1 Introduction
Arsenic (As), a metalloid element, is widely distributed in the soil environment and As contamination is commonplace (
Kwon et al., 2012). As contamination in soil may cause toxicity in plants and animals (
Pendergrass and Butcher, 2006;
Wang et al., 2018;
Tang et al., 2020). Arsenic content in soils varies (3.5–935 mg As kg soil
–1) in different reports (
Huang et al., 2006;
Liu et al., 2010). Sodium arsenite is an important inorganic arsenicals. It is usually a component of in insecticides and preservatives, and is still extensively used in modern industry (
Mandal and Suzuki, 2002). Arsenite has high affinity for thiol groups in organisms, thus may cause toxic effects (
Oremland and Stolz, 2003).
Earthworms are very important soil fauna, they play an important role in maintaining soul fertility. Earthworms can also take in the soil pollutants via their skin and alimentary canal, and thus they are recognized as indicators of soil ecosystem (
Gong and Perkins, 2016). The physiological and biochemical changes in earthworm body can indirectly reflect the environmental change and now several earthworms have been suggested as sentinels to monitor the terrestrial ecosystem (
Sauve et al., 2002; Ricketts et al., 2004;
Li et al., 2016).
Proteomics mainly studies the functional proteins in the cells, tissues or organisms (
Wang et al., 2010b; Tang et al., 2020). Using proteomics analysis, we can get direct information of the samples at protein level (
Naaby-Hansen et al., 2001). The information obtained provides meaningful and comprehensive results that assist in understanding the impact of a toxin to an organism at a protein level, including how protein interact with one another. These interactions will provide more information than genomic/transcriptomic studies (
Fanous et al., 2008). The proteomic response to arsenite has been studied in a range of cell types and species, including
Klebsiella pneumoniae (
Daware et al., 2012), human lung cells (
Lau et al., 2004), Litopenaeus vannamei (
Ning et al., 2019) and rats (
Wu et al., 2018). However, proteomics research in earthworms lags behind other model species (
Wang et al., 2010b). There is one previous study investigating the effects of roxarsone on the earthworm (
Guo et al., 2015), roxarsone is an organic arsenic, and its toxicity is less than inorganic arsenic. In that study, the author studied only one concentration of the roxarsone, so there is a need to study the toxicity of inorganic arsenic on the earthworm. Data on protein profiling of earthworms following arsenite exposure is still lacking in the research literature. In this study, we use the 2-DE method to analyze the proteomic response in earthworm
Eisenia fetida exposed to As
3+. The objective was to identify the differentially expressed proteins (DEPs) of the earthworm response to arsenite, then explore the underlying mechanism of arsenite toxicity.
2 Materials and methods
2.1 Reagents, soils and animals
Sodium arsenite was purchased from Merck KGaA (Germany). All the reagents used for extracting proteins (Trichloroacetic acid (TCA), dithiothreitol (DTT), iodoacetamide, acetone) were purchased from Sigma-Aldrich (St Louis, MO, USA). Reagents used for 2-DE (lauryl sodium sulfate (SDS), Immobilized pH gradient (IPG) strips (17 cm, linear pH 4–7) and 2-dimensional electrophoresis buffer (2-DE starter Kit) were purchased from Bio-Rad (Hercules, CA, USA). Primary antibodies of Transferrin Receptor (CD71, BM4886), Cytokeratin 8 (CK8, BM4225), Serum Albumin (BSA, BM4963), Dystrophin (DMD, PB0292), Cingulin (21369-1-AP), HSP 70 (BM4335), β-actin (BM0627) and corresponding secondary antibodies were all purchased from Boster Biological Technology (Boster Biological Technology Co., Ltd., Wuhan, China). The other reagents were purchased from Sangon Biotech (Shanghai, China). The solution used in this process was same as
Lu et al. (2018). The Coomassie brilliant blue staining solution were: 0.12% dye, 10% ammonium sulfate, 10% phosphoric acid, and 20% methanol. The decoloring solution was the ultrapure water (18 MΩ.cm).
