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FİRUZ DEMİR YAŞAMIŞ Siyasal Bilgiler Fakültesi’ni bitirmiştir (1968). University of Southern California’da planlama (kentsel ve bölgesel çevre) ve kamu yönetimi yüksek lisans programlarını bitirmiştir (1976). Siyaset ve Kamu Yönetimi Doktoru (1991). Yerel Yönetimler, Kentleşme ve Çevre Politikaları bilim dalında doçent (1993). Başbakanlık Çevre Müsteşarlığı’nın kuruluşu sırasında müsteşar vekili. (1978-80) UNICEF Türkiye temsilciliği. (1982-84) Dünya Bankası’nın Çukurova Kentsel Gelişme Projesi’nde kurumsal gelişme uzmanı. (1984-86) Çankaya Belediyesi’nin kurumsal gelişme projesini yürütmüştür. (1989-91) Yedinci Kalkınma Planı “Çevre Özel İhtisas Komisyonu”nun başkanlığı. DPT “Çevre Yapısal Değişim Projesi” komisyonu başkanlığı. Cumhurbaşkanlığı DDK’nun Devlet Islahat Projesi raportörü. (2000-1) Çevre Bakanlığı Müsteşarı (Şubat 1998 – Ağustos 1999). Sabancı Üniversitesi tam zamanlı öğretim üyesi. (2001-2005) Halen yarı zamanlı öğretim üyesi olarak çeşitli üniversitelerde ders vermektedir. Şimdiye kadar ders verdiği üniversiteler arasında Ankara, Orta Doğu, Hacettepe, Fatih, Yeditepe, Maltepe ve Lefke Avrupa (Kıbrıs) üniversiteleri bulunmaktadır.
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EVİM: ARKEON, TUZLA, ISTANBUL, TÜRKİYE

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27 Ağustos 2007 Pazartesi

STATE REFORM IN TURKEY

State Reform in Turkey:
Reasons, Needs and Strategies


Dr. Firuz D. Yasamis
Associate Professor
School of Arts and Social Sciences
Sabanci University
Turkey







ABSTRACT
The state structure in Turkey including all its branches of government (executive, legislative and judicial) at both the national and local levels has shown to be ineffective, and even irrelevant, to the ingrained demographic, social, economic and political exigencies of the country. One of the main reasons behind this is the collapse of public finance. Conventional rhetoric limiting solutions to administrative reform fails to provide a sufficiently broad enough context within which public sector reform in Turkey can be discussed. Turkey’s determination to become a full member of the EU also necessitates a comprehensive and radical overhaul of the Turkish public sector with respect to efficiency and productivity. Five main strategies are proposed to assist Turkey in overcoming its state governance predicament: initiating and carrying out a state-wide reform by employing modern principles of public management; understanding and solving the problem of internal and external debts; enhancing the conditions of governance, reintroducing and strengthening the principle of meritocracy in public sector; and cooperating more with the EU.
Given the present social, economic and political conditions of the world, the term “public administration reform” is conceptually inadequate to delineate the extent of the problems faced by public sector organizations in their attempt to meet the need for more productive, effective and efficient utilization of scarce public resources. As indicated by the World Bank Report and others (see World Bank 2000, Christensen 2001), reforming public institutions requires comprehensive and integrated efforts rather than dealing with the crucial issues on piece-meal basis. This is especially valid for developing countries, where the task of poverty eradication is of paramount importance, while the sources available to do so are rather limited. This combination thus creates an enormous burden on the establishment of corruption-free and merit-based governance in these societies. A recent World Bank Report (1997) supports this view: “Around the World, the state is in the spotlight. Far-reaching developments in the global economy have us re-visiting basic questions about government: what its role should be, what it can and can not do, and how best to do it.” The OECD is of the same opinion (OECD 1999, 2000). Moreover, the World Bank public finance reform programs have the same goal all over the world.
With respect to state governance reform, priority should be on solving public finance problems through comprehensive and coordinated efforts. While perhaps more evident in those countries in transition from a collective economy and central planning system to a market economy and for the developing countries, the more prosperous northern countries of our globe are not immune from having to make similar considerations with respect to the use of limited public revenue (Gore 1996, World Bank 1997, 2000). However, as measured by Transparency International (TI), governance, many societies fall short of this expectation [something is missing in this sentence- I don’t understand it]. The main reason for this is effectively explained in a World Bank Report (2000): “In countries where institutions are weak, policymaking and resource allocation typically proceed in nontransparent ways, with decisions generally skewed in favor of those who are well connected to centers of power.” As Caiden (1969) and the World Bank (1997, 2000) and several OECD reports have pointed out in this context, while the executive functions of public administration have conventionally been the main concern of reform efforts, it is necessary to embrace both the legislative and judicial functions as well.

