Introduction
As a consequence of global warming and human activity, some countries across the world are likely to encounter high river water levels in the nearest future. There also going to be increased levels of river degradation and in the present day, river degradation is a significant issue of natural resource management that is facing such a country as Australia (Brierley, et al, 2002).
In relation to the issue of high river water levels, Samuels et al (2006) point out that, rather than fighting and engaging in the control of flood hazards âwith ever higher dikes, new management styles focus on understanding and managing flood riskâ (Samuels, 2006, p.142).
Taking the case of the Netherlands, for instance, there is embodying of this policy approach by a national policy referred to as âRoom for Riverâ (De Groot, 2010). The objective of this national policy is to ensure creation of additional space for water storage and this is carried out by engaging in relocating dikes âland inwards or constructing side channelsâ (De Groot, 2010, p.89).
In an effort to ensure combining of a bigger discharge capacity with other functions, in most cases, go together with recreation, nature conservation and river restoration (Van Stokkom, 2005). There has been well documentation of public support for âRoom for Riverâ policies and this support is found out to be high.
To this overall finding, it has been pointed out that public support to specific âRoom for Riverâ measures may not be higher, like in the case when these involve removing trees (De Groot & de Groot, 2009).
The special interest in this paper is to gain insight into the factors which may give an explanation to the level of people in adhering to âRoom for River policyâ. The question that comes is; does the adherence that people have correlate with their general ethics on nature, with the way they utilize the river, their good judgment of place, with their age, or with no any of these?
Within this scope of factors, the special interest in the paper will lie in peopleâs ethics with nature. Is what people believe about the suitable relationship between humans and nature give a reflection in the opinions they have on more solid policies such as Room for River?
In this paper, there is going to be an assessment of where levels of adherence to river management styles resonate with public environmental ethics and the paper will reflect on the Australian situation.
Human/Nature relationships and river meanings
The human/nature relationship images are a portion of wider âvisions of natureâ concepts as given description to by Van den Born et al (2001). These researchers give a distinction between three components. The first component is images of nature, the second is nature values and the third is images of relationship.
All these components give a reflection of the issues which are subject to debate that has been held by the environmental ethicists. Therefore, as Van de Born (2008) point out, the empirical study about the visions of nature that the lay people have can be referred to as empirical philosophy.
A large number of philosophers call these âbasic attitudesâ (Zweers, 2000) or âworld viewsâ (Norton, 1991).Such views do not essentially need to be a well developed philosophy, they can as well be several assumptions that âthe respondents hardly ever recognize or think aboutâ (Norton, 1991, p.20).
The human/nature relationship images are formed on the basis of the philosophical categorization in to the âMastery over nature, Stewardship of nature, partnership with nature and Participation in natureâ (De Groot, 2010, p.91).
Considering âMastery over natureâ, people stand above nature and they may utilize in the way they like, unfettered by ethical chains. Looking at âStewardship of natureâ, people are charged with the responsibility to care for nature towards the generations to come or God. Even if this image âis less anthropocentric, Stewardship resembles the Master in the positioning of human beings above natureâ (De Groot, 2010, p.91).
Looking at âPartnership with natureâ, this is considered as a metaphor for a relationship that is equal between nature and the human beings; they operate jointly in a dynamic process of mutual development. It is pointed out that âin the most ecopocentric image, Participation in nature, human beings are part of nature in the sense that the connectedness with nature gives meaning to the Participantâs lifeâ (De Groot, 2010, p.91).
The studies that were previously conducted on âVisions of Natureâ were based on open ended as well as structured interviews and the Human Nature Scale indicates that the Dutch do discard âMastery over Natureâ and accept âStewardship over Natureâ (De Groot, 2010, p.91).
However, this Stewardship becomes a different variant from the traditional variant; rather than putting human beings above nature; the respondents engage in adhering to a Steward that is a portion of nature. They seem to undertake combination of âParticipation with Stewardshipâ (De Groot, 2010, p.91).
It is pointed out that even if the interviews conducted in Canada by De Groot and Van de Born (2003) made confirmation of such findings, still much has not been known regarding the images people have of relationship in the rest of the Western World (De Groot, 2010).
When looking for other studies in this field of empirical work presented by some environmental ethicists, you find such studies conducted by people like Norton (1991), Minteer and Mannings (1999) and Berghofer et al (2008) and all of them indicate that basically âNature-friendly ethics prevail among the Western populationâ (De Groot, 2010, p.91).
