Sorted but Still Buried: Hong Kong’s Unfinished Plastic Loop

After pouring away the remaining half bottle of distilled water, you put the plastic bottle, with its cap and label still attached, into the brown bin on the street corner. As far as you are concerned, that is the end of the bottle’s story.


Professor Guojun He and Ms Qidan Wang

8 July 2026

After pouring away the remaining half bottle of distilled water, you put the plastic bottle, with its cap and label still attached, into the brown bin on the street corner. As far as you are concerned, that is the end of the bottle’s story. However, there is a good chance that the bottle will not make its way to recycling, but will instead be sent to a landfill.

Plastic reduction works, but recycling lags behind

The story begins with two sets of figures from 2024. On the one hand, the disposal of waste plastics in Hong Kong declined from 2,120 tonnes per day in 2023 to 1,885 tonnes per day, representing a decrease of 11.1% (see Note 1). Under the Product Eco-responsibility (Amendment) Ordinance 2023, the first phase of regulation of disposable plastic products was implemented in 2024. Coupled with other plastic-reduction measures, such as enhancements to the Plastic Shopping Bag Charging Scheme, these initiatives are beginning to take effect. On the other hand, the quantity of plastics recycled over the same period dropped sharply from 128,200 tonnes to 101,500 tonnes, representing a decrease of more than 20%, roughly equivalent to the weight of 1,800 double-decker buses.

Less plastic is being discarded at source, yet the amount recovered for recycling has declined even more. If progress has been made in plastic reduction, why has recycling fallen behind?

Tracing the roots of the recycling bottleneck

Let us examine the three stages of the recycling chain, one by one.

First, exports. In explaining the decline in plastics recycled, the Environmental Protection Department cited the backdrop of tighter global import controls under the amendments to the Basel Convention. However, plastics recycling in Hong Kong has barely relied on exports in recent years. Research by the Legislative Council indicates that “almost all recovered plastics in Hong Kong are processed locally” (see Note 2). In 2024, exports of plastics amounted to only about 10,000 tonnes (see Note 3), far too little to explain the decrease of 26,700 tonnes.

Second, local processing. At present, Hong Kong’s only near-food-grade plastic bottle recycling facility can convert waste plastics into recycled polyethylene terephthalate (rPET). Its maximum monthly capacity of about 1,200 tonnes is theoretically sufficient to handle around half of all plastic beverage containers sold locally. However, since commencing operation in 2022, the facility has suffered from insufficient intake; in 2025, it was operating at only about 40% of its capacity. This shows that the bottleneck lies not in processing capacity, but in the actual amount recovered.

Having ruled out these two factors, the decline clearly lies at the front end of the chain. Plastic bottles are either not placed in recycling bins by members of the public in the first place, or, after being deposited, are treated as rubbish because they are heavily contaminated. The former concerns “quantity”, while the latter concerns “quality”. Both point to the same problem―how the public handles waste plastic containers and how producers design their products.

Who should be responsible for the clean-up

In the late 1990s, the government introduced colour-coded recycling bins (blue, yellow, and brown), helping the public develop the concept of waste classification. Unfortunately, the issue of contamination was never properly addressed. Once plastic bottles are mixed with food waste, tissues, or residual liquid, the purity of the feedstock falls, and the costs of each subsequent processing step rise accordingly. If an entire bin of materials is too heavily contaminated, frontline contractors, after weighing costs and benefits, can only treat it as waste. This is one reason for the underutilization of local recycling and reprocessing facilities―even when waste plastic containers are collected, they often fail to meet near-food-grade standards because of contamination.

Product design is another key factor. Whether a plastic bottle can be “reborn” is, to a large extent, already determined at the moment it is manufactured. Clear, colourless PET is ideal. Coloured bottles, polyvinyl chloride (PVC) labels, and full-wrap labels all substantially reduce recycling value. Japan has long relied on industry self-regulation to make clear, colourless PET the mainstream material for plastic bottles. The Plastic Resource Circulation Act, implemented in 2022, further incorporated the plastic life cycle into integrated management. Members of the public also proactively remove labels and caps before recycling, resulting in exceptionally high feedstock purity for back-end processing.