The soil used in this study was from farm land in Minhang district, Shanghai. The soil properties were represented in
Wang et al. (2018).
Healthy adult earthworms (Eisenia fetida) were used in this experiment. These earthworms (300–500 mg) were purchased from an earthworm farm and kept in the collected soil for two weeks.
2.2 Arsenite exposure experiments
NaAsO2 was added to the prepared soil different As concentration (5, 10, 20, 40, 80 mg As kg–1 dry soil). After aging the soil for one month, the E. fetida were added to the different soil group. Each group has 3 replicates. These groups were kept in the dark at 20±1°C for 60 d. The earthworms were sampled on 60 d. The earthworms were depurated at 20±1°C for 2 d. Proteins for 2-DE were extracted from the freshly depurated earthworms. The earthworms used for western blot were frozen in liquid nitrogen and stored at −80°C until used.
2.3 2-DE electrophoresis
Proteins were extracted using the trichloroacetic acid-Acetone (TCA-A) procedure (
Wu et al., 2013; Lu et al., 2018). IPG strips were rehydrated overnight with 380 μL IEF buffer containing an estimated 1.8 mg protein. The process of IEF and strip balance was outlined by
Lu et al. (2018). The strips were transferred to 10% SDS-PAGE gels for vertical electrophoresis using a Bio-Rad gel system with SDS electrophoresis buffer. The electrophoresis conditions were 120 V for 45 min and then 300 V for 4 h. Each sample we did at least 3 replicates.
2.4 Image analysis
After the 2-DE electrophoresis, the gels were stained by coomassie brilliant blue (G-250) and washed by ultrapure water until the background of the gels was clear. Stained gels were scanned and calibrated with a higher resolution scanner (Bio-Rad, USA). Image analysis was carried out using 2-DE Analysis Software (PDQuest™ Basic- 8.0.1, Bio-Rad, USA). The protein spots were analyzed using the automated software. In this step, we detected and matched the protein spots. The expression of these protein spots was calculated. When the expression of these spots varied more than 2-fold change between untreated group and As treated groups, these protein spots were defined as meaningful protein spots (MPSs). These MPSs were selected for further analysis.
2.5 Protein identification and database search
The MPSs were cut from the gels and analyzed by MALDI TOF/TOF™ Analyzer (ABI, Foster City, CA, USA). The specific process and the database search method is as described by
Lu et al. (2018). Functional characterization of the identified proteins was conducted using the Gene Ontology Tool (http://www.uniprot.org).
2.6 Western blot analysis
To verify whether the identified proteins were truly overexpressed or under expressed in the earthworm, the DEPs with important physiologic function and with major roles in the interaction of the protein network were selected to be measured in earthworm body using western blot. Therefore, transferrin CD71, CK8, BSA, DMD, cingulin and HSP 70 were selected (their functions are described below). The relative fluorescence of CD71, CK8, BSA, DMD, cingulin and HSP 70 compared to β-actin (expressed as relative fluorescence intensity, RFI) was used to assess relative protein expression level.
2.7 Quantitative data analysis
All the protein data were analyzed in SPSS 22.0 (SPSS, Chicago, IL, USA). The protein–protein interaction (PPI) information for DEPs was obtained from the STRING database (http://string-db.org/).
3 Results and discussion
3.1 Identification of differentially expressed proteins (DEPs) related to As3+ stress
After 60 days of exposure to different As3+ contaminated soil and control group, the number of the spots detectable on the 2-DE gels was 1279, 1001, 993, 825, 1018, 1151, respectively (Fig. 1). In these spots, we found most of them did not have significant changes. 36 MPSs were more than 2-fold difference (either increase or decrease) between the control and the As3+ groups of the earthworms. 26 of them were upregulated and 10 of them were downregulated.