The Main Reason for State Reform in Turkey: Shortage of Public Resources
The conditions described above also apply to Turkey, which is a very good example of a country where a comprehensive overhaul of public administration is necessary. All components of state governance, ranging from the executive, legislative and judicial components, to the administration of the national economy are to be considered together. Presently, the most serious problem Turkey has is the critical shortages and bottlenecks encountered in public finance. The charts given below indicate the conditions of public finance in Turkey. (1)
INSERT CHART 1 HERE
As indicated in the Chart 1, in 1980 the revenues of the state were almost equal to those of spending. However, 21 years later, mainly due to the economic, financial and social policies applied between 1984-1992, the situation is now very different. The ambitious developmental projects, expensive infrastructural investments and social policies have created considerable burden on the public finance. Internal and external debts have been used to finance domestic consumption and public employee salaries. As a result, both inflation and interest rates have skyrocketed at times to over 150%. This spiral is continuing. However, austerity measures imposed by the IMF and World Bank aimed at setting limits for state expenditures and increasing tax revenues have begun to have an impact. Combined with lowered purchasing power levels, inflation and the interest rates have dropped below 30% [did I get this right???]. At the moment, instead of relative equality, there is a gross discrepancy between the state’s income and its expenditures.
INSERT CHART 2 AND 3 HERE
Charts 2 and 3 above analyze the revenue structure of the state. The revenues have increased during the last 20 years. However, Chart 3 is most strikingly indicative of this structure. As of 1990s, the share of the indirect taxes in the total tax revenues has exceeded the income obtained from the direct taxes. This basically means that there is no further room for increasing the direct taxes on wealth, profit and income. Thus, the only way to increase the tax revenues is to get more taxes from consumption. This also means that the state has reached the upper limits of its extractive ability. Charts 4, 5, 6 and 7 below are reflective of the conditions of state expenditures.
INSERT CHARTS 4, 5, 6 AND 7 HERE
Chart 4 reflects the structure of state expenses. Total expenses have increased four-fold during the last two decades while investments have remained constant. Current expenses have increased almost two-fold. Conspicuously, transfer payments, which consist of interest payments on domestic and external debts and transfers to the State Economic Enterprises (SEEs) and other transfers, have increased almost ten-times. No increase in investments and a limited increase in current expenses indicate that public spending has been severely curtailed, thus causing serious bottlenecks and quality problems in public services and public infrastructures.
Chart 5 illustrates the situation on current expenditures. The increase in current expenses is mainly due to the increase in personnel expenditures especially in the period of 1985-1990. In the mean time, the number of public employees has increased so as to alleviate the pressures on politicians and public administrators for more job opportunities. Since the quality and the quantity of public services is determined by the low financial resources, this result basically indicates the mismanagement of scarce financial resources thus requiring a reform initiative for public personnel policy.
Transfer payments indicated in Chart 6 illustrates the most important features of public finance in Turkey. Transfers to the SEEs are negligible and other transfer payments have slightly increased. However, the most salient development is related to interest payments, which have increased enormously during the last 20 years. Therefore, the main increase in public expenditures is basically due to the interest payments on public debts. Chart 7 shows the composition of the interest payments. The share of the foreign debt interest payments is bearable although increasing while the share of the domestic debt interest makes up the lion’s share of the composition of debt. This means that the state is relying mainly on borrowing from the domestic financial markets to cover domestic debt services – a trend that is upwardly spiraling.

