- freely available
Mar. Drugs 2010, 8(5), 1518-1525; doi:10.3390/md8051518
Published: 28 April 2010
Abstract: Chitin and chitosan are natural polysaccharide polymers. These polymers have been used in several agricultural, food protection and nutraceutical applications. Moreover, chitin and chitosan have been also used in biomedical and biotechnological applications as drug delivery systems or in pharmaceutical formulations. So far, there are only few studies dealing with arsenic (As) removal from groundwater using chitin or chitosan and no evidence of the use of these natural polymers for arsenic trioxide (As2O3) delivery in tumor therapy. Here we suggest that chitin and/or chitosan might have the right properties to be employed as efficient polymers for such applications. Besides, nanotechnology offers suitable tools for the fabrication of novel nanostructured materials of natural origin. Since different nanostructured materials have already been employed successfully in various multidisciplinary fields, we expect that the integration of nanotechnology and natural polymer chemistry will further lead to innovative applications for environment and medicine.
Chitin is an abundant natural polysaccharide produced by arthropods and crustaceans. Chitin is found in diatoms, nematodes, molluscs and as a structural polysaccharide in basidiomycetes and filamentous fungal cell walls, constituting almost 16% of the dry weight of the organism . Chitin deacetylation leads to the formation of chitosan. The process involves the use of strong alkali solutions for the removal of N-acetyl groups both at room or elevated temperatures [2,3]. Chitin and chitosan are suitable functional materials due to their excellent properties such as biocompatibility, biodegradability, non-toxicity and adsorption properties, to cite only a few . Chitin and chitosan are highly basic polysaccharides with unique properties like the ability to form films  to react with polyanions [6,7] as well as to chelate and remove metal ions . A wide variety of medical applications for chitin and chitosan derivatives have been reported in the last few years [9–11].
However, the versatitily of chitin and chitosan was emphasized in two recent, and somehow controversial, applications in the field of arsenic chemistry. In fact, the potential of chitin and chitosan can be exploited either for inorganic arsenic removal in groundwater or in the design of novel delivery vectors for arsenic trioxide (As2O3) in tumor therapy. While a high dose of inorganic arsenic (iAs) is toxic for individuals, As2O3 is used as an antineoplastic agent in most common malignancies. We think that this interesting paradoxical behavior merits a deeper investigation in the near future by investigators and clinicians involved in these two different research fields.
2. Chitin and Chitosan for Arsenic Species Complexation and Removal
Arsenic (As) is a metalloid that occurs naturally in the environment and is present in soil, groundwater and plants . Inorganic arsenic (iAs) is the most toxic form, and has been classified in group 1 as carcinogenic to humans by the International Agency for Research on Cancer . In fact, arsenic may induce lung, urinary bladder and primary skin cancer.
In China, India and Bangladesh, As contamination ([As] > 100.000 μg/L) of groundwater used for drinking is a serious threat for human health . The WHO provisional guideline value for arsenic in drinking water has been set to 10 μg/L . Moreover, some cereal grains and cereal-based products (i.e., rice) can be contaminated by a high amount of arsenic. Besides, the influence of processing and cooking of these foods should be taken into account if iAs-contaminated water is used [16,17]. The need to regulate As exposure in infants consuming rice-based products has been recently highlighted by us since the European Union has not fixed a maximum tolerable limit for these foods so far .
Therefore, the identification and use of low-cost methods and safe materials to remove As from drinking water is highly desirable . Several methods are available for the removal of As and have been reviewed by Mohan et al. . Among them, we mention co-precipitation, flotation, ion exchange, ultrafiltration, and reverse osmosis. Arsenic adsorption from aqueous solution has received more attention due to its higher efficiency. Activated alumina , activated carbon  and bauxsol  have been used as efficient adsorbents. Even goethite and hematite , iron oxide-coated sand , ferrihydrite , and Fe(III)-loaded resins  have been employed because of the selectivity and affinity of Fe(III) toward iAs species. Although these resins are efficient and selective in removing As, their applicability is limited due to their high cost. For these reasons, adsorption of arsenic using natural products has emerged as a viable option [28,29]. Chitin and chitosan have been reported to be efficient heavy metal scavengers due to the presence of hydroxyl and amino groups . In a recent study by Sun et al.  it was observed that sulfur atoms also have a strong affinity for arsenic. Therefore, the authors prepared polyaspartate and chitosan blends derivatized with -SH functionalities. Blends were reacted with mercaptoacetic (thioglycolic) acid affording the –SH derivative. This polymer showed better arsenic-removal behavior (As removal > 22%) than other adsorbents, leading to a lower arsenic equilibrium concentration.
