Laura-Jayne A.
Ellis
and
Iseult
Lynch
*
School of Geography, Earth and Environmental Sciences, University of Birmingham, Edgbaston, Birmingham B15 2TT, UK. E-mail: i.lynch@bham.ac.uk
First published on 4th September 2020
Identifying proteins present on the surface of nanomaterials (NMs) incubated with plasma, serum, and cell lysates can offer insights into the biological interactions of the NMs, including uptake and toxicity. Organisms such as Daphnia magna respond to the presence of toxicants by secreting proteins and other biomolecules; we demonstrate that the eco-corona acquired during exposure to NMs can provide similar important insights regarding the mechanistic pathways induced by the NM exposure as part of an ecotoxicity assessment. Using freshly dispersed (pristine) and ‘medium aged’ NMs (as environmental pollutants), differing in core material, size and surface properties, the influence of NM physicochemical characteristics and exposure environment on the protein corona composition and potential for in vivo uptake by the model test species Daphnia magna are investigated. Surface bound protein corona compositions changed between NM type, NM ‘age’ and the environmental medium in which the NMs were incubated, thus changing the NM biological identity and interactions. Proteins identified on the freshly dispersed NM surfaces were largely associated with metabolic damage, DNA damage, mitochondrial breakdown and energy processes, all of which are associated with cytotoxic damage. Significantly fewer proteins were bound to the aged NMs in all medium conditions, compared to the freshly dispersed NMs. Proteins bound only to the aged NMs were involved in calcium ion binding and cell redox homeostasis, indicative of significantly lower toxic responses to the aged NMs. Thus, NM protein corona composition can facilitate detection of organism responses to NM exposure and potentially identification of the molecular initiating events in adverse outcome pathways.
Environmental significanceUnderstanding nanomaterial–biological interactions, and organism responses to the presence of nanomaterials (NMs), is a crucial step in elucidating the environmental safety of NMs and facilitating their regulation. Model organisms were exposed to a variety of pristine and aged silver and titanium NMs in a standard culture medium and two natural water proxies. NMs recovered from the exposure media after 7 days of incubation with Daphnia magna (set-up as per OECD reproductive test) had surface-bound protein coronas which varied between NM type, ageing and medium composition. Compared to the aged NMs, the pristine NMs had the highest numbers of bound proteins relating to metabolic and cytotoxic damage, giving insights into the selectivity of the endogenous pathways triggered by the NMs. This study facilitates a better understanding of how exposure to pristine and aged NMs disrupts biological processes that would otherwise safeguard health, and provides key pointers regarding molecular initiating events for further study and establishment of adverse outcome pathways for NMs in the environment. |
The entry of NMs into organisms and their translocation across biological barriers is particularly important for determining subsequent adverse outcomes. Due to their size and surface reactivity, NM-corona complexes can engage with a range of endogenous processes and potentially reach all tissues and organs.11 As a result, the range of affinities of biomolecules for NM surfaces,12 can change the corona composition as the NM moves from outside to inside cells. Additionally, the corona itself may provide insights into the uptake and translocation pathways utilised by the NMs,13–15 and give insights into the cellular responses following NM exposure.16 In mammalian systems, NMs associate with soluble serum compounds to form surface coronas, which affect the NM interactions in vivo. For example, common proteins identified in the coronas of NMs exposed to blood plasma were linked to lipid translocation, complement activation and ion transport.17 Connections between the NM properties and the corona composition and conformation of adsorbed proteins can provide insights into the biological impacts and interactions of the NMs. For example, protein unfolding related activation of cellular receptors and associated biological signalling pathways involved with the production of inflammation have been induced following fibrinogen binding to specific sizes of poly(acrylic acid)-coated gold NMs.18 Other studies have identified significant protein groups sharing 80% homology from exposure to two differently sized polystyrene particles, suggesting that the surface molecular properties are important when determining NM protein coronas.17 However, these studies all relate to the investigation of protein coronas acquired in human cell lines and blood plasma, with much less known about the role of the coronas acquired in the environment. Additionally, the range of biomolecules available in the environment is much broader, including the aforementioned proteins, as well as polysaccharides, hemicelluloses, lipids, small molecules and more, coming from a range of species.6