These 36 MPSs were analyzed by mass spectrometry (MALDI-TOF/TOF-MS). 24 of them (DEPs) were successfully identified and matched in the database (Table 1). The results of MALDI-TOF/TOF-MS of spot 7601 is shown in Fig. 2. Because the database (NCBI and SwissProt databases) of the earthworm proteome is limited, only 11 protein spots were identified through matching with earthworm protein sequences.
3.2 Distribution of the differentially expressed proteins in the earthworms exposed to different As3+ concentration
The fold change of 24 DEPs under different As3+ concentration can be seen in Fig. 3. The largest number of upregulated DEPs was found in the 10 mg kg–1 group, followed by the 5 mg kg–1 group. While the largest number of downregulated DEPs was found in the 20 mg kg–1 and 80 mg kg–1 groups. The maximum fold change of the upregulated DEPs was found in the 40 mg kg–1 group and reached 50-fold change (spot 8711). Two of the DEPs (6505 and 3306) were new occurrences in the As3+ treated groups.
The protein expression of the 24 DEPs on the 2-DE did not present an obvious correlation with the As3+ concentration except for spot 7601. This spot exhibited a 6-fold upregulation in the 5 mg kg–1 treatment, extending to 7-fold in 10 mg kg–1, 9-fold in 20 mg kg–1, 10-fold in 40 mg kg–1 and 11-fold change in the 80 mg kg–1 treatment groups. At 60 days’ exposure, two proteins (6505 and 3306) occurred in the added As groups, they were upregulated in the groups with different As3+ concentrations, the two proteins were not expressed in the control group.
DEPs were classified based on their function. There were 7 categories, and the proportion of each group is shown in Fig. 4. These DEPs were analyzed by their number and fold changes, different groups of the DEPs were found to have a similar proportion in the two methods. The largest proportion was classified as metabolism. This is similar to previous studies investigating earthworm response to Cd and enrofloxacin exposure (
Zhang et al., 2017;
Lu et al., 2018). The second dominant group was “regulation proteins” and “transport proteins” accounting for 13% of the all DEPs, followed by “cytoskeletal protein,” “stress-related,” “signal transduction” and “predicted and hypothetical proteins” respectively. This result is in line with those found in experiments on
Staphylococcus sp. #NIOSBK35 under the arsenite exposure (
Shah and Damare, 2018).
3.3 Functional analysis of different expressed proteins
3.3.1 Metabolism
In the 24 DEPs, 8 DEPs were grouped into the metabolism category (Table 1), accounting for 1/3. Spot 2104 (CELA3B in Fig. 5; same below) was identified as lumbrokinase-5, chymotrypsin-like elastase family, member 3B, efficient protease with alanine specificity but only little elastolytic activity. Lumbrokinase is an effective enzyme extracted by a method modified from Mihara in 1983 from a Chinese traditional herb (Mihara and Akazawa, 1983; Mihara et al., 1991). In this study, it was associated with only one other spot, CTRL, upregulated in the 5, 10, 20 and 40 mg kg
–1 As group, but downregulated in the 80 mg kg
–1 group. The expression of the spot 2104 reached maximum in the 20 mg kg
–1 group, the fold change times reached 3.2. Lumbrokinase has fibrinolytic activity, and it can prevent blood coagulation in earthworms (
Ge and Lang, 2003).
The spot 3108 (KLKB1) and 1101 (KLKB1) were identified as a fibrinolytic enzyme. The enzyme cleaves the bonds between Lys-Arg and Arg-Ser. In a reciprocal reaction, the fibrinolytic enzyme can active factor XII. The fibrinolytic enzyme release bradykinin from the HMW kininogen. Bradykinin is very important in the renin-angiotensin system. KLKB1 was first found in
Lumbricus rubellus in 1991 (
Mihara et al., 1991). The expression of two spots in this study is different, the spot 3108 was upregulated in all the As treated groups, and the maximum fold change reached 53.4 under the 80 mg kg
–1 group, the minimum is the 20 mg kg
–1 group, where fold change reached 2.5. Conversely, spot 1101 was downregulated in all the As treated groups except the 10 mg kg
–1 group. The expression of spot 1101 reached maximum under the 10 mg kg
–1 group, but the fold change only reached 1.1, while the minimum is in the 80 mg kg
–1 group, where the fold change reached 7.0 compared to the control group.