Removal of arsenic from contaminated drinking water was also studied on a chitosan/chitin mixture that showed a capacity of 0.13 μ-equivalents As/g (pH = 7.0) .
Recently, removal of both As(III) and As(V) by chitosan-coated alumina or molybdate-impregnated chitosan was reported [33,34]. These methods show a very high adsorption capacity at pH = 4 (56.50 and 96.46 mg/g for As(III) and As(V), respectively), but other interfering ions (i.e., phosphate) may limit or abolish the efficiency of this adsorbent.
Chitin and chitosan were comparatively employed for remediation of chromated copper arsenate (CCA) preservative-treated wood in recent years due to release of chromium, copper, and arsenic elements from waste wood during land filling, burning, composting, and other disposal methods . Limiting the analysis to As species only, chitin removed 63% of As from treated sawdust, while using the same amount of chitosan the recovery was only 30%. These results clearly show that even this acetylated polysaccharide can be efficiently employed for arsenic removal. However, chitosan is generally preferred over chitin in the vast majority of applications [36,37].
3. Chitosan for As2O3 Incorporation and Delivery
In a completely different field, arsenicals and compounds like arsenic trioxide (As2O3) have been used therapeutically in traditional Chinese medicine for a long time. Arsenic trioxide administered intravenously was reintroduced in the year 2000 by the US Food and Drug Administration as an anticancer agent for the treatment of acute promyelocytic leukemia (APL), even for patients with relapsed or refractory forms .
It was hypothesized that the anticancer mechanisms of As2O3 may be due not only to the induction of apoptosis as previously reported by Zhang , but also by reactivation of silenced tumor suppressor genes through DNA demethylation .
Other studies reviewed by Cui et al. investigated the use of As2O3 in the treatment of solid tumors, including liver, prostate, neuroblastoma, head and neck, gastric, transitional cell, and renal cell carcinoma, esophageal, prostate, colorectal cancer, fibroblastoma, and melanoma .
However, the efficacy of As2O3 against human solid tumors is poor, even at a high As dosage. Consequently, different strategies aimed at increasing its efficacy such as local delivery (intratumoral injection) have been devised . This strategy not only increases the localization of specific drugs in the tumor, but also reduces the unspecific uptake by other organs (targeted delivery) and presents an anti-invasive activity .
The incorporation of As2O3 with chitosan nanospheres to form novel arsenic-containing chitosan-based nanocarriers represents an innovative strategy that might be exploited. Additionally, chitosan itself has been claimed to show antineoplastic activities tested both in vitro and in vivo  even if the results are still controversial . These nanovectors, as other common nanomaterials, can be potentially used for their ability to exploit the Enhanced Permeability and Retention (EPR) effect already used for the delivery of small molecules [45,46]. The EPR effect is based on the fact that tumor cells grow quickly and stimulate the production of blood vessels for nutrition and oxygen supply. These newly formed tumor vessels are usually abnormal in form and architecture. They present wide fenestrations where engineered systems may enter and deliver their cargo. Therefore, such delivery vehicles have the property to accumulate much more in tumor tissues than in normal tissues just exploiting their dimensions. To achieve the EPR effect, As2O3 can be therefore incorporated into chitosan nanospheres, which might assure a quite prolonged diffusion, biocompatibility and safety, while exploiting the EPR effect. An already reported example is represented by chitosan nanospheres . These nanospheres have been studied for their efficient DNA incorporation and delivery properties.
Alternatively, due to the versatility of chitosan to give larger biocompatible microspheres, As2O3 can be incorporated into larger microspheres, as already achieved with DNA, using various fabrication methods . Size and shape of these systems are important factors for several medical applications: to improve bioavailability (i.e., overcoming enzymatic or adsorption barriers and in the case of nasal administration the mucociliary clearance) and to prolong the residence time of drug delivery systems at the site of drug absorption .
4. Interactions of Arsenite, Arsenate and Arsenic Trioxide (As2O3) with Chitosan
It is generally believed that electrostatic interactions, metal chelation and ion pairs formations are the three main mechanisms hypothesized to occur when a metal is adsorbed by chitosan [30,50]. Surface adsorption, chemi- and physisorption, diffusion and adsorption-complexation mechanisms may also occur  as a consequence of ion-exchange, hydrogen bonds, hydrophobic and van der Waals interactions.
The occurrence of interactions between chitosan and anionic molecules (dyes) was studied by thermodynamic methods recognizing that chemisorption (ion-exchange, electrostatic attractions) is the most prevalent mechanism with the pH as the main factor affecting adsorption [52,53].
