Krystyna Rauba

Białystok Technical University

Poland

 

Social acceptance of investments in sewage management on the  deurbanised areas

 

 

Summary

In the paper there are shown the results of examinations of the willingness to pay for the use of communal sewage treatment service in three chosen districts determined with the use of CVM method. The districts chosen to the research do not possess the systems of communal sewage treatment. Most of households solves the problem with sewage by using cesspools.

 

Introduction

One of the tasks of districts is to provide habitants with the system of sewage treatment. However the investments in water supply and sewage disposal need considerable financial outlays. Moreover after completion of project, the enterprise which is responsible for providing services, incur costs which later reflects in the level of charges for sewage paid by clients who are the habitats of district. That is why, while planning the sewage policy the district should take into account the opinion of local community to make a decision about possible construction or extension of sewage system. To accomplish this objective it can be used Contingent Valuation Method (CVM).

While planning the level of prices for sewage treatment service it is necessary to bear in mind the rule of the reimbursement of water service costs which was formulated in Water Frame Directive[1]. The term ‘water service costs’ described in the directive has the same meaning as water and sewage service.  The total reimbursement of these services means the cover of operators costs , environmental and resource costs by charges made by clients.

 

1.     The subject of the examination

The examinations connected with the sewage management on the area of not sewered districts were done in three districts: Zbójna, Miastkowo and Dubicze Cerkiewne.

The district of Zbójna is situated in Łomża county. In 19 villages on the area of 18 579 ha (186 km2) there live 4570 habitants. The district is not sewered and does not possess the sewage treatment plant. The sewage from the districts are taken to sewage treatment plant in Łomża which is 20 km far from Zbójna.  However 80% of households use water-pipe network and 25% - telephone service. Landscape amenities and natural environment wealth are main tourist attractions of this district.  The central and east part of the district are located within protected landscape area ‘Drumliny Zbójenskie’[2].

The district of Mistkowo is situated on the west part of Łomża county. In 22 villages on the area of 11 485 ha (115 km2) there live about 4500 habitants. The large part of villages is sewered, whereas the district is not sewered and does not have a sewage treatment plant. Sewage from he districts of Zbójna and Miastkowo are taken 20 km away to a sewage treatment plant in Łomża[3].

The district of Dubicze Cerkiewne is located in Hajnówka county nearby the Białowieża forest on the area of protected landscape of high touristic and landscape amenities. In 17 villages and 29 towns on the area of 15 144 ha (151 km2)  there live 1994 habitants. During last years in this district there were done many district-planning changes among other things all villages were connected to municipal pipe network and the village of Dubicze Cerkiewne was sewered. In the future the district is planning to sewer other villages and towns, but also to build communal sewage treatment[4].

In all three analysed districts 90% of sewages is stored in cesspools.

 

2.     The characteristics of examination method

To study the opinions of habitants on completion of communal sewage treatment in chosen districts there was used Contingent Valuation Method (CVM). It is based on questionnaire examinations conducted among responders who were interested in particular good or service.  The pollster can ask a question to people who are polled in the form of WTP (Willingness To Pay), which means the level of price which they can pay for particular good or service or in the form of WTA (Willingness To Accept) which means how much they can take for tolerating disadvantageous changes in analysed element or limiting the access to it. Generally, it is assumed that WTP is used to estimate the value of proecological project and environmental benefits, while WTA to assess the ecological loss caused by the emission of pollutions to the environment[5].

In the world this method is used to estimate rare and threatened species of plants and animals[6] or to assess the actions decreasing flood hazard[7] .

The examinations connected with the quality of water sources were conducted for example in France. As the results show, both industry and agriculture do not incur the costs caused by contamination of water sources. The largest part in the water protection expenses have households. Each group expressed willingness to pay for improvement of quality of river water at the level of maximum 200 euro. This declared amount did not allow to cover the costs generated by households (500 euro) and agriculture (230 euro).

There was also made an attempt to use Contingent Valuation Method in Poland. The examinations of environment value based on this method were held by Warsaw Ecological Economics Centre attached to Faculty of Economics Sciences at University of Warsaw. The aim of one of the examination was to estimate Biebrza swamps. Respondents were asked about their willingness to pay for the protection of this area. The second question concerned the estimation of the quality of Oligocene water in Warsaw. The widest known examination is the one (called ‘Baltic’), in which the habitants of Poland were asked how much they can pay to prevent eutrophication of Baltic Sea. Taken actions effected in the decrease of the number of closed seaside resorts and renovation of life in the sea.

Questionnaire examinations held in the districts of Zbójna, Miastkowo and Dubicze Cerkiewne were based on a question in a form of WTP. The questionnaire was built of three parts. The first one had introductory questions, which let to assess the level of respondents’ knowledge about sewage management  issues in particular district. The second part of the questionnaire contained the questions about the ways and problems with sewage disposal from households and the knowledge of problems connected with water contamination on the area of the district, but also the interest of respondents in extension of communal sewage treatment. The respondents were also asked questions about the cost of sewage discharge and the frequency of cesspools emptying (in a case they were owned by respondents).

