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Phases, levels and circles in policy development: the cases of higher education and environmental quality assurance

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Abstract

This article examines parallel developments in the fields of quality assurance in higher education and in environmental policy. Starting from empirically grounded analytical frameworks for the two fields separately, Fischer's framework of policy argumentation is overlaid on both to gain deeper understanding of underlying similarities and contrasts. We argue that quality management in the field of higher education faces choices already addressed in environmental quality assurance. In the light of these practical and theoretical lessons, the relative success with higher education quality assurance may be less of a reason for optimism.

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Figure 1

Notes

  1. We stress, first, that the perception of issues as a social fact may well be more important than any ‘objective’ state of affairs. Second, this perspective of fast-changing temporary compromises instead of once-and-for-all solutions of problems is relatively new, at least for universities, which until the 1960s (or later?) were characterised often as ‘ivory towers’ that accommodated societal change at a low pace and only on ‘purely rational’ grounds.

  2. The more or less autonomous development can be overridden by external events. The final row in the table, illustrating some consequences of the ‘Bologna process’, is an example of such ‘disturbances’, setting new challenges in a new context, for European higher education. We list this row for completeness’ sake, but the issue needs to remain beyond our current focus (van der Wende & Westerheijden, 2001; Westerheijden & van der Wende, 2001).

  3. We are not the first ones to apply the general model to analysis of specific problems in specific policy fields. See, for example, Hoppe and Pranger (1993).

  4. Major governmental budget cuts took place in the UK and the Netherlands just before the introduction of quality assurance instruments. Our point is that efficiency issues will crop up within quality assurance frameworks too.

  5. This question is addressed extensively in Magelhães (2001).

  6. Note that this definition is static and has not changed since then. In other words, the thinking on environmental care has not progressed from a certain phase to another, at least not at the policy level. Environmental care systems so defined are connected to the outside world, although only to a limited extent. First, in the years after the introduction of voluntary environmental care systems a practice of auditing has emerged and environmental care systems that contain the eight elements generally pass the audit. This result is sometimes communicated to the relevant public, most notably customers and suppliers. The second connection with the outside world is with the public authorities that issue licenses to the relevant industry. This interaction is probably the single most important element in influencing the environmental goals that the company adopts. As long as public authorities do not redefine these goals (and they often do not), the goals essentially stay the same. There is little impetus for firms to change the care system progressively. This implies that they must be placed at the level of problem solving in Fischer's terms.

  7. Still, one should keep in mind that the tension between short-term success and long-term results remains unresolved. Short-term success may produce the very source of discontent about the social function of higher education.

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Huitema, D., Jeliazkova, M. & Westerheijden, D. Phases, levels and circles in policy development: the cases of higher education and environmental quality assurance. High Educ Policy 15, 197–215 (2002). https://doi.org/10.1016/S0952-8733(02)00007-7

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