By contrast, Hong Kong lacks both regulation and industry standards. Plastic bottle manufacturers focus more on shelf appeal and bear no financial responsibility for the after-use management of their products. With bottles produced in a variety of colours and labels designed in different forms, many are destined to be nonrecyclable from the outset. In practice, this amounts to shifting costs from producers onto society as a whole and the downstream recycling system.

Sending price signals to both supply and demand sides

Clearly, price signals are missing at both ends. Producers do not take recycling costs into account when designing packaging. When people discard plastic bottles, whether the containers are clean and whether they are returned to a recycling point have no effect on their own wallets. To realign dispersed individual decisions with environmental objectives, price signals should be provided on both the supply and demand sides.

Two tools are available on the supply side. First, fees under the Producer Responsibility Scheme could be tiered: higher fees should be charged for designs that are difficult to recycle, while fee reductions or exemptions should be granted for clear, colourless, single-material designs with easy-to-remove labels. References can be made to the practices of “recyclability ratings” under the European Union’s Packaging and Packaging Waste Regulation 2025/40 and the UK’s Plastic Packaging Tax. Second, a deposit-refund system could be introduced at the consumption level, putting a price on whether bottles are returned, so that returning plastic bottles becomes not merely an environmental good deed, but also an economic incentive. Germany’s deposit system, under which a deposit of 0.25 euros (approximately HK$2) is charged on certain plastic beverage bottles, has been sufficient to raise the recycling rate of these bottles to over 90%. Hong Kong need not copy this model wholesale, but even starting with a deposit of HK$0.5 to HK$1 per bottle would probably be sufficient to change public recycling behaviour.

It should also be noted that if no one purchases rPET, local recycling facilities will still be underutilized. This is because rPET usually costs more than virgin PET, while the environmental externalities of the latter have yet to be priced. Demand-side requirements must therefore be strengthened by incorporating a “mandatory recycled-content escalation schedule” into the Producer Responsibility Scheme. For example, plastic beverage bottles sold in Hong Kong could be required to contain at least 15% locally recycled rPET from 2027, rising to 30% by 2030. The fact that some local beverage brands have already adopted bottles made from 100% locally recycled rPET proves that these targets are technically achievable. What is lacking is a mechanism to turn this choice from a voluntary action by a small number of brands into a standard requirement across the entire industry.

Taken together, these three tools would constitute a complete closed loop. Differentiated fees push costs back to the design stage, a deposit-refund system attaches costs and incentives to the point of return, and mandatory recycled content creates market demand for rPET. Once all three signals are in place, there will be strong enough incentives for producers to improve product design, for consumers to return plastic bottles in a clean condition, and for recyclers to obtain a reliable supply of clean materials for reprocessing and sale.

Conclusion: think twice before you throw away a plastic bottle

The decline in the quantity of plastics recycled in 2024 is not due to external export controls or insufficient local processing capacity. Rather, it reflects failures in both supply and quality at the front end of the recycling chain, as well as a back-end market that has yet to make room for recycled materials. As plastic reduction at source begins to take effect and local processing facilities long remain underused, this rupture in the middle of the chain is precisely the missing link that Hong Kong must address for its plastics closed loop to shift from quantity to quality. Differentiating fees according to recyclability, introducing a deposit-refund system, and mandating recycled-content standards can simultaneously send the price signals missing on both the supply and demand sides. However, whether these signals can reach all the way from public recycling bins to reprocessing lines will depend on whether the system is designed with sufficient precision.

Prior to the implementation of this system, everyone should take a few extra seconds emptying any remaining liquid, removing the bottle cap, and tearing off the label. This will not solve all the problems, but it is one link in this long recycling chain where every citizen can do their part. The real test of Hong Kong’s plastics closed loop begins with the choice made in these two seconds―and with whether the system can make these two seconds worth the effort.