INSERT CHART 8 HERE
In Chart 8, three main parameters are compared: total revenues of the state, the share of transfer expenditures including interest payments and the share of interest payments. In 1980, revenues exceeded transfer payments even as interest payments were negligible. However, in 2001, the volume of transfer payments was greater than the state revenues, a situation essentially caused by interest payments on domestic debts. At the moment, even the share of the interest payments is more than the total state revenues. Therefore, in Turkey, all the state revenues are basically spent on interest payments, thus leaving no opportunity for financing any other public spending except through further borrowing from domestic and external sources. According to the latest budget performance data for 2002, state revenues were insufficient to finance the debt service of domestic and foreign debts, let alone providing for the financing of other public needs. The amount of interest paid for the debts reached 110 percent of budget revenues. In the period January-March 2002, budget revenue increased 42.3 per cent compared to the same period in 2001. This is in contrast to an increase of 159.7 % in budget expenditures. The main increase in the expenditures was caused by the increase in the interest payments. Interest payments increased by 243.9 per cent from 2001 to 2002.
These results lead to two very important questions: “How will the needs of the people and the state be met?” and “What does all said above mean for the Turkish economy, public finance and state governance?”

Impacts of the Main Reason and Other Contributing Factors
The Administration
The conditions and parameters described above could create significant adverse impacts on the state governance in Turkey. The present situation indicates that public finance in Turkey is approaching insolvency. State revenues are inadequate to meet state expenditures. State debt has reached such a critical level that nearly all state revenues go to financing debt services. As a result, state governance needs to take appropriate austerity measures. Possible measures may include a drastic reduction in public expenditures by diminishing the number of civil servants, cutting the services and lowering the quality of services. Moreover, due to an enormous decline in income-generating capacity, public financing is experiencing great difficulties just at a time when the cost of debt service is rapidly increasing as a consequence of the growth in public debt.
The factors contributing to the situation described above are numerous. First, the state has experienced a decline in internal and external borrowing capacity, just as domestic debts have soared, making management of domestic debt increasingly more difficult. While international borrowing is still available, it is a very expensive option. The IMF and the World Bank have launched in Turkey an intervention program that is the most ambitious of its kind in the history of these institutions. As a result, Turkey has become the world leader in terms of money borrowed from international sources. It is not certain yet just how long the IMF and the World Bank will continue to assist Turkey in alleviating the economic predicament brought about by a shortage of hard currency. Therefore, at the moment, additional foreign or domestic borrowing potential of the country appears to be rather limited. What are more positive in recent developments are the decreased rates of inflation and interests. These encouraging developments may alleviate the burden on the public service, but for anytime in the foreseeable future, the paramount problem of eradicating the stock of domestic and international debts promises to remain. It also needs to be pointed out that the state cannot readily increase tax revenues as a means to solve the problem.
This set of circumstances requires that the Turkish State make critical decisions with respect to effective and efficient governance. And it cannot simply expect that tinkering with certain aspects of public administration will be adequate, given the seriousness of the problems it faces. Trends require an overhaul of the entire structure of the state apparatus. Its internal organization, including interdepartmental and intersectoral relations, must be revised. All of this demands a new understanding of what constitutes management and its procedures and principles. In order words, comprehensive public sector reform in Turkey is a must.
Wide-scale corruption is the second factor contributing to poor public sector governance in Turkey. Corruption goes against the very principles of bureaucratic ethics. One of the pillars of the bureaucratic ethics is the notion of meritocracy, which includes the principles of eligibility, competency, career and seniority. Recent researches by Okcesiz (1999) and “Turkish Foundation on Economic and Social Studies” (TESEV) (2001) conducted in this area emphasize the extent to which corruption and bribery have become a wide-scale social, administrative and political problem in all branches of the state machinery. Moreover, the semi-autonomous Council on Banking Affairs has revealed that the cost to the state of the recently bankrupted private banks is almost 43.6 billion US dollars by September 2003, which is nearly one-fifth of total debts of the Country (BDDK 2003:12).
TESEV’s above-mentioned Report (2001) indicates that the Turkish people’s satisfaction with services provided by various public administrations throughout the country, and the faith of people in both the bureaucracy and bureaucrats is low. Furthermore, the dimensions of bribery and corruption have reached widespread proportions, with the number of citizens who think that public officials treat them equitably and who believe that the principle of meritocracy is applied in the case of public hiring is low. The National Security Council believes that corruption poses a serious threat for national security. On October 1st 2003, the President Sezer also voiced similar concerns: “One of the most basic problems of the Country which has to be emphasized strongly and has to be struggled against collectively by all sections is the corruption which results in a wasting of the scarce resources of the nation while favoring private interests of some circles.” Similarly, the OECD has also indicated in various reports that when there is a scarcity of public funds, corruptive forces are likely to play an important role in the distribution of the national income (OECD 1994).
High levels of unemployment and a rapidly increasing population makes employment in the public sector rather attractive despite the very low salaries vis-à-vis the cost of living in the country. Likewise, contracting companies, which are dependent on public work projects, are under great financial pressures due to the diminishing ability of the state to make infrastructure investments. These social and economic dynamics have paved the way for an emerging intermediary class consisting of local and national politicians who work on the basis of commission taking the form of either financial or political rewards (Yasamis 2001). Differing forms of corruption (ranging from bribery to nepotism and basic fraud to tampering with official documents and wire-tapping) can be observed in public transactions, including any kind of governmental compliance management activity.