Indeed, protein and biomolecule corona relevance in the environment is at an early stage of investigation. For example, in earthworm coelomocytes, lysenin was identified as the major corona protein for silver (Ag) NMs in vitro (Hayashi et al., 2013 (ref. 73)). Gao, Lin19 identified specific proteins (vitellogenin and zona pellucida) in Ag NMs coronas that related to gender differences in the fish plasma in which they were exposed. The research raises the possibility of the Ag NMs being translocated into developing oocytes and the role of NM induced reproductive toxicity. Furthermore, analysis of the corona of titanium dioxide (TiO2) NMs, exposed to sea urchin (P. lividus) immune cells (and cell conditioned medium), found that negatively charged proteins bound preferentially to the NMs. The main proteins identified in the sea urchin cell-conditioned TiO2 NM protein coronas were involved in cellular adhesion and cytoskeletal organization (actin and tubulin).20 Differential secreted proteins related to cell-to-cell signalling were identified in polystyrene NM coronas exposed to Daphnia magna,21 and the acquired protein corona was shown to influence the gut retention, dissolution and toxicity of cerium dioxide and zinc oxide NMs.22
Daphnia magna are considered a perfect ecological test species as they have a complete sequenced genome, which is advantageous for monitoring stress/adaptive changes to their environments;23 they reproduce parthenogenetically, such that disturbing homeostasis leads to compensatory, responsive, and adaptive processes which can be measured by various omics techniques. There is a body of evidence that supports protein functions and their related pathways (expressed by the genome) being evolutionally conserved across species via lineage specific expansions identified by their sequenced genomes.24–27 Therefore, the biochemical properties of such proteins, including their mechanistic pathway involvements, interactions with receptors and cellular responses, have not changed with species evolution.28Daphnia have a complete set of protein sequences (UP000076858) which can easily be mapped to identify specific molecular pathways via their ‘GO’ (gene ontology) terms in the Uniprot database (https://www.uniprot.org/). Furthermore, Daphnia are a keystone species recognised by the Organization for Economic Cooperation and Development (OECD) for use in standard regulatory testing protocols29,30 although having been designed for molecular chemicals these tests require adaption for NMs,31 including the need to consider biomolecule corona formation from secreted biomolecules32 or from the natural organic matter present in typical freshwaters, and how this influences subsequent NM uptake and toxicity.
It was recently shown that the chronic (reproductive) ecotoxicity of Ag and TiO2 NMs to Daphnia magna is dramatically reduced by environmental ageing of the NMs in media of different ionic strengths and natural organic matter contents.33,34 Understanding the different proteins acquired by freshly dispersed (pristine engineered) and aged NMs in different environmentally relevant media, and their biological functions will provide important insights into their mechanisms of NM toxicity. Thus, as part of the overall assessment of the NMs chronic toxicity (Ellis et al., 202033), we characterised the secreted protein coronas that the NMs had acquired after 7 days in contact with Daphnia magna under each of the different medium conditions. The NMs tested were various surface coated Ag and TiO2 NMs in their pristine engineered (freshly dispersed) and 6-months medium-aged forms, to identify medium-specific and ageing-related effects on the composition of the protein coronas acquired in the presence of Daphnia magna. By choosing the 7-day time point, the hypothesis was that the organisms would have responded to the exposure of the NMs, secreting proteins into the medium, which are subsequently adsorbed by the NMs still in solution, thereby evolving their coronas. Additionally, as part of their filter feeding nature, we assume that at least some of the NMs in solution at day 7 will have passed though the daphnia gut, where their coronas would have further evolved due to contact with a different biological environment. By identifying the composition of the proteins adsorbed onto the various pristine and aged NMs coronas, in the different medium conditions, we can learn about the possible endogenous pathways activated by the specific NMs. Comparing the pristine and medium aged variants allows determination of protein binding selectivity and distinction of corona compositions between different NM core speciation and surface coatings. Additionally, we assessed if the water conditions had any influence on the preferential binding of proteins to the surface of the NMs. This was achieved by using 3 chemically differently waters, two of which were environmentally relevant in terms of their ionic strengths and natural organic matter contents, in comparison to the salt-only Daphnia culturing media recommended for use in the OECD standard test guidelines.
Dynamic light scattering (DLS), was used to measure hydrodynamic sizes of the pristine and aged NMs, using a Malvern Nanosizer 5000 (Table S2†). NM samples for transmission electron microscopy (TEM) were prepared by depositing a 20 μL drop of the NM suspension onto a 300 mesh carbon-coated copper TEM grid (Agar Scientific, UK) (Table S2†). A JEOL 1400EX 80 kV Max system was used to image the samples.