Note 1: https://impact.hkubs.hku.hk/wp-content/uploads/2026/08/292079-msw2024_eng.pdf

Note 2: https://impact.hkubs.hku.hk/wp-content/uploads/2026/08/292079-ISSH10_2024_20240520_en.pdf

Note 3: https://impact.hkubs.hku.hk/wp-content/uploads/2026/08/292079-fc_25-26_eng.pdf

Acknowledgements

The authors would like to thank Ms 鄭倩薇 for providing industry information for this article.

Translation

膠樽進填埋   減塑難閉環

你把喝剩的半支蒸餾水倒掉,然後把膠樽連蓋帶標籤投進街角的啡色桶。對你而言,這支膠樽的故事到此為止;但它有頗大機會並不會通往回收再造之路,而是被送到堆填區。

減塑見效但回收退步

故事從 2024 年的兩組數字說起。一方面,香港廢塑膠棄置量由2023年每日2,120 公噸下降至1,885 公噸,跌幅 11.1%【註1】。《2023年產品環保責任(修訂)條例》下,首階段管制即棄膠產品於2024 年實施,加上優化塑膠購物袋收費計劃等「走塑」措施,正在發生作用。另一方面,塑膠的循環再造量同期由128,200 公噸大幅下跌至101,500 公噸,跌幅超過兩成,大約等於1,800 架雙層巴士的重量。

源頭丟棄少了,但收回來再造的更少。減塑已取得進展,為何回收卻退步?

循環再造瓶頸溯源

不妨沿着回收鏈3個環節,逐一排查。

首先是出口。環境保護署在解釋跌幅時引述了《巴塞爾公約》修正案下全球進口管制趨嚴的背景。但過去幾年香港塑膠回收幾乎從不依賴外運,立法會研究指本港「幾近所有回收塑膠均在本港處理」【註2】,2024 年塑料出口量僅約1 萬公噸【註3】,遠不足以解釋這26,700 公噸跌幅。

其次是本地處理。目前本港唯一的準食品級膠樽回收設施,能將廢樽轉化成再生聚酯(rPET ),每月最高處理量約1200 公噸,理論上足以消化全港約一半的飲品膠樽銷售量。但自2022年投產以來,該廠的回收量不足,2025年只佔處理能力的4成。由此可見,瓶頸不在能否處理,而在實際回收量。

排除了這兩個因素,跌幅顯然就在最前端。膠樽要麼根本沒被市民投入回收箱,要麼在投入之後,卻因污染過重而被當垃圾處理。前者關乎「量」,後者涉及「質」;兩者都指向同一問題——市民如何處理廢膠樽,以及生產商如何設計產品。

誰來承擔善後責任

1990 年代末,政府推出藍、黃、啡三色回收桶,讓市民建立了分類概念,可惜始終未觸及污染一環。一旦膠樽混入食物殘渣、紙巾或殘留液體,純度下降,後續每一步驟的成本便逐級上升。當整桶物料污染過重,前線承辦商在成本效益權衡下,只能當作垃圾處理。本港回收再造設施產能過剩的原因之一正在於此——即使收到廢膠樽,也往往因污染而無法達到準食品級標準。

至於產品設計方面,一支膠樽能否「重生」,其實被裝瓶那刻已寫好一大半。無色透明 PET 最為理想,雜色樽身、聚氯乙烯(PVC)標籤、整樽包覆的長標籤,都會大幅削弱再造價值。日本長期透過行業自律,達至膠樽以無色透明PET 為主流。2022 年實施的《塑膠資源循環促進法》更把生命周期納入綜合管理;市民回收時主動除去標籤與樽蓋,使後端進料純度極高。

反觀香港,由於缺乏監管與行業標準,生產商側重貨架上的視覺吸引力,毋須為產品善後承擔任何經濟責任。樽身用色繁雜、標籤形制不一,不少從源頭便已注定無法再生。這實際上是把生產端成本,變相轉嫁給整體社會與後端回收系統。

