (chloragogen cells or eleocytes). These cells contain characteristic granules called chloragosomes which are thought to be involved in the protection of cells and organisms against foreign substances [11,12].

Immunity is a vital function to maintain an organism’s well-being and represents a sensitive physiological indicator that may be affected even at low concentrations of nanomaterial exposure. Only a handful of studies exist so far to aid the current understanding of immune responses to nanomaterials in invertebrates, particularly earthworms. This includes the in vitro study on Eisenia fetida exposed to silver nanoparticles (AgNPs) [2] supporting molecular responses observed in vivo[13] and studies on other earthworm species by Vander Ploeg and coworkers where Lumbricus rubellus was exposed to the carbon-based nanoparticle C60 fullerene in vivo (2011) and in vitro (2012). Carbon-based nanomaterials can affect the life history traits of Eisenia veneta[14], E. fetida[15] and L. rubellus[16]. Peterson et al. [17] also reported bioaccumulation of C60 fullerenes in E. fetida and in Lumbriculus variegatus. Cholewa et al. [18] proved the internalizing property of coelomocytes of L. rubellus for polymeric NPs (hydrodynamic diameter of 45 ± 5 mm) apparently involving energy-dependent transport mechanisms (clathrin- and caveolin-mediated endocytosis pathways) [19]. These studies are only indicative of the extent to which nanomaterials may interfere with the function of the earthworm’s immune system.

Manufactured NPs have a wide range of applications, having unique properties as compared with their bulk counterparts [20]. Estimation of the worldwide investment in nanotechnology previews that US$3 trillion will be attained in 2014 [21]. However, there is a growing concern regarding the safety of NPs for their toxicity. Several studies have reported the potential risk to human health from NPs based on evidences of inflammatory reaction by metal-based NPs [22]. Recent studies however suggest that NPs may be released from these products through normal use and then enter in waste water streams [23]. A significant portion of NPs in waste water is expected to partition to sewage sludge [24,25]. Depending on local practices, varying proportions of sewage sludge are disposed of in landfills, incinerated or applied to agricultural lands as biosolids. Therefore, terrestrial ecosystems are expected to be an ultimate sink for a larger portion of NPs [26].

This raises concern about the potential of NPs for ecological effects, entry into the food web and ultimately human exposure by consumption of contaminated agricultural products. Therefore, it is of great interest to determine if intact NPs can be taken up by organisms from soil. Since not much work has been carried out in this direction regarding the uptake of these NPs and to find out the natural scavengers, the present investigation was done to study the influence and cellular uptake of NPs by coelomocytes of the model detritivore E. fetida (Savigny, 1826) by using ZnO NPs (next-generation NPs of biological applications including antimicrobial agents, drug delivery, bioimaging probes and cancer treatment). Our objective was to understand the influence of these NPs on coelomocytes of E. fetida and the underlying mechanisms in order to provide more information on their uptake in the soil ecosystem.

Methods

Experimental animal

Adult earthworms E. fetida (Savigny, 1826) were collected from Vermiculture Research Station, DS College (Dr BRA University), Aligarh, India, and were assimilated in an experimental chamber without light, at low temperature (approximately 24°C), and kept in earthworm beddings. The worms were acclimated for 2 weeks before cell collection following Brousseau et al.[27] with regular feeding.

Extrusion of coelomocytes

Earthworm coelomocytes were collected using a non-invasive method following [28-30]. Briefly, each worm was rinsed in cold water and placed on a paper towel. One fourth of the posterior part was massaged to expel the content of the lower gut. Then, each worm was placed for 3 min in a 15-ml polypropylene tube containing 30 ml of cold extrusion medium [Nacl (71.2 mM), EDTA disodium salt (6.7 mM), GGE (50.4 mM), ethanol (2% v/v) and a supplement of antibiotic and antimycotic agents: penicillin G sodium salt (100 U/ml), streptomycin sulphate (100 μg/ml), amphotericin B (25 mg/ml)]. Ethanol (5%) was added to the extrusion medium immediately before cell extrusion. After 3 min, the worm was removed and the volume was made up to 12 ml by adding ice-cold Ca-free Luria Broth Agar Media containing 1.5 mM NaCl, 4.8 mM KCl, 1.1 mM MgSO4 · 7H2O, 0.45 M KH2PO4, 0.3 mM Na2PO4 · H2O and 4.2 mM NaHCO3 adjusted to pH 7.3 and osmolarity adjusted to 300 mosM [27]. Finally, the cells were re-suspended in Ca-LBSS (containing 3.8 mM CaCl2) and loaded in a culture plate with Dulbecco’s Modified Eagle Medium (DMEM) supplement with foetal bovine serum. The selected choloragocytes were subjected to subculturing.