Fig. 1 Experimental design showing how the three different water types are incubated for 7 days with the Daphnia (both NM containing and NM free) and the NM ageing process. |
Fig. 2 Schematic diagram of how the samples were prepared and split for protein and corona analysis after the daphnia were incubated with NMs (and NM free-controls) media for 7 days. |
A second set of 25 mL water samples containing NMs were also taken and sent for protein identification by mass spectrometry. Preparation for these samples also involved centrifugation and washing steps at 5200g at 20 °C for 15 minutes (three times) except ultrapure water was used (instead of PBS) keeping the NM pellet at the bottom each time. Importantly, there was no final suspension in the SDS-containing loading buffer used for the PAGE analysis, as SDS causes interference with the mass-spectrometer. The NM pellets were analysed using liquid chromatography tandem mass spectrometry (LC-MS/MS) using an ‘on particle’ digestion technique at the Functional Genomics and Proteomics Laboratories at the University of Birmingham (https://www.birmingham.ac.uk/facilities/genomics/index.aspx), as described in detail in the ESI† section 1.4. An UltiMate 3000 HPLC series (Dionex, Sunnyvale, CA USA) was used for peptide concentration and separation. The MS and MS/MS scans were searched against the Uniprot database (http://www.uniprot.org) using Proteome Discoverer 2.1 (ThermoFisher Scientific). Variable modifications are deamidation (N and Q), oxidation (M) and phosphorylation (S, T and Y). The precursor mass tolerance was 10 ppm and the MS/MS mass tolerance was 0.02 Da. Two missed cleavages were allowed and identified proteins are accepted as a real hit protein with at least two high confidence peptides. The corresponding molecular ‘Go’ functions were identified using http://www.uniprot.org.
A Pierce BCA assay protein kit protein was used to quantify the total protein secreted by the Daphnia into the media.21 A range of dilutions (0–2 mg mL−1) of bovine serum albumin (BSA) of known concentration in triplicate were made using UPW water to create a standard curve (Fig. S1†) using a 96-well plate (Costar). Samples (100 μL each) of the test mediums were put into separate wells in the 96-well plate in triplicate. A 50:1 mixture of reagent A to reagent B was made ensuring enough volume to add 200 μL to each sample in the wells (total volume 300 μL). The 96-well plate was microwaved for 30 seconds alongside a beaker of water to act as a heat sink. The absorbance function set to 560 nm was used to obtain the absorbance of the different reaction wells. Samples of unknown concentration could then be found by inserting the absorbance provided by the plate reader for each of the samples to calculate their protein concentration. Further details are described in the ESI† section 1.4. A complete list of the NMs identified on each NM, pristine and aged, in each medium, including protein identifications, functions, % coverage and accession numbers are located in the Appendix; Workbooks 1–27.
Nanomaterial | Starting concentration (μg L−1) | HH combo | Class V | Class I | ||
---|---|---|---|---|---|---|
Freshly dispersed Ag NM exposure | Aged Ag NM exposure | Freshly dispersed Ag NM exposure | Aged Ag NM exposure | Aged Ag NM exposure | ||
Measured Ag uptake per daphnid (μg L−1) | Measured Ag uptake per daphnid (μg L−1) | Measured Ag uptake per daphnid (μg L−1) | Measured Ag uptake per daphnid (μg L−1) | Measured Ag uptake per daphnid (μg L−1) | ||
Uncoated Ag | 20 | 0.4 ± 0.09 | 0.7 ± 0.01 | 0.6 ± 0.01 | 0.3 ± 0.07 | 1.8 ± 0.04 |
PVP Ag | 20 | 0.7 ± 0.00 | 0.5 ± 0.05 | 0.7 ± 0.01 | 0.3 ± 0.02 | 0.2 ± 0.00 |
Ag2S | 100 | 0.7 ± 0.01 | 0.2 ± 0.03 | 1.3 ± 0.07 | 1 ± 0.03 | 1.2 ± 0.02 |
TiO2 PVP | 5000 | 1.5 ± 0.09 | 1.2 ± 0.21 | 1.5 ± 0.07 | 1.2 ± 0.14 | 0.7 ± 0.03 |
TiO2 uncoated | 5000 | 4.3 ± 0.11 | 1.2 ± 0.08 | 1.8 ±0.10 | 1.4 ± 0.09 | 1.1 ± 0.02 |
Preliminary assessments using PAGE qualitatively identified the presence of proteins on the surface of the NMs (Fig. S3†). Strong bands in the region of 20–100 (kDa), were also confirmed as the most abundant masses of proteins present when analysed by LC-MS (Fig. 3). Proteins identified in this mass region using LC-MS/MS were related to a range of molecular functions including, but not limited to, GTP-binding nuclear proteins, histone proteins, putative ATP synthase subunit alpha, mitochondrial, heat shock 70 kDa protein cognate, all of which are associated with DNA binding, APT energy binding mechanisms and metabolic processes. The complete protein ID datasets are provided in the ESI;† Workbooks 1–27.
