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OriginalThese desiderata originate in resource recovery in the manufacturing and processing processes. WBEV recycling is receiving more attention, and the relevant research is expanding.
中文这些需求源于制造和加工过程中的资源回收。 WBEV回收越来越受到关注,相关研究也在不断扩大。
OriginalFigure 1a demonstrates that papers on WBEV recycling were uncommon prior to 2016, but their numbers began to increase after 2017. However, this report found only 851 articles with the keywords "EV battery recycling," "electric vehicle recycling," or "power battery recycling" in the web of science (WOS) core collection database on 17 September 2022.
中文图 1a 表明,关于 WBEV 回收的论文在 2016 年之前并不常见,但其数量在 2017 年之后开始增加。 然而,该报告在2022年9月17日的Web of Science(WOS)核心合集数据库中仅发现了851篇含有“电动汽车电池回收”、“电动汽车回收”或“动力电池回收”关键词的文章。
OriginalSimilarly, as shown in Figure 1b, on 17 September 2022, this paper found only 695 articles containing the keywords "car battery recycling" or "power battery recycling" on the China National Knowledge Infrastructure (CNKI) website.
中文同样,如图1b所示,2022年9月17日,本文在中国知网(CNKI)网站上仅找到包含“汽车电池回收”或“动力电池回收”关键词的文章695篇。
OriginalSustainability 2023, 15, x FOR PEER REVIEW 4 of 21 system (including consumption and use). Natural resources should be used rationally in the production and processing process, energy and raw materials should be processed into environmentally friendly products as much as possible using advanced technology and onsite recycling, and final products should be consumed in a rational manner during the circulation process and consumption.
中文可持续发展 2023, 15, x FOR PEER REVIEW 4 of 21 系统(包括消耗和使用)。 在生产加工过程中合理利用自然资源,利用先进技术和就地回收尽可能将能源和原材料加工成环保产品,最终产品在流通过程和消费过程中合理消耗。
OriginalThese desiderata originate in resource recovery in the manufacturing and processing processes. WBEV recycling is receiving more attention, and the relevant research is expanding.
中文这些需求源于制造和加工过程中的资源回收。 WBEV回收越来越受到关注,相关研究也在不断扩大。
OriginalFigure 1a demonstrates that papers on WBEV recycling were uncommon prior to 2016, but their numbers began to increase after 2017. However, this report found only 851 articles with the keywords "EV battery recycling," "electric vehicle recycling," or "power battery recycling" in the web of science (WOS) core collection database on 17 September 2022.
中文图 1a 表明,关于 WBEV 回收的论文在 2016 年之前并不常见,但其数量在 2017 年之后开始增加。 然而,该报告在2022年9月17日的Web of Science(WOS)核心合集数据库中仅发现了851篇含有“电动汽车电池回收”、“电动汽车回收”或“动力电池回收”关键词的文章。
OriginalSimilarly, as shown in Figure 1b, on 17 September 2022, this paper found only 695 articles containing the keywords "car battery recycling" or "power battery recycling" on the China National Knowledge Infrastructure (CNKI) website.
中文同样,如图1b所示,2022年9月17日,本文在中国知网(CNKI)网站上仅找到包含“汽车电池回收”或“动力电池回收”关键词的文章695篇。
Original(a) (b) Figure 1. Articles with the topic of WBEV recycling in WOS and CNKI: (a) articles with the topic of WBEV recycling from 1995~2022 in WOS; (b) articles with the topic of WBEV recycling from 2004~2022 in CNKI.
中文(a) (b) 图 1。 WOS和CNKI中WBEV回收主题的文章:(a)WOS 1995~2022年WBEV回收主题的文章; (b) 主题为 WBEV 回收的文章 2004~2022年中国知网。
Original2.1. Recycling Modes of WBEVs
中文2.1. WBEV的回收模式
OriginalThe literature primarily discusses four types of recycling systems: (1) a recycling mode driven by manufacturers (Mode ), who recycle WBEVs directly from consumers through their sales channels [20,21]; (2) a recycling mode driven by retailers (Mode ), whom the manufacturers have encouraged to take on the responsibility for recycling [4]; (3) a recycling mode (Mode ) in which producers outsource the recycling process to wellequipped third parties [21,22]; (4) a recycling mode (Mode ), that is often constituted of manufacturers or sellers and has the benefit of a scale economy [21].