WTP question was formulated with reference to three initial amounts. The first amount was determined by taking into account only the costs of exploitation of sewage disposal and treatment system (price I), the second one covered the costs of exploitation and amortisation of the system (price II), while planning the third one there were taken into account the costs of exploitation, amortisation and profit of enterprise which provided service (price III). In Table 1 there are shown suggested levels of prices for particular district.

 

 

 

 

 

 

 

 

 

Table 1.

Characteristic of suggested levels of prices for particular district

 

 

 

 

District

Current average cost of sewage disposal

zł/m3

Price I

zl/m3

Price II

zl/m3

Price III

zl/m3

Zbójna

4,50

4,59

 

5,86

7,03

Dubicze Cerkiewne

13,05

3,18

8,86

10,63

Miastkowo

 

18,68

5,24

8,71

10,45

Source: Own study on he basis of data obtained form districts

 

In case when respondents did not accept the level of suggested amount, they could propose maximal amount, which they were inclined to pay for solving the problem with sewage  and give also the reason why they did not choose suggested prices.

 

3.    The description of results of questionnaire examinations held in particular districts

Altogether there were done 250 questionnaires.

Statistical analysis of obtained results was done on the basis of SPSS programme using  ‘Analysis-Regression Binary – Logistic’ procedures.

The willingness to pay for communal sewage treatment shown 118 people (47,2%).

Among those who did not want to pay, 67 respondents claimed that sewage treatment should be free of charge. What is more, 34 of respondents admitted that they could not afford to pay for construction of sewage treatment plant, while 10 of them stated that if a new sewage treatment plant was built it would not improve the situation of sewage treatment in particular district.  Moreover, 13 of respondents admitted that they are tired of paying taxes for social aims, 3 of them did not see the problem with sewage treatment and 5 gave other reasons.

Statistically significant variables were shown in Table 2 and they show: the agreement to build a waste treatment plant (WWTP), perceiving the lack of water (WATS) as substantial problem, people who walk voluntary in the open air (WALK), the age of respondents (AGE).

 

 Table 2.

Statistically significant variables in a regression equation and their significance in a model

 

Type of a factor

B

Wald

Significance

Constant

 

-3,412

21,055

0,000

 

 

Variables

WWTP

1,489

8,077

0,004

WALK

0,828

7,880

0,005

WATS

0,782

5,543

0,019

AGE

0,017

3,035

0,081

                    Source: Own study

As the above model shows, the people who agree with waste plant construction (WWTP) have a will to pay for it , which is something expected.

People who perceive the lack of water (WATS) as a substantial problem, also agree to pay for sewage treatment  . This result can be explained by the lack of sources of high quality water which connected with the purity of surface water contaminated by disposal of treatable sewage. Other statistically significant variable was the one which described respondents who walk voluntary in the open air (WALK). Those people are ready to pay for sewage treatment . That is why it can be concluded that people who run active life style and care about environment, have a will to pay for the construction of sewage treatment plant to prevent the degradation of environment by disposal of treatable sewage to surface water or to the ground.

Other statistically significant variable is the age of respondents. Elderly people show a willingness to pay, whereas younger people are not ready to do it . This situation can be caused by problems with migration from countryside to cities. Young people want to move to bigger cities or to go abroad to find better job, while elderly people would like to have sewage treatment problems on their area solved. Perhaps old people have higher savings. Moreover, unemployment is much higher among young people especially in this part of Poland.

 

Conclusions

The method of questionnaire examinations based on WTP question can be used to examine the level of social acceptance of investments into sewage management in a district. Te result of examinations can be useful for districts while making decisions about investments in communal water supply and sewage treatment.

The examinations which were held in three districts showed that most of habitants agree to build a sewage treatment plant (88,4%).

Not everyone is inclined to pay for its construction. Most of respondents do not want to pay higher charges than the current ones for sewage disposal and treatment. As the results of examinations show, many people can not afford to pay more and some of them think that water and sewage services should be free of charge. That is why the substantial problem is how to obtain funds to build sewage treatment plans when the habitants can not afford to cover the costs of their construction and the cost of their exploitation in the future.

 



[1] Directive 2000/60/EC of the European Parliament and of the Council of 23 October 2000 establishing a framework for Community action in the field of water policy

[2] www.zbojna.powiatlomzynski.pl

[3] www.mastkowo.pl

[4] www.dubicze-cerkiewne.pl

[5] Ocena i wycena zasobów przyrodniczych edited by J. Szyszko, J. Rylke, P. Jeżowskiego, SGGW Edition, Warsaw 2002, p. 245.

[6]  J. Loomis, D. White: Economic Benefits of Rare and Endangered Species: Summary and Meta-Analysis. Ecological Economics, 1996, 18, p.197-206.

[7] L. Shabman, K. Stephenson: Searching for the Correct Benefits Estimate: Empirical Evidence for Alternative Perspective, Land Economics, 1996, 72.