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Nandanpawar P. C, Rather M. A, Badhe M. R, Sharma R. Assessment of DNA Damage During Gene Delivery in Freshwater Prawn by Chitosan Reduced Gold Nanoparticles. Orient J Chem 2018;34(2).
Manuscript received on : 16 February 2018
Manuscript accepted on : 20 March 2018
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Assessment of DNA Damage During Gene Delivery in Freshwater Prawn by Chitosan Reduced Gold Nanoparticles

Priyanka C. Nandanpawar1, Mohd Ashraf Rather2, Mohan Ramesh Badhe1 and Rupam Sharma1

1Fish Genetics and Biotechnology Central Institute of Fisheries Education Panch Marg, Versova Mumbai – 400061, India.

2College of Fisheries shirgaon, Ratnagiri-India.

Corresponding Author E-mail: mashraf38@gmail.com

DOI : http://dx.doi.org/10.13005/bbra/2606

ABSTRACT: The increasing application of nanoparticles both in industries and in agricultural fields has led to its accumulation in the aquatic ecosystem through water run-off. Insights into the validity of safer nanoparticles such as gold and chitosan are fairly established. However, its effect on aquatic invertebrates has been less studied. The  present  study  was  aimed  to  study  effects  of  chitosan reduced gold nanoparticles (CRGNPs) during green fluorescent  protein (GFP) encoding plasmid delivery in giant freshwater prawn, macrobrachium rosenbergii. The mean particle size and zeta potential CRGNPs was 33.7 nm and 24.79 mV respectively. Prawn juveniles were  exposed to nanoparticles concentrations (10 µg/L, 20 µg/L) of CRGNPs by immersion treatment for a period of 36 hours. GFP was ubiquitously expressed in muscle tissues of prawns. The comet assay indicated dose dependent genotoxicity of CRGNPs in  gill, pleopod and muscle tissues which  was  in  conformity  with  its  bioaccumulation  pattern  in  vivo. The  highest  bioaccumulation of CRGNPs was found in Gills, followed by pleopods and least in muscles. Hence, the toxicological potential of CRGNPs to the environment cannot be denied and demands more research on the particular aspect. The doses standardized in the present study would be helpful in safer nano-gene delivery in aquatic invertebrates and development of transgenics employing less cost.

KEYWORDS: Bioaccumulation; Comet Assay Gold Genotoxicity; GFP; Nanoparticles;

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Nandanpawar P. C, Rather M. A, Badhe M. R, Sharma R. Assessment of DNA Damage During Gene Delivery in Freshwater Prawn by Chitosan Reduced Gold Nanoparticles. Orient J Chem 2018;34(2).

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Nandanpawar P. C, Rather M. A, Badhe M. R, Sharma R. Assessment of DNA Damage During Gene Delivery in Freshwater Prawn by Chitosan Reduced Gold Nanoparticles. Orient J Chem 2018;34(2). Available from: http://www.biotech-asia.org/?p=29484


In this era of modern biomedical sciences, nanoparticles are being extensively used for applications such as delivery of genes, hormones, vaccines, peptides or proteins intended for therapeutic purpose. Moreover, cell labeling (Bhirde et al., 2011), drug targeting ( Hans and Lowman 2002), biosensors, and hyperthermia therapy are only a portion of the wide nanoparticle application spectrum (Jeng and Swanson.,2006). Various metal and polymeric nanoparticles (1-100 Nanometers) like gold, Titanium oxide (Ghosh et al. 2008; Rather et al., 2013)) and Chitosan (Rather et al.,2016; Duceppe and Tabrizian 2010)) (Kashyap et al.,2015)), poly Lactic-co-Glycolic Acid (PLGA)(Li Y-P et al., 2001), polyLactic Acid (PLA)(Kumari et al.,2010), poly-ε-caprolactone (PCL)(Tang  et al., 2014)) and gelatin etc. are used for the above purposes. (Soppimath et al., 2001; Mahapatro A and Singh DK. 2011). These nanoparticles are being used mainly because of their unique properties such as electrostatic binding, higher intracellular uptake, convenient release profiles and better encapsulation efficiency (Shan et al.,2012). In mammalian systems such as humans, rats and mouse models, nanoparticles are being used for cancer treatments, targeted gene integration and generation of immunogenic potential(Roy et al. 1999). Various non-mammalian and vertebrate models such as zebrafish, black seabream, are also being studied for efficient gene/drug delivery and payload efficiency using nanoparticles (Li et al., 2013; Sharif et al.,2012)Despite the enormous research done in nanoparticle applicability, little is known about its ill effects to aquatic animal models. The nanoparticles are reported to be genotoxic to host DNA , alters nucleic acids, causes mutations and random inactivation of genes (Shinde et al., 2012). Commonly used nanoparticles such as Titanium oxide, silver nanoparticles, carbon nanotubes, fullerenes are responsible to produce chronic cellular damage, apoptosis, genotoxicity and bioaccumulation ( Lai et al.,2008 ; Chang  et al.,2012 ;Zhu et al.,2016;Cheng SH.,2012) has been recently documented. A number of non-mammalian animal models such as zebrafish have been used to assess the risk associated with nanoparticles on human health (Asharani et al; 2008)). Even the widely used gold nanoparticles are biocompatible and believed to be non-toxic, but, but several studies have indicated its semi lethal effects such as lipid peroxidation, cytotoxicity and oxidative stress. (Tedesco et al.,2010; Pan et al., 2007; Freese et al., 2012 Sharma et al.,2016).