中文文献主要讨论了四种类型的回收系统:(1)制造商驱动的回收模式(模式),制造商通过销售渠道直接从消费者那里回收WBEV[20,21]; (2)零售商推动的回收模式(模式),制造商鼓励零售商承担回收责任[4]; (3)回收模式(Mode),生产者将回收过程外包给装备精良的第三方[21,22]; (4)回收模式(Mode),通常由以下组成 制造商或销售商,并具有规模经济的好处[21]。
OriginalThe ideal recycling structure and pathways have been addressed in the literature. Tang et al. [4] investigated the social welfare implications of single-channel recycling modes (as ModeM, ModeR, and ModeTP) as well as competing dual-channel recycling modes (as mode ModeM,R, ModeM,TP, and ModeR,TP), concluding that ModeM,R is the optimal recycling method.
中文文献中已经讨论了理想的回收结构和途径。 唐等人。 [4]研究了单渠道回收模式(如ModeM、ModeR和ModeTP)以及竞争性双渠道回收模式(如模式ModeM,R、ModeM,TP和ModeR,TP)的社会福利影响,得出结论:ModeM,R是最佳回收方法。
OriginalAccording to Zan and Zhang [21], the ideal recycling method for manufacturers is determined by the trade-offs between recycling and reuse costs. Li [22] examined the EV battery supply chain using ModeM, ModeR, ModeTP, and dualchannel modes, claiming that the best mode to use is determined by competition and third-party economies of scale.
中文根据Zan和Zhang的研究[21],制造商理想的回收方法是由回收和再利用成本之间的权衡决定的。 李 [22]使用ModeM、ModeR、ModeTP和双通道模式检查了电动汽车电池供应链,声称最佳使用模式是由竞争和第三方规模经济决定的。
OriginalWBEV recycling is mostly carried out by industry organizations and partnerships in Europe and the United States, and the government has developed a deposit system to encourage battery registration and required restitution [23].
中文WBEV回收主要由欧洲和美国的行业组织和合作伙伴进行,政府制定了押金制度以鼓励电池注册和要求归还[23]。
OriginalIn Japan, battery manufacturers create recycling routes using reverse logistics, and recycling is subsidized by the government [23]. According to the "Measures for the Management of Recovery and Utilization of Power Batteries for New Energy Vehicles" law in China, EV producers are responsible for recycling WBEVs and must develop power battery recycling routes within the EPR system.
中文在日本,电池制造商利用逆向物流创建回收路线,回收由政府补贴[23]。 根据我国《新能源汽车动力电池回收利用管理办法》,电动汽车生产企业应承担以下责任: 能够回收WBEV的企业必须在EPR系统内开发动力电池回收路线。
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OriginalSustainability 2023, 15, 2630 5 of 20
中文可持续发展 2023, 15, 2630 5 of 20
Original2.2. Literature Review on Consumers' WTR WBEVs
中文2.2.消费者 WTR WBEV 文献综述
OriginalConsumers are the most important participants in the WBEV recycling process. Since the Chinese government encouraged the use of EVs in 2015, the market share of EVs has grown year after year.
中文消费者是WBEV回收过程中最重要的参与者。 自2015年中国政府鼓励使用电动汽车以来,电动汽车的市场份额逐年增长。
OriginalEV market share has increased from 0.34% in 2015 to 2.6% in 2021, as shown in Figure 2a. EV batteries have a lifespan of 5–8 years. Consumers can change batteries when their performance is no longer good.
中文电动汽车市场份额从 2015 年的 0.34% 增长至 2015 年的 2.6% 2021年,如图2a所示。电动汽车电池的使用寿命为 5 至 8 年。消费者可以 当电池性能不再良好时更换电池。
OriginalThe retired batteries form a massive mound of WBEVs. Typically, consumers have four options for participating in WBEV recycling: up of EV manufacturers and cascade usage firms.
中文退役的电池形成了一大堆WBEV。 通常,消费者有四种参与 WBEV 回收的选择:电动汽车制造商和梯级使用公司。
OriginalFormal recyclers are regulated a proved facilities that process garbage with some level of industrial hygiene and w protection, and they are typically equipped with the finest recycling equipment po and are subject to highly stringent environmental protection standards [25–27].
中文正规回收商受到监管和经过验证的垃圾处理设施,具有一定程度的工业卫生和保护,他们通常配备最好的回收设备,并遵守高度严格的环境保护标准[25-27]。
Originalexpansion of the recycling sector, the number of batteries recycled from official rec is quickly growing. As seen in Figure 2b,c, the recycling volume of lithium batte China rose by more than 20% between 2020 and 2021, and the recycling market sc panded by more than 50% over the same period.