Spots 4108 and 4004 (CTRL) was identified as a fibrinolytic protease. 4108 was upregulated in all the As treated group, the maximum was found in the 10 mg kg
–1 As treatment, where the fold change reached 10.6, the minimum one was the 40 mg kg
–1 group, where the fold change reached 3.5. The expression of spot 4004 was upregulated in the 5 mg kg
–1 group and 10 mg kg
–1 group, downregulated in the 20, 40 and 80 mg kg
–1 groups. The maximum fold change reached 8.4 under the 80 mg kg
–1 As treatment. In the PPI (Fig. 5), CTRL was associated with two protein spots (CELA3B and ALB). CTRL is an important chemotherapeutic agent, dissolving blood fibrin clots (
Park et al., 1999). The expression of this protease is changed by the environment conditions, such as pressure and temperature (Akazawa et al., 2018). The protein was upregulated under enrofloxacin exposure. These results were in line with those of
Lu et al., (2018), whereby the protein was upregulated under enrofloxacin exposure.
Lumbrokinase (spot 4110, TMPRSS9) presents both kinase activity and serine-type endopeptidase activity. Lumbrokinase can prevent blood coagulation in earthworms (
Ge and Lang, 2003). In all the As
3+ treatments of this experiment, the expression of spot 4110 was all downregulated, the minimum was in the 20 mg kg
–1 group, the fold change here reached 5.9. It was free from correlations with other proteins in the PPI (Fig. 5).
Spot 4307 (2GTL_M) was identified as Chain M which is a component of laminin. It has been demonstrated that the laminins are a family of heterotrimeric glycoproteins present specifically in basement membranes. There is no information on this protein in the STRING database. Laminins have many biological activities, such as the promotion of cell adhesion, migration, neurite outgrowth, tumor metastasis and angiogenesis (
Katagiri et al., 2014). Laminin-2 (formerly merosin) is composed of α2 chain (formerly M chain), α1 chain homolog, β1 and γ1 chains. In this study, this protein was upregulated under exposure of all the As-treatments except the 80 mg kg
–1 group, suggesting As exposure seriously affects the cell growth of
E. fetida. The maximum fold change is in the 10 mg kg
–1 group and reached 8.6.
Actin (spot 6512, ACTG1) is a highly abundant protein in the body. It forms the filaments which make up the cytoskeleton. Actin has an important role in many cellular activities, such as cytoplasmic flow, cell migration, cell division, and muscle contraction (
Ciryam et al., 2013;
Szewczak-Harris and Löwe, 2017). In the present study, actin was upregulated in all the As treatments, the maximum fold change reaching 38.2. This was similar to the results from another study on
E. fetida under 2,2', 4,4-tetrabromodiphenyl ether exposure (
Ji et al., 2013). The function of actin is like GapA. GapA is also essential for the maintenance of basic cellular functions. GapA was also upregulated under the ciprofloxacin exposure in
Escherichia coli (
Ye et al., 2016).
3.3.2 Signal transduction
Three spots (6505, 8608 and 3306, LMNA) were identified as cytoplasmic intermediate filament proteins in Phascolion strombus and intermediate filament gliarin in Hirudo medicinalis, respectively. Spot 6505 and spot 3306 were new expression proteins. Those were no expression under the control group, but under the As treated groups, these proteins were expressed, and these proteins were upregulated under all the As treated groups. Spot 8608 was upregulated in all the As groups except the 80 mg kg–1 group, the maximum fold change reached 8.31 in the 10 mg kg–1 group.
