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Molecular Cloning and mRNA Expression of Heat Shock Protein Genes and Their Response to Cadmium Stress in the Grasshopper Oxya chinensis

Abstract

Heat shock proteins (Hsps) are highly conserved molecular chaperones that are synthesized in response to stress. In this study, we cloned the full-length sequences of the Grp78 (glucose-regulated protein 78), Hsp70, Hsp90, and Hsp40 genes from the Chinese rice grasshopper Oxya chinensis. The full-length cDNA sequences of OcGrp78, OcHsp70, OcHsp90, and OcHsp40 contain open reading frames of 1947, 1920, 2172, and 1042 bp that encode proteins of 649, 640, 724, and 347 amino acids, respectively. Fluorescent real-time quantitative PCR (RT-qPCR) was performed to quantify the relative transcript levels of these Hsp genes in different tissues and developmental stages. The mRNAs encoding these four Hsp genes were present at all developmental stages and in all tissues examined but were expressed at varying levels. Additionally, we investigated the mRNA expression profiles of these four Hsps in O. chinensis subjected to Cadmium (Cd) stress. OcGrp78, OcHsp70, OcHsp90, and OcHsp40 mRNA expression was induced under acute Cd stress; the levels reached a maximum within a short time (6 h), were reduced significantly at 12 h, and were lowered to or below control levels by 48 h. Regarding induction efficiency, OcHsp70 was the most sensitive gene to acute Cd stress. Chronic Cd exposure showed that dietary Cd treatment induced increased OcGrp78, OcHsp90, and OcHsp40 expression. However, dietary Cd induced a significant reduction of OcHsp70 expression. In the period tested, no significant difference in the mortality of the grasshoppers was observed. Our results suggest that these four Hsps genes, especially OcHsp70, are sensitive to acute Cd stress and could be used as molecular markers for toxicology studies. However, our results also indicate that OcHsp70 is not suitable for use as a molecular marker of chronic Cd contamination.

Introduction

Heat shock proteins (Hsps), or stress proteins, are a group of conserved proteins that are synthesized by organisms upon exposure to environmental stressors, including heat shock, radiation, pesticides, metal, and other environmental contaminants. As molecular chaperones, Hsps play an essential role by assisting in the correct folding of proteins to maintain cellular homoeostasis under stress conditions [12]. Hsps can be categorized into five families, which are named according to their molecular weights, conserved sequences, and molecular functions: Hsp100, Hsp90, Hsp70, Hsp60, Hsp40 and the small Hsps [3]. Eukaryotes have multiple Hsp70 family members that are located in the lumen of the endoplasmic reticulum (e.g., glucose-regulated protein 78, Grp78) and in the cytoplasm, including constitutive heat shock cognate 70 protein (Hsc70) and inducible Hsp70 [4]. Hsp gene expression is widely accepted as a suitable molecular indicator of adverse biological effects because Hsps respond to minor environmental stress and are evolutionarily conserved [56]. Therefore, much of the research on cellular responses to metals and other pollutants has focused on Hsps, especially Hsp70 because of its high conservation and sensitivity to stress factors [610].

Cadmium (Cd) is produced as a result of industrial and agricultural processes and is a highly toxic metal to many organisms; therefore, recent research has focused on the toxicology of and the molecular response mechanism to Cd. Cd is best known as a widespread pollutant that can have harmful effects on human health. Cd accumulates through the food chain or respiratory system due to both natural and factitious release into the environment. Metal accumulation can affect many physical and biochemical processes in living organisms, including the effects of Hsp responses to metal [1113].

Oxya chinensis (Orthoptera: Acridoidea) is widely distributed in China and is an important agricultural rice pest. Metals in the agricultural environment can transfer into the bodies of grasshoppers through the food chain. Our previous studies have shown that Cd accumulates in grasshoppers, inducing antioxidant enzyme activity and metallothionein (MT) expression to resist its toxic effects [1417]. However, studies on the effects of Cd in grasshoppers at the molecular level of Hsps have not been reported.

The present study aimed to clone and identify four full-length cDNAs of Hsp genes (Hsp70, Grp78, Hsp90, and Hsp40) from O. chinensis. We then analyzed the expression patterns of these four Hsp genes in different tissues and at different developmental stages. We also investigated the temporal expression profile of Hsp mRNAs in O. chinensis following Cd injection. Finally, we analyzed the mRNA expression patterns of Hsp genes in O. chinensis fed Cd-infected wheat seedlings.

Materials and Methods

Insect and tissue collection

O. chinensis eggs were collected from the area surrounding Jinyang Lake, Shanxi Province, China in October 2011. The eggs were incubated in a growth chamber (MGC-350NR2, Shanghai, China) at 26±1°C and 60% relative humidity (RH) with a 14:10-h light:dark (L:D) photoperiod. After hatching, insects were reared on fresh wheat seedlings. Tissue samples (brain, epidermis, foregut, midgut, gastric caeca, hindgut, Malpighian tubule, and fat body) were collected from 5th instar nymphs. Eggs that had not started hatching and whole bodies of 1st-5th instar nymphs and adults were collected to analyze the stage-specific distribution of Hsp genes at day 3 of each stage. We explicitly confirmed that no specific permissions were required for these locations and activities and that the field studies did not involve endangered or protected species.