The most well-known is the âNew Ecological Paradigm (NEP) presented which undertakes the measurement of the ecological worldviews (De Groot & de Groot, 2009). Even if the extensive utilization of this scale has offered much insight in to the ecological beliefs across the world, this scale basically draws out levels of anthropocentricism, âranging from Mastery to Stewardshipâ (De Groot, 2010, p.91).
The respondents can just engage in agreeing or disagreeing to this representation that is not wide of environmental ethics with no whichever differentiation in the ecocentric alternatives. This is quite a big deficit when putting into consideration the ecocentric ethics as drawn out in earlier Human Nature studies and the âgenerally high scores on intrinsic value statementsâ (De Groot, 2010, p.91).
The other scale is the âConnectedness to Nature Scaleâ presented by Mayer and Frantz (2004). The focus of this scale is more on ecocentric end of the spectrum. Even if their statements match with the experiences and affections in nature to a large extent which makes up a central theme in the ecocentric relationships, this scale is not used in measuring the environmental ethics.
A study which takes both ends of the spectrum in to account is the one that was conducted by Thomson and Barton (1994) into ecocentrism and anthropocentrism. These researchers point out that âto ecocentrics nature has a spiritual dimension and intrinsic value that is reflected in their experiences in nature and feelings about natural settingsâ (Thomson and Barton, 1994, p.149).
They engage in combining images of nature and values to capture a worldview concerning the position of human beings in nature. In such sense, the study conducted by Thompson and Barton (1994) can be considered as the âforerunner of HaN-scale studiesâ (De Groot, 2010, p.91).
Besides ecocentrism and anthropocentricism, the HaN-scale as well fills in the âmiddle groundâ between both ends by drawing out âStewardship of natureâ and âPartnership with natureâ (De Groot, 2010).
Other than the images of relationship, there can be expectation of large number of other factors to undertake prediction and explanation of the adherences to flood risk management. In looking for variables that are supposed to be considered, the interpretative exploration carried out by Davenport and Anderson (2005) became an important base because of the inductive character it has.
On the basis of semi-structured interviews, these researchers draw a distinction between four meanings which the members of the community members in Nebraska attribute to the Niobrara River, that is âa river as sustenance, as nature, as tonic and as identityâ (Davenport and Anderson, 2005, p.625).
Considering âRiver as sustenanceâ, this ascertains the river as being a source of water that greatly is coveted and scarce and as economic revenue. Considering âRiver as a tonicâ, this suggests the river as being âgood for mind, body and soulâ (De Groot, 2010, p.92).
On the other hand, âRiver as natureâ gives expression of the appreciation of the respondents for the ecology and âriver as identityâ ties the river to the sense of people of who they are.
In an effort to undertake adaption of these four river meanings to the North Western European situation, ââriver as sustenanceâ was dropped because previous interviews suggested that this aspect of the river played a minor role in the personal lives of river residentsâ (De Groot, 2010, p.92).
They rarely lingered over the reliance they have on the river for water supply or over the economic activities that are linked to the river.
In connection to the study conducted by Buijs (2009) as well as that conducted by De Groot and De Groot (2009), there was inclusion of questions instead and this was for the reason of its noticeable relatedness to river management. The river meanings presented by Davenport and Anderson are a product of âGrounded theoryâ approach which began from âSense of Placeâ theories (De Groot, 2010).
This implies that the meanings âriver as natureâ as well as âriver as tonicâ do not have a theoretical grounding. In order to undertake expression of the theoretical background in a better way, De Groot (2010) made a decision to give names to meanings basing on the theories that were used; âSense of Placeâ, âLeisure experiencesâ and âVisions of Natureâ (De Groot, 2010, p.92).
Sense of Place, Leisure experiences and Visions of Nature
The measurement of leisure experiences were carried out on the basis of the topology of Elands and Lengkeek (2000). The leisure experiences are considered as âa confrontation with out-other-ness, a play with what is masked in everyday lifeâ (De Groot, 2010, p.93).
Typology can be viewed as a continuum which runs âfrom experience in which the difference between out-other-ness and everyday is rather smallâ to those where the âotherâ is rather unknown and inaccessibleâ (De Groot, 2010, p.93).
Because both river management styles bring about a different landscape and hence different opportunities for particular leisure experiences, there is expectation of this topology to correlate with the adherence to the styles of management.
Moreover, the âSense of Placeâ or âSOPâ is a portion of the literature that is fragmented on human beings and spatial settings consisting of other concepts like place meaning, place attachment and place identity. Even if a large number of scholars engaged in studying the attachment to the urban environment, among these, there are those that engage in studying a more rural setting, in an outdoor recreation setting, or a river (De Groot, 2010).
