{"id":323485,"date":"2024-10-19T22:24:37","date_gmt":"2024-10-19T22:24:37","guid":{"rendered":"https:\/\/pdfstandards.shop\/product\/uncategorized\/bsi-pd-iso-tr-140492012\/"},"modified":"2024-10-25T20:58:44","modified_gmt":"2024-10-25T20:58:44","slug":"bsi-pd-iso-tr-140492012","status":"publish","type":"product","link":"https:\/\/pdfstandards.shop\/product\/publishers\/bsi\/bsi-pd-iso-tr-140492012\/","title":{"rendered":"BSI PD ISO\/TR 14049:2012"},"content":{"rendered":"
This Technical Report provides examples about practices in carrying out a life cycle inventory analysis (LCI) as a means of satisfying certain provisions of ISO 14044:2006. These examples are only a sample of the possible cases satisfying the provisions of ISO 14044. They offer \u201ca way\u201d or \u201cways\u201d rather than the \u201cunique way\u201d for the application of ISO 14044. These examples reflect only portions of a complete LCI study.<\/p>\n
PDF Pages<\/th>\n | PDF Title<\/th>\n<\/tr>\n | ||||||
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9<\/td>\n | Scope General <\/td>\n<\/tr>\n | ||||||
11<\/td>\n | Examples of developing functions, functional units and refer Context of ISO\u00a014044 Overview <\/td>\n<\/tr>\n | ||||||
13<\/td>\n | Identification of functions Selection of functions and definition of functional unit <\/td>\n<\/tr>\n | ||||||
14<\/td>\n | Identification of performance of the product and determinati Additional examples Examples of distinguishing functions of comparative systems Context of ISO\u00a014044 <\/td>\n<\/tr>\n | ||||||
15<\/td>\n | Overview <\/td>\n<\/tr>\n | ||||||
16<\/td>\n | Identification and selection of functions <\/td>\n<\/tr>\n | ||||||
17<\/td>\n | Equivalence of reference flows <\/td>\n<\/tr>\n | ||||||
18<\/td>\n | Adjusting for performance differences <\/td>\n<\/tr>\n | ||||||
19<\/td>\n | Examples of establishing inputs and outputs of unit processe Context of ISO\u00a014044 <\/td>\n<\/tr>\n | ||||||
20<\/td>\n | Overview Determining the product system\u2019s unit processes and their bo <\/td>\n<\/tr>\n | ||||||
23<\/td>\n | Initial collection of data at each unit processes <\/td>\n<\/tr>\n | ||||||
24<\/td>\n | Initial estimate of material and energy flows <\/td>\n<\/tr>\n | ||||||
26<\/td>\n | Applying decision rules Decision rules for mass contribution Decision rules for energy <\/td>\n<\/tr>\n | ||||||
27<\/td>\n | Decision rules for environmental relevance 5.7 Inputs, outputs and system boundaries established Examples of avoiding allocation Context of ISO\u00a014044 <\/td>\n<\/tr>\n | ||||||
28<\/td>\n | Overview <\/td>\n<\/tr>\n | ||||||
29<\/td>\n | Example of allocation avoidance by dividing the unit process Example of allocation avoidance by expanding the boundaries <\/td>\n<\/tr>\n | ||||||
31<\/td>\n | Examples of allocation Context of ISO\u00a014044 <\/td>\n<\/tr>\n | ||||||
32<\/td>\n | Overview Description of the examples Example of allocation on a purely physical relationships <\/td>\n<\/tr>\n | ||||||
34<\/td>\n | Example of allocation on a purely economic basis <\/td>\n<\/tr>\n | ||||||
35<\/td>\n | Example of applying allocation procedures for recycling Context of ISO\u00a014044 <\/td>\n<\/tr>\n | ||||||
36<\/td>\n | Overview <\/td>\n<\/tr>\n | ||||||
37<\/td>\n | Description of the examples Example of closed loop recycling <\/td>\n<\/tr>\n | ||||||
38<\/td>\n | Example of open-loop with closed loop recycling procedure <\/td>\n<\/tr>\n | ||||||
41<\/td>\n | Open loop recycling <\/td>\n<\/tr>\n | ||||||
42<\/td>\n | Basis for allocation <\/td>\n<\/tr>\n | ||||||
43<\/td>\n | Determination of uses for recovered\/recycled kraft bleached <\/td>\n<\/tr>\n | ||||||
44<\/td>\n | Calculation of the number of uses <\/td>\n<\/tr>\n | ||||||
45<\/td>\n | Calculation of the allocation factor based on the number of <\/td>\n<\/tr>\n | ||||||
46<\/td>\n | Final loadings to the different systems Examples of conducting data quality assessment Context of ISO\u00a014044 <\/td>\n<\/tr>\n | ||||||
47<\/td>\n | Overview <\/td>\n<\/tr>\n | ||||||
48<\/td>\n | Data requirements to establish the specific listing of sites Time-related coverage <\/td>\n<\/tr>\n | ||||||
49<\/td>\n | Geographical coverage Technology coverage Requirements to characterize the quality of the data Precision Completeness <\/td>\n<\/tr>\n | ||||||
50<\/td>\n | Representativeness Consistency Reproducibility Identification of anomalies\/missing data <\/td>\n<\/tr>\n | ||||||
51<\/td>\n | Examples of performing sensitivity analysis Context of ISO\u00a014044 Overview <\/td>\n<\/tr>\n | ||||||
52<\/td>\n | Description of the examples General <\/td>\n<\/tr>\n | ||||||
53<\/td>\n | Prioritization of the parameters to be tested Selection of the parameters to be tested Overview of the example <\/td>\n<\/tr>\n | ||||||
54<\/td>\n | Types of sensitivity analysis applicable to the study Selecting a range of values within feasible boundaries <\/td>\n<\/tr>\n | ||||||
55<\/td>\n | Calculations Conclusions <\/td>\n<\/tr>\n<\/table>\n","protected":false},"excerpt":{"rendered":" Environmental management. Life cycle assessment. Illustrative examples on how to apply ISO 14044 to goal and scope definition and inventory analysis<\/b><\/p>\n |