RNA isolation, cDNA synthesis, and degenerate PCR

Total RNA was extracted from the samples using TRIzol (Invitrogen, USA) according to the manufacturer’s instructions. cDNA was synthesized by reverse transcription in 25 μL reactions containing 1 μg of total RNA, 40U RNase inhibitor, 1 μL dNTP mixture (10 mM), 1 μL Oligo d(T)18 primer (500 ng μL-1), and PrimeScript reverse transcriptase (TaKaRa, Japan) at 42°C for 1 h. The reaction mixture was stored at -20°C.

Primers were designed using Primer Premier 5.0 based on published sequences in other insects (Table 1). Degenerate PCR was conducted using Taq DNA Polymerase (Tiangen, Beijing, China) with a reaction volume of 25 μL. Fragments were purified using a Gel Extraction Mini Kit (Tiangen, Beijing, China), cloned into the pGEM-T Easy vector (Promega, Madison, WI, USA) and then sequenced.

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Table 1. List of primers used in RT-PCR, RACE-PCR, and real time PCR.

https://doi.org/10.1371/journal.pone.0131244.t001

Rapid amplification of cDNA ends (RACE)

cDNA was synthesized using the SMART RACE cDNA amplification kit (Clontech, USA) according to the manufacturer’s instruction. For amplification of the 3' and 5' end cDNA sequences, the SMART RACE cDNA amplification kit (Clontech) was used according to the manufacturer’s protocol. Amplified products from each reaction were purified using a Gel Mini purification kit (Tiangen), and the isolated amplification products were quantified, subcloned into the pGEM-T Easy vector (Promega) and then sequenced.

Sequence characterization and alignment

Open reading frame (ORF) prediction and cDNA translation into amino acid sequences were performed using the translation tool in ExPaSy (http://www.expasy.org/tools/dna.html). The molecular mass and isoelectric points (pIs) were predicted based on the amino acid sequences. The deduced amino acid sequences of the Hsp genes in O. chinensis (OcHsps) were compared with those Hsp sequences in other insects deposited in GenBank using the ‘BLAST-N’ tools available on the National Center for Biotechnology Information (NCBI) website and GENEDOC software (Nicholas et al., 1997). A phylogenetic tree was constructed by MEGA 5.0 using the neighbor-joining method.

Cd treatment

Acute Cd treatment.

Healthy and uniform 5th instar nymphs were selected for acute Cd treatment. To examine the induction profile of OcHsps at different time points, the nymphs were exposed to Cd for 48 h and sampled at set intervals. A Cd concentration of 2.7 mg·kg-1 was used to avoid increased mortality with prolonged treatment. To examine the induction profile of OcHsps at different Cd concentrations, 5th instar nymphs were exposed to different doses of Cd and sampled after 6 h. The concentrations used were 2.7, 5.4, and 10.8 mg·kg-1; these concentrations can cause approximately 5–10% mortality according to the previously determined LC5 (2.49 mg·kg-1) and LC10 (11.52 mg·kg-1) values at 48 h. Then, 4 μL of Cd solution at the various concentrations was injected into the hemocoel through the membrane between the second and third abdominal segments using a micro syringe. Distilled water was used as a control. Ten insects (5 females and 5 males) were used for gene expression analysis at 0 h, 2 h, 6 h, 12 h, 24 h, and 48 h after injection.

Chronic Cd treatment.

In this experiment, 1st instar nymphs were fed on wheat seedlings cultured with a CdCl2 solution. The Cd2+ concentration in the solution was 20, 40, or 80 mg L-1, and distilled water was used as a control. The Cd2+ concentrations were selected according to a previous study [16]. The Cd concentrations in the wheat seedlings were 0, 2.6±0.3, 6.3±0.8, and 13.4±1.5 mg·kg-1 dry weight with distilled water and 20, 40, and 80 mg L-1 CdCl2 solutions, respectively. Samples were collected from 3-day-old adults. Ten individual adults (5 females and 5 males) were collected per replicate. The samples were immediately frozen in liquid nitrogen and stored at -80°C until used for RNA extraction.

Quantitative real time PCR (qPCR)

A qPCR assay was carried out to examine the Hsp gene mRNA levels; the primers used are shown in Table 1. qPCR was performed using an ABI 7300 real-time PCR detection system (ABI, USA) and Maxima SYBR Green qPCR Master Mix kit (TaKaRa, Dalian, China). The relative Hsp gene mRNA levels were assessed using the following cycling parameters: an initial denaturation at 95°C for 3 min followed by 40 cycles of 95°C for 20 s, 55°C for 20 s and 72°C for 20 s. After PCR, the homogeneity of the PCR product was confirmed by melting curve analysis. β-actin was used as an internal control, and the ratios of Hsps/β-actin mRNA expression were calculated. The fold changes in all experiments were calculated according to the 2-ΔΔCt method [18]. qPCR was repeated three times for each gene. Each replication comprised two technical replicates.

Statistical analysis

Statistical analyses were carried out using SPSS 16.0 software (SPSS Inc., Chicago, IL, USA). The SPSS program was used for the statistical analysis of differences in mRNA expression by analysis of variance (ANOVA). The differences among means were determined using Duncan’s multiple comparison, and the significance level was set at P < 0.05.