The indicators that are utilized in the industry are on the basis of the âSense of Place-scaleâ presented by Jorgensen and Stedman (2001) that gave a definition of the Sense of Place as âthe meaning attached to spatial setting by a person or group (Jorgensen and Stedman, 2001, p.233). They carry out the measurement of the âSense of Placeâ in three dimensions which are; identity, attachment and dependence.
It is important to note that âsense of Placeâ overlaps partially with leisure experiences. As on one hand strong attachment to a place is clearly the basis of dedication, on the other hand, the other experiences can be considered as being more âmoderate or very light forms of Sense of Placeâ (De Groot, 2010, p.93).
Basing on the study that was undertaken by Buijs (2009), there is expectation of Sense of Place to correlate in a negative way with the adherences to âRoom for Riverâ and this is for the reason that this measure impacts more âon the identity of the riverine placeâ (De Groot, 2010, p.93).
In addition, the preceding experience with flooding, âthe likelihood of having oneâs house flooded and the safety perception are expected to influence the adherence to flood risk managementâ (De Groot, 2010, p.93).
Making discovery of this correlation directly is easy after the occurrence of a flood; this is for the reason that, in situations like these, reinforcement support of dikes among the affected residents is high in general. However, the studies conducted previously on the subject of risk perceptions of river floods indicate that the risk perception of the public is usually low and mostly in the Netherlands (De Groot, 2010).
Management Styles
Going towards the interrelationships that exist between the âpublic environmental ethics as well as adherences to the management styles, it is realized that there is a correlation between Mastery and dike reinforcement and on the other hand, a correlation exists between Guardianship and the sustainable style.
This matches with the hypothesis that is made which give a presumption that the two management styles are formed on the basis of a different ethic. Basing on what is held by the public, a fundamental change occurs within a flood risk management at a time of having a shift from one style to the other style.
It is also pointed out that no Prediction is made by image of Participation of any style and on the hand; the image of Partner has a negative correlation with dike reinforcement. This gives room for having another hypothesis that makes a presumption that environmental ethics are not quite significant in carrying out the prediction of the public adherence to policy.
It is stated in this hypothesis by Norton (1991) that âweak anthropocentrists can reach the same policy objective as the ecocentricsâ (Norton, 1991, p.20). Basing on theory, more ecocentric river policies are very imaginable. However, it may here have been that the descriptions given to the two management styles âdo not relate readily enough to the wordings of Partnership and Participation itemsâ (De Groot, 2010, p.105).
For carrying out the interpretation of such conclusions, it is imperative to take into consideration the low explanatory power of the two regression analyses. In addition, the ethics of the public are among the several variable that carry out the prediction of the adherence to each style of river management; like ârecreation experiences, the place of the residence and the age of the respondentsâ (De Groot, 2010, p.105).
Considering the case of Australia, river degradation is a significant issue of natural resource management that is currently facing Australia.
For instance, it was found out that about eighty five percent of the river length that was assessed by the âNational Land and Water Resources Auditâ was affected by catchment disturbance. Moreover, it was found out that more than 50 percent of the rivers that were assessed are affected by the changes to riverine habitat (Brierley, et al, 2002).
Under normal circumstances, the work of catchment rehabilitation in this country has been carried out by the community groups having limited skills as well as resources in regard to priority are identification fro rehabilitation investment The resources for the work of river rehabilitation are limited and there are competing demands for these resources (Brierley, et al, 2002).
There is need to have tools in order for them to help in making decisions on which area to undertake application of resources and effort to realize the highest effectiveness in regard to river rehabilitation.
The âRiver stylesâ was set up out of a âLand & Water Australia funded project carried out by Macquarie University in response to the need for a framework that linked reliable knowledge of the nature of different river types and biophysical attributes within catchmentsâ (Brierley, et al, 2002, p.91).
âRiver Stylesâ offers a biophysical template for river management which is directly suited to âstructure and function of the Australia Riversâ (Brierley, et al, 2002, p.91). It offers a âbaseline geomorphic assessment of river character, behavior and condition, and is based on the premise that effective management strategies must âwork with natureââ (Brierley, et al, 2002, p.92).
Conclusion
In conclusion it can be pointed out that; it has been realized that following climate change that has brought about the problem of global warming, the countries in several parts of the world have a likelihood of being faced with extremely high river water levels in the shortest time to come. Moreover, sustainability comes up as a main international policy driver, bringing in different approach to flood defense.