A natural consequence of this is that the principles of meritocracy have failed to become embedded in the state machinery. Eligibility, for example, is not the main factor considered when making appointments to public posts. Rather, it is political fidelity that determines who gets appointed to well-paid senior-level positions (Tutum 1994). Similarly, competency, even where it is a necessary aspect of a post, is not the sole consideration. On the contrary, the criteria for selection and promotion are the desire to divide and share the “public pie” with “friends.” As was seen in the notorious “Susurluk” (3) scandal, public officials can set up ties with illicit forces and attempt to use the public power of their official duties to get their share of “profits” made on the “black market.” What remains consistent in this nexus are some politicians who have considerable superiority in establishing and maintaining contacts between bureaucrats, entrepreneurs and “mafia-like” illegal organizations.
Another indication of the corruption in the public sector is the newly established decentralized (“distributed public governance” as termed by the OECD) bodies (OECD 2002). These ‘supreme committees’ are relatively autonomous vis-à-vis the central government and therefore the political pressure held over these bodies is intended to be limited. The plethora of recently explored autonomous “supreme councils” in the public administration is basically due to the attempts to break the controlling power of some politicians over public resources and interests.
The economic dimension or economics of the corruption apparently is rather considerable, so much so that it has reached a point where it has begun to adversely affect the national economy. There is, however, no extant report on the economic dimension of the corruption published within Turkey. However, the works of UN ECOSOC and other UN bodies (UN-ODCCP 2001), IMF good governance activities, anticorruption works of the World Bank, OECD and TI (2003) provide some insights on the issue. All agree that it is rather difficult to assess the economic parameters of a secret transaction and therefore an exact description is complicated, if not impossible. However, again all agree that corruption hits hardest the poor but the rich least and also that there is a strong correlation between levels of corruption and lowered economic performance.
The third primary factor contributing to poor public sector governance in Turkey and that therefore demands state reform is institutional. The organizational structure of public administration was essentially shaped during the second half of the 19th century under the Ottoman Empire. These structures are now outmoded, inefficient, ineffective and heavily centralized. Two important studies of TODAIE (2) indicate that since the advent of the Republic, the structure of the central government has evolved and matured only incrementally (1963, 1991). Since the establishment of the Republic, excessive centralization in public service provision has been re-explored and re-institutionalized. The need to utilize scarce public resources in a more productive manner, to establish essential infrastructure and industries, and for capital to make an efficacious contribution to national economic development are the main roots of excessive centralization in Turkey. While excessive centralization remains a problem in Turkey, the original assumptions underlying the need for such centralization are no longer valid or relevant given the contemporary social, political and economic realities of the country. Compared to 80 years ago, the economy has changed dramatically, the standard of living has improved considerably, and well-entrenched social and political transformations have occurred. Hence, the classic concept of “Provider and Protector State” has changed into the concept of “Enabler State.” The conventional and classic role of the state and the considerably large share of it in the public economy are now being questioned. Within this context, there has arisen a perceived need for devolution of public services and authority out of the hands of politicians in the capital toward more control over those services and authority being vested in local governments. The first dynamic is the product of requests made by new democratic elements of society for more public participation. The second, on the other hand, is being made at the behest of circles opposed to the nepotism flourishing in the capital that skews the distribution of scarce public resources to their own political cohorts.
As indicated by Michalski (OECD 2001:7-28) and by Tarschys (OECD 2001:30), public administrators are eager to retain maximum power and authority in their own hands and are reluctant to delegate to lower echelons, even within the same state institution. Consequently, the center becomes burdened with an excessive workload, which produces delays, confusion, ambiguity and frustration amongst the decision-makers, as in the case of Turkey. Red tape, “non-transparent” working conditions and the general lack of trust in the ethical and moral integrity ordinary citizens and employees exhibited by public administrators create conditions whereby recipients and providers of public services alike suffer from excessive centralization. Accordingly, these kinds of trends require a fundamental restructuring of overall public machinery, including the powers, authorities, responsibilities, the legal statutes, and the relations amongst the public bodies in every country regardless the level of development.
The fourth factor that makes overall public sector reform a necessity, as indicated by a report published by the Turkish Association of Industrialists and Businessmen, (TUSIAD 1995), is the ineffective, inefficient and nonproductive management practices that have given rise to expensive and low quality service production in the public sector. The notion that public administration can actually have a scientific basis is generally not well developed in the Turkish public sector. This lack of development can be seen in the way individual public bodies are organized. They tend to be set up in a random manner and do not reflect any scientific theory of organization. Management practices are far from the modern, and contemporary understandings of management. Rather than being even incremental, decision-making is coincidental and biased towards political and economic interest sharing. Planning, either corporate or operational, is not dependable in the public sector. Daily operational planning of work based upon the concept of resource planning is minimal at best in public organizations. An exceptional development in this regard is the computerization occurring in public bodies. The rapidly enlarging computer-aided projects in the public arena do not intimidate managers and employees. Yet, the audit function is merely based upon legitimacy-controlling concerns and such audit concepts as “performance auditing” or “value-for-money” controlling have not yet found its way into the public sector (TODAIE 1991).
The fifth essential factor why reform of the public sector is imperative is the absence of effective financial management, planning and analysis ability in the public sector. It is clear from examining existing budgeting and accounting systems that they are unable to incorporate such essential ingredients of any modern management accounting system and cost/revenue centers. As indicated by the SPO (DPT 2000: 31), the cost (total or unit) of the public service provided usually is not a concern for the public administrators in Turkey. Moreover, revenue-generating activities are mostly disdained.
The last but not least factor contributing to the need for reform concerns the relations between Turkey and the EU. As a candidate country for full membership, Turkey is working hard to meet the Copenhagen criteria for accession and the adoption of the EU’s “acquis communautaire.” One of the Copenhagen criteria for accession is the improvement of public administration and in the public service delivery capacity of the candidate country (EU Commission, 2000).