Results

Analysis of cDNAs and the deduced amino acid sequences of OcHsps

The cDNA and protein characteristics of four Hsp genes are shown in Table 2. Classical HSP protein signature motifs, including IDLGTYYS (aa 9–16), IFDLGGGTFDVSIL (aa 197–210), and IVLVDDSTRIPKIQA (aa 335–349), were found in OcHsp70. The ATP/GTP-binding site AEAFLGGQ (aa 131–138), the non-organellar consensus motif RARFEEL (aa 300–306), and the conserved cytosolic EEVD motif in the C-terminus were also observed in OcHsp70 (S1 Fig). OcGrp78 also has three signature sequences commonly found in eukaryotic Hsps, including IDLGTTYS (aa 31–38), VFDLGGGTFDVSL (aa 219–231), and IVLVGGSTRIPKVQQ (aa 356–370). The endoplasmic HSP70-specific motif (KDEL) is located at the C-terminus. In addition, a special ATP/GTP binding site, AEAYLGKP (aa 154–161), was found in OcGrp78 (S2 Fig). OcHsp90 contains a conserved MEEVD motif and five characteristic protein sequences of the Hsp90 family, NKEIFLRELISNSSDALDKIR (aa 36–56), LGTIAKSGT (aa 103–111), IGQFGVGFYSAYLVAD (aa 127–142), LKLYVRRVFI (aa 353–362), and GVVDSEDLPLNISRG (aa 379–393) (S3 Fig). OcHsp40 has three distinct regions. The first region is the J-domain (the N-terminal 73 amino acids), which is the most conserved region in these proteins. The second domain (aa 81–125) is referred to as the G/F domain and is rich in glycine and phenylalanine. The third motif is located at the C-terminal end and includes the substrate binding sites of Hsp40 (S4 Fig). The full-length nucleotide sequences and the deduced amino acid sequences are shown in the supporting information, and the characteristic sequences described above are indicated in the figures.

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Table 2. Characteristics of the four Hsps in O. chinensis.

https://doi.org/10.1371/journal.pone.0131244.t002

Phylogenetic relationship of OcHsps with those in other insects

To investigate the relationship of Hsp genes in O. chinensis with those in other insects, a phylogenetic analysis of their deduced protein sequences was performed using the neighbor-joining method and based on their sequences in other insects obtained from GenBank. Fig 1 shows that OcGrp78, OcHsp70, OcHsp90, and OcHsp40 genes belong to the Hsp70, Hsp90, and Hsp40 families, respectively. The amino acid sequences of OcHsp70, OcHsp90, and OcHsp40 are closest to the sequences obtained for Orthoptera insects. The amino acid sequence of OcGrp78 was closest to that of Grp78 in Locust migratoria. Our analysis also placed the Grp78 sequence in a group containing Hsc70-3 from other insects.

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Fig 1. Phylogenetic analysis of O. chinensis Hsps and Hsps from other insects.

Multiple alignment of the sequences used in the analysis was conducted using CLUSTAL W. A neighbor-joining tree construction program (MEGA 5.0) was used for this phylogenetic analysis. Information on the sequences used in this analysis is shown in Table 3.

https://doi.org/10.1371/journal.pone.0131244.g001

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Table 3. A complete list of species used in the phylogenetic analysis and accession numbers for Hsp sequences.

https://doi.org/10.1371/journal.pone.0131244.t003

mRNA expression of OcHsps in tissues not challenged with Cd

OcGrp78, OcHsp70, OcHsp90, and OcHsp40 mRNA expression was examined in several different tissues (Fig 2). ANOVA showed that OcGrp78, OcHsp70, OcHsp90, and OcHsp40 mRNA expression is significantly different in different tissues (OcHsp70, P<0.001; OcGrp78, P = 0.001; OcHsp90, P<0.001; OcHsp40, P<0.001). OcGrp78 expression was highest in the fat body, followed by the Malpighian tubule and midgut, which was 9.13-, 4.1-, and 3.5-fold higher than the brain, respectively. Relatively high OcHsp70 expression was observed in the fat body and brain, followed by the Malpighian tubule and hindgut, whereas the lowest expression was found in the gastric caecum and midgut, which was only 4.3% and 1.9% of the brain expression, respectively. OcHsp90 expression was relatively high in the Malpighian tubule and fat body, was lower in the brain, gastric caecum, hindgut, and midgut, and was lowest in the foregut and epidermis. The order of relative OcHsp40 expression was the Malpighian tubule, followed by the fat body, hindgut, and brain, and then by the foregut, epidermis, gastric caecum and hindgut.

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Fig 2. The tissue expression pattern of O. chinensis Hsps in 5th instar nymphs.

The bars represent the mean ± SE (n = 3) of target gene mRNA expression in different tissues. The small letters on the bars indicate significant differences between tissues (Duncan’s multiple comparison, P< 0.05). BR: brain; EP: epidermis; FG: foregut; GC: gastric caecum; MG: midgut; HG: hindgut; MT: Malpighian tubule; FB: fat body. The mRNA level in the brain was arbitrarily taken as 1.0.

https://doi.org/10.1371/journal.pone.0131244.g002

OcHsps mRNA expression at developmental stages when not challenged with Cd

The mRNA expression of these four Hsps at all developmental stages of O. chinensis is shown in Fig 3. An ANOVA showed that the relative mRNA expression of OcGrp78 was not significantly different (P = 0.09) at the various stages. However, OcHsp70, OcHsp90, and OcHsp40 mRNA expression was significantly different (OcHsp70, P<0.001; OcHsp90, P = 0.017; OcHsp40, P<0.001) at the different developmental stages. The OcHsp70 transcript levels in 3rd and 4th instar nymphs were 11.6 and 11.5 times higher than in the eggs, respectively. Although the relative OcHsp90 and OcHsp40 mRNA levels differed over time, the changes in mRNA levels were similar. The mRNA levels of OcHsp90 and OcHsp40 increased from eggs to 4th instar nymphs but declined in 5th instar nymphs and adults.