It has been found out that, instead of fighting and engaging in the control of flood hazards with ever higher dikes, the focus of the new management styles is put on having knowledge about and managing the risk of posed by floods.
In the Netherlands, there has been well documentation of public support for âRoom for Riverâ policies and this support is found out to be high. To this overall finding, it has been pointed out that public support to specific âRoom for Riverâ measures may not be higher, like in the case when these involve removing trees
For the reason that the more ecocentric images of the relationship such as Participation and Partnership are as well well-liked among people, the river managers have a concrete basis in attempting to ensure incorporation of more ecocentric values in their long-standing policies and move beyond comparatively incremental and technical room for river policies that prevail at present day.
Explorations like these ones are supposed to be carried out in a way which ensures inclusion of the civilians from the very start in order for the parties to jointly engage in learning from one another in a process that is open.
It is important for us as individuals in engage in fruitful activities that can help as to effectively deal with the environmental problems that come up. It is important for us to emulate what others are doing elsewhere to be able to apply it in our own context.
The problems of river flooding and river degradation are facing several countries across the world, Australia being among them. Since these problems are predicted to intensify in the near future, it is important that appropriate measures be taken urgently in order to curb the situation.
References
Berghofer, U., Rozzi, R. & Jax, K., 2008, âLocal versus Global Knowledge: Diverse Perspectives on Nature in the Cape Horn Biosphere Reserveâ, Environmental Ethics Vol.30, pp. 273-294.
Brierley, G., Fryirs, K., Outhet, D. & Massey, C.,2002, Application of the River Styles framework as a basis for river management in New South Wales, Australia. Applied Geography, vo.22,no.1, pp.91â122.
Buijs, A. E., 2009. âPublic support for river restoration. A mixed-method study into local residents support for and framing of river management and ecological restoration in the Dutch floodplainsâ Journal of Environmental Management, vol. 90, pp.2680-2689.
Davenport, A. &D. H. Anderson, 2005, âGetting from Sense of Place to Place-Based Management; An Interpretive Investigation of Place Meanings and Perceptions of Landscape Changeâ, Society and Natural Resources, vol. 18, pp.625-641.
De Groot, M., 2010, Humans and nature: public visions on their interrelationship, Academic press, New York.
De Groot, M.& W. T. De Groot, 2009, âRoom for Riverâ measures and public visions in the Netherlands: A survey on river perceptions among riverside residentsâ, Water Resources Research 45.
De Groot, W. T.& R. J. G. Van den Born, 2003, âVisions of Nature and landscape type preferences: an exploration in the Netherlandsâ Landscape and Urban planning, Vol. 63, pp. 127-138.
Elands, B. &J. Lengkeek, 2000, Typical Tourists: Research into the theoretical and methodological foundations of a typology of tourism and recreation experiences. Backhuys Publishers, Leiden,.
Jorgensen, B. S. & R. C. Stedman, 2001, âSense of Place as an Attitude: Lakeshore Owners Attitudes toward their Propertiesâ Journal of Environmental Psychology, vol.2, pp. 233-248.
Mayer, F. S. & C. Frantz, 2004, âThe Connectedness to Nature Scale: A measure of individualsâ feeling in community with natureâ, Journal of Environmental Psychology, Vol. 24, pp. 503-515.
Minteer, B. A. & R. E. Manning, 1999, âPragmatism in Environmental Ethics: Democracy, Pluralism, and the Management of Natureâ Environmental Ethics, vol. 21, no.2, pp.191-208.
Norton, B. G., 1991, Toward Unity among Environmentalists, Oxford University Press,. Oxford.
Samuels, P., F. Klijn & J. Dijkman, 2006, âAn analysis of the current practice of policies on river flood risk management in different countriesâ, Irrigation and drainage, Vol.5, pp. 141-150.
Thompson, S. C. & M. A. Barton, 1994, âEcocentric and Anthropocentric Attitudes toward the Environmentâ, Journal of Environmental Psychology, vol. 14, pp. 149-157.
Van den Born, R. J. G., 2008, âRethinking Nature: Visions of Nature of a Dutch publicâ, Environmental Values, Vol. 17, No.1, pp. 83-110.
Van Stokkom, H. T. C., 2005, âFlood Defense in The Netherlands. A new Era, a New Approachâ, Water International, Vol. 30 no.1, pp. 76-87.
Zweers, W., 2000, Participating with nature. Outline for an Ecologization of our Worldview, International books, Utrecht.