The intermediate filament protein is an important component of the nuclear lamina. The nuclear lamina was in the nucleoplasmic slide of the inner nuclear membrane. The nuclear membrane provides a framework for the nuclear envelope and may also interact with chromatin. This protein plays an important role in nuclear assembly, chromatin organization, nuclear membrane and telomere dynamics. This protein can be found in the
Trichinella spiralis adult worm infected by trichinellosis (
Yang et al., 2015).
3.3.3 Stress-related
The spot 7601(HSPA8) was identified as heat shock protein (HSP). The HSPs are a kind of heat stress protein, they widely exist in bacteria and mammals. Usually the HSPs are not expressed until the cells are stimulated externally such as heavy metals, heat, salinity, and oxidative stress (
Cara et al., 2005). In this experiment, spot 7601 was upregulated in all the As treated groups. The expression of the spot 7601 increased with the As concentration increased, the maximum of the fold change times reached 10.7 in the 80 mg kg
–1 group. In the PPI (Fig. 5), it was correlated with three other spots. This result was similar to the earthworm exposure to enrofloxacin (
Lu et al., 2018) and human lung cells to arsenite (
Lau et al., 2004), whereby this protein was upregulated in response to exposure to the two chemicals, interestingly HSP70 was downregulated in earthworm under Cd exposure (
Zhang et al., 2017), suggesting that maybe the mechanisms employed in response to different heavy metals is varied.
Lumbricine kinase (spot 3404, CKB) has an important activity in ATP binding. This protein has a crucial role in coupling energy production to energy utilization in the body (
Ellington, 2001). In this study, the protein lumbricine kinase was downregulated in all the As treatments, while in other studies such as
Escherichia coli O157:H7 (
Wang et al., 2010a) to cadmium stress, this protein was upregulated. These results are different to this study. In this study, the expression of spot 3404 decreased with the increasing As concentration except in the 40 mg kg
–1 group. The minimum was in the 80 mg kg
–1 group, here the fold change reached 9.4. The reason might be that the different pollutants cause different responses. The process is very complicated in the body. The mechanism is not clear until now.
3.3.4 Transport
Spot 7710 (MFI2) was similar to the transferrin in the tobacco hornworm. Transferrin is an iron carrier protein in serum. The iron can be transported into the cell via receptor-mediated endocytosis (
Andrews and Schmidt, 2007). This protein is an iron binding transport protein which binds the Fe
3+ ion in association with the binding of an anion. Transferrin is required for cell survival and growth, and this protein transferrin as well as L-glutamine, were identified as crucial regulators of ferroptosis, they can induce the life-essential protein cytochrome c pro-death in the intrinsic apoptotic pathway (
Gao et al., 2015). This protein was downregulated in all the As treated groups, the maximum fold change reached 4.35 under the 20 mg kg
–1 group, while the minimum was in the 80 mg kg
–1 group, the fold change time is 1.29. With transferrin downregulated, it is possible that the iron cannot be loaded to the cell and thus the earthworms’ growth may be influenced, this result can be seen in the Table S1.
Spot 8711 (GOLGA5) was similar to the golgin subfamily A member 5 OS in mouse. The GOLGA5 is involved in maintaining Golgi structure, and this protein stimulates the formation of Golgi stacks and ribbons. This protein was upregulated in all the As treated groups except the 5 mg kg–1 group and 40 mg kg–1 group. The expression of spot 8711 was different in the different As concentration, the maximum fold change reached 20.4 under the 40 mg kg–1 group. These two proteins have no interactions with the other proteins in Fig. 5.