We hypothesized a model of interaction between chitosan and As(III) (arsenite)/As(V) (arsenate) species or arsenic oxide As2O3 that we have presented in Figure 1. The arsenite anion may preferentially form electrostatic interactions with protonated chitosan amino groups. Arsenate may instead interact with the polymer through electrostatic interactions and hydrogen bonds. For what concerns the arsenic oxide As2O3, the interaction might occur mainly through hydrogen bonds.
From all the studies appearing in the literature over the last few years, it appears clear that the use of chitin and chitosan for toxic inorganic As removal or As2O3 delivery for tumor therapy is quite a neglected topic. We think that nanotechnology and biomedicine applied to these two aspects would help to solve not only some environmental pollution aspects, but also to improve the life quality of future generations and to devise novel prevention strategies and innovative therapeutic approaches.
Authors thank the Italian Ministry of Health for financial support, editors and reviewers for their suggestions and comments.
- Samples Availability: Available from the authors.
References and Notes
- Muzzarelli, RAA. Chitin nanostructures in living organisms. In Chitin Formation and Diagenesis; Gupta, SN, Ed.; Springer: New York, NY, USA, 2010. [Google Scholar]
- Roberts, GAF. Chitin Chemistry; Macmillan: London, UK, 1992. [Google Scholar]
- Chitin Enzymology; Muzzarelli, RAA, Ed.; Atec Edizioni: Grottammare, Italy, 1996; Volume 2.
- Muzzarelli, RAA. Natural Chelating Polymers; Pergamon Press: Oxford, UK, 1973. [Google Scholar]
- Yusof, NL; Lim, LY; Khor, E. Flexible chitin films: structural studies. Carbohydr Res 2004, 339, 2701–2711. [Google Scholar]
- Acosta, N; Aranaz, I; Peniche, C; Heras, A. Tramadol Release from a Delivery System Based on Alginate-Chitosan Microcapsules. Macromol Biosci 2003, 3, 546–551. [Google Scholar]
- Peniche, C; Argüelles-Monal, W; Peniche, H; Acosta, N. Chitosan: An Attractive Biocompatible Polymer for Microencapsulation. Macromol Biosci 2003, 3, 511–520. [Google Scholar]
- Bhatnagar, A; Sillanpaa, M. Applications of chitin- and chitosan-derivatives for the detoxification of water and wastewater--a short review. Adv Colloid Interface Sci 2009, 152, 26–38. [Google Scholar]
- Jayakumar, R; Selvamurugan, N; Nair, SV; Tokura, S; Tamura, H. Preparative methods of phosphorylated chitin and chitosan--an overview. Int J Biol Macromol 2008, 43, 221–225. [Google Scholar]
- Shi, C; Zhu, Y; Ran, X; Wang, M; Su, Y; Cheng, T. Therapeutic potential of chitosan and its derivatives in regenerative medicine. J Surg Res 2006, 133, 185–192. [Google Scholar]
- Chandy, T; Sharma, CP. Chitosan--as a biomaterial. Biomater Artif Cells Artif Organs 1990, 18, 1–24. [Google Scholar]
- Garelick, H; Jones, H; Dybowska, A; Valsami-Jones, E. Arsenic pollution sources. Rev.
- IARC Working Group on the Evaluation of Carcinogenic Risks to Humans. Overall Evaluations of Carcinogenicity: An Updating of IARC Monographs Volumes 1 to 42, Lyon, France, 10–18 March 1987.
- Nickson, R; Sengupta, C; Mitra, P; Dave, SN; Banerjee, AK; Bhattacharya, A; Basu, S; Kakoti, N; Moorthy, NS; Wasuja, M; Kumar, M; Mishra, DS; Ghosh, A; Vaish, DP; Srivastava, AK; Tripathi, RM; Singh, SN; Prasad, R; Bhattacharya, S; Deverill, P. Current knowledge on the distribution of arsenic in groundwater in five states of India. J Environ Sci Health A Tox Hazard Subst Environ Eng 2007, 42, 1707–1718. [Google Scholar]
- World Health Organization. Regional Office for Europe. Drinking-Water Quality: Guidelines for Selected Herbicides; World Health Organization, Regional Office for Europe: Copenhagen, Denmark, 1987; p. 23.