In the present aquaculture scenario, the emerging use of nanoparticles for maintaining water quality (Pradeep T and Anshup.,2009), sedimentation of algal biomass (Xu et al ., 2011), growth promoting and gene delivery for production of transgenic is taking a step forward. Nanotechnology based DNA vaccines are being developed against White Tail disease in shrimps (Ramya et al., 2014), but such treatments may leave behind traces of nanoparticle residues which may find its way to the biological systems. When released as effluents into the aquatic environment, the metal nanoparticles may accumulate in invertebrates and can enter the human food chain. (Baun et al.,2008 ;(Judy et al.,2011).Since this nanotoxicity is size and dose dependent, it becomes mandatory to formulate the safe dose of nanoparticles before delivering it in farmed conditions (Rather et al., 2013).

The giant freshwater prawn (Macrobrachium  rosenbergii) is a commercially important species for aquaculture and is recently being used in various genetic improvement programs. Very scarce literature is available regarding gene delivery in this species (Ramya et al.,2014) and hence, this species was considered as an aquatic invertebrate model to test the possibility of standardization of safer nano-gene delivery doses for transgenic production.

The CRGNPs are reported to be nontoxic in the case of mammalian systems ( Pokharkar et al., 2009; Bhumkar et al.,2007; Stefan et al.,2013) but the toxicity potential of these is yet to be established in non-mammalian aquatic invertebrates. Another reason for considering CRGNPs includes the fact that chitosan acts as a penetration enhancer (Bhumkar et al.,2007) and hence is helpful in gene delivery practices. As chitosan imparts positive charge to the gold nanoparticles, it has better electrostatic affinity towards the negatively charged DNA/Plasmid. The present study aims to demonstrate Chitosan reduced gold nanoparticles as gene delivery vehicles in M. Rosenbergii and its possible effects on cells as well as genetic gradients.

Materials and Methods


For the synthesis of CRGNPs, Gold chloride, Chitosan (degree of deacetylation 90%) were procured from  Sigma  Aldrich  (St. Louis,  MO)  company.  For comet assay,  Dimethyl Sulphoxide (DMSO) and Low Melting Point Agarose (LMPA) from SRL (Mumbai, India) company were used. Triton X-100 (Sigma) for comet assay  and other laboratory wares were obtained from Tarsons (GIBCO, BRL, UK). All other chemicals were of analytical and molecular biology grade. Plasmid PDB402 having 367 bp GFP (Green Fluorescent Protein) gene with CMV (Cytomegalovirus) promoter was procured from Central Institute of Fisheries Education (CIFE), Mumbai,India.