Strong bands in the polyacrylamide gel were identified around 100–120 kDa (Fig. S3†), which are associated with (but not limited to) the following proteins identified in specific NMs coronas using a shot-gun proteomic approach (Appendix; Workbooks 1–27); carbamoyl-phosphate synthase large chain (identified in the NM coronas of the pristine TiO2 PVP, pristine Ag2S NMs and pristine bulk Ag all in HH combo medium; aged TiO2 PVP, aged uncoated Ag and aged PVP Ag NMs all in HH combo medium; aged TiO2 PVP and aged PVP Ag NMs in class V water; and aged TiO2 uncoated, aged TiO2 PVP and aged uncoated Ag NMs in class I water), chorion peroxidase (identified in pristine uncoated Ag NMs in HH combo medium; aged Ag2S NMs in HH combo medium; and aged TiO2 uncoated NMs in class V water), ATP-dependent RNA helicase DDX23, (identified in pristine TiO2 PVP NMs in HH combo medium and aged TiO2 PVP NMs in HH combo), putative copper–zinc superoxide dismutase (identified in pristine PVP Ag NMs in HH combo medium; pristine bulk Ag and pristine PVP Ag NMs in class V water), putative ATP-binding cassette sub-family (identified in pristine bulk Ag and pristine Ag2S NMs in HH combo medium; aged uncoated Ag, aged PVP Ag and aged Ag2S NMs in HH combo medium), matrix metalloproteinase 1 (identified in aged TiO2 PVP and aged Ag2S NMs in HH combo medium; pristine bulk Ag in class V water; aged TiO2 uncoated, aged uncoated Ag, aged PVP Ag NMs in class V water and in the control in class V water).
Interestingly, the number of individual identified proteins by LC-MS was always higher for the pristine NMs when compared the aged NMs (Fig. 4). It was also possible to identify differential protein binding patterns, with some proteins binding uniquely to the pristine NMs and some only to the aged NMs. There were also several proteins that were absent entirely from the control populations, indicating that they were secreted by the Daphnia in response to interaction with the NMs. For example (but not limited to), apoptosis-inducing factor 1, a mitochondrial protein was unique to the pristine PVP Ag NM corona in the class V water. The 2-domain haemoglobin protein (involved in heme and oxygen binding), 60S acidic ribosomal protein (ribosome biogenesis), 60S ribosomal L14 (ribosomal protein), creatine kinase U-type, (mitochondrial protein-energy metabolism) nucleoside diphosphate kinase and nucleosome assembly proteins (both ATP binding) were only identified in the coronas of pristine PVP Ag NMs in HH combo and class V water. Adenosine deaminase (catalytic and metal ion binding activity) proteins were identified in the coronas of both the aged PVP and uncoated Ag NMs in the class V water.
Additionally, there were proteins that were only identified once and were unique to the PVP Ag NMs. For example, aldehyde dehydrogenase was unique to the pristine PVP Ag NMs in HH combo media, alpha,alpha-trehalose-phosphate synthase and apoptosis-inducing factor 1 were uniquely associated with the pristine PVP Ag in class V water, and the 2-oxoglutarate dehydrogenase E1 protein (oxoglutarate dehydrogenase and tricarboxylic acid cycling) was unique to the corona of aged PVP Ag NMs in the class V water (Fig. S4†). Similarly, there were proteins unique to the corona of aged TiO2 PVP NMs in HH combo, including the anion exchange protein, and apolipoprotein D, highlighting that different proteins and interaction pathways are triggered by the different NMs, with both core and coating or surface species affecting corona composition. Fig. S5† identifies some of the ancestor pathways associated with the GO terms of these uniquely identified proteins.
Unique proteins were also associated the aged NMs across the different media, including (but not limited to); calmodulin, involved in calcium ion binding (aged Ag2S and aged uncoated Ag NMs in HH combo; pristine uncoated Ag NMs in class V; aged uncoated TiO2, aged TiO2 PVP, aged uncoated Ag, aged PVP Ag and aged Ag2S NMs in class I:), lethal(3)malignant blood neoplasm (aged uncoated TiO2 NMs in class V), lysine-specific histone demethylase 1A (aged uncoated TiO2 in class I), mitotic control dis3 (aged Ag2S in class V; pristine Ag2S and pristine PVP Ag NMs in HH combo), and boundary element associated factor proteins involved in peroxiredoxin activity and cell redox homeostasis (aged PVP Ag NMs in class V).