Spot 7401 (ALB) was identified as serum albumin in the golden hamster. Serum albumin is the main components of the plasma and the protein has good binding ability to water, Ca
2+, Na
+, K
+, fatty acids, hormones, bilirubin and drugs. The amount of the serum albumins in the circulatory system is very much. Serum albumins is abundant in the circulatory system and mainly participate in binding and transporting endogenous and exogenous ligands (
Zolese et al., 2000). Serum albumin can enhance the apparent solubility of hydrophobic drugs in plasma and modulate their delivery, disposition, efficacy and distribution to cells
in vivo and
in vitro (
Xu et al., 2008; Chaturvedi et al., 2015). Serum albumin is the major zinc transporter in plasma, typically binding about 80% of all plasma zinc. This protein was downregulated in all the As treated groups except the 5 mg kg
–1 group. The maximum fold change reached 9.9 in the 20 mg kg
–1 group. The highest expression was found in the 5 mg kg
–1 group. It was upregulated compared to the control group. The fold change time is 1.2. It was associated with six proteins spots (CTRL, KLKB1, KRT8, DMD, HSPA8 and CKB).
3.3.5 Regulation
Spot 7713 (EFR3A) is similar to the protein EFR3 homolog in Caenorhabditis elegans, which is the component of a complex required to localize phosphatidylinositol 4-kinase (PI4K) to the plasma membrane. This protein is involved in the maintenance and structural degeneration of sensory and motor nervous tissue. The EFR3A was upregulated in all the As treated groups, the maximum fold change was 12.2 in the 20 mg kg–1 As group, the minimum was 4.3 in the 40 mg kg–1 group.
Spot 8701 (FAM184B) showed similarity to a human protein, FAM184B. This protein is involved in the interaction between the microtubules and chromatin. Information on FAM184B is limited, one paper reported that variants within the FAM184B gene were associated with feed intake in cattle (
Lindholm-Perry et al., 2011). This protein was upregulated in all the As treated groups. The expression of spot 8701 reached maximum in the 10 mg kg
–1 group. The minimum was in the 80 mg kg
–1 group. This may suggest that As induced the
FAM184B gene.
Spot 6706 (CGN) was similar to the cingulin in Sorex araneus, this protein plays an important role in the formation and regulation of the tight junction paracellular permeability barrier. The protein CGN was upregulated in all the As treated groups. The expression of the spot 6706 increased with the As concentration except in the 80 mg kg–1 group. The highest was in the 40 mg kg–1 group. The fold change reached 5.0, while the lowest was in the 5 mg kg–1 group.
3.3.6 Other
Spot 7716 (DMD) was identified as dystrophin, and it was associated with three other spots. DMD anchors the extracellular matrix to the cytoskeleton via F-action and DMD is a ligand for dystroglycan. It is reported that the DMD is the component of the dystrophin-associated glycoprotein complex found around the synapses in the nervous system and the neuromuscular junction. The synapses are an important part of information transmission. In the mid-1800s, DMD was first described (
Meryon, 1852). This protein usually found on the cytoplasmic surface of skeletal muscle cell membranes. The protein is absent in Duchenne muscular dystrophy as well as mdx (X-linked muscular dystrophy) (
Bernier et al., 1995). DMD protects the sarcolemma during muscle contraction (
Petrof et al., 1993). DMD plays an important role in myofiber integrity, mainly by interactions with β-dystroglycan and other members of the transmembrane dystrophin-associated protein complex (
Vulin et al., 2014). In this study, this protein was downregulated in all the As treated groups, the maximum fold change reached 7.71.
Spot 8610 (KRT8) showed similarity to keratin, type II cytoskeletal 8 in rat. The combination of KRT8 and KRT19 plays an role in linking the contractile apparatus to dystrophin. This protein was upregulated in the 10, 40, 80 mg kg–1 As treated groups, the maximum fold change reached 7.1 in the 10 mg kg–1 group, suggesting that the arsenite may enhance this protein expression.
Spot 3204 (TMPRSS9) was upregulated in all the As treatments except the 20 mg kg
–1 group, and the highest was in the 80 mg kg
–1 group, fold change reached 7.3. This protein was identified as a lumbrokinase-3 precursor in the database. This protein can degrade the fibrinogen in the blood. This may be related to the formation of the blood clots (
Lu et al., 2018). This result was like those found in earthworms exposed to enrofloxacin (
Lu et al., 2018). This may be indicative that this protein is particularly affected by exposure to hazardous materials in the earthworm.