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Fig 3. The developmental expression pattern of O. chinensis Hsps in eggs, nymphs and adults.

The bars represent the mean ± SE (n = 3) of target gene mRNA expression at different developmental stages. The different small letters on the bars indicate significant differences between developmental stages (Duncan’s multiple comparison, P< 0.05). EG: eggs; 1st: first instar nymphs; 2nd: second instar nymphs; 3rd: third instar nymphs; 4th: fourth instar nymphs: 5th: fifth instar nymphs; AD: adults. The mRNA level in the eggs was arbitrarily taken as 1.0.

https://doi.org/10.1371/journal.pone.0131244.g003

The effect of acute Cd on OcHsps mRNA expression

As shown in Fig 4, OcHsp70 transcript levels began to increase 2 h after Cd treatment, reaching more than 6.2-fold those of the control at 6 h and followed by a rapid decrease at 24 h. OcGrp78 mRNA levels also reached more than 2.1-fold those of the control at 6 h, but the decrease in OcGrp78 levels occurred less rapidly than that for OcHsp70. OcHsp90 mRNA levels increased up to 4.9-fold those of the control 6 h after treatment. At 12 h, OcHsp90 levels decreased to approximately 2.0-fold those of the control, and these levels were maintained for 48 h. OcHsp40 expression increased to 2.0-fold that of the control until 24 h, followed by a decrease at 48 h. These results show that OcHsp70, OcGrp78, and OcHsp90 (but not OcHsp40) mRNA levels are highest after 6 h of exposure to 2.7 mg·kg-1 Cd.

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Fig 4. mRNA expression of O. chinensis Hsps at different times after acute Cd exposure.

The bars represent the mean ± SE (n = 3) of target gene mRNA expression in 5th instar nymphs 0 h, 2 h, 6 h, 12 h, 24 h and 48 h after the injection of 2.7 mg·kg-1 Cd. The small letters on the bars indicate significant differences between the different treatment times (Duncan’s multiple comparison, P< 0.05). The mRNA level at 0 h was arbitrarily taken as 1.0.

https://doi.org/10.1371/journal.pone.0131244.g004

The above results show that the expression of all the examined Hsp genes, except for OcHsp40, reached their highest levels at 6 h. To evaluate changes in Hsp gene transcript levels with different Cd concentrations, mRNA levels were analyzed by qPCR in control 5th instar nymphs and 5th instar nymphs exposed to different Cd concentrations for 6 h. As shown in Fig 5, OcHsp70 expression was increased to 7.8-, 22.5-, and 23.1-fold that of the control after exposure to the various Cd concentrations. These results suggest that OcHsp70 is induced in a dose-dependent manner. After a 6 h exposure, OcGrp78 was also activated by Cd, but no difference in OcGrp78 mRNA levels was found between the lower Cd concentration (2.7 mg·kg-1) and the middle Cd concentration (5.4 mg·kg-1). However, OcGrp78 transcript levels were increased by 3.8-fold after exposure to the highest Cd concentration (10.8 mg·kg-1) compared with the control. OcHsp90 expression increased after Cd acute exposure, but no significant differences in expression were observed with increasing Cd concentrations. No difference in OcHsp40 expression was observed in the Cd-treated groups relative to the controls.

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Fig 5. mRNA expression of O. chinensis Hsps 6 h after exposure to different Cd concentrations.

The bars represent the mean ± SE (n = 3) of target gene mRNA expression in 5th instar nymphs 6 h after the injection of different Cd concentrations. The small letters on the bars represent significant differences between different Cd concentrations (Duncan’s multiple comparison, P< 0.05). Distilled water was used as a control. The value of the control was arbitrarily taken as 1.0.

https://doi.org/10.1371/journal.pone.0131244.g005

The effect of chronic cadmium exposure on OcHsps mRNA levels

The expression profiles of OcHsp70, OcGrp78, OcHsp90, and OcHsp40 after exposure to Cd for 48 days are shown in Fig 6. In our experiments, no significant numbers of insect deaths were observed for any treatment regimen. OcHsp70 expression significantly decreased following chronic Cd exposure compared with the control; however, no significant differences in OcHsp70 levels were observed among the various Cd concentrations. OcGrp78 mRNA levels first increased and then decreased with increasing Cd concentrations. OcHsp90 expression increased at a lower Cd concentration (2.6 mg·kg-1) and decreased at a higher concentration (6.3 mg·kg-1); however, OcHsp90 expression was equal at the highest Cd concentration (13.4 mg·kg-1) to that at the lowest concentration. OcHsp40 mRNA levels increased at a Cd concentration of 6.3 mg·kg-1, but no significant difference was observed at the 2.6 mg·kg-1 and 13.4 mg·kg-1 Cd concentrations.

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Fig 6. mRNA expression of O. chinensis Hsps after chronic Cd exposure.

