Osnabrück Environmental Management Model for Universities ------------------------------------------------------------------
The building blocks and their implementation
    Environmental Audit
(building block EM 4)

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  Building block 4 involves carrying out an environmental audit of the university in order to obtain an overview of its environmental relevance. With a list of all input and output materials and energy flows at the university it can be determined where extensive measures need to be implemented to reduce resource consumption. Simultaneously, the lists form the basis for an analysis of the effects the respective materials have on the environment. There are several different ways of carrying out an ecoaudit; in Osnabrück it was implemented by way of a life cycle assessment (LCA) based on ISO 14 040. Following this an LCA includes the four steps: goal and scope definition, inventory analysis, impact assessment and interpretation (ISO 1997).

Inventory Analysis

  The inventory analysis was first of all carried out for the University of Osnabrück, the objectives of which were as follows:
  • The inventory analysis aims to give an overview of the (most important) material and energy flows concerning the university and its buildings. Only then are the specific measures taken in the individual buildings or environmental areas (top-down procedure). The advantage of the top-down as opposed to the bottom-up procedure, where individual buildings are first investigated in depth and the results are then adjusted to the whole university, is that the evaluator does not get bogged down with too much detail, thus forgetting the overall objective.
  • Another objective was not just to consider the direct influence of the university, but also to include the material and energy flows that occur before and after their actual consumption. For electricity consumption, for example, this means the chain from the extraction of the raw material via the power stations to its delivery to the university. The aim of this is to include processes that hardly affect the direct running of the university, but the manufacture or disposal of which make a great environmental impact. The omission of these would falsify the comprehensive balance. The inventory analysis can therefore be split into two separate balances: the core and the complementary balances. According to the Swiss method "Ökobilanzen für Unternehmen" (Ecobalances for companies) the core balance includes those processes that occur in the company itself (e.g. energy supply or waste disposal). All other areas belong to the complementary balance (e.g. company commuter travel, sewage treatment) (Siegenthaler 1994).
  • Finally, special attention should be paid to the university's CO2 emissions. With regard to the CO2 reduction target of the federal government (a 25% reduction by the year 2005 in relation to 1990) and the decision of the City of Osnabrück to reduce its CO2 emissions (a reduction of 50% by the year 2010 in relation to 1987), the University is also obliged to reduce its CO2 emissions. The aim was therefore to identify the CO2 emissions on the university scale, and for each separate building. Besides the first two objectives, which are the prerequisite for an exact audit of CO2 emissions, the (energy-related) emissions are to traced back to the individual buildings, so that a table of CO2 emitters can be drawn up. Moreover, it should be possible to compare CO2 emissions related to energy, traffic and (waste) water.
The following table shows for which areas the life cycle inventory analysis has been carried out:

Area

Material and energy flows

Period

of time

Core

balance

Complementary

balance

Modelling,

generation

 

 

 

Univ.

Preproc.

Postproc.

 

Energy

All consumption of heat and electricity in the individual buildings and their pre-processes, as well as the emissions caused by it

1996

X

X

/

Umberto®

Traffic

Energy consumption and emissions due to commuter traffic (staff and students) and internal traffic (business trips and vehicles), both directly and in the pre-processes

(1995),

1996

X

X

/

Umberto®

Water

All water consumption in the individual buildings

1996

X

F

c.f. waste water

Umberto®

Waste

water

Waste water from the University, as well as material and energy consumption involved in waste water disposal

1996

X

/

X

Umberto®

Materials

Consideration of chemicals, the most important office items, use of paper and some sanitary materials

1995

X

F

c.f.

waste

Excel®

Waste

All occurring waste, such as hazardous waste, electronic waste, residual waste, paper, plastics and polystyrene

1996/

1997

X

/

F

Excel®

Area

Consideration of the built on, sealed and natural areas

1996

X

/

/

Excel®

 

X = already carried out, / = not applicable, F = consideration has yet to be carried out

Data from 1996 were generally used for the overall balance. The areas of energy, traffic, water and waste water were modelled using the ecobalance software Umberto®, an interactive tool developed by the Institute of Energy and Environmental Research (IFEU) in Heidelberg and the Institute of Environmental Computer Sciences (IFU) in Hamburg (Häuslein und Hedemann 1995). The other areas were compiled using Excel® tables.

 

Impact Assessment

  The impact assessment phase of the LCA was carried out following the "UBA-Method" of the German Federal Environmental Agency (UBA) which is based on the method of impact categories described in ISO 14 040. The inventory data was assigned to ten different impact categories and modelled within these categories. Finally, the categories were weighted against each other. The most significant results are that the University contributes "considerably" towards both categories "Depletion of fossil energy resources" and "Climate change". The main causes of this are electricity and heat consumption as well as traffic. In order to improve its environmental situation the University was recommended to reduce its CO2 emissions, its consumption of fossil energy resources and its methane emissions. The implementation of these measures would in turn lead to an improvement of those categories for which a "medium-sized" impact was ascertained: "Ecotoxicological impacts of NOX", "Photo-oxidant formation", "Acidification", "Eutrophication" und "Human toxicological impacts of lead and dust".

 

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