Procurement of Animals

Juvenile prawns were collected from a local prawn hatchery at Bharuch, Gujarat, India and kept in FRP (fiber reinforced Plastic) tanks at the density of 10 prawns/tank of 50 litre capacity  in the wet  lab of Central Institute of Fisheries Education, Mumbai, India. They were acclimatized to hatchery conditions for two weeks before commencement of the experiment. The water quality parameters were checked fortnightly following APHA guidelines (APHA,1999). The photoperiod maintained in the tank was 12h light/ 12 h darkness. The research undertaken complies with the current animal welfare laws in India. The care and treatment  of  animals  used  in  this  study  were  in  accordance  with  the  ethical guidelines  of  ICAR-Central Institutute of Fisheries Education, Mumbai,India. As the experimental animal Macrobrachium  rosenbergii is not an endangered shellfish, the provisions of the Govt of India’s Wildlife  Protection Act of 1972 are not applicable for experiments on this shellfish.

Preparation and Confirmation of CRGNP- plasmid Conjugates

CRGNPs were prepared by Turkevich et al. method (Turkevich et al.,1951)  with slight modification. 100 ml of aqueous solution of chloroauric acid (HAuCl 4 ) of 8mM (4ml) concentration was added to 10 ml of chitosan solution (6.92mg/ml) prepared in 1% acetic acid and heated for 15 min to reduce the chloroauric acid which yields a ruby-red solution. The ruby red colored solution formed is the indication of formation of gold nanoparticles.

For preparing CRGNP- plasmid conjugates, 1 ml of CRGNP solution was dissolved in 9 ml triple distilled water and topped the volume up to 10ml ( Rajeshkumar et al.,2009). Different concentrations of plasmid solutions (50ng/μl, 100ng/μl) were prepared by dissolving in 50mM sodium sulfate buffer separately followed by heating at 550C. Both plasmid and nanoparticles of variable concentrations were mixed proportions and vortexed on magnetic stirrer at 700 g for 30 seconds. Lastly,the solutions were stored at room temperature. The characterization of resultant nano-plasmid conjugates was done with Beckman Coulter Delsa Nano C- Nano Particle Size Analyzer.for the mean particle size and size distribution. For Scanning electron microscopy, drops of the nanoparticle dispersions were placed on carbon-coated grids. The solution was allowed to air-dry for 1 min. After drying of the samples, they were treated with a high energy  electron  beam  and  analyzed  using  Quanta  200  Environmental  Scanning Electron Microscopy (ESEM) system at Icon analytics, Mumbai.

Gel Retardation Assay

Conjugation of DNA with the CRGNPs was confirmed by centrifuging the conjugate solution at 13,000 g at 480 C for 20 min ( Wu et al.,2010);(Shan et al., 2012).After discarding the supernatant, 20 ml autoclaved triple distilled water was added to the pellets. The solution was vortexed for 10 min and then loaded onto 1% agarose gel. The agarose gel was stained with 1μg/mL ethidium bromide and visualized under UV (Ultraviolet) transilluminator (Syngene, UK).

Dose Administration and Sampling

The CRGNP doses selected for the study were selected by performing a preliminary test to confirm the rate of mortality in prawns.The CRGNP test  concentrations were 10,20,30,40 ug/L of tank water. An immersion treatment to 10 prawn juveniles/ tank was given for 24 hrs.  Accordingly, doses which caused least mortality(10ug/L,20ug/L) were selected for final treatement.

The treatment of CRGNP-plasmid conjugates were given (viz. 10ug/L,20ug/L)to animals by immersion treatment in Fibre Reinforced Plastic(FRP) tanks for a period of 36 hours. The animals were stocked at the rate of 6 individuals/Litre in every tank. The animals were not fed 24 hours prior to the treatment. Regular aeration was maintained during the treatment.  After 36 hours of treatment, the tissue samples were collected from animals by anaesthetizing them with MS222.

Fluorescence Microscopy and Comet Assasy

The freshly sampled tissue sections were washed in triple distilled water and the exoskeleton was removed with the help of forceps. The muscle tissues of midbody and near tail end of prawns were then analysed under TCS-SP Leica microscope (Germany) for fluroscence detection. GFP fluorescence absorption peak on 488nm and an emission peak on 509nm was observed.

The comet assay was performed on gills, pleopods and muscle tissues following the method of singh et al. [Pavlica et al.,2001] with  slight  modifications.  As a positive control, silver nanoparticles (2μg/L) were administered to prawns. For comet assay, the tissues were placed in 1ml of cold Hanks Balanced Salt Solution (HBSS) containing 20mM EDTA in 10% DMSO. The tissues were minced into fine pieces and a suspension was prepared.  Slides were prepared in triplicates per concentration and were immersed in cold lysis solution (4oC) at pH 10 for 60 minutes.