Wheat seedlings cultured in distilled water were used as a control. During this experiment, significant numbers of insect deaths did not occur. The bars represent the mean ± SE (n = 3) of target gene mRNA expression after chronic Cd exposure. The small letters on the bars represent significant differences between different Cd concentrations after the insects fed on dietary Cd (Duncan’s multiple comparison, P< 0.05). The value of the control was arbitrarily taken as 1.0.

https://doi.org/10.1371/journal.pone.0131244.g006

Discussion

In this study, four Hsp transcripts, Hsp70, Grp78, Hsp90, and Hsp40, were cloned from O. chinensis. As expected, the typical characteristics of Hsp70 family members were observed in the deduced amino acid sequences of OcHsp70 and OcGrp78. The "EEVD" motif located at the C-terminus of OcHsp70 indicates that this Hsp70 is a cytosolic homolog. The results of previous studies investigating the "GGMP" repeat located at the C-terminus indicate that HSP70 and HSP90 might form a chaperone complex [6]. However, OcHsp70 lacks this "GGMP" tetrapeptide repeat at the C-terminus. OcGrp78 possesses a conserved C-terminal sequence, "KDEL", which functions as an ER localization signal. In addition, the typical motifs of Hsp70 family members were also observed in OcHsp70. The presence of the consensus sequence "MEEVD" indicates that OcHsp90 is a cytosolic homolog [19]. Five Hsp90 family member domains and a conserved motif, "GXXGXG", in the OcHsp90 amino acid sequence suggest that OcHsp90 is functional and belongs to the Hsp90 family. The Hsp40 family has three distinct regions, the J-domain (at the N-terminal, 74 amino acids), the G/F domain, and a third motif at the C-terminal end [1920]. These characteristic domains of Hsp40 family members are found in the N and C-termini of OcHsp40. The conserved "HPD" tripeptide at the DnaJ-N motif is critical for the chaperone function of Hsp40 family members [20].

Phylogenetic analysis suggests that the OcGrp78, OcHsp70, OcHsp90, and OcHsp40 amino acid sequences are closest to those obtained from Orthoptera insects. In the phylogenetic tree, OcGrp78 is closest to Grp78 in L. migratoria; this analysis also placed Grp78 in groups containing Hsc70-3 of other insects. Five different Hsc70 genes exist in Drosophila melanogaster; the encoded proteins are localized in the cytosol (Hsc70-1, Hsc70-2, and Hsc70-4), mitochondria (Hsc70-5), and endoplasmic reticulum (Hsc70-3) and have unique functions [21].OcGrp78 might be a homologous gene of Hsc70-3; this finding has not been previously reported.

We then found that the four Hsp mRNAs are expressed in all tissues examined, possibly because OcGrp78, OcHsp70, OcHsp90, and OcHsp40 are essential for normal physiology and metabolism [2225]. Although these four Hsp genes are found in all of the studied tissues, we observed higher Hsp mRNA levels in the fat body, Malpighian tubule, and brain. This expression pattern was similar to that of the moth Spodoptera litura, in which Hsp70 and Hsp90 expression was highest in the fat body, followed by the cuticle and midgut [26]. However, this mRNA expression pattern differs from other insects such as the flesh fly Sarcophaga crassipalpis [27], Lucilia sericata [28], and Helicoverpa zea [29], in which Hsp70 and Hsp90 expression is higher in the midgut than in other tissues. Our results suggest that the effects of metals on OcHsps are not specific to digestive tissue. Indeed, the higher expression in the brain and detoxification organs (fat body and Malpighian tubule) may reflect a greater ability of these tissues to respond to Cd exposure.

The mRNA expression of the four Hsp genes significantly varied during all developmental stages. OcGrp78 mRNA levels in the eggs and the 3rd instar nymphs did not significantly vary. Our results are consistent with those reported by Gonzalez-Gronow [30]. Previous studies have also illustrated that Grp78 is essential for cell growth and pluripotent cell survival. Developmental regulation of the Hsp70 and Hsp90 genes in various organisms has also been reported [2, 26, 3132]; however, only a few studies have reported on the developmental regulation of Hsp40 in insects. In this study, OcHsp70, OcHsp90 and OcHsp40 expression significantly increased from the eggs to the 4th instar nymphs, which is consistent with findings in L. migratoria [2]. Our results are also similar to those in Manduca sexta, in which Hsp70 mRNA levels tend to increase during the larval period [32]. OcHsp70, OcHsp90, and OcHsp40 gene expression in 5th instar nymphs and adults was lower than that in 3rd and 4th instar nymphs. The expression pattern of OcHsp70 is consistent with that found in Drosophila, in which pupae and adults produce less Hsp70 than do young larvae [33]. Mahroof et al. (2005) reported that a significantly greater amount (33%) of Hsp70 is synthesized in young larvae compared with that in other developmental stages in the red flour beetle Tribolium castaneum [31]. However, Shu et al. (2011) found that the highest Hsp70 and Hsp90 levels were present in adults, with the lowest observed in the 5th instar larvae of Spodoptera litura [26]. These differences in insect Hsp mRNA expression among developmental stages may be related to the physiological features of the various insects. In O. chinensis, eggs with a strong egg sac protect the insect body from stress. Therefore, eggs may have lower Hsp mRNA levels than the instar nymphs and adults.