- Signes, A; Mitra, K; Burlo, F; Carbonell-Barrachina, AA. Effect of cooking method and rice type on arsenic concentration in cooked rice and the estimation of arsenic dietary intake in a rural village in West Bengal, India. Food Addit Contam Part A Chem Anal Control Expo Risk Assess 2008, 25, 1345–1352. [Google Scholar]
- Zhu, YG; Williams, PN; Meharg, AA. Exposure to inorganic arsenic from rice: a global health issue? Environ Pollut 2008, 154, 169–171. [Google Scholar]
- Masotti, A; Da Sacco, L; Bottazzo, GF; Sturchio, E. Risk assessment of inorganic arsenic pollution on human health. Environ Pollut 2009, 157, 1771–1772. [Google Scholar]
- Sen Gupta, B; Chatterjee, S; Rott, U; Kauffman, H; Bandopadhyay, A; DeGroot, W; Nag, NK; Carbonell-Barrachina, AA; Mukherjee, S. A simple chemical free arsenic removal method for community water supply--a case study from West Bengal, India. Environ Pollut 2009, 157, 3351–3353. [Google Scholar]
- Mohan, D; Pittman, CU, Jr. Arsenic removal from water/wastewater using adsorbents--A critical review. J Hazard Mater 2007, 142, 1–53. [Google Scholar]
- Lin, TF; Wu, JK. Adsorption of arsenite and arsenate within activated alumina grains: equilibrium and kinetics. Water Res 2001, 35, 2049–2057. [Google Scholar]
- Reed, BE; Vaughan, R; Jiang, L. As(III), As(V), Hg, and Pb Removal by Fe-Oxide Impregnated Activated Carbon. J Environ Eng 2000, 126, 869–873. [Google Scholar]
- Genc-Fuhrman, H; Tjell, JC; McConchie, D. Increasing the arsenate adsorption capacity of neutralized red mud (Bauxsol). J Colloid Interface Sci 2004, 271, 313–320. [Google Scholar]
- Gimenez, J; Martinez, M; de Pablo, J; Rovira, M; Duro, L. Arsenic sorption onto natural hematite, magnetite, and goethite. J Hazard Mater 2007, 141, 575–580. [Google Scholar]
- Thirunavukkarasu, OS; Viraraghavan, T; Subramanian, KS; Chaalal, O; Islam, MR. Arsenic Removal in Drinking Waterâ€”Impacts and Novel Removal Technologies. Energy Sources Part A 2005, 27, 209. [Google Scholar]
- Raven, KP; Jain, A; Loeppert, RH. Arsenite and Arsenate Adsorption on Ferrihydrite: Kinetics, Equilibrium, and Adsorption Envelopes. Environ Sci Technol 1998, 32, 344–349. [Google Scholar]
- Katsoyiannis, IA; Zouboulis, AI. Removal of arsenic from contaminated water sources by sorption onto iron-oxide-coated polymeric materials. Water Res 2002, 36, 5141–5155. [Google Scholar]
- Hasan, K; Halim, MA; Hossain, MK; Rana, MS; Waliul Hoque, SAM. Bioadsorbtion of Arsenic by Prepared and Commercial Crab Shell Chitosan. Biotechnology 2009, 8, 160–165. [Google Scholar]
- Yadanaparthi, SK; Graybill, D; von Wandruszka, R. Adsorbents for the removal of arsenic, cadmium, and lead from contaminated waters. J Hazard Mater 2009, 171, 1–15. [Google Scholar]
- Guibal, E. Interactions of metal ions with chitosan-based sorbents: A review. Sep Purif Technol 2004, 38, 43–74. [Google Scholar]
- Sun, B; Mi, Z; An, G; Liu, G; Zou, J. Preparation of Biomimetic Materials Made from Polyaspartyl Polymer and Chitosan for Heavy-Metal Removal. Ind Eng Chem Res 2009, 48, 9823–9829. [Google Scholar]
- Elson, CM; Davies, DH; Hayes, ER. Removal of arsenic from contaminated drinking water by a chitosan/chitin mixture. Water Res 1980, 14, 1307–1311. [Google Scholar]
- Boddu, VM; Abburi, K; Talbott, JL; Smith, ED; Haasch, R. Removal of arsenic (III) and arsenic (V) from aqueous medium using chitosan-coated biosorbent. Water Res 2008, 42, 633–642. [Google Scholar]
- Chen, CY; Chang, TH; Kuo, JT; Chen, YF; Chung, YC. Characteristics of molybdate-impregnated chitosan beads (MICB) in terms of arsenic removal from water and the application of a MICB-packed column to remove arsenic from wastewater. Bioresour Technol 2008, 99, 7487–7494. [Google Scholar]
