DPSIR
Criticisms and Limitations
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== Criticisms and Limitations == |
== Criticisms and Limitations == |
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Despite the adaptability of the framework, it has faced several criticisms. One of the main goals of the framework is to provide environmental managers, scientists of various disciplines, and stakeholders with a common forum and language to identify, analyze and assess environmental problems and consequences. However, several notable authors have mentioned that it lacks a well-defined set of categories, which undermines the comparability between studies, even if they are similar.{{Cite journal |last=Cooper |first=Philip |date=October 2013 |title=Socio-ecological accounting: DPSWR, a modified DPSIR framework, and its application to marine ecosystems |url=https://purehost.bath.ac.uk/ws/files/16854238/Cooper_2013_Ecological_Economics_94_106.pdf |journal=Ecological Economics |volume=94 |pages=106–115 |doi=10.1016/j.ecolecon.2013.07.010 |s2cid=153432235 |issn=0921-8009|url-access= }} For instance, climate change can be considered as a natural driver, but is primarily caused by [[greenhouse gas]]es ( |
Despite the adaptability of the framework, it has faced several criticisms. One of the main goals of the framework is to provide environmental managers, scientists of various disciplines, and stakeholders with a common forum and language to identify, analyze and assess environmental problems and consequences. However, several notable authors have mentioned that it lacks a well-defined set of categories, which undermines the comparability between studies, even if they are similar.{{Cite journal |last=Cooper |first=Philip |date=October 2013 |title=Socio-ecological accounting: DPSWR, a modified DPSIR framework, and its application to marine ecosystems |url=https://purehost.bath.ac.uk/ws/files/16854238/Cooper_2013_Ecological_Economics_94_106.pdf |journal=Ecological Economics |volume=94 |pages=106–115 |doi=10.1016/j.ecolecon.2013.07.010 |s2cid=153432235 |issn=0921-8009|url-access= }} For instance, climate change can be considered as a natural driver, but is primarily caused by [[greenhouse gas]]es (GHGs) produced by human activities, which may be categorized under "pressure". A [[Wastewater treatment|wastewater treatment plant]] is considered a response while dealing with [[water pollution]], but a pressure when [[effluent]] runoff leading to eutrophication is taken into account. This [[ambivalence]] of variables associated with the framework has been criticized as a lack of good communication between researchers and between stakeholders and policymakers.{{Cite journal |last1=Carr |first1=Edward R. |last2=Wingard |first2=Philip M. |last3=Yorty |first3=Sara C. |last4=Thompson |first4=Mary C. |last5=Jensen |first5=Natalie K. |last6=Roberson |first6=Justin |date=December 2007 |title=Applying DPSIR to sustainable development |journal=International Journal of Sustainable Development & World Ecology |language=en |volume=14 |issue=6 |pages=543–555 |doi=10.1080/13504500709469753 |s2cid=16526139 |issn=1350-4509}} Another criticism is the misguiding simplicity of the framework, which ignores the complex [[synergy]] between the categories. For instance, an impact can be caused by various different state conditions and responses to other impacts, which is not addressed by DPSIR. Some authors also argue that the framework is flawed as it does not clearly illustrate the cause-effect linkage for environmental problems.{{Cite journal |last1=Rekolainen |first1=Seppo |last2=Kämäri |first2=Juha |last3=Hiltunen |first3=Marjukka |last4=Saloranta |first4=Tuomo M. |date=December 2003 |title=A conceptual framework for identifying the need and role of models in the implementation of the water framework directive |journal=International Journal of River Basin Management |volume=1 |issue=4 |pages=347–352 |doi=10.1080/15715124.2003.9635217 |s2cid=989048 |issn=1571-5124}} The reasons behind these contextual differences seem to be differences in opinions, characteristics of specific case studies, misunderstanding of the concepts and inadequate knowledge of the system under consideration. |
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DPSIR was initially proposed as a conceptual framework rather than a practical guidance, by global organizations. This means that at a local level, analyses using the framework can cause some significant problems. DPSIR does not encourage the examination of locally specific attributes for individual decisions, which when aggregated, could have potentially large impacts on sustainability. For instance, a farmer who chooses a particular way of livelihood may not create any consequential alterations on the system, but the aggregation of farmers making similar choices will have a measurable and [[Tangibility|tangible]] effect. Any efforts to evaluate sustainability without considering local knowledge could lead to misrepresentations of local situations, misunderstandings of what works in particular areas and even project failure. |
DPSIR was initially proposed as a conceptual framework rather than a practical guidance, by global organizations. This means that at a local level, analyses using the framework can cause some significant problems. DPSIR does not encourage the examination of locally specific attributes for individual decisions, which when aggregated, could have potentially large impacts on sustainability. For instance, a farmer who chooses a particular way of livelihood may not create any consequential alterations on the system, but the aggregation of farmers making similar choices will have a measurable and [[Tangibility|tangible]] effect. Any efforts to evaluate sustainability without considering local knowledge could lead to misrepresentations of local situations, misunderstandings of what works in particular areas and even project failure. |
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