In addition to metallothionein (MT), Hsps have been suggested as potential biomarkers of metal contamination [26]. Previous studies have indicated that acute or sub-acute Cd can induce Hsp expression in insects [6, 10, 26, 3436]. We found that OcHsp70, OcGrp78, OcHsp90 and OcHsp40 gene expression is induced by acute Cd exposure. Among the various Hsp isoforms, Hsp70 is often the prominent protein expressed under a variety of stress conditions [22, 36]. In the present study, the OcHsp70 gene was also the most sensitive gene under Cd acute exposure; this finding is consistent with previous reports in other insects [6, 36]. Grp78, as an ER chaperone, can be induced by Cd exposure. Organisms can increase the mRNA expression of ER chaperone proteins to improve the protein folding capacity of the ER and to resist ER stress caused by Cd exposure [37]. In our study, acute Cd exposure led to increased OcGrp78 expression. Another possible reasons for the increase in Grp78 expression is that it participates in the protein synthesis and folding process of MT or other related proteins. In Venerupis philippinarum, Hsp40 expression is first elevated and is then downregulated at 48 h in the lowest Cd concentration group [35]. In this study, the same expression pattern was observed for OcHsp40 mRNA. In contrast, in the aquatic midge Chironomus riparius, Hsp40 and Hsp90 gene expression remained unaltered from Cd treatment [36]. However, OcHsp90 expression was induced and reached a maximum level at 6 h. Clearly, changes in Hsp mRNA expression vary by magnitude, species, and duration, based on the level of Cd exposure.

Studies of the effects of chronic Cd exposure on Hsp genes are relatively few. Warchałowska-Śliwaa et al. (2005) found that the grasshopper Tetrix tenuicornis has decreased inducible Hsp70 levels after heavy metal exposure compared with the control [38]. Our results are consistent with this finding. We speculate that Cd accumulation in the body of insects may affect Hsp70 protein synthesis. The decrease of Hsp70 indicates that Hsp70 does not function in a protective role or alternatively, that insects exposed to chronic Cd have adapted to this environment and do not need to synthesize more Hsp70 protein [38]. OcGrp78 expression increased at lower Cd concentrations. Grp78 expression can be induced by intracellular Cd accumulation, and Grp78 may participate in the unfolded protein response (UPR) signaling pathway to address Cd-induced ER stress [39]. We speculate that decreased Grp78 expression may result from the inhibition of protein synthesis at the highest Cd concentration. Gao et al. found a clear dose-dependent Hsp90 expression pattern in the Zhikong scallop Chlamys farreri after Cd exposure (50–200 μg·L-1) for 10–20 days [40]. Hsp90 expression is also induced in the oyster Crassostrea gigas after long-term Cd exposure [34]. In our study, OcHsp90 mRNA expression significantly increased at Cd concentrations of 2.6 mg·kg-1 and 13.4 mg·kg-1; however, OcHsp90 expression decreased after 6.3 mg·kg-1 Cd exposure, which was not completely consistent with previous reports. At the concentration of 6.3 mg·kg-1 Cd, OcHsp40 gene expression was induced. Hsp40 plays an essential role in protein metabolism by regulating the polypeptide binding and release cycle of Hsp70 [19]. The difference in expression pattern of these OcHsps may be due to a compensation effect among the Hsp genes. We speculate that the expression of certain Hsp genes is elevated to compensate for the loss of other Hsp genes under Cd stress.

Supporting Information

S1 Fig. The nucleotide and deduced amino acid sequences of Oxya chinensis Hsp70.

The poly A tail includes one possible polyadenylation signal (AATAA) and two AU-rich elements (ARE:ATTTA). The stop codon is marked with an asterisk. Three signature sequences of the HSP70 family are shown in the blue boxes. An ATP/GTP-binding site (AEAFLGGQ) is shown in the red box. A non-organellar consensus motif (RARFEEL) is shown in the green box. The cytosolic Hsp70 motif (EEVD) of eukaryotic cells is underlined.

https://doi.org/10.1371/journal.pone.0131244.s001

(DOC)

S2 Fig. The nucleotide and deduced amino acid sequences of Oxya chinensis Grp78.

The poly A tail includes one possible polyadenylation signal (AATAA) and two AU-rich elements (ARE:ATTTA). The stop codon is marked with an asterisk. Three signature sequences of the HSP70 family are shown in the blue boxes. An ATP/GTP-binding site (AEAFLGKK) is shown in the red box. A non-organellar consensus motif (RAKFEEL) is shown in the green box. An endoplasmic Hsp70 special motif (KDEL) of eukaryotic cells is underlined.

https://doi.org/10.1371/journal.pone.0131244.s002

(DOC)

S3 Fig. The nucleotide and deduced amino acid sequences of Oxya chinensis Hsp90.

The poly A tail includes one possible polyadenylation signal (AATAA) and two AU-rich elements (ARE:ATTTA). The stop codon is marked with an asterisk. The five highly conserved amino acid segments that characterize all members of the Hsp90 family are shown in the blue boxes. The conserved motif (GXXGXG) is underlined in the blue boxes. The C-terminal pentapeptide MEEVD is underlined.

https://doi.org/10.1371/journal.pone.0131244.s003

(DOC)

S4 Fig. The nucleotide and deduced amino acid sequences of Oxya chinensis Hsp40.

The poly A tail includes three possible polyadenylation signals (AATAA) and three AU-rich elements (ARE: ATTTA). The asterisk indicates the stop codon. Conserved DnaJ-N domain and DnaJ-C motifs are shown in the red and blue boxes, respectively. The HPD tripeptide is underlined in the red box. The G/F domain is shown in the green box.

https://doi.org/10.1371/journal.pone.0131244.s004

(DOC)

Acknowledgments

This work was supported by grant 31071980, 31172161 from National Science Foundation of China. The authors thank Yuying Xi and Baozhen Li for technical assistance with cadmium content measurements.

