Flender/Flender Gear Units/Bevel-helical gear box B2
le for this purpose, in which an even dispersion of nutrients and microorganisms, as well as standardisation, can most readily

be ensured The test duration is from 2 to 6 days, depending on the degradation behaviour and the test system

employed Monitoring of degradation via the BOD in an aerobic environment Monitoring of degradation via the COz release in an

aerobic environment Monitoring of degradation via the production of biogas (methane and CO?) in an anaerobic . environment 2.2 Simulation

of waste disposal conditions Trials under realisticconditionswere carried out atthe same time in order to be ableto investi- gate the relevance and/or transferability of short-time test in an aqueous environment. Household landfill and composting facilities are of primary interest as regards the disposal of waste. Composting on laboratory scale Landfill simulation 2.3 Simulation of environmentally relevant conditions Soil burial Aquariums for simulating surface water 1 ,-_____I 3. Results 3.1 Screening tests The biodegradability of films and powdery materials can be monitored via the BOD and the evolution of C0 in an aerobic environment and via the biogas release in an anaerobicenviron- ment. In the case of materials which comprise more than one component, the summary para- meter BOD or C0 alone is not sufficient as the sole assessment variable to establish the com- plete degradation of the material; an approximate balance should also be drawn up. Non- automated systems, such as the Sturm Test, are only suitable for short trial periods. Materials which require an incubation time longer than 3 to maximum of 6 days should be investi- gated in automated systems (BSB-Digi, Denimat, Methanomat: Buhler, Bodelshausen) or by simulation. The screening methods in the aerobic and anaerobic aqueous environment were tested and largely optimised as regards the media, inocula and analytical methods employed. 3.2 Realistic trials 3.2.1 Compost simulation