在供求兩端傳遞價格訊號

顯而易見,兩端都缺乏價格訊號。生產商設計在包裝過程中,並未考慮回收成本;市民丟掉膠樽時,容器潔淨與否、是否歸還回收點,也無關自身錢包。要讓分散的個人決策重新與環境目標接軌,可在供給方與需求方同時提供訊號。

供給方有兩個工具。一、《生產者責任計劃》的收費可分檔釐定,難以回收的設計收費較高,無色透明、單一材質、易撕標籤者則予以減免。可參考歐盟《包裝及包裝廢物法規》(Packaging and Packaging Waste Regulation 2025/40)與英國《塑膠包裝稅》(Plastic Packaging Tax)對「可回收性等級」的做法。二、在消費層面配以按金退還,為歸還與否標價,使交回膠樽不再只是環保善舉,而成為一項經濟誘因。德國對特定飲料塑膠瓶實施每樽 0.25 歐元(約港幣兩元)的按金制度,已足以將這類瓶子回收率推高至九成以上。香港不必照搬,但即使以每樽0.5 1 港元起步,相信已足以改變市民的回收行為。

不可不察的是,若無人購買 rPET,本地再造設施仍會吃不飽。原因在於rPET 成本通常高於原生PETvirgin PET),後者的環境界外效應(environmental externality)未被定價。需求方因此必須強化,在《生產者責任計劃》中加入「強制再生含量遞增表」,例如 2027 年起,本地售賣的飲品膠樽須含至少15% 本地rPET,至2030 年則提升至30%。現時部分本地飲品品牌已採用百分之百本地再造rPET 製樽,證明技術上可達標;缺的只是讓這個選擇從少數品牌的自願行動,變成整個行業的規定動作。

三項工具合起來,便構成一個完整的閉環。差別徵費把成本壓回設計端,按金退還把成本聚焦於回收點,強制再生含量則令市場關注 rPET 。當3道訊號同時到位,就有足夠誘因令生產商改良設計、市民把膠樽潔淨歸還,回收商因而獲得充足的潔淨物料,加以再造出售。

結語:下次扔膠樽前的那兩秒

2024 年塑膠回收量下滑,並非源於外圍出口管制,也非本地處理能力不足,而是回收鏈前端的供應與質素雙雙失守,以及後端市場仍未為再生物料留位。當源頭減塑開始見效、本地處理設施又長期閒置,夾在中間的這道斷裂,正是香港塑膠閉環從量走向質必須補上的一環。將收費因應回收難易程度分級、引入按金退還、規定再生含量標準,可同時發出供給與需求兩方所欠缺的價格訊號;但制度設計是否足夠精細,將決定訊號能否貫穿由公共回收桶到再生處理線的鏈條。

在制度尚未落實之前,人人不妨多花幾秒鐘,倒乾殘液、取下樽蓋、撕去標籤。這不會解決所有問題,但它是在這條長長回收鏈上,每個市民都可盡力參與的唯一環節。而香港塑膠閉環的真正考驗,也正始於這兩秒的選擇——以及制度能否讓這兩秒,值得被付出。

註1:環境保護署:《香港固體廢物監察報告——2024 年的統計數字》,2025 12 月。

註2:立法會秘書處資料研究組:《香港廢物回收面對的挑戰》,2024 5 月。

註3:環境保護署:《審核 2025–26 年度開支預算管制人員對立法會議員初步問題的答覆》。

鳴謝

本文獲業界鄭倩薇女士提供行業資料,特此致謝。

何國俊教授
香港大學賽馬會基金經濟學教授、香港大學賽馬會環球企業可持續發展研究所所長

王芑丹女士
香港大學賽馬會環球企業可持續發展研究所專職研究員

(本文同時於二零二六年七月八日載於《信報》「龍虎山下」專欄)