Author Contributions

Conceived and designed the experiments: YZ EM YG. Performed the experiments: YZ YL. Analyzed the data: YZ YL. Contributed reagents/materials/analysis tools: YZ JZ EM. Wrote the paper: YZ YL.

References

  1. 1. Feder ME, Hofmann GE (1999) Heat shock proteins, molecular chaperones, and the stress response: evolutionary and ecological physiology. Annu Rev Physiol 61: 243–282. pmid:10099689
  2. 2. Wang HS, Wang XH, Zhou CS, Huang LH, Zhang SF, Guo W, et al. (2007) cDNA cloning of heat shock proteins and their expression in the two phases of the migratory locust. Insect Biochem Mol Biology 16: 207–219.
  3. 3. Sørensen JG, Kristensen TN, Loeschcke V (2003) The evolutionary and ecological role of heat shock proteins. Ecol Lett 6: 1025–1037.
  4. 4. Hung JJ, Cheng TJ, Chang MD, Chen KD, Huang HL, Lai YK, (1998) Involvement of heat shock elements and basal transcription elements in the differential induction of the 70-kDa heat shock protein and its cognate by cadmium chloride in 9L rat brain tumor cells. J Cell Biochem 71: 21–35. pmid:9736451
  5. 5. Yoshimi T, Minowa K, Karouna-Renier NK, Watanabe C, Sugaya Y, Miura T (2002) Activation of a stress-induced gene by insecticides in the midge, Chironomus yoshimatsui. J Biochem Mol Toxicol 16: 10–17. pmid:11857772
  6. 6. Morales M, Planelló R, Martínez-Paz P, Herrero O, Corté E, Martínz-Guitarte JL,et al. (2011) Characterization of Hsp70 gene in Chironomus riparius: Expression in response to endocrine disrupting pollutants as a marker of ecotoxicological stress. Comp Biochem Physiol C: Toxicol Pharmacol 153: 150–158.
  7. 7. Boone AN, Vijayan Mathilakath M (2002) Constitutive heat shock protein 70 (GRP78) expression in rainbow Trout hepatocytes: effect of heat shock and heavy metal exposure. Comp Biochem Physiol C: Toxicol Pharmacol 132: 223–233.
  8. 8. Karouna-Renier NK, Rao KR (2009) An inducible HSP70 gene from the midge Chironomus dilutus: characterization and transcription profile under environmental stress. Insect Mol Biol 18: 87–96. pmid:19196349
  9. 9. Schill RO, Görlitz H, Köhler HR (2003) Laboratory simulation of a mining accident: acute toxicity, hsc/hsp70 response, and recovery from stress in Gammarus fossarum (Crustacea, Amphipoda) exposed to a pulse of cadmium. BioMetals 16: 391–401. pmid:12680701
  10. 10. Yoshimia T, Odagiria K, Hiroshigea Y, Yokoborib S, Takahashia Y, Sugava Y, et al. (2009) Induction profile of HSP70-cognate genes by environmental pollutants in Chironomidae. Environ Toxicol Pharmacol 28: 294–301. pmid:21784019
  11. 11. Henson MC, Chedrese PJ (2004) Endocrine disruption by cadmium, a common environmental toxicant with paradoxical effects on reproduction. Exp Biol Med 229: 383–392.
  12. 12. Yalin S, Comelekoglu U, Bagis S, Sahin NO, Ogenler O, Hatunqil R. (2006) Acute effect of single dosecadmium treatment on lipid peroxidation and antioxidant enzymes in ovariectomized rats. Ecotox Environ Saf 65: 140–144.
  13. 13. Thompson J, Bannigan J (2008) Cadmium: toxic effects on the reproductive system and the embryo. Reprod Toxicol 25: 304–315. pmid:18367374
  14. 14. Wu HH, Yan HP, Sun G, Guo YP, Zhang XM, Xi YY, et al. (2009) Comparisons of cadmium and lead concentrations and antioxidant enzyme activity in different body segments of Oxya chinensis. J Agro Environ Sci 28: 471–475.
  15. 15. Li LJ, Guo YP, Wu WL, Wang Y, Ma EB (2010) Toxic effects of Cd2+ on protective enzyme systems in different developing stage of Oxya chinensis (Orthoptera: Acridoidae). J Agro Environ Sci 29: 1448–1454.
  16. 16. Zhang YP, Sun G, Yang ML, Wu HH, Zhang JZ, Song SJ, et al. (2011) Chronic Accumulation of Cadmium and Its Effects on Antioxidant Enzymes and Malondialdehyde in Oxya chinensis (Orthoptera: Acridoidea). Ecotoxicol Environ Saf 74: 1355–1362. pmid:21435721
  17. 17. Liu YM, Wu HH, Kou LH, Liu XJ, Zhang JZ, Guo YP, et al. (2014) Metallothionein genes in Oxya chinensis: molecular characteristics, expression patterns and roles in heavy metal stress. Plos One 9: e112759. pmid:25391131
  18. 18. Livak KJ, Schmittgen TD (2001) Analysis of relative gene expression data using real-time quantitative PCR and the 2-ΔΔCt method. Methods 25: 402–408. pmid:11846609
  19. 19. Wang HH, Lei ZR (2005) Current Developments of Heat Shock Proteins in Insect. Sci Agri Sinica 38: 2023–2034.