中文随着回收行业的扩大,官方回收的电池数量正在快速增长。 如图2b、c所示,2020年至2021年间,中国锂电池回收量增长了20%以上,同期回收市场规模增长了50%以上。
Original(4) Informal recyclers buy the WBEVs or EOL EVs. Unlike formal recyclers, in recyclers are not regulated by the government [25,28]. They are tiny and disadvan businesses with a low profit threshold, no registration, no tax, no social welfare be and a high labor intensity [29,30].
中文(4) 非正式回收商购买WBEV 或EOL EV。 与正规回收商不同,回收商不受政府监管[25,28]。 它们是规模小、条件差的企业,盈利门槛低、不注册、不纳税、无社会福利、劳动强度高[29,30]。
OriginalInformal recyclers have fewer operational expens can offer greater prices than authorized recyclers. Despite the advantages of auth recyclers, most consumers choose to sell WBEVs to informal recyclers, since they provide substantial compensation and door-to-door service [31].
中文非正式回收商的运营费用较少,可以提供比授权回收商更高的价格。 尽管正规回收商具有优势,但大多数消费者选择将WBEV出售给非正规回收商,因为他们提供丰厚的补偿和上门服务[31]。
OriginalOn the other ha formal recycling is harmful to the environment and endangers human health. (a) (b) (c) Figure 2. (a) Statistics of EV ownership in China from 2015 to 2021 (10,000 pieces).
中文另一方面哈 正规回收对环境有害,危害人体健康。 (a) (b) (c) 图2. (a) 2015年至2021年中国电动汽车保有量统计(万辆)。
OriginalData China Economic Industry Research Institute, Ministry of Public Security. Note: The percen lustrates the proportion of EV ownership in the total car ownership. (b) Recovery volume of batteries in China from 2018 to 2021(10,000 tons).
中文公安部数据中国经济产业研究院。 注:百分比表示电动汽车保有量占汽车总保有量的比例。 (b) 2018-2021年中国电池回收量(万吨)。
OriginalData source: EV Tank, China Economic In Research Institute. (c) Recycling market size of power lithium batteries in China from 201 (RMB 100 million). Data source: EV Tank, China Economic Industry Research Institute.
中文数据来源:EV Tank、中国经济研究院。 (c) 201年以来中国动力锂电池回收市场规模 (人民币1亿元)。 数据来源:EV Tank,中国经济产业研究院。
OriginalN percentage indicates the annual growth rate; 2022E is a prediction.
中文N百分比表示年增长率; 2022E是一个预测。
OriginalFigure 2. (a) Statistics of EV ownership in China from 2015 to 2021 (10,000 pieces).
中文图2.(a)2015年至2021年中国电动汽车保有量统计(万辆)。
OriginalData source: China Economic Industry Research Institute, Ministry of Public Security. Note: The percentage illustrates the proportion of EV ownership in the total car ownership. (b) Recovery volume of lithium batteries in China from 2018 to 2021 (10,000 tons).
中文数据来源:公安部中国经济产业研究院。 注:百分比表示电动汽车保有量占汽车总保有量的比例。 (b)2018-2021年中国锂电池回收量(万吨)。
OriginalData source: EV Tank, China Economic Industry Research Institute. (c) Recycling market size of power lithium batteries in China from 2019–2022 (RMB 100 million). Data source: EV Tank, China Economic Industry Research Institute.
中文数据来源:EV Tank,中国经济产业研究院。 (c) 2019-2022年中国动力锂电池回收市场规模(亿元)。 数据来源:EV Tank,中国经济产业研究院。
OriginalNote: the percentage indicates the annual growth rate; 2022E is a prediction. (1) Return the EOL EVs to 4S stores or auto salvage yards. (2) Return the WBEVs to 4S stores or battery leasing businesses.
中文注: 百分比表示年增长率; 2022E是一个预测。 (1)将报废的电动汽车退回4S店或汽车报废场。 (2)将WBEV返还给4S店或电池租赁商。
Original(3) Return the WBEVs to recycling facilities. Collected WBEVs will be transported to recycling centers via 4S retailers, vehicle salvage yards, battery leasing firms, or directly by customers.
中文(3) 将 WBEV 返回回收设施。 收集到的WBEV将通过4S零售商、汽车报废场、电池租赁公司或由客户直接运输到回收中心。
OriginalFollowing this, WBEVs will be cascade used or recycled (the flow of WBEVs is illustrated in Figure 3). Recycling centers are official recyclers that are primarily made up of EV manufacturers and cascade usage firms.