Viability determination

The cell viability was determined by both trypan blue staining and flow cytometry. In this case, 5 μl of a 1 mg/l propidium iodide solution was added to 500 μl of cell suspension and the fluorescence measured in FL3.

Exposure of ZnO NPs

Chloragocytes were seeded into a 96-well plate at 5 × 105 cells/ml and treated with ZnO NPs (for 3, 6, 12, 24 and 48 h) of diameters 100 and 50 nm (0.5, 1.0, 2.0, 3.0, 4.0 and 5.0 mg/l). ZnO NPs were purchased from Sigma-Aldrich (St. Louis, MO, USA), and their morphology and size were examined by transmission electron microscopy (TEM) at The Energy Research Institute, New Delhi, India.

DNA damage analysis

The Comet assay was performed as described by Singh et al.[31]. Ethidium bromide-stained nuclei were examined with a fluorescent microscope (Leica Microsystems, Wetzlar, Germany). Images were analyzed with the software CASP according to the method of Collins et al.[32] (Figure 1).

Figure 1

DNA damage of coelomocytes (A) in the control and (B) after exposure to 100-nm NPs (3 mg/l).

Statistical analysis

Results are the means of three replicates. Two-way analysis of variance (ANOVA) was performed by using the SPSS 10.5 software.

Results and discussion

The total viability of coelomocytes after exposure to 100-nm ZnO ranged from 6 ± 1.02 to 24 ± 3.12 × 104/ml (Figure 2). At 12 h of exposure, the highest viability of cells was recorded: 6 ± 10.03 × 104/ml, which was consistently the same in all concentrations of exposure. However, at 24 h of exposure, the highest viability (18 ± 2.14 × 104/ml) was recorded at the doses of 0.5 and 1.0 mg/l and the total cell count decreased from 16 ± 2.01 × 104/ml to 14 ± 1.02 × 104/ml at exposure of 2 to 5 mg/l ZnO NPs. This reflects that at high concentration the viability of coelomocytes decreases significantly. Similarly, at 36 h of exposure of up to 1 mg/l, the viability of coelomocytes recorded was 20 ± 2.01 × 104/ml, and this was gradually decreased (14 ± 2.01 × 104/ml) by increasing the concentration of nanoparticles. At 48 h, the number of coelomocytes was similar to that of control (24 ± 2.12 × 104/ml) at 0.5 mg/l but gradually decreased with the increase in the concentration of nanoparticles. Results indicate that the viability of coelomocytes deceases with the increase in the concentration of NPs (100 nm).

Figure 2

Viability of coelomocytes after exposure to ZnO NPs (100 nm) at different intervals.

After exposure to 50-nm ZnO at 12 h, the viability recorded was 6 ± 1.0× 104/ml which was dependent on neither the size nor the concentration of NPs. However, at 24 h, the uptake of NPs triggers cell replication and increases the number of coelomocytes from 10 ± 2.04 × 104/ml to 18 ± 3.12 × 104/ml (Figure 3). However, there was a little trend in the decrease in the number of coelomocytes: 14 ± 1.12 × 104/ml. At 48 h, the highest cell count was recorded at exposure of 0.5 mg/l. There was a gradual decrease in coelomocytes (18 ± 2.08 × 104/ml to 12 ± 1.06 × 104/ml). However, the total viability ranges were between 6 ± 1.02 × 104/ml and 20 ± 3.12 × 104/ml. Results indicate that exposure up to 1 mg/l increases the replication of coelomocytes (Figure 4). Yang et al. [33] also recorded the uptake of NPs which depends on their size and concentration.

Figure 3

Viability of coelomocytes after exposure to ZnO NPs (50 nm) at different intervals.

Figure 4

Total viability of coelomocytes after exposure to ZnO NPs: (A) 100 nm and (B) 50 nm.