  20. 20. Ramos CHI, Oliveira CLP, Fan CY, Torriani IL, Cyr DM (2008) Conserved central domains control the quaternary structure of type I and type II Hsp40 molecular chaperones. J Mol Biol 383: 155–166. pmid:18723025
  21. 21. Gupta SC, Sharma A, Mishra M, Mishra RK, Chowdhuri DK (2010) Heat shock proteins in toxicology: How close and how far? Life Sci 86: 377–384. pmid:20060844
  22. 22. Zhao L, Ackerman SL (2006) Endoplasmic reticulum stress in health and disease. Curr Opin Cell Biol 18: 444–445. pmid:16781856
  23. 23. Vollmer S, Haan C, Behrmann I (2010) Oncostatin M up-regulates the ER chaperone Grp78/BiP in liver cells. Biochem Pharmacol 80: 2066–2073. pmid:20650266
  24. 24. Kwonga RWM, Andresb JA, Niyogib S (2011) Effects of dietary cadmium exposure on tissue-specific cadmium accumulation, iron status and expression of iron-handling and stress-inducible genes in rainbow trout: Influence of elevated dietary iron. Aquat Toxicol 102: 1–9. pmid:21371606
  25. 25. Li J, Soroka J, Buchner J (2012) The Hsp90 chaperone machinery: Conformational dynamics and regulation by co-chaperones. Biochim Biophys Acta 1823: 624–635. pmid:21951723
  26. 26. Shu YH, Du Y, Wang JW (2011) Molecular characterization and expression patterns of Spodoptera litura heat shock protein 70/90, and their response to zinc stress. Comp Biochem Physiol A: Physiol 158: 102–110.
  27. 27. Denlinger DL, Rinehart JP, Yocum GD (2001) Stress proteins: a role in insect diapause? In: Denlinger DL, Giebultowicz JM, Saunders DS (Eds.), Insect Timing: Circadian Rhythmicity to Seasonality. Elsevier, Amsterdam, pp: 155–171.
  28. 28. Tachibana S, Numata H, Goto SG (2005) Gene expression of heat shock proteins (Hsp23, Hsp70, and Hsp90) during and after larval diapause in the blow fly Lucilia sericata. J Insect Physiol 51: 641–647. pmid:15993128
  29. 29. Zhang Q, Denlinger DL (2010) Molecular characterization of heat shock protein 90, 70 and 70 cognate cDNAs and their expression patterns during thermal stress and pupal diapause in the corn earworm. J Insect Physiol 56: 138–150. pmid:19782689
  30. 30. Gonzalez-Gronow M, Selim MA, Papalas J, Pizzo SV (2009) GRP78: a multifunctional receptor on the cell surface. Antioxid Redox Signal 11: 2299–2306. pmid:19331544
  31. 31. Mahroof R, Zhu KY, Lisa N, Bhadriraju S, Bai JF (2005) Expression patterns of three heat shock protein 70 genes among developmental stages of the red flour beetle, Tribolium castaneum (Coleoptera: Tenebrionidae), Comp Biochem Physiol A: Physiol 141: 247–256.
  32. 32. Rybczynski R, Gilbert LI (1995) Prothoracicotropic hormone-regulated expression of a hsp 70 cognate protein in the insect prothoracic gland. Mol Cell Endocrinol 115: 73–85. pmid:8674867
  33. 33. Krebs RA, Feder ME (1998) Hsp70 and larval thermotolerance in Drosophila melanogaster: how much is enough and when is more too much. J Insect Physiol 44: 1091–1101. pmid:12770408
  34. 34. Choi YK, Jo PG, Choi CY (2008) Cadmium affects the expression of heat shock protein 90 and metallothionein mRNA in the Pacific oyster, Crassostrea gigas. Comp Biochem Physiol C: Toxicol Pharmacol 147: 286–292.
  35. 35. Li CH, Li LY, Liu F, Ning XX, Chen AQ, Zhang LB, et al. (2011) Alternation of Venerupis philippinarum Hsp40 gene expression in response to pathogen challenge and heavy metal exposure. Fish Shellfish Immunol 30: 447–450. pmid:21056105
  36. 36. Planelló R, Martínez-Guitarte JL, Morcillo G (2010) Effect of acute exposure to cadmium on the expression of heat-shock and hormone-nuclear receptor genes in the aquatic midge Chironomus riparius. Sci Total Environ 408: 1598–1603. pmid:20089296
  37. 37. Ni M, Lee AS (2007) ER chaperones in mammalian development and human diseases. FEBS Lett 581: 3641–3651. pmid:17481612
  38. 38. Warcha owska-Śliwaa E, Niklińskab M, Görlichc A, Pyza E (2005) Heavy metal accumulation, heat shock protein expression and cytogenetic changes in Tetrix tenuicornis (L.) (Tetrigidae, Orthoptera) from polluted areas. Environ Pollut 133: 373–381. pmid:15519468
  39. 39. Yokouchi M (2007) Atypical bidirectional regulation of cadmium-induced apoptosis via distinct signaling of unfolded protein response. Cell Death Differ 14: 1467–1474. pmid:17464326
  40. 40. Gao Q, Song LS, Ni DJ, Zhang H, Chang YQ (2007) cDNA cloning and mRNA expression of heat shock protein 90 gene in the haemocytes of Zhikong scallop Chlamys farreri. Comp Biochem Physiol B: Biochem Mol Biol 147: 704–715.