The Parliament
Similar to the conditions for administration stated above, it is widely accepted that the legislative assembly in Turkey is less effective and efficient vis-à-vis the felt needs of the country (Yasamis 2001, Turan 2000). The Parliament in Turkey has two main tasks: to enact legislation and to supervise the activities of the administration, of which the former is primary. While such legislation seems to be very effective under the present single-party majority government at the moment, it has in the past undergone a series of crises under coalition governments of the past. Inappropriate working procedures and the lack of faith between the parties in power and the opposition result in lengthy and time-consuming legislative activities.
Controlling the executive, the Parliament’s second task, has always been problematic and ineffective. Governing parties generally have the majority in the Parliament, which leads to ineffectiveness in legislative control. This is because having this majority creates an obstacle an adequate functioning of a separation of the powers, and thereby the benefits expected thereof. Moreover, in the past it has been the case that positions taken by certain politicians before their entering Parliament had had a deleterious impact on legislative activities once they became parliamentarians. [The last sentence is really vague – it seems like you have something in mind but you don’t express it. So it leaves the reader wondering what you are talking about]

The Judiciary
The judiciary is also not immune from the liabilities mentioned earlier. The main criticism of the judiciary has to do with the lower level of effectiveness of the principles of State with respect to the Rule of Law and the Supremacy of Law. Moreover, it is also concerned with the distribution justice in the society, reservations over the full realization of the principle of independence of judges, inefficiencies in the management of judicial services, inappropriate institutional setups, complex judicial bureaucracy and excess red-tape, insufficiency of salaries and wide-scale corruption in judiciary (Yasamis 2001, Okcesiz 1999, TESEV 2001). All these point to the need for a radical reform in the judiciary.
[The “poor” judiciary seems like an “after thought” compared to the space you give the administrative and the legislative branches of government! You don’t even give it a REAL “second thought” later in your analysis.]