Earthworms in general are tolerant to many chemical contaminants including heavy metals and organic pollutants in soil and can bioaccumulate them in their tissue [34]. They absorb the dissolved chemicals through their moist body wall due to the interstitial water and also ‘ingest’ by mouth while the soil passes through the gut. They either ‘biotransform’ or ‘biodegrade’ chemical contaminants, rendering them harmless in their bodies. Satchell [35] suggested that earthworms can uptake chemicals from soil pore water through passive ‘absorption’ of the dissolved fraction through their body wall. Coelomic uptake can also occur as soil is ingested and passed through the coelomic cavity. Earthworms apparently possess a number of mechanisms for uptake, immobilization and excretion of heavy metals and other chemicals. However, the internalization mechanisms and intracellular trafficking of NPs require further study. This study examined the intracellular localization and subsequently the uptake mechanism. After 6 h, the uptake of 50-nm NPs was higher than that of 100-nm NPs. Smaller sized NPs were distributed throughout the whole cell. However, 100-nm NPs were mostly co-localized with endosomes, indicating that the cellular uptake was associated with endosomes. After 12 h of exposure, the cellular uptake of 50-nm NPs was still higher than that of 100-nm NPs while localization of 100-nm NPs decreased and the fluorescence of NPs was dispersed throughout the chloragocyte, suggesting that NPs might escape from endosomes into the cytoplasm or be resorted to other organelles [36]. However, some metals are taken up by earthworms and bound by proteins called ‘metallothioneins’ which have the capacity to bind metals. Ireland and Richards [37] found that cadmium and lead are concentrated in the chloragogen cells of earthworms.

Comet, tail DNA and Olive tail moment (OTM) were chosen to evaluate DNA damage in coelomocytes of E. fetida after exposure to 100- and 50-nm ZnO NPs at 1.0, 3.0 and 5.0 mg/l at different intervals (12, 24, 36 and 48 h). Results are shown in Table 1 and Figures 5, 6, 7 and 8. Coelomocytes exhibited DNA damage when exposed to 100-nm ZnO NPs at 36 and 48 h at the doses of 3.0 and 50 mg/l, while up to 24 h, there was no significant DNA damage. After exposure to 50-nm ZnO NPs at the dose of 3.0 mg/l, coelomocytes showed significant DNA damage at 40 h, and at 5.0 mg/l, significant Olive tail moment of comet was recorded at 36 and 48 h. However, no DNA damage was observed when the exposure dose was 1.0 mg/l for both 100- and 50-nm ZnO NPs. The results of the comet assay have shown clearly that the earthworm coelomocytes experienced DNA damage at exposure of more than 3 mg/l after 24 h. The study corroborates the finding of Bystrzejewska-Piotrowska et al. [38] who observed the capability of earthworms to extract zinc from soil exposed to ZnO nanoparticles. Cholewa et al. [18] demonstrated the capability of internalizing polymeric NPs (hydrodynamic diameter 45 ± 5 nm) by free circulating amoebocytes of the earthworm L. rubellus apparently involving an energy-dependent transport mechanism (clathrin and caveolin-mediated endocytosis pathways). Although NP uptake mechanisms are largely unknown in coelomocytes, uptake probably occurs by macropinocytosis [39]. In mammals, macropinocytosis initiates with cell membrane ruffling via actin rearrangement, suggesting an intriguing possibility of passive uptake of NPs that are membrane-adhered. Amongst invertebrates, ascidian haemocytes are able to engulf particles via RGD motif-dependent macropinocytosis [40]. However, such mechanisms are not yet known in earthworms. Another potential phagocytic pathway is via scavenger receptors that are expressed by both human macrophages and macrophage-like THP-1 cells [39]. Scavenger receptors are a conserved pattern known to bind lipids and polyanions for phagocytosis. In invertebrates, haemocytes from insects [41] and molluscs [42] are known to affect the scavenger receptor-mediated uptake of pathogens and apoptotic cells. To date, scavenger receptors are yet to be identified in earthworms; however, their ubiquitous presence suggests an unequivocally conserved role in innate immune recognition that may be involved in NP uptake as in the vertebrate counterpart. The coelomic fluid of earthworms is sometimes assumed, in the immunological context, to be equivalent to blood plasma in mammals, both representing a protein-rich immune-competent circulatory system. Distinct from the mammalian counterpart is the existence of chloragocytes involved in the regulation of essential minerals, haemoglobins and metallothioneins in response to natural stressors [43]. This is probably by functional analogy with the hepatic/renal systems of vertebrates, and chloragocytes may contribute to regulation of the total protein balance in coelomic fluid.

