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Handling and reporting environmental information
The structured procedure for implementing ISO/TS 14048 and
PHASETS in order to handle environmental data at production sites includes 4
steps. The procedure was developed to fit the Swedish pulp and paper industry,
but could be adapted also by other industry sectors. The steps are:

Figure 1: Working procedure for implementing ISO/TS 14048 and PHASETS
in pulp and paper industry.
Step 1 – Survey the organization's needs for environmental data, by
identifying stakeholders requesting environmental data and their requirements on
that data. The survey is conducted to determine which models are needed and to
prioritize further work. See
example on identified
stakeholders and their needs for environmental data.
Step 2 – Prepare draft models of production systems, which describe the
production of the selected products or product groups based on the survey of
environmental data needs. Depending on the stakeholders' requests, these models
can either be simple or compiled of many sub-parts, see example of a
model of a
production system. In this step the parameters to be reported are
also selected. An example of a reported parameter is fossil CO2. However, the system
boundaries depend on the stakeholders' scope. In the European Emission Trading
Scheme, only the emissions from the juridical site are included, but other
related reporting schemes, e.g.
The Greenhouse Gas
Protocol, also include greenhouse gases from external upstream
sources. Examples of other parameters can be found in the report
Methodology for
handling forest industry environmental data – Manual, appendix 2. This report
also describes how data can be collected at the production sites.
Step 3 – Process data for selected parameters. The processing includes
e.g. specification of parameters and measurement systems, acquisition of
measured values and compilation of measured values into mean values. In the pulp
and paper industry, a great deal of environmentally related parameters are
measured, however method of measurement, frequency and exact location of
measurement varies and need to be documented in order to draw the right
conclusions from a reported parameter. E.g. the reliability of a parameter
measured continuously might be higher than for a parameter measured once a year.
Allocation issues for the draft models are also investigated. Few stakeholders
set specific demands on how allocation should be performed when deriving product
related environmental data. Suggestions on how to allocate in these cases can be
found in the report
Industrial Management of Environmental Data.
Allocation is the partitioning of environmental impacts on two or more products
resulting from one process. Allocation is needed, when further modeling that
separates the two (or more) products from another, is not possible.
Step 4 – Make a final compilation of models, based on the information that
has been acquired and prepared in the previous stages of the implementation. A
model in this context is a calculation procedure made from linked unit
processes (please compare LCA). An example of a model is available
here. The resulting models are then typically
designed to correspond to the most detailed requests. Possibly, alternative
calculation models can be designed for less detailed requests, e.g. when only
site related information is needed.
Report and document
Document and report all results from the steps above in the ISO/TS 14048 LCA –
data documentation format to facilitate quality assurance and verification of
the procedure and data. The ISO/TS 14048 format specifies the information that
is to be documented and how the documentation is to be structured. Both
documentation and reporting is facilitated by using the appropriate software
that is based on the ISO/TS 14048 format, e.g.
LCI@CPMand
WWLCAW
both designed at
IMI, Chalmers. The use of internationally
standardized format for data documentation facilitates easier communication,
verification and data quality assurance (please see LCA more about)
Experiences

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