2011
DOI: 10.1016/j.wasman.2010.10.003
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Generation of and control measures for, e-waste in Hong Kong

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Cited by 82 publications
(51 citation statements)
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“…However, the average fraction of DBDPE for Hong Kong sites was 0.60 ± 0.16, significantly greater than 0.5 (p < 0.0001); while that for Daya Bay sites was 0.38 ± 0.14, significantly less than 0.5 (p = 0.036), further corroborating the above-mentioned notion that the life cycles of electronic products have been generally shorter in Hong Kong than in mainland China. 43 Sediment Records of Halogenated Flame Retardants Related to Industrializing Process. To reconstruct the sedimentation histories of HFRs, two sediment cores were collected from two locations with relatively stable depositional conditions.…”
Section: ■ Results and Discussionmentioning
confidence: 99%
“…However, the average fraction of DBDPE for Hong Kong sites was 0.60 ± 0.16, significantly greater than 0.5 (p < 0.0001); while that for Daya Bay sites was 0.38 ± 0.14, significantly less than 0.5 (p = 0.036), further corroborating the above-mentioned notion that the life cycles of electronic products have been generally shorter in Hong Kong than in mainland China. 43 Sediment Records of Halogenated Flame Retardants Related to Industrializing Process. To reconstruct the sedimentation histories of HFRs, two sediment cores were collected from two locations with relatively stable depositional conditions.…”
Section: ■ Results and Discussionmentioning
confidence: 99%
“…Several methods to forecast the amount of waste that will emerge have been developed, as described in Chancerel (2010), Polák and Drápalová (2012). These methods have been applied to forecast e-waste generation in several regional and national studies (Polák and Drápalová, 2012;Huisman et al, 2012;Yang et al, 2008;Dwivedy and Mittal, 2010;Chung et al, 2011;Zhang et al, 2011;Araújo et al, 2012). However, the results of these studies are mainly aimed to provide a baseline to optimize planning of e-waste policies, management of take-back systems and monitoring of legislative implementation (Beigl et al, 2008).…”
Section: Introductionmentioning
confidence: 99%
“…Brazil (Araújo et al 2012 ), China (Liu et al 2006 ;Yang et al 2008 ;Chung 2012 ;Zhang et al 2012 ;Habuer et al 2014 ;Li et al 2015 ), Chile (Steubing et al 2010 ), Czech Republic (Polak and Drapalova 2012 ), Germany (Walk 2009 ), Hong Kong (Chung et al 2011 ;Lau et al 2013 ), India (Dwivedy and Mittal 2010a , b ), Indonesia (Andarani and Goto 2014 ), Iran (Rahmani et al 2014 ;Alavi et al 2015 ), Japan (Yamasue et al 2007 ;Oguchi et al 2008 ;Yoshida et al 2009 ), Nigeria Nnorom and Osibanjo 2008 ), South Korea (Lee et al 2007 ;Kim et al 2013 ), Spain (Gutierrez et al 2010 ), USA (Kang and Schoenung 2006 ;Leigh et al 2007 ;Kahhat and Williams 2012 ;Lam et al 2013 ;Schumacher et al 2014 ), and in the global economy (Yu et al 2010 ). Some studies have estimated fl ows of specifi c materials contained in e-waste such as steel, aluminum, copper, lead, nickel, and zinc (Yamasue et al 2007 ;Lam et al 2013 ;Habuer et al 2014 ) and parts such as lithium-ion batteries (Chang et al, 2009 ).…”
Section: End-of-life Vehicles and E-wastementioning
confidence: 99%