本文件（所有部分）规定了确定ICT&；排放试验箱（ETC）中预期运行期间的CE设备。 本文件（所有部分）包括使用耗材（如打印机）的设备和不使用耗材（如显示器和PC）的设备的具体方法。 第1部分规定了确定使用耗材的电子设备中VOC和羰基化合物、臭氧、颗粒物、细颗粒物（FP）和超细颗粒物（UFP）排放率的方法。 这些方法包括在受控ETC中进行准备、取样（或监测）、储存和分析、计算和报告排放率。 第1部分介绍了测定VOC和羰基化合物排放率的两种不同方法。这两种方法分别使用准平衡模型（QEM）和恒定排放模型（CEM）两种不同的排放模型来确定预处理期间VOC和羰基化合物的排放率- 操作阶段。 准平衡模型方法的开发考虑了办公室或家庭使用的硬拷贝设备，这些设备的节能模式在操作之间的大部分时间间隔内自动激活。运行前阶段的排放率计算基于附录C中所示的准平衡假设。 由于试验程序的规定范围比其他方法（CEM）更窄，因此使用该方法确定的排放率可用于比较同一等级的设备。 恒定排放模型（CEM）是为硬拷贝设备开发的，其节能模式对VOC和羰基化合物排放率的测定影响可忽略不计，因此附录D中所示的通用恒定排放模型可用于在预运行阶段测定其排放率。这种方法比QEM提供了更灵活的测试程序。 由于这种方法的这些特点，它可用于通常在两次操作之间的整个间隔内保持空闲模式的硬拷贝设备，例如专业使用的大型硬拷贝设备。它也可用于具有不同功能和结构的各种设备，以满足其预期用途，以及由于缺乏灵敏度而需要更长取样时间的羰基化合物的测定。 附录A规定了在使用耗材的EUT运行阶段使用的单色和彩色打印图案。 根据附录B确认AMS的作战准备状态。 根据确定的排放率预测“实际室内”浓度不在本文件范围内。

This document (all parts) specifies methods to determine chemical emission rates of analytes from ICT & CE equipment during intended operation in an Emission Test Chamber (ETC). This document (all parts) includes specific methods for equipment using consumables, such as printers, and equipment not using consumables, such as monitors and PC’s. Part 1 specifies the methods to determine the emission rates of VOC and carbonyl compounds, ozone, particulate matter, fine particles (FP) and ultra-fine particles (UFP) from electronic equipment using consumables. The methods comprise preparation, sampling (or monitoring) in a controlled ETC, storage and analysis, calculation and reporting of emission rates. Part 1 has two different methods for the determination of emission rates of VOC and carbonyl compounds. The two methods use two different emission models, the quasi-equilibrium model (QEM) and the constant emission model (CEM) respectively, to determine the emission rates of VOC and carbonyl compounds during the pre-operating phase. The quasi-equilibrium model method has been developed with hard copy devices for office or home use in mind whose energy-saving modes automatically activate during most intervals between operations. The calculation of emission rates during the pre-operating phase is based on the quasi-equilibrium assumption as shown in Annex C. The emission rates determined with this method can be used to compare equipment in the same class since test procedures are specified more narrowly than the other method (CEM). The constant emission model (CEM) has been developed for hard copy devices whose energy-saving modes have such a negligible effect on the determination of emission rates of VOC and carbonyl compounds that the generalised constant emission model shown in Annex D can be used for the determination of their emission rates during the pre-operating phase. This method presents more flexible test procedures than the QEM. Due to such features of this method, it may be used for hard copy devices whose idling mode usually lasts throughout intervals between operations, such as large hard copy devices used professionally. It may also be used for various equipment having different functions and structure for its intended use and the determination of carbonyl compounds requiring longer sampling duration due to a lack of sensitivity. Annex A specifies monochrome and colour print patterns for use in the operating phase of EUT using consumables. The operational readiness of AMS is confirmed according to Annex B. Predictions of “real indoor” concentrations from the determined emission rates are outside the scope of this document.