Common proteins that were secreted in response to NM exposure and identified in all NM coronas (except control secreted proteins) include (but are not limited to) the 40S ribosomal proteins, 60S ribosomal protein L13, actin-alpha skeletal muscle proteins, ADP-ribosylation factor (energy and GTP binding), ATP synthase subunit alpha/beta (ATP binding), copper–zinc superoxide dismutase (lipid transport, metal ion binding and superoxide metabolic processes), c analogous to peritrophins (chitin binding), elongation factor protein (GTP binding), and histone proteins (DNA binding) (Appendix Workbooks 1–27). Actin, a major component of the cytoskeleton (and muscle fibres), is one of the most abundant and highly conserved proteins in eukaryotes and is usually encoded in multiple genes.45,46 Actin was observed in the majority of the NM exposures (except controls) irrespective of medium or NM ageing. As evidenced by the differential and unique number of proteins on the NM surfaces, it is crucial to consider that the same NMs with different surface coatings, aged in different media will have different uptake potentials based on differences in their acquired coronas, the compositions of which are influenced by the ionic strength and NOM concentration in the medium (Table 2). This also demonstrates that NM transformation is a multi-parameter process driven by NM size, surface coating, age and the medium in which the NMs are dispersed prior to and during exposure.
Material | HH combo ‘pristine’ NMs | HH combo ‘aged’ NMs | Class V ‘pristine’ NMs | Class V ‘aged’ NMs | Class I ‘aged’ NMs | ||||||||||
---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
Number of identified proteinsa | Number of identified molecular pathways | Number of molecular pathways unique to the control | Number of identified proteins | Number of identified molecular pathways | Number of molecular pathways unique to the control | Number of identified proteins | Number of identified molecular pathways | Number of molecular pathways unique to the control | Number of identified proteins | Number of identified molecular pathways | Number of molecular pathways unique to the control | Number of identified proteins | Number of identified molecular pathways | Number of molecular pathways unique to the control | |
a Note: the number of proteins includes the total number of proteins identified in the NM coronas. This does not reflect the individual unique number of proteins, but reflects the collective total, including multiple identifications of proteins of the same origin. | |||||||||||||||
Control | 27 | 10 | NA | 27 | 10 | NA | 11 | 8 | NA | 11 | 8 | NA | NA | NA | NA |
Bulk Ag | 27 | 12 | 9 | NA | NA | NA | 21 | 13 | 7 | NA | NA | NA | NA | NA | NA |
Uncoated Ag | 79 | 13 | 8 | 58 | 19 | 15 | 117 | 19 | 13 | 104 | 22 | 16 | 85 | 17 | 14 |
PVP Ag | 223 | 32 | 27 | 35 | 17 | 14 | 246 | 43 | 37 | 81 | 23 | 18 | 54 | 13 | 11 |
Ag2S | 58 | 18 | 14 | 126 | 25 | 19 | 32 | 11 | 6 | 49 | 20 | 15 | 79 | 21 | 16 |
TiO2 uncoated | 35 | 15 | 12 | 12 | 8 | 6 | 15 | 9 | 8 | 108 | 23 | 17 | 101 | 26 | 20 |
TiO2 PVP | 48 | 14 | 11 | 64 | 19 | 14 | NA | NA | NA | 61 | 22 | 16 | 83 | 19 | 17 |
There were also clear differences in the total number of combined surface bound proteins attached to the freshly dispersed and 6-month medium aged NM surfaces after exposure to the daphnids (Table 2). Previous studies have suggested that there are only a few tens of proteins that form a corona around a NM surface when introduced to complex media and environments.7 Interestingly, we were able to identify a total number of 223 surface bound proteins associated with the pristine PVP NMs in HH combo and 246 surface bound protein associated with freshly-dispersed PVP Ag NMs in class V water (Table 2). In most cases, there were higher total numbers of surface bound proteins identified on the freshly-dispersed NM surfaces in the HH combo media than on those that were aged under the same conditions, the exceptions being Ag2S and TiO2 PVP NMs. For the NMs in the class V water the trend was also that the freshly-dispersed NMs had the highest total of surface bound proteins in their corona, compared to their aged counterparts (exceptions; TiO2 uncoated). Explanations for the lower total surface bound proteins on the pristine Ag2S and TiO2 PVP NM in the HH combo media and TiO2 uncoated in the class V water, may be due to particle agglomeration, which is consistent with the size data (Table S2†). Thus, agglomeration reduces the free NM surface area available for protein binding and therefore, reduces the number of proteins identified. For the NMs in the class V water, NOM will competitively bind to the NM surface, also reducing the free surface available for protein binding.47 Agglomeration is driven by the ionic strength of the medium (HH combo) and by the presence of NOM (class V) interacting with the surface of the NMs changing their physicochemical properties.48
Although we did not analyse the NM coronas from NMs that were internalized in the daphnids, the higher number of total surface bound proteins on the pristine NMs corresponds with the increased total bioaccumulated metal concentrations recovered from the whole organisms (Table 1). In comparison, lower metal concentrations were identified in the whole organisms when exposed to the aged NMs. Several possibilities explain the higher internalized concentration of the freshly-dispersed NMs and their higher number of surface proteins. Firstly, freshly-dispersed NMs will have an increased binding affinity, due to higher surface reactivity49,50 particularly in the NOM free HH combo medium. Therefore, once taken up by the Daphnia, the NMs are more likely to concentrate and be retained in the gut by adhesion to the gut epithelium cells (Fig. 5). Moreover, the NMs will have a higher affinity to proteins and vesicles allowing their translocation into other cellular and tissue compartments. By contrast, the aged NMs are less surface reactive, and those aged in the artificial natural waters (class I and V) are likely to have NOM coronas that must be displaced by higher affinity proteins in order to form the protein corona, resulting in less surface bound proteins in the NM coronas.