中文此后,WBEV 将被级联使用或回收(WBEV 的流程如图 3 所示)。 回收中心是官方回收商,主要由电动汽车制造商和梯级使用公司组成。
OriginalFormal recyclers are regulated and approved facilities that process garbage with some level of industrial hygiene and worker protection, and they are typically equipped with the finest recycling equipment possible and are subject to highly stringent environmental protection standards [25–27].
中文正规回收商是受监管和批准的垃圾处理设施,具有一定程度的工业卫生和工人水平 他们通常配备尽可能最好的回收设备,并遵守高度严格的环境保护标准[25-27]。
OriginalWith the expansion of the recycling sector, the number of batteries recycled from official recyclers is quickly growing. As seen in Figure 2b,c, the recycling volume of lithium batteries in China rose by more than 20% between 2020 and 2021, and the recycling market scale expanded by more than 50% over the same period.
中文随着回收行业的扩大,官方回收商回收的电池数量正在迅速增长。 如图2b、c所示,2020年至2021年间,中国锂电池回收量增长了20%以上,同期回收市场规模扩大了50%以上。
Original(4) Informal recyclers buy the WBEVs or EOL EVs. Unlike formal recyclers, informal recyclers are not regulated by the government [25,28]. They are tiny and disadvantaged businesses with a low profit threshold, no registration, no tax, no social welfare benefits, and a high labor intensity [29,30].
中文(4) 非正式回收商购买WBEV 或EOL EV。 与正规回收商不同,非正式回收商不受政府监管[25,28]。 它们是小型弱势企业,利润门槛低,无需注册,无需纳税,无社会福利,劳动强度高[29,30]。
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OriginalFigure 4 provides an illustration of the study's structure and hypotheses. Sustainability 2023, 15, x FOR PEER REVIEW 9 of 21 following areas: (1) 𝐺𝑃 : efficacy in promoting WBEV recycling; (2) 𝐺𝑃 : efficacy in supervising WBEV recycling; (3) 𝐺𝑃 : efficacy in alerting against illegal recycling; and (4) 𝐺𝑃 : efficacy in standardizing recycling disposal behavior.
中文图4 提供了研究结构和假设的说明。 可持续发展 2023, 15, x 供同行评审 21 个以下领域中的 9 个:(1) 𝐺𝑃:促进 WBEV 回收的功效; (2) 𝐺𝑃:监督WBEV回收的功效; (3)𝐺𝑃:对非法回收具有警示作用; (4)𝐺𝑃:规范回收处置行为的功效。
OriginalFigure 4. Study architecture and hypotheses. The second motivator of 𝑊𝑇𝑅 , 𝐸𝐴 , pertains to consumer attitudes about the environment. 𝐸𝐴 is determined by consumers' assessments of environmental effects in the following scenarios: (1) 𝐸𝐴 : irresponsible disposal of WBEVs; (2) 𝐸𝐴 : incineration of WBEV components; (3) 𝐸𝐴 : random dumping of WBEVs; and (4) 𝐸𝐴 : inappropriate disassembly of WBEVs.
中文图 4. 研究架构和假设。 𝑊𝑇𝑅 的第二个动机 𝐸𝐴 与消费者对环境的态度有关。 𝐸𝐴是根据消费者对以下情况下的环境影响的评估来确定的: (1) 𝐸𝐴:不负责任地处置WBEV; (2)𝐸𝐴:WBEV部件的焚烧; (3)𝐸𝐴:WBEV的随机倾销; (4) 𝐸𝐴:WBEV 的不当拆卸。
OriginalSome research has suggested a substantial positive association between environmental views and recycling behavior [58]. Kurz et al. [59] discovered a minimal link between environmental concern and recycling behavior.
中文一些研究表明环境观点和回收行为之间存在显着的正相关关系[58]。 库尔兹等人。 [59]发现了一个 环境问题和回收行为之间的联系最小。
OriginalAccording to the consumer theory of microeconomics, consumers make decisions based on the utility maximization principle [60]. On the other hand, consumers are frequently reported to stray from utility maximization theory, because traditional consumer theory is driven by the market mechanism, and it believes that consumers are completely rational and market knowledge is comprehensive [61].