After unwinding in the electrophoresis buffer (300 mM NaOH: 1 mM Na2EDTA) at pH13. for 20 min, electrophoresis was conducted at a constant voltage of 25 V and 300 mA at 4oC.Slides were neutralized in 0.4 M Tris having a pH of 7.5 for 5 min and then stained with 75μL Ethidium  bromide,  cover  slipped  and  immediately  analyzed  in  Zeiss  axiophore  image analyser. Twenty cells per slide ( Pavlica et al., 2001) were examined using the software from metasystems (Germany) at the National Center  for  Preclinical  Reproductive  and  Genetic Toxicology Genetic Toxicology in National Institute for Research in Reproductive Health (NIRRH), Mumbai.

Bioaccumulation studies by Graphite Furnace- Atomic Absorption Spectroscopy (GF-AAS)

GF-AAS was performed on Gill, muscle and pleopod tissues following the method of kehoe ( Kehoeet al (1988)) with some modifications. The tissues were wet digested using concentrated supra-pure trace-metal free HNO3 (Nitric acid) followed by Conc HClO4 (Perchloric acid). The dried residue was dissolved in 5ml 0.1M HNO3. GF-AAS was performed using a Perkin–Elmer Model-800 atomic absorption spectrophotometer with a Perkin–Elmer HGA-600 graphite furnace. For the analysis graphite tubes were used. After digestion, the sample was diluted with 0.25N supra-pure nitric acid @ 1:2 v/v, prior to analysis. For calibration of the equipment, elemental gold standard (Merck) was used(Lasagna et al., 2010).

Data Analysis

The results were analyzed by one-way ANOVA and the comparisons of mean values were carried out by Duncan’s multiple range test (DMRT). Statistical analysis was performed using SPSS 16.0 software (SPSS, Chicago, IL). All the data analyses were expressed as a mean ± standard error.


Different concentrations of  CRGNPs showed color variations ranging from bright red to magenta color (Fig 1).  The mean particle size ,polydispersity index  and zeta potential of CRGNPs was found to be 33.7nm,0.292 and 24.6mV respectively. The results of SEM confirmed that nanoparticles were compact, spherical in structure and well dispersed. (Fig 1 and 2).

 Figure 1: Chitosan Reduced Gold Nanoparticles of variable concentrations Figure 1: Chitosan Reduced Gold Nanoparticles of variable concentrations


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Figure 2: Particle size distribution and Scanning Electron Microscopy of chitosan reduced gold nanoparticles Figure 2: Particle size distribution and Scanning Electron Microscopy of chitosan reduced gold nanoparticles


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The conjugation of plasmid with CRGNPs was confirmed by gel retardation assay. Blank CRGNPs  and naked plasmid DNA (pDB 402) was used as controls. The CRGNP- plasmid nanoconjugate did not migrate in the gel. On the other hand, control DNA showed migration from the well (Fig 3). CRGNPs devoid of plasmid did not show any fluorescence in the gel. Further, the bands developed by the CRGNP- plasmid nanoconjugate were less bright than the naked DNA indicating encapsulation of plasmid by CRGNPs.

 Figure 3: Gel retardation assay Lane 1: Blank gold nanoparticles, Lane 2: Blank plasmid, Lane 3:DNAse treated plasmid GNP solution, Lane 4:DNAse treated blank plasmid Figure 3: Gel retardation assay Lane 1: Blank gold nanoparticles, Lane 2: Blank plasmid, Lane 3:DNAse treated plasmid GNP solution, Lane 4:DNAse treated blank plasmid


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The intracellular distribution of CRGNP- plasmid nanoconjugates after 36 hours of exposure was detected mostly in gill lamellae (Fig 4a), Pleopods and uropod muscles (Fig 4b, 4c) suggesting the protein expression of the transfected GFP gene.  There was no significant difference between GFP expression intensities of samples administered with variable CRGNP- plasmid nanoconjugates concentrations.