The Needs to Be Satisfied by State Reform
The factors laid out above create several political and administrative needs that have to be met. These are needs that are perceived by the public to be the main obstacles to effective, efficient and productive state governance in Turkey.
The first and the most important need is for more rational and effective utilization of scarce public resources (TODAIE 1963, 1972, 1991). There are several other factors that make the situation more complex. These factors are called the “holes” in the central government budget. The first big hole is the compensation provided by the central budget for the losses of the SEEs. Almost all of them are operating in the red, with negative balance sheets, with their losses being met by the central government.
The second “hole” is related to the local governments. In Turkey, local revenue base of the local governments is virtually low and the local governments are mainly dependent on the income to be derived from the central government in terms of having a share from the nationally collected taxes, grants-in-aids and compulsory payments of the local governments’ centrally insured international debts from the national budget (TODAIE 1992, TUSIAD 1992).
The third “hole” in the national budget has been created by the social security system of white and blue-collar workers and the self-employed. Since the system is not self-sufficing or self-financing, all social security institutions in Turkey are substantially financed by the central government, which, of course, is another financial burden and source of “leakage” of state revenue.
The collective and cumulative impact of the unfavorable conditions of the public finance and the above described “holes” basically means that resources are extremely limited vis-à-vis the social and economic needs of the people.
The second need to be satisfied is related to public management. The dysfunctional principles, values and assumptions of the “old guard” must be replaced with modern ones that emphasize efficiency, productivity, efficacy as well as accountability and transparency. Peoples right of getting information and participation in public decision making are somehow not satisfactory. Because public policy decisions are not made openly, the public interest may not always be the sole criterion in decision-making. This makes it difficult for public officials to be held accountable to the people who are to be affected by policy decisions. Limiting this access and participation, the public stands to remain isolated from the very institutions of governance whose function it is to serve it (OECD 1987).
Thirdly, public sector reform also necessitates the inculcation of meritocracy in bureaucracy. Accordingly, there needs, for example, to be a comprehensive and unquestionable re-institutionalization of the principles of eligibility, competency and seniority within the civil service career system.
The fourth need is related to the quality of policymaking, policy implementation and even the “politicians” themselves (Yasamis, 1997b). Because of the cynicism and contempt the general public has of what they view as self-serving politicians, even the merits of democracy are questioned by the ordinary man on the street. IMF seems to be having a closer outlook on the issue and therefore trying to insolate the politicians from the day-to-day operations of public administration in their negotiations for the new credit schemes.
The fifth need for public administration reform concerns relations with the EU. The EU’s main principle regarding the overall structuring of services and functions is that of “subsidiarity.” This principle, when translated into the internal public organization of member states, means that public services should be provided at the closest point to the end-users or beneficiaries of these services. Simply, this principle means maximum deconcentration of public responsibilities ordinarily concentrated in the Capital, with maximum decentralization of public services from the central government to the local governments.

Strategies of State Reform
Why reform of the public sector in Turkey is imperative and what promises to be satisfied as a result of a better and more effective functioning of that sector has been laid out above. What is more difficult is determining the strategy to be followed for realizing a meaningful state reform in the country. The strategy, or strategies, to be developed and implemented will also be rather complicated and cumbersome (OECD 1999 and Jenkins 1995).
One possible way to approach public sector reform is decentralization, which aims at devolving many of the public services conventionally provided by the central government to local governments (TUSIAD 1992). In practice, what this means is providing local municipalities with the necessary discretionary powers, as well as financial authority and capacity to be able to efficiently use available resources and seek additional ones in order to make and carry out efficacious policies having a positive and meaningful impact at the local level. Reforming local governments and the “intergovernmental” relations within the Turkish state apparatus is an enormous task that will require concerted effort on the part of both local governments and the central government in the capital. In order for such reform to be carried out, local governments first have to be strengthened and empowered in a number of areas. Strengthening the effectiveness of the financial, organizational, managerial and resource planning capabilities of local government is yet another direction towards which reform of the Turkish state sector can take. Similarly, diminishing the supervisory tutelage of the central government over local governments (Yasamis, 1997c) can contribute to the rise of more confident and robust local administration.
Likewise, delegating such administrative powers and services generally concentrated in the capital as planning available resources, making budget proposals, procurement, hiring new personnel, human resources management and auditing to the field units of the central government can have a positive impact on deconcentrating the public sector and making it more administratively responsive to local needs.