中文根据微观经济学的消费者理论,消费者根据效用最大化原则进行决策[60]。 另一方面,消费者经常被报道偏离效用最大化理论,因为传统消费者理论是由市场机制驱动的,它认为消费者是完全理性的,市场知识是全面的[61]。
OriginalThese assumptions are frequently contradicted by reality. As a result, behavioral economics incorporates psychology into classical economics to explain the disparity [62]. The cost–benefit analysis technique, which is based on behavioral economics, is useful in analyzing recycling-related decisionmaking behavior, such as the recycling of resource materials [63], the construction of reverse logistics systems [64], the recycling of onsite residential graywater [65], the recycling of e-waste [66], the recycling of waste photovoltaic modules [67], and the construction of a municipal solid waste recycling facility [55].
中文这些假设常常与现实相矛盾。 因此,行为经济学将心理学纳入其中。 古典经济学来解释这种差异[62]。 基于行为经济学的成本效益分析技术可用于分析与回收相关的决策行为,例如资源材料的回收[63]、逆向物流系统的建设[64]、现场住宅灰水的回收[65]、电子垃圾的回收[66]、废弃光伏组件的回收[67]以及城市生活垃圾回收设施的建设[55]。
OriginalOn the basis of cost–benefit theory, this article examines the mediating effects from an economic standpoint. As mediators, 𝑃𝐵 and 𝑃𝐿 are presented. 𝑃𝐵 refers to consumers' understanding of the positive effects of WBEV recycling on the environment, society, or individuals.
中文本文以成本收益理论为基础,从经济学角度考察中介效应。 𝑃𝐵 和 𝑃𝐿 作为调解者出现。 𝑃𝐵 指消费者对WBEV 回收对环境、社会或个人的积极影响的理解。
OriginalThe purported benefits of recycling include decreasing trash disposal in landfills, conserving resources, lessening negative environmental consequences, generating economic benefits, and educating youngsters [68].
中文回收据称的好处包括减少垃圾填埋场的垃圾处理、节约资源、减少负面环境影响、产生经济效益和教育年轻人[68]。
OriginalSimilarly, 𝑃𝐵 is determined by consumers' assessments of the benefits of WBEV recycling, including: (1) 𝑃𝐵 : resource utilization optimization; (2) 𝑃𝐵 : risk reduction of environmental contamination; (3) 𝑃𝐵 : land saving; and (4) 𝑃𝐵 : economic benefits.
中文类似地,𝑃𝐵 由下式确定 消费者对WBEV回收效益的评估,包括:(1)𝑃𝐵:资源利用优化; (2)𝑃𝐵:降低环境污染风险; (3)𝑃𝐵:节省土地; (4)𝑃𝐵:经济效益。
OriginalPrevious research has shown that perceived benefits influence residents' pro-environmental intentions and behaviors [15,69,70]. 𝑃𝐿 denotes the monetary or non-monetary expenses involved in the recycling of WBEVs.
中文先前的研究表明,感知到的好处会影响居民的环保意图和行为[15,69,70]。 𝑃𝐿 表示 WBEV 回收所涉及的货币或非货币费用。
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OriginalA lack of acceptable facilities, a complicated operational method, time consumption, great distance, and economic loss are all factors that contribute to perceived loss Figure 4.
中文缺乏可接受的设施、复杂的操作方法、耗时、距离远和经济损失都是导致感知损失的因素(图4)。
OriginalStudy architecture and hypotheses. Consumers' recycling strategies can be categorized as "participate" or "not participate," and their WTR may vary depending on the economic results.
中文研究架构和假设。 消费者的回收策略可以分为“参与”或“不参与”,其WTR可能根据经济结果而变化。
OriginalTherefore, three alternative situations are used to measure "WTR0": (1) WTR1: consumers' WTR for a recycling fee; (2) WTR2: consumers' WTR for a recycling reimbursement; (3) WTR3: consumers' WTR for neither a reimbursement nor a recycling fee.
中文因此,可以采用三种替代情况来衡量“WTR0”:(1)WTR1:消费者对回收费的WTR; (2) WTR2:消费者回收补偿的WTR; (3) WTR3:消费者的WTR,既不报销也不收取回收费。
OriginalAdditionally, consumers' willingness to pay (WTP) is offered as a financial assessment for consumers' WTR [55,56]. The first motivator of WTR0, GP0, is judged by consumers' perceptions of policy efficacy in boosting recycling market growth, improving recycling supervision, warning of unlawful recycling behavior, and restraining residents' recycling behavior.