3.3.7 Predicted and hypothetical proteins
Because the data of the earthworms in the database is limited, spots 7509 and 8606 cannot be found in the database, and they were looked as predicted and hypothetical proteins. They were labeled as ACTG1 and LMNA in Fig. 5, respectively. The two spots were upregulated in all the As treated groups. The maximum change fold of the spot 7509 reached 31 in the 10 mg kg–1 group, while the spot 8606 is 3 under 10 mg kg–1 group.
3.4 Validation of differentially expressed proteins
Western blots were conducted to verify the results of mass spectrometry for six proteins. The expression of BSA (spot 7401) was different compared to the proteomic results, BSA was significantly downregulated in the 20 and 40 mg kg–1 As groups, but in the western blot the results showed that this protein was only significantly downregulated in the 80 mg kg–1 group. The CD71 (spot 7710) expression by western blot was similar to the results by 2-DE, the protein was significantly downregulated in all the As treated groups, in the 2-DE, the 5 and 20 mg kg–1 groups were the minimum, but in the western blot results, the minimum was the 5 mg kg–1 group. The cingulin (spot 6706) expression by western blot was also different compared to the 2-DE results. They were significantly upregulated in all the As treated groups, but in the western blot results, the cingulin was significant upregulated only in the 40 mg kg–1 group. The expressions of CK8 (spot 8610), DMD (spot 7716) and HSP70 (spot 7601) were similar to the 2-DE results. DMD was significantly downregulated in all the As treated groups. HSP70 was upregulated in all the As treated groups. Generally, western blot results were in concordance with the proteomic analyses.
3.5 Protein–protein interactions of the different expressed proteins
We can see the interactions of the DEPs in Fig. 5. The protein–protein interactions (PPI) networks were constructed according to the STRING database. Different color lines indicate types of evidence for interactions between proteins. Usually, the more line present, the greater important the protein. So, in this study, ALB is the most important protein. ALB was identified as serum albumin, regarded as the major lipid binding protein in plasma (
Guo et al., 2009). It is the most abundant carrier protein in blood plasma and plays an important role in determining the absorption, distribution, metabolism and excretion of drugs. ALB was related to 6 other proteins (KLKB1, KRT8, DMD, HSPA8, CK8 and CTRL), followed by DMD and HSPA8 (related to three other proteins). There were also relationships among CELA3B, CTRL, KLKB1, KRT8, DMD, ACTG1, CKB, HSPA8 and ALB. The remaining proteins acted independently. In this study, As
3+ influenced the metabolism, stress-related proteins, this result is like results published by
Zhang et al. (2020). The expression of the protein changed under different As
3+ concentration (
Zhang et al., 2020), the As influenced the liver of the rat, causing the damage of the liver, containing oxidative stress, apoptosis, and inflammation.
4 Conclusion
As we know, this is the first toxicoproteomic analysis of earthworm exposed to As3+. The exposure of As3+ significantly changes the expression of many functional proteins in earthworm. 36 DEPs were found in the gel maps and 24 of them were successfully identified. 79.2% of the DEPs were upregulated compared to the control group. The maximum fold change reached 53.8 in spot 3108 in the 80 mg kg–1 As group. The mechanisms of As3+ toxicity involve metabolism, signal transduction, stress response, transport, and other cellular functions, and gives a starting point for further functional research. The protein–protein interaction between the DEPs indicated that ALB is very important, as it is related to 6 other proteins. Western blot results were in line with the proteomic analyses. This study implies that it is possible to develop techniques to detect heavy metal pollution in soil using earthworms. An important animal in terrestrial ecology, earthworms have potential to be an animal model for the assessment of heavy metal pollution and its environmental risk.