- Kartal, SN; Imamura, Y. Removal of copper, chromium, and arsenic from CCA-treated wood onto chitin and chitosan. Bioresour Technol 2005, 96, 389–392. [Google Scholar]
- Aranaz, I; Mengíbar, M; Harris, R; Paños, I; Miralles, B; Acosta, N; Galed, G; Heras, Á. Functional Characterization of Chitin and Chitosan. Curr Chem Biol 2009, 3, 203–230. [Google Scholar]
- Mcafee, BJ; Gould, WD; Nadeau, JC; Costa, ACA. Biosorption of metal ions using chitosan, chitin and biomass of Rhizopus oryzae. Sep Sci Technol 2001, 36, 3207. [Google Scholar]
- Chen, GQ; Shi, XG; Tang, W; Xiong, SM; Zhu, J; Cai, X; Han, ZG; Ni, JH; Shi, GY; Jia, PM; Liu, MM; He, KL; Niu, C; Ma, J; Zhang, P; Zhang, TD; Paul, P; Naoe, T; Kitamura, K; Miller, W; Waxman, S; Wang, ZY; de The, H; Chen, SJ; Chen, Z. Use of arsenic trioxide (As2O3) in the treatment of acute promyelocytic leukemia (APL): I. As2O3 exerts dose-dependent dual effects on APL cells. Blood 1997, 89, 3345–3353. [Google Scholar]
- Zhang, P. The use of arsenic trioxide (As2O3) in the treatment of acute promyelocytic leukemia. J Biol Regul Homeost Agents 1999, 13, 195–200. [Google Scholar]
- Cui, X; Kobayashi, Y; Akashi, M; Okayasu, R. Metabolism and the paradoxical effects of arsenic: carcinogenesis and anticancer. Curr Med Chem 2008, 15, 2293–2304. [Google Scholar]
- Gochi, A; Orita, K; Fuchimoto, S; Tanaka, N; Ogawa, N. The prognostic advantage of preoperative intratumoral injection of OK-432 for gastric cancer patients. Br J Cancer 2001, 84, 443–451. [Google Scholar]
- Yu, J; Qian, H; Li, Y; Wang, Y; Zhang, X; Liang, X; Fu, M; Lin, C. Arsenic trioxide (As2O3) reduces the invasive and metastatic properties of cervical cancer cells in vitro and in vivo. Gynecol Oncol 2007, 106, 400–406. [Google Scholar]
- You-Jin, J; Se-Kwon, K. Antitumor activity of chitosan oligosaccharides produced in ultrafiltration membrane reactor system. J Microbiol Biotechnol 2002, 12, 503–507. [Google Scholar]
- Kim, S; Rajapakse, N. Enzymatic production and biological activities of chitosan oligosaccharides (COS): A review. Carbohydr Polym 2005, 62, 357–368. [Google Scholar]
- Gabizon, AA; Shmeeda, H; Zalipsky, S. Pros and cons of the liposome platform in cancer drug targeting. J Liposome Res 2006, 16, 175–183. [Google Scholar]
- Maeda, H; Bharate, GY; Daruwalla, J. Polymeric drugs for efficient tumor-targeted drug delivery based on EPR-effect. Eur J Pharm Biopharm 2009, 71, 409–419. [Google Scholar]
- Masotti, A; Bordi, F; Ortaggi, G; Marino, F; Palocci, C. A novel method to obtain chitosan/DNA nanospheres and a study of their release properties. Nanotechnology 2008, 19, 055302. [Google Scholar]
- Masotti, A; Ortaggi, G. Chitosan micro- and nanospheres: fabrication and applications for drug and DNA delivery. Mini Rev Med Chem 2009, 9, 463–469. [Google Scholar]
- Soane, RJ; Frier, M; Perkins, AC; Jones, NS; Davis, SS; Illum, L. Evaluation of the clearance characteristics of bioadhesive systems in humans. Int J Pharm 1999, 178, 55–65. [Google Scholar]
- Varma, AJ; Deshpande, SV; Kennedy, JF. Metal complexation by chitosan and its derivatives: a review. Carbohydr Polym 2004, 55, 77–93. [Google Scholar]
- Crini, G; Badot, P. Application of chitosan, a natural aminopolysaccharide, for dye removal from aqueous solutions by adsorption processes using batch studies: A review of recent literature. Prog Polym Sci 2008, 33, 399–447. [Google Scholar]
- Stefancich, S; Delben, F; Muzzarelli, RAA. Interaction of soluble chitosans with dyes in water. I. Optical evidence. Carbohydr Polym 1994, 24, 17–23. [Google Scholar]
- Delben, F; Gabrielli, P; Muzzarelli, RAA; Stefancich, S. Interaction of soluble chitosans with dyes in water. II. Thermodynamic data. Carbohydr Polym 1994, 24, 25–30. [Google Scholar]
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