中文此外,消费者的支付意愿(WTP)作为消费者支付意愿的财务评估[55,56]。 WTR0的第一个推动因素GP0是根据消费者对政策在促进回收市场增长、完善回收监管、警告非法回收行为、约束居民回收行为等方面的效果的认知来判断的。
OriginalRecycling legislation and regulations limit consumers' recycling behavior. However, its impact is determined by the government's capacity to implement policy and consumers' perceptions of the success of government policy.
中文回收立法和法规限制消费者的回收行为。 然而,其影响取决于政府执行政策的能力以及消费者对政府政策成功的看法。
OriginalAsymmetric information theory holds that information disclosure is critical in determining consumer trust in the government. Similarly, according to source credibility theory, message exposure is the most important element in determining families' faith in the government [57].
中文信息不对称理论认为,信息披露对于决定消费者对政府的信任至关重要。 同样,根据信源可信度理论,信息曝光是决定家庭对政府信心的最重要因素[57]。
OriginalGP0 is measured in this article by perceptions of policy efficacy in the following areas: (1) GP1: efficacy in promoting WBEV recycling; (2) GP2: efficacy in supervising WBEV recycling; (3) GP3: efficacy in alerting against illegal recycling; and (4) GP4: efficacy in standardizing recycling disposal behavior.
中文本文通过对以下领域政策有效性的认知来衡量 GP0:(1)GP1:促进 WBEV 回收的有效性; (2) GP2:WBEV回收监管效能; (3) GP3:对非法回收的警示效果;和 (4)GP4:规范回收处置行为的功效。
OriginalThe second motivator of WTR0, EA0, pertains to consumer attitudes about the environment. EA0 is determined by consumers' assessments of environmental effects in the following scenarios: (1) EA1: irresponsible disposal of WBEVs; (2) EA2: incineration of WBEV components; (3) EA3: random dumping of WBEVs; and (4) EA4: inappropriate disassembly of WBEVs.
中文WTR0 的第二个推动因素 EA0 与消费者对环境的态度有关。 EA0是根据消费者对以下场景环境影响的评估来确定的: (1) EA1:不负责任地处置WBEV; (2) EA2:WBEV部件焚烧; (3) EA3:WBEV随机倾销; (4) EA4:WBEV 的不当拆卸。
OriginalSome research has suggested a substantial positive association between environmental views and recycling behavior [58]. Kurz et al. [59] discovered a minimal link between environmental concern and recycling behavior.
中文一些研究表明环境观点和回收行为之间存在显着的正相关关系[58]。 库尔兹等人。 [59]发现了一个 环境问题和回收行为之间的联系最小。
OriginalAccording to the consumer theory of microeconomics, consumers make decisions based on the utility maximization principle [60]. On the other hand, consumers are frequently reported to stray from utility maximization theory, because traditional consumer Sustainability 2023, 15, 2630 9 of 20 theory is driven by the market mechanism, and it believes that consumers are completely rational and market knowledge is comprehensive [61].
中文根据微观经济学的消费者理论,消费者根据效用最大化原则进行决策[60]。 另一方面,消费者经常被报道偏离效用最大化理论,因为传统的消费者可持续发展2023,15,2630 9 of 20理论是由市场机制驱动的,它认为消费者是完全理性的,市场知识是全面的[61]。
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Original(2) The negative path coefficient between EA0 → PL0 indicates that consumers with higher environmental attitudes have a lower perception of loss. (3) The negative path coefficient between PL0 → WTR0 indicates that consumers with a higher sense of loss are less likely to recycle.
中文(2) EA0→PL0之间的负路径系数 表明环境态度较高的消费者对损失的感知较低。 (3)PL0→WTR0之间的负路径系数表明,失落感较高的消费者回收的可能性较小。
OriginalSustainability 2023, 15, x FOR PEER REVIEW 12 of 21 Figure 5. The path weighting scheme and the path coefficients of the PLS-SEM model. Note: *** p < The test of the model validity is illustrated in the Table 1.
中文可持续发展 2023, 15, x 用于同行评审 12 of 21 图 5。 PLS-SEM模型的路径加权方案和路径系数。 注:*** p < 模型有效性检验如表1所示。
OriginalThe indicators used to assess the reliability and validity of PLS-SEM model are Cronbach's alpha (𝐶𝐴), Dillon– Goldstein's rho (𝑟ℎ𝑜_𝐴), composite reliability (𝐶𝑅), average variance extracted (𝐴𝑉𝐸), 𝑅 , and 𝐴𝑑𝑗. 𝑅 .