To confirm cellular translocation, pristine PVP Ag and pristine PVP TiO2 (HH combo medium exposures) were visualised in the gut and in cellular material when imaged under TEM (Fig. 5). There was also a high abundance of proteins related to the cell surface, cytoskeleton, cytosol and lipid transport identified in the corona of the pristine PVP Ag NMs in the HH combo medium exposures, including endocuticle structural glycoprotein SgAbd-2, putative Ccp84Ae and copper–zinc superoxide dismutase proteins. Similarly, the pristine uncoated Ag (HH combo medium exposures), Ag2S (class V exposures), aged TiO2 uncoated TiO2 PVP (class V) NMs also contained these and similar pathway related proteins, suggesting transport of the respective NMs into the cells of the gut epithelium. Additionally, the importin subunit alpha-4 protein, which is responsible for importing proteins into the nucleus was identified in the corona of the pristine PVP Ag NMs in the class V water exposure, further evidencing NM translocation via protein binding in the corona.
Fig. 6 The total number of ‘GO’ molecular pathways uniquely identified compared to the controls for each NM condition. |
Fig. 7 TiO2 NM coronas for each medium condition, showing the associated GO terms relating to biological and molecular pathways for each protein ID. Note, not all the protein IDs are not listed on the Y axis due to character spacing, the figure is intended to give an insight into the most popular GO terms and associated pathways. Some proteins are involved in multiple pathways, and therefore are listed only as their primary GO terms for comparison as described at http://www.uniprot.org. A full list of the protein IDs are located in the ESI† Table S4. |
Fig. 8 The collective Ag NM coronas for each medium condition, showing the associated GO terms relating to biological and molecular pathways for each protein ID. Note, not all the protein IDs are not listed on the Y axis due to character spacing; the figure is intended to give an insight into the most popular GO terms and associated pathways. Some proteins are involved in multiple pathways, and therefore are listed only as their primary GO terms for comparison as described at http://www.uniprot.org. A full list of the protein IDs are located in the ESI† Table S4. Individual Ag NMs and associated GO terms are identified in Fig. S9–S11.† |
The proteins secreted by the unexposed control organisms were mainly associated with pathways involved in general cellular homeostasis, biological and metabolic processes, catalytic activity, molecule function, ion and small molecule binding, all of which are normal organism functions (Table S4 ESI†). By contrast, the unique pathways associated with the proteins secreted by the daphnids in response to all NM exposures and subsequently incorporated into the NM coronas were mainly associated with metabolic activity, DNA damage, mitochondrial break down and energy processes associated with cytotoxic damage.
Proteins involved in DNA binding including DNA-directed RNA polymerase subunit beta, and various histone proteins which were identified in the NM coronas. Histones are central for transcription regulation, DNA repair, DNA replication and chromosomal stability.54 DNA accessibility is regulated via a complex set of post-translational modifications of histones,55 such as histone H1.3, histone H2A, histone H2B, histone H3.2, histone H2B, and histone H4, all of which were identified in high abundance in the all freshly dispersed and aged NM coronas, irrespective of media. Therefore, each of these pathways were mediated by both the pristine and aged NM exposures, since they were not identified in the control media in the absence of NMs (Daphnia secreted proteins only).