Figure 4: GFP gene expression in treated animals by fluorescence microscope A: Gills B: Pleopods C: Muscles Figure 4: GFP gene expression in treated animals by fluorescence microscope A: Gills B: Pleopods C: Muscles


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Results of cell viability assay showed no significant change in viability compared to Control cells. The %  tail DNA content (±S.D) at 10μg/L  was  34.7±16.3%  for gills, 41.37±17.7% for pleopods and 14.39 ±11.5%  for muscles (Fig 5). At concentration of20 ug/L, it was  48.536±36.03% for gills, 37.6±21.3% for pleopods and 10.9±7.2% for muscles was detected. The negative control group showed very less damaged DNA content in tail DNA(9.75±6.1%) while the positive control (2ug/L silver nanoparticles) it was highest (75.12± 13.8) confirming heavy DNA damage (Fig 6).

 Figure 5: Percentage of tail DNA in various tissues. Figure 5: Percentage of tail DNA in various tissues.


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Figure 6: Genotoxicity caused by Chitosan Reduced gold nanoparticles (Comet assay), a: Positive control , b: 10 μg/L, c: 20 μg/L d: Negative control. Figure 6: Genotoxicity caused by Chitosan Reduced gold nanoparticles (Comet assay), a: Positive control , b: 10 μg/L, c: 20 μg/L d: Negative control.


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DNA damage is visible in positive control(Silver nanoparticles) while tail length shows concentration dependant damage. No DNA damage is present in negative control shown by absence of tail.

 Figure 7: Concentration dependant (10ug/L and 20ug/L)bioaccumulation of chitosan reduced gold nanoparticles(GF-AAS). Figure 7: Concentration dependant (10ug/L and 20ug/L)bioaccumulation of chitosan  reduced gold nanoparticles(GF-AAS).


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Least bioaccumulation is evident in muscle tissues and highest in gills

GF-AAS study showed maximum accumulation of CRGNPs in gill tissues of the treated due to maximum exposure to tank water containing nanoparticles.


The polymer coated metal nanoparticles are becoming popular as they are known to have less toxicity (Castillo et al., 2008 ;Singh et al., 2009). The unique features of CRGNPs are tunable core size, large surface to volume ratio, monodispersity and easy functionalization with many biomolecules ( Shan et al., 2012; Zhang et al., 2010). The mean particle size of gold nanoparticles was found to be in the size range as previously reported in studies. Many authors have reported size of the gold nanoparticles ranging from 20 nm to 450nm ( Gan et al .,200; Li et al.,2010). Analysis of gold nanoparticles by polydipersity index suggested narrow range of particle size distribution. Nanoparticles had higher value of zeta potential which showed moderate stability as zeta potential above 30 mV are considered to be more stable ( Torchilin VP.,2007) (Fig 1). CRGNPs were synthesized using Chitosan which acted as a reducing agent and provided the positive charge to nanoparticles. The overall positive charge on CRGNPs was evident in Zeta potential measurement and also confirmed the presence of a Chitosan coating over gold nanoparticles. GNP concentrations (10µg/L,  20µg/L)  were  administered  to  the animals  to  ascertain  toxic effect  on  various tissues. Concentration above 80µg/L was found to be toxic by initial trials carried out in our lab. (Li et al.,2010) found gold nanoparticles toxicity at the dose of 15µg/L during immersion treatment in Daphnia magna. Immersion treatment facilitated even distribution of GNPs in the solution.

Conjugation of plasmid DNA to CRGNPs  was the deciding factor during the study. Since the conjugation could be detected as soon as the buffer containing DNA was added to the nanoparticle solution as evidenced by the change in coloration. The conjugated solution looked purplish in color suggesting increased particle size and increased light scattering resulting in red-shift effect (Huang X and El-Sayed M  2010). When the gel retardation assay for conjugated nanoparticles was carried out, the DNA-nanoconjugates could not migrate in the gel as the neutralization of the negatively charged phosphate group in DNA with the positive charge of nanoparticle obstructed its migration (Wu et al.,2010).This confirmed the conjugation of DNA with nanoparticles. Lesser fluorescence in DNA-nanoconjugates was mainly due to fluorescence quenching by gold nanoparticle and increase in publication in the nano-conjugated sample (Kainthan et al.,2006).