中文用于评估 PLS-SEM 模型信度和效度的指标包括 Cronbach's alpha (𝐶𝐴)、Dillon–Goldstein's rho (𝑟ℎ𝑜_𝐴)、综合信度 (𝐶𝑅)、平均方差提取 (𝐴𝑉𝐸)、𝑅 和 𝐴𝑑𝑗。 𝑅 。
OriginalAccording to Urbach et al. [80], 𝐶𝐴 and 𝐶𝑅 should not be lower than 0.6, and the proposed threshold value of 𝐴𝑉𝐸 is 0.5. As shown in Table 1, the reliability and convergent validity of the variables are acceptable.
中文根据乌尔巴赫等人的说法。 [80],𝐶𝐴和𝐶𝑅不应低于0.6,并且𝐴𝑉𝐸的建议阈值为0.5。 如表1所示,变量的信度和收敛效度是可以接受的。
OriginalIn addition, bootstrapping was used to test the significance of path coefficients, and the results are shown in Table 2. According to the findings, 𝐻1 and 𝐻2 are well supported.
中文此外,引导程序还用于 检验路径系数的显着性,结果如表2所示。 根据研究结果,𝐻1和𝐻2得到了很好的支持。
OriginalBoth 𝐸𝐴0 and 𝐺𝑃0 have large positive direct causal impacts on 𝑊𝑇𝑅0. Furthermore, 𝑃𝐵0 and 𝑃𝐿0 strongly influence the link between 𝐺𝑃0 → 𝑊𝑇𝑅0 and 𝐸𝐴0 → 𝑊𝑇𝑅0. The multi-group analysis approach was used to investigate the moderating impact of consumer attributes.
中文𝐸𝐴0 和𝐺𝑃0 都对𝑊𝑇𝑅0 产生巨大的正向直接因果影响。 此外,𝑃𝐵0和𝑃𝐿0强烈影响𝐺𝑃0→𝑊𝑇𝑅0和𝐸𝐴0→𝑊𝑇𝑅0之间的联系。 多组分析方法用于研究消费者属性的调节影响。
OriginalTable 3 shows the results of moderating effects of 𝑃 , 𝑃 , 𝑃 , 𝑃 , 𝑃 , and 𝑃 for consumers whose gender had no significant moderating effects on their WTR. All moderators had no significant moderating effects on 𝐸𝐴 → 𝑃𝐵 , 𝑃𝐵 → 𝑊𝑇𝑅 and 𝐸𝐴 → 𝑃𝐵 → 𝑊𝑇𝑅 , indicating that the impacts of 𝐸𝐴 → 𝑃𝐵 , 𝑃𝐵 → 𝑊𝑇𝑅 and 𝐸𝐴 → 𝑃𝐵 → 𝑊𝑇𝑅 were not significantly different among various groups of consumers.
中文表 3 显示了 𝑃 、 𝑃 、 𝑃 、 𝑃 、 𝑃 和 𝑃 对于性别对其 WTR 无显着调节作用的消费者的调节作用结果。 所有调节者对 𝐸𝐴 → 𝑃𝐵 、𝑃𝐵 → 𝑊𝑇𝑅 和 𝐸𝐴 → 𝑃𝐵 → 𝑊𝑇𝑅 没有显着调节作用,表明 𝐸𝐴 → 𝑃𝐵 的影响, 𝑃𝐵→𝑊𝑇𝑅和𝐸𝐴→𝑃𝐵→𝑊𝑇𝑅在不同消费者群体中没有显着差异。
OriginalTable 1. Reliability and convergent validity of the model. Variables 𝑪𝑨 𝒓𝒉𝒐_𝑨 𝑪𝑹 𝑨𝑽𝑬 𝑹𝟐 𝑨𝒅𝒋. 𝑹𝟐 𝑊𝑇𝑅 0.84 0.87 0.90 0.69 0.96 0.95 𝑃𝐵 0.93 0.94 0.95 0.83 0.77 0.76 𝑃𝐿 0.90 0.90 0.93 0.77 0.68 0.76 𝐺𝑃 0.97 0.97 0.98 0.91 - - 𝐸𝐴 0.97 0.97 0.98 0.91 - - Table 2.
