【手术室的包装废弃物】。

Unfallchirurgie (Heidelberg, Germany) Pub Date : 2025-02-01 Epub Date: 2024-12-10 DOI:10.1007/s00113-024-01508-z
Caroline Lopez Lopez, Marie-Jacqueline Reisener, Nikolaus Kreitz, Veit Kleine-Doepke, Sönke Landschoof, Christian A Kühne
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引用次数: 0

摘要

背景:气候变化是我们未来的一个核心问题。大气中温室气体数量的增加促进了所谓的温室效应,导致气候变化。在世界范围内,塑料垃圾的数量约为80亿吨。医疗保健行业占全球温室效应净排放量的4.4%左右。应相应地实施减少医疗保健部门二氧化碳排放的措施。为了使手术部门的塑料废物问题更加明显,在本研究中,我们检查并计算了桡骨远端骨折治疗中产生的包装废物。材料和方法:临床储存两种不同的种植体(无菌包装 = I组vs种植体托盘 = II组)用于治疗桡骨远端骨折。在12个月期间(2022年7月至2023年7月),收集所有手术治疗的桡骨远端骨折的包装废弃物并称重。测量两组取出、打开和提供种植体所需的时间(称为准备时间)。将患者资料记录在专门的登记册中,并计算统计学意义。结果:共治疗桡骨远端骨折124例。该队列的平均年龄为67.9岁,其中74.2%为女性。使用无菌单独包装系统(I组)治疗骨折29次,使用螺旋托盘系统(II组)治疗骨折94次。无菌包装处理每次手术产生104.5g塑料废弃物和67.4g无塑料包装废弃物,而种植托盘处理每次手术产生21.6g塑料废弃物和12.8g无塑料包装废弃物(p = 0.0001)。I组提供螺钉的平均时间为527.8 s,明显高于II组使用种植托盘治疗的138 s (p = 0.0001)。讨论:在目前的研究中,我们发现使用单独包装的植入物会显著增加塑料废物。为了减少塑料废物的产生,强制性的手术室废物分类指南似乎是明智的。诸如回收和回收可循环利用的塑料废物以及改进包装设计和使用生物基、可生物降解和可堆肥塑料等措施是进一步减少废物的可能性。
本文章由计算机程序翻译,如有差异,请以英文原文为准。
[Packaging waste in the operating room].

Background: Climate change is a central issue for our future. The increase in the amount of greenhouse gases in the atmosphere promotes the so-called greenhouse effect, resulting in climate change. Worldwide, the amount of plastic waste amounts to approximately 8 billion tons. The healthcare sector is responsible for around 4.4% of global net emissions contributing to the greenhouse effect. Measures to reduce CO2 emissions within the healthcare sector should be implemented accordingly. To make the issue of plastic waste in the operational sector more visible, in the present study we examined and calculated the packaging waste generated in the treatment of distal radius fractures.

Material and methods: The clinic stocks two different implants (sterile packaging = group I vs. implant tray = group II) for the treatment of distal radius fractures. Over a period of 12 months (July 2022-July 2023), the packaging waste from all surgically treated distal radius fractures was collected and weighed. The time required to retrieve, unpack and provide the implants in both groups (referred to as preparation time) was measured. Patient data were recorded in a dedicated register and statistical significances were calculated.

Results: A total of 124 distal radius fractures were treated. The average age of the cohort was 67.9 years with 74.2% being female. The system with sterile individual packaging (group I) was used for fracture treatment 29 times, while the system with the screw tray (group II) was used 94 times. For treatment with sterile packaging 104.5g of plastic waste and 67.4g of plastic-free packaging waste were generated per operation, while treatment with the implant tray resulted in 21.6g of plastic waste and 12.8g of plastic-free packaging waste (p = 0.0001). The average time for providing the screws in group I was significantly higher at 527.8 s compared to treatment with the implant tray in group II at 138 s (p = 0.0001).

Discussion: In the present study we found a significant increase in plastic waste when using individually packaged implants. To reduce the production of plastic waste, mandatory guidelines for waste separation in the operating room appear to be sensible. Measures such as the return and recycling of recyclable plastic waste as well as improvements in packaging design and the use of bio-based biodegradable and compostable plastics, represent further possibilities for waste reduction.

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