Consequently, the nanoconjugates after administration to experimental animals via immersion treatment, may possibly escape the endo-lysosomal sections and entered the cytoplasm. Upon entering in endosomes, the proton sponge effect of nanoparticles caused osmotic swelling and subsequent endosomal rupture. This facilitated the escape of DNA-gold nanoconjugate into the cytoplasm and subsequent integration in the nuclear DNA (Guo et al.,2010 ;Benjaminsen et al.,2012).

Successful delivery of nanoparticles also brings with it the chances of toxic effects.( Li et al., 2010; Nandanpawar et al.,2013) has reported that the toxicity of silver nanoparticles ranged from 3-4 µg/L in Daphnia magna. (Bar-Ilan et al., 2009) exposed  transparent zebrafish embryos to colloidal silver nanoparticles at various sizes (3, 10, 50, and 100 NM), at a concentration  of 100  or 250  μM,  from  4  to 120  hours post  fertilization  (hpf). Silver nanoparticles produced almost 100% mortality at 120 hpf. In our experiment, when the prawns were exposed to silver nanoparticles (2µl/L) as a positive control, significant mortality was observed and necrosis was visible. Comet assay for CRGPs showed significant DNA damage at higher dose, i.e. 20 µg/L was found to be significant. Higher percentage of tail DNA was indicative of more DNA damage as a consequence of single and double strand breaks (AshaRani et al., 2009). On the contrary (Schulz et al., 2012) found no genotoxicity in the trachea of rats at 18 μg concentrations of GNPs. However, in the present study, dose dependant toxicity of GNPs was evident since the exposure time of animals to the variable concentrations was constant. The similar result was also reported by various researchers (Wiwanitkit et al., 2009; Hirn et al., 2011). The concentration of gold nanoparticles@10µg/L was less toxic with wide tissue distribution and hence could be considered as a safe dose for using CRGNP as delivery vehicles in biomedical applications like gene and vaccine delivery. Low toxicity may be attributed to the non-toxic polymer Chitosan coating over CRGNPs. (Das et al.,2012) established a correlation between the capping material and genotoxicity of Gold Nanoparticles. The highest toxicity was reported in gold nanoparticles capped with aspartic acid treatment, while those coated with bovine serum albumin (GNPB) were most biocompatible.

Our study showed a direct correlation between CRGNP dose and bioaccumulation in the organs like gill, pleopods and muscle (Fig 7). The extent of DNA damage and bioaccumulation of gold nanoparticles in pleopods on an average were lesser than gills (Fig 5,7) which may be due to the hardened cell structure of pleopods. The least bioaccumulation was found in muscle tissues. (Lasagna et al.,2010) reported reduced bioaccumulation of GNPs as the dose increased. Our study supported this finding as concentration dependant bioaccumulation was observed (Fig 7). The systemic toxicity of gold nanoparticles in the intermediate size range (18–37 nm) was linked to major organ damage in the liver, spleen, and lungs   in mice. The muscles being less exposed to aquatic environment had less chances of damage as the treatment was given by immersing the animals in the nanoparticles suspended water. In vivo studies of gold nanoparticles have reported bioaccumulation in important body organs, acute inflammation and apoptosis in the liver ( Wiwanitkit et al.,2009; Xia et al ., 2006). On the  other  hand,  repeated  administration  of  higher  dose  caused  no  toxicity  of  gold nanoparticles  in  mice  ( Lasagna et al.,2010). The absence of mortality at lower doses may be because of the hardy nature of prawn juveniles as compared to the zebrafish embryos.


The present study concludes that gold nanoparticles do not cause significant genotoxicity but is responsible for bioaccumulation at higher concentrations. The toxicologically safe doses identified in this study can be used for various applications like gene and drug delivery. The immersion treatment can be considered as an efficient and  convenient  method  of  nanoparticles  administration  when  large numbers  of animals have to be treated simultaneously with minimum stress. Though Chitosan nanoparticles and gold nanoparticles are considered as safe in nature, their combined effects may indicate some chemical or biological interactions that are still uncharacterized. Further studies on the interaction of these nanoparticles to different biological systems also needs to be advocated for the development of a better delivery system in terms of safety and efficiency.


The authors are thankful to ICAR, New Delhi and Director, ICAR-CIFE for providing funds and necessary equipments for this research.

Conflict of Interest Statement

The authors declare that there is no conflict of interest.


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