中文表 1. 模型的可靠性和收敛有效性。 变量𝑪𝑨𝒓𝒉𝒐_𝑨𝑪𝑹𝑨𝑽𝑬𝑹𝟐𝑨𝒅𝒋。 𝑹𝟐 𝑊𝑇𝑅 0.84 0.87 0.90 0.69 0.96 0.95 𝑃𝐵 0.93 0.94 0.95 0.83 0.77 0.76 𝑃𝐿 0.90 0.90 0.93 0.77 0.68 0.76 𝐺𝑃 0.97 0.97 0.98 0.91 - - 𝐸𝐴 0.97 0.97 0.98 0.91 - - 表 2.
OriginalSignificance of path coefficients. Path Total Indirect Effect Total Effect Path Specific Indirect Effect 𝐸𝐴 → 𝑃𝐵 0.54 *** 𝐸𝐴 → 𝑃𝐿 → 𝑊𝑇𝑅 0.12 *** 𝐸𝐴 → 𝑃𝐿 −0.45 *** 𝐺𝑃 → 𝑃𝐿 → 𝑊𝑇𝑅 0.21 *** 𝐸𝐴 → 𝑊𝑇𝑅 0.26 *** 0.15 *** 𝐸𝐴 → 𝑃𝐵 → 𝑊𝑇𝑅 0.20 *** Figure 5.
中文路径系数的显着性。 路径总间接效应 总效应 路径特定间接效应 𝐸𝐴 → 𝑃𝐵 0.54 *** 𝐸𝐴 → 𝑃𝐿 → 𝑊𝑇𝑅 0.12 *** 𝐸𝐴 → 𝑃𝐿 -0.45 *** 𝐺𝑃 → 𝑃𝐿 → 𝑊𝑇𝑅 0.21 *** 𝐸𝐴 → 𝑊𝑇𝑅 0.26 *** 0.15 *** 𝐸𝐴 → 𝑃𝐵 → 𝑊𝑇𝑅 0.20 *** 图 5.
OriginalThe path weighting scheme and the path coefficients of the PLS-SEM model. Note: *** p < 1%. The test of the model validity is illustrated in the Table 1. The indicators used to assess the reliability and validity of PLS-SEM model are Cronbach's alpha (CA), Dillon– Goldstein's rho (rho_A), composite reliability (CR), average variance extracted (AVE), R2, and Adj.R2.
中文PLS-SEM模型的路径加权方案和路径系数。 注:*** p < 1%。 模型有效性检验如表1所示。 用于评估PLS-SEM模型信度和效度的指标有Cronbach's alpha (CA)、Dillon-Goldstein's rho (rho_A)、综合信度(CR)、平均方差提取(AVE)、R2和Adj.R2。
OriginalAccording to Urbach et al. [80], CA and CR should not be lower than 0.6, and the proposed threshold value of AVE is 0.5. As shown in Table 1, the reliability and convergent validity of the variables are acceptable.
中文根据乌尔巴赫等人的说法。 [80],CA和CR不应低于0.6,建议AVE阈值为0.5。 如表1所示,变量的信度和收敛效度是可以接受的。
OriginalIn addition, bootstrapping was used to test the significance of path coefficients, and the results are shown in Table 2. According to the findings, H1 and H2 are well supported.
中文此外,引导程序还用于 检验路径系数的显着性,结果如表2所示。 根据研究结果,H1和H2得到了很好的支持。
OriginalBoth EA0 and GP0 have large positive direct causal impacts on WTR0. Furthermore, PB0 and PL0 strongly influence the link between GP0 → WTR0 and EA0 → WTR0 . The multi-group analysis approach was used to investigate the moderating impact of consumer attributes.
中文EA0 和 GP0 对 WTR0 都有很大的积极直接因果影响。 此外,PB0和PL0强烈影响GP0→WTR0和EA0→WTR0之间的链接。 多组分析方法用于研究消费者属性的调节影响。
OriginalTable 3 shows the results of moderating effects of PA, PI, PE, PR, PRE, and PO for consumers whose gender had no significant moderating effects on their WTR. All moderators had no significant moderating effects on EA0 → PB0 , PB0 → WTR0 and EA0 → PB0 → WTR0 , indicating that the impacts of EA0 → PB0 , PB0 → WTR0 and EA0 → PB0 → WTR0 were not significantly different among various groups of consumers.
中文表3显示了PA、PI、PE、PR、PRE和PO对性别对其WTR没有显着调节作用的消费者的调节作用结果。 所有调节因子对 EA0 → PB0 、PB0 → WTR0 和 EA0 → PB0 → WTR0 均无显着调节作用,表明 EA0 → PB0 、PB0 → WTR0 和 EA0 → PB0 → WTR0 的影响在不同消费者群体中没有显着差异。