We suggest that the Daphnia try to counteract the cytotoxic responses from exposure to the NMs by increasing basic energy metabolism, as evidenced by the amount of secreted proteins incorporated in the NM coronas that are associated with ATP binding pathways compared to the controls (Fig. 7 and 8). As NMs come into contact with the cells, the cell treats the NM as a foreign body by coding for certain proteins involved in the cellular metabolism and defence mechanisms including: chymotrypsin BI, aldehyde dehydrogenase, copper–zinc superoxide dismutase, chorion peroxidase, and putative actin, alpha skeletal muscle proteins,56,57 which were identified in a range of the NM coronas (Appendix; Workbooks 1–27). To protect against cytotoxic damage the daphnids increased protein degradation via carboxypeptidase activity, and increased the regulation of cellular cycles via the activity of cyclin dependant kinase, as observed in the coronas of the NMs associated with the pristine Ag2S in the HH combo medium, aged PVP Ag NMs in the HH combo medium, aged TiO2 PVP in both the HH combo and class I media as examples. Proteins associated with cell cycle regulation were observed in all media irrespective of NM ageing, suggesting that the effects on the daphnids are a general response to NM exposure, since these proteins were not secreted in the NM-free controls.
Furthermore, cysteine synthase (identified in the pristine PVP-coated TiO2 NM coronas in the HH combo) are proteins involved in glutathione synthesis,58 whose expression may have increased as a result of inhibition of homeostasis by the affected Daphnia when exposed to the NMs. Other pathways that were indicative of cytotoxic damage include GTP binging processes (Ras-related protein Rab-11B), and isocitrate dehydrogenase (NADP+) activity, lipid transporter activity, nucleotide binding and oxidoreductase activity, which were all identified in the coronas of the pristine and aged NMs irrespective of the medium (Fig. 7 and 8).
Further evidence of induced stress caused by exposure to the NMs was via the presence of heat-shock proteins which were not observed in the control populations. The intracellular build-up of damaged proteins can lead to proteotoxic stress, resulting in ageing phenotypes due to increased stress.59 Heat-shock proteins provide a molecular defence mechanism against proteotoxic stress, facilitating protein folding and unfolding, which essentially renatures or degrades damaged proteins, to restore normal cellular homoeostasis.45,60 Heat shock proteins were present in high abundance in the NM coronas of both pristine and aged Ag2S, pristine and aged PVP Ag, aged uncoated Ag NMs and pristine bulk Ag in HH combo medium; aged uncoated TiO2, aged TiO2 PVP, aged uncoated Ag, and aged Ag2S NMs in class I water; aged uncoated TiO2, aged TiO2 PVP, aged uncoated Ag and aged PVP Ag NMs, and pristine PVP Ag NMs in class V water, confirming cytotoxic stress. Moreover, this pathway is also involved in the ageing processes as the presence of apolipoprotein D (identified specifically in the corona of aged TiO2 PVP in HH combo medium) was also identified alongside the heat shock proteins and matrix metalloproteinase 1, which is responsible for apoptosis. As it is widely understood, if any living cell is unable to break down/remove the foreign body (in this case the NM) then the cell switches to apoptosis to kill the cell.61 Both the aged and pristine PVP Ag NMs (HH combo exposure) had evidence of lysosomal proteins in their NM coronas, evidencing that signalling pathways for DNA damage and apoptosis were triggered. Further evidence of apoptosis driven by cytotoxic responses to the NMs included the presence of (among others) cytochrome c-2, matrix metalloproteinase 1 proteins and the presence of apolipoprotein D.
Apolipoprotein D (observed in the corona of aged PVP-coated TiO2 NM in the HH combo medium) is also linked to ageing, lipid transport and other developmental processes (Fig. S5†).62 Apolipoprotein D, is part of the lipocalin family which has a high degree of sequence conservation from insects to mammals.62 It is a lipid binding protein whose expression is strongly induced in the mammalian brain during ageing62 and age-dependent neurodegenerative diseases63 such as Alzheimer's disease (AD), where it can play an important function as a neuroprotective and antioxidant protein. Increasing evidence suggests that the gradual increase in free radicals and oxidative stress with age is the primary determinant of ageing.64 The presence of ageing related proteins in the NMs coronas is consistent with the morphological evidence presented previously34,65 that exposure to Ag NMs results in dramatic tail shortening and increased lipid droplets, two phenotypical traits of ageing, suggesting that the NMs induce accelerated ageing in the developing daphnids. Other proteins which have a high degree of species conservation that were linked to lipid transport, antioxidant processes and developmental processes are copper–zinc superoxide dismutase, vascular endothelial growth factor receptor, and S-adenosylmethionine synthase. Copper–zinc superoxide dismutase were found in most of the NM coronas irrespective of NM ageing and media type, and is a highly conserved protein that provides antioxidant processes that counteract ROS. If ROS remains elevated in the cells, it can cause lipid peroxidation, inactivation of enzymes and DNA/protein oxidation.57,66 Fig. S6† describes the main copper–zinc superoxide dismutase molecular and biological pathways. Vascular endothelial growth factor receptor (found in the coronas of aged PVP Ag and aged TiO2 PVP NMs in HH combo) in crustaceans plays a pivotal role in growth, development, cell division and the differentiation of endothelial cells.67 In mammalian cells, inhibition of the vascular endothelial growth factor receptors have been linked to hypotension and cardiovascular disease and such inhibitors have uses in anticancer and antitumor activity therapies.68,69 Fig. S7† shows the binding processes, signalling pathways and receptor activation pathways. Lastly, S-adenosylmethionine synthase is the main methyl donor for DNA, RNA and histone methylation reactions in one-carbon metabolism.70 Metal contaminants have been shown to interrupt the regulation of DNA methylation of the one-carbon cycle, having implications for the fitness of Daphnia.71 Fig. S8† shows the S-adenosylmethionine synthase cycle related biological processes.
