Nanoscale iron particles for complete reduction of chlorinated ethenes

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Abstract

This paper examines the potential for using laboratory synthesized nanoscale Pd/Fe bimetallic particles to reduce chlorinated ethenes. Rapid and complete dechlorination was achieved for six chlorinated ethenes: tetrachloroethene (PCE, C2Cl4), trichloroethene (TCE, C2HCl3), 1,1-dichloroethene (1,1-DCE, C2H2Cl2), cis- and trans-1,2-dichloroethene (c-DCE, t-DCE, C2H2Cl2), and vinyl chloride (VC, C2H3Cl). The chlorinated ethenes (20 mg l−1) were completely reduced within 90 min at a metal loading of 5 g l−1. Ethane was the primary product from these reactions, amount to 60–90% of the total carbon. Ethene (3–20%) was produced during the transformation of TCE, DCEs and VC. No chlorinated intermediates or final products were detected above the method detection limit (<5 μg l−1). The remarkable performance of the nanoscale particles can be attributed to: (1) High specific surface area of the nanoscale metal particles, approximately 35 m2 g−1, tens to hundreds of times higher than commercial grade micro- or milli-scale iron particles; (2) Increased reactivity per unit metal surface area, largely due to the presence of the noble metal (Pd) on the surface. Values of the surface-area-normalized rate coefficients (kSA) were two orders of magnitude higher than those reported in the literature for larger iron particles. Due to their small particle size and high reactivity, the nanoscale bimetallic particles may be useful in a wide array of environmental applications including subsurface injection for groundwater treatment.

Introduction

The rediscovery of zero-valent iron for the transformation of chlorinated organic compounds has led to the development and proliferation of a number of environmental applications, particularly in so far as groundwater remediation is concerned. Research in the past few years has demonstrated that metals such as iron and zinc can effectively reduce a broad array of organic compounds such as chlorinated aliphatics [1], [2], [3], [4], [5], [6], nitro aromatics [7], polychlorinated biphenyls (PCBs) [8], pesticides and related compounds [9], [10]. Applications of zero-valent iron for remediating contaminated soils, sediments and aquifers have received particular attention. An attractive feature is that it can be readily incorporated into reactive subsurface barriers via the ‘funnel and gate’ approach [11], [12], [13]. As contaminated water passes through the permeable wall of iron particles, organic contaminants react with iron to form primarily non-toxic end products such as hydrocarbons and chloride ion.

Bimetallic particles (e.g. Pd/Fe, Pd/Zn) have been shown to exhibit a high efficacy for the transformation of many chlorinated compounds. For example, palladized iron has been demonstrated to rapidly dechlorinate chlorinated ethenes such as PCE, TCE, 1,1-DCE, c-DCE, and t-DCE [14]. These compounds can be completely reduced to ethane in just a few minutes. The palladized iron was also noted for its effective transformation of PCBs [15]. Ni/Fe and Cu/Fe were used to transform 1,1,1-trichloroethane [16]. Other bimetals such as Pt/Fe, Pd/Zn have been reported for the degradation of chlorinated benzenes [17].

We reported using nanoscale metallic particles for transformation of TCE, chlorinated benzenes and polychlorinated biphenyls (PCBs) [18], [19]. The nanoscale metallic particles, with diameter on the order of 1 to 100 nm, were synthesized in the laboratory. A small amount (∼0.05% wt.) of Pd was deposited on the iron surface to enhance the reactivity of the metal particles. Preliminary experimental results suggest that reactivity of Pd/Fe particles is significantly higher than that of commercial grade iron particles. Due to their small particle sizes and high reactivity, the nanoscale metal particles may be useful in a wide array of environmental applications. For example, the metal particles could be injected directly into contaminated soils, sediments and aquifers [20], [21] for in situ treatment of chlorinated hydrocarbons, offering a relatively low-cost alternative to such conventional technology as pump and treat, air sparging or reactive barriers.

In this paper, systematic laboratory studies applying the nanoscale bimetallic particles for transformation of chlorinated ethenes (PCE, TCE, t-DCE, c-DCE, 1,1-DCE, VC) are presented. These compounds are among the most prevalent contaminants in soils and aquifers [22], [23]. They have been listed as priority pollutants by the US Environmental Protection Agency, and also on the Superfund National Priority List. These compounds are known or potential threats to public health and the environment so there is an urgent need to develop effective control methods. This study was aimed to: (1) characterize and quantify reaction intermediates and final products; (2) assess the stability of the nanoscale metal particles; and (3) examine their reactivity compared to larger commercial grade iron particles. This information is essential for exploring the possible environmental applications of the nanoscale metal particles.

Section snippets

Preparation of nanoscale metal particles

Synthesis of nanoscale iron particles was achieved by adding 1:1 volume ratio of NaBH4 (0.25 M) into FeCl3 · 6H2O (0.045 M) [17], [18], [19]. The solution was mixed vigorously under room temperature for 5 min (22±1 °C). Ferric iron was reduced by borohydride according to the following reaction:4Fe3++3BH4+9H2O→4Fe0+3H2BO3+12H++6H2The borohydrate to ferric iron ratio added was 7.4 times of the stoichiometric requirement according to Equation 1. Excessive borohydrate was the key factor for rapid

Reactions of chlorinated ethenes with nanoscale metallic particles

Reactions of the six chlorinated ethenes with the nanoscale Pd/Fe bimetallic particles are shown in Fig. 1(a–f). Concentrations in the figure are expressed as the molar ratio to initial organic concentrations. As shown in Fig. 1(a), 20 mg l−1 PCE was completely dechlorinated within 90 min. We observed the immediate appearance of ethane corresponding to the disappearance of PCE. Average yield of ethane was 89% after 1 h. Trace amounts of TCE were detected briefly (<1 h). The amount of TCE was

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