Table 1

DNA damage after exposure to ZnO NPs on coelomocytes of at different intervals

Serial number	Dose (mg/ml)	Size of NPs (nm)	Time (h)	Head	Tail	Comet	Head DNA	Tail DNA	Tail moment	Olive tail moment
1	0.0	Nil	0	51	52	103	72.62	27.37	14.23	10.27
2	1.0	100	12	50	51	104	72.62	26.43	14.12	10.17
3	1.0	100	24	51	52	103	72.61	27.32	14.13	10.17
4	1.0	100	36	52	53	104	72.51	27.03	14.23	10.23
5	1.0	100	48	51	52	104	72.61	27.31	14.34	11.23
6	1.0	50	12	50	51	104	72.62	26.43	14.12	10.17
7	1.0	50	24	51	52	102	71.12	27.32	14.13	10.17
8	1.0	50	36	52	53	104	72.51	27.03	14.23	10.23
9	1.0	50	48	51	52	104	72.61	27.31	14.34	11.23
10	3.0	100	12	77	56	133	82.5	17.49	9.79	7.79
11	3.0	100	24	111	144	255	85.39	18.62	21.03	12.82
12	3.0	100	36	105	176	281	73.24	26.75	57.04	25.17
13	3.0	100	48	109	116	225	60.67	39.32	45.6	33.83
14	3.0	50	12	83	42	125	89.12	10.87	4.56	4.66
15	3.0	50	24	71	62	133	81.98	18.01	11.17	8.18
16	3.0	50	36	71	74	245	91.25	18.74	6.47	8.23
17	3.0	50	48	75	121	296	57.59	42.41	51.3	27.63
18	5.0	100	12	83	32	115	90.96	9.03	2.89	4.22
19	5.0	100	24	77	52	129	70.83	15.16	15.16	12.64
20	5.0	100	36	129	74	203	83.72	16.27	12.04	14.34
21	5.0	100	48	105	176	281	73.24	26.75	47.09	25.17
22	5.0	50	12	113	87	200	85.8	14.19	12.34	10.42
23	5.0	50	24	115	132	247	80.92	19.07	25.18	16.43
24	5.0	50	36	85	155	240	65.69	34.32	53.17	27.82
25	5.0	50	48	65	135	242	35.69	64.31	86.8	41.53

Figure 5

Comet assay of coelomocytes after exposure to 50-nm ZnO NPs (3 mg/l) at different intervals.

Figure 6

Comet assay of coelomocytes after exposure to 50-nm ZnO NPs (5 mg/l) at different intervals.

Figure 7

Comet assay of coelomocytes after exposure to 100-nm ZnO NPs (5 mg/l) at different intervals.

Figure 8

Comet assay of coelomocytes after exposure to 100-nm ZnO NPs (3 mg/l) at different intervals.

In general, toxicological implications arising from selective cellular uptake of nanomaterials are profound. Metal-based nanomaterials readily dissolve and liberate bioactive metal ions and react with biomolecules (proteins and DNA) of the cellular components in a similar manner as a reactive oxygen species (ROS). NPs and free ions co-exist extracellularly and/or intracellularly, indicating a multitude of stress pathways [33,44]. The intracellular uptake of ZnO NPs is likely to involve subsequent fusion with lysosomes that may accelerate the oxidative dissolution of ZnO NPs as indicated in the present study. This implies that ZnO NPs may have targeted impact on coelomocytes as a result of preferential accumulation and subsequent in situ molecular damages by liberated Zn+ ions [2] at higher concentration. Time course profiling of representative gene expressions, in parallel with flow cytometric analysis of the intracellular ROS level, favours the view that coelomocyte populations are under oxidative stress that can signal-transduce to immune cascades downstream [13]. Recently, coelomocytes were found to recruit calcium for activation [45], and they may possess similar biochemistry to that of calcium and similar signalling to that in higher organisms, linking stress responses to activation of immune systems [46].

Conclusions

In light of our current understanding of nanomaterial uptake, the present investigation was carried out. The phagocyte population of coelomocytes seems to be a susceptible target of nanomaterials. To evaluate the cellular uptake of ZnO NPs by coelomocytes of earthworm in the soil ecosystem, cell viability with comet assay for genotoxicity investigation was observed. The results from these aspects showed the following: (i) Coelomocytes were viable after exposure to 100- and 50-nm ZnO NPs (up to exposure of 5 mg/l). However, there was a decrease in viability when the exposure dose was 3 mg/l particularly at 48 h. (ii) Exposure to 50-nm NPs triggered the replication of coelomocytes which may be due to the high rate of internalization of NPs. (iii) Exposure to 100- and 50-nm ZnO NPs did not show any significant DNA damage up to exposure less than 3 mg/l. (iv) Coelomocytes effectively uptake the 100- and 50-nm ZnO NPs up to 3 mg/l exposure dose within 24 to 36 h without causing any significant DNA damage. The study explicitly implies the NP recognition involved in cellular uptake as well as sub- and inter-cellular events that may uncover further intriguing insights into the earthworm as nanoscavenger.

Competing interests

The authors declare that they have no competing interests.

Authors’ contributions

SG designed the experiment, analysed the data and was involved in drafting the manuscript. TK replicated the experiment and statistically analysed the data. SY gave the final approval for publication. All authors read and approved the final manuscript.