Orthologous proteins have the same structure and evolutionary origin (homologous) and the genes that code for these proteins are therefore conserved between species. By identifying the domain architecture in the sequential arrangement along a protein sequence, we can be identify the functional annotation transfer between species.72 Using orthologs of species that have complete mapped genomes it is possible to identify the pathways that have been conserved across species deep in the evolutionary origins in the animal phylogeny.24 When checked against the ancestry ortholog (via OrthoDB at https://www.orthodb.org/) it was possible to find common ancestral genes that are conserved between Daphnia magna and Homo sapiens by identifying the overlapping homologous superfamilies.
For apolipoprotein D, both Homo sapiens and Daphnia magna had matches at InterPro domain at IPR022271, 12674, 02969 and 00566. Similarly, between Daphnia magna and Homo sapiens for copper–zinc superoxide dismutase there were 35% overlaps between the InterPro domain IPR036163 06121 24134 36423 01424 18152 and 30% at InterPro domain IPR036423 24134 01424 18152. For the vascular endothelial growth factor receptor, there were overlaps with the InterPro domain at IPR029034 00072, and for S-adenosylmethionine synthase there were overlaps at InterPro domain at IPR002133 22636 22628 22629 22631 22630 between the two species.
The overall interpretation of this data highlights that the biological and molecular pathways induced are not unique to Daphnia and are in fact shared between a host of species. Although this evidence is based primarily on the identification of specific proteins via linked pathways, the research is still fundamental for identifying the provoked pathways in model non-mammalian species shared between common ancestral phylogeny. This information strengthens the findings from eco-toxicological studies, towards a more general understanding of how exposure to NM pollutants disrupts biological processes that otherwise ensure animal (including human) health. With the increasing move away from animal testing, extraction of increased mechanistic understanding of the toxicity of NMs, and subsequent building of adverse outcome pathways becomes possible. The identification of proteins related to mechanisms of toxicity in the acquired protein coronas on NMs recovered from the exposure waters, especially in the pristine NMs, indicates that NMs may be usefully applied as probes of modes of action in studies with a range of pollutant types, wherein the NMs could be utilised to concentrate low abundance proteins following removal of the test organisms from the solution to ensure no contribution of organism response to the presence of the NMs. Even more importantly, future work should also focus on exploring organism responses at more environmentally realistic concentrations – for example at predicted exposure concentrations, as the data presented here suggest that the NM corona can concentrate and support identification of proteins involved in normal organism function and repair functions.
The proteins secreted by the unexposed control organisms were mainly associated with pathways involved in general cellular homeostasis, biological and metabolic processes, catalytic activity, molecule function, ion and small molecule binding, all of which are normal organism functioning. By contrast, although the aged NMs had significantly less proteins identified in their coronas, the unique pathways associated with the proteins secreted by the daphnids in response to all NM exposures (pristine and aged NMs) were mainly associated with metabolic activity, DNA damage, mitochondrial break down and energy processes associated with cytotoxic damage.
The information presented provides a snapshot in time; the chronic studies themselves continued to day 24 (and beyond in cases where the NMs resulted in reproductive delays), and as such, further studies should include characterisation of the corona at later time points, wherein the effects from the NMs are more diversified. The distinct differences in acquired coronas, and the convergence of pathways activated even with the low-toxic aged NMs, provides important new insights that will be helpful in the establishment of adverse outcome pathways for NMs. Furthermore, the results also demonstrate the risk of over estimating the toxicity of pristine NMs using the current regulatory tests, as in real environments NOM and secreted biomolecules with essentially instantaneously bind to the NMs reducing their surface reactivity and consequent toxicity to aquatic organisms.
Footnote |
† Electronic supplementary information (ESI) available. See DOI: 10.1039/d0en00625d |
This journal is © The Royal Society of Chemistry 2020 |