Strategy 1: Reforming state governance
Carrying out state reform is never easy and not always successful (OECD 1995a) since the task requires strong political will and the processes involved are complicated. In Turkey, for instance, such reform can only be attained if it is all encompassing, including all branches of the state simultaneously since all these branches are adversely affected by the same factors. This is especially valid for parliamentarian systems in which the same political parties in power control the executive and the legislative branches of the state. In the case of Turkish judiciary there is a widespread consensus on the necessity of radical shake up in all related circles [this a vague statement – maybe you should add a few brief explanatory examples]. Reforming state governance requires the adoption of new concepts and understanding in three important areas. First, reducing the share of the public sector in the overall economy is an option that can be considered. This has the potential of increasing market competitiveness. Companies in the private sector can be encouraged to provide services ordinarily provided by the state in its monopolistic capacity of provider of public services. What could change using this strategy are the areas in which the state would continue to provide services. These areas mainly include what are considered “essential” public services (TUSIAD 1995, Yasamis 1997a).
Second, a redefinition of the role and status of the central government can be promoted as a consequence of the reduction of its share in the economy and as monopoly provider of public services. Since the establishment of the Turkish Republic in 1923, the central government has assumed the role of promoter of social change and economic development in Turkey. Economically, this mission has included the construction of essential industries and fundamental infrastructure. Socio-politically, it has taken the form of promoting the creation and development of a modern western society. Since then, the private sector has developed, sufficient capital has accumulated, and the technical capabilities of the country have expanded. Therefore, the importance of the role played by the central government as a promoter of social and economic development has diminished. Turning over public sector activities to the private sector is important strategy to be considered over the coming years in Turkey (TUSIAD 1992, 1995, Yasamis 2001). More power, authority and responsibility can be devolved and/or delegated to provincial and district representatives of the central government. Ultimately, much of the power, authority and responsibility currently exercised by the central government can be transferred to local municipalities in the periphery in line with the principle of subsidiarity of the EU (TUSIAD 1992, TODAIE 1992, OECD 1987).
Furthermore, the large-scale influx of the population since the early 1950s into urban areas has created unmanageable conditions (Yasamis 1996) in the urban areas of the country. (Yasamis 1995) The urban population has increased three-fold while the ratio of municipal incomes to GNP has only doubled during the last 50 years. As a result, municipalities in Turkey have begun to succumb to the pressures caused by urbanization (Yasamis 1991, 1992, 1993). Municipalities have suffered the most in such areas as municipal finance, municipal organization, manpower, urban economics, urban engineering, urban planning and urban management. The situation is even more severe in big cities, metropolitan areas and in the Megalopolis of Istanbul (Yasamis 1997d). Therefore, there is evidence to support the claim that municipal reform must make it possible for municipalities and other forms of local administration to become the primary provider of public services throughout the country (TODAIE 1992). However, without the necessary conditions for full discretion of local self-governance, attempts at decentralization may not be successful. In this regard, the future of Turkey lies in the merits and potential of strong municipalities rather than strong “provincial special administrations.”

Strategy 2: Solving the problem of internal and external debt
It is obvious that this strategy requires radical changes in the management of the national economy. Therefore, this strategy also includes economic reform activities that are beyond the scope of this analysis to discuss. However, there are several possible administrative strategies to be followed in this regard as explained below. One effective approach in this regard seems to lie in the sphere of increasing private sector involvement in the provision of public services. Existing SEEs have become unproductive and costly to run. Therefore, one way of increasing their productivity (through curbing down unnecessary work-force and current expenses and adopting realistic pricing systems) thus reducing financial burden upon the national budget would be to privatize them by selling them outright or by transferring the right of operation to private companies when there is no any other way to make these institutions self-sufficing. Privatization attempts in Turkey have been futile and the income derived it is nearly equivalent to the expenditures incurred. However, in the case of the former East Germany, for example, outmoded state enterprises were sold cheaply, with financial subsidies even being provided to the purchasers [but doesn’t this example still show that privatization attempts actually provide a loss to the state rather than a gain? If in East Germany, state enterprises were both sold cheaply AND with subsidies to the purchasers, how does that make it a benefit to the state. I think you would have to mention something like selling the outmoded state enterprises, even with subsidies actually benefited the state because it help “get rid of” institutions that were economic burdens to the state. On the other hand, aren’t some of the state enterprises being sold in Turkey actually “money makers” rather than a burden to the state????]
Another form of privatization in the public sector could be a push towards commercialization and “corporatization” of state-owned and operated enterprises. This would entail their transformation into companies working within the framework of private commercial law. As a result, instead of operation on a not-for-profit basis, they could be free to seek profits and distribute profit shares to shareholder or stockholders. Such a strategy would mean to employ more market-based management tools by the public administration.

Strategy 3: Enhancing the conditions of public management
The experiences of Finland, Australia and New Zealand had shown that modern concepts of public management, when adopted, offer several strategies and techniques that can enhance the performance of the governance function of the state. (OECD 1999, Finland 1994, Marsden, Wood 1993) These concepts mainly include “accountable management,” “management-by-objectives,” “end-management,” “result management” and “performance management” (OECD 1994, 1995a, Frederickson, 1999). Ultimately, what is needed is a revamping of the structure and practices of public administration in the direction of “sustainable (or, continuous) development” (Bank 1992, Kettl 2000, Pollitt 2000). This requires a multi-level revision of the way in which public services are provided. Instead of creating new large-scale public bodies, priority ought to be given to constructing process-oriented organizational development techniques (Pollitt 2000). Organizational assessment, feasibility studies, and legislative impact analyses need to be performed prior to the launching of important reform projects and the seeking of legislative reform in the public sector. Furthermore, the promulgation and implementation of public service standards is an important part of state reform. This could include, for example, “a charter for citizens” that indicates the basic rights of the people vis-à-vis public administrators, and the basic responsibilities of civil servants have respect to those seeking public services. Another might be an “administrative procedures law” that lays down the main principles and procedures of state governance and public administration (OECD 1996a). The auditing concept in the public sector could also be enhanced. The prevailing approach of controlling the legitimacy in public activities should also be strengthened with performance auditing approach thus insuring the re-appraisal of the public resources used (OECD 1995a).

Strategy 4: Reintroducing meritocracy in public sector
“Bureau-pathologies” existing in public administration in Turkey have reached such levels that not only is the provision of essential public services in jeopardy, but also the security and interests of the Country. While Turkey is signatory to a number of international accords whose aims are to prevent corruption and bribery (OECD 1996b) in economic transactions, the necessary internal legislative preparations have not yet been completed for full compliance. An integral component of such legislation is the re-introduction of the principle of merit in hiring, appointment and promotion within the public bureaucracy. This includes as well, such principles as competency, eligibility, career and seniority. Accompanying the principle of merit must be the re-institutionalization of ethics in the public sector (Mosher 1974).

Strategy 5: Cooperating and coordinating with the EU
A final strategy might be the acceleration of cooperation and coordination with the EU to reform and upgrade the service delivery capacity of the public administration. As a candidate for full membership in the EU, Turkey is obliged to upgrade its public administration within the framework of the Copenhagen criteria for enlargement. There currently exists a discord between the European Union’s (EU) understanding of what constitutes contemporary European public administration and what is currently present in Turkey. The major points of disagreement need to be identified, addressed and reconciled so as to ensure that Turkey makes effective progress towards reaching the standards set by the EU.

Conclusion
Reform of the public sector Turkey is needed to insure a proper management of scarce resources and to prevent a decline in the quality of state governance. Effective resource management demands public finance that is based on proven principles. In Turkey, the financial resources available to the state are indeed limited and the future is not anymore promising. Therefore, the ultimate objective for the public administrators should be the maximization of economical, efficient and effective utilization of scarce public resources. Nevertheless, without ridding the system of corruption and reintroducing meritocracy, not only will the provision of public services continue to suffer but also public administration reform will remain futile. Overhauling public administration must be confronted on a number of fronts, including the legislative and judicial branches. State reform in Turkey requires nothing less than a full-scale reformation of its state apparatus.


Notes

1. The data used in the charts is obtained from the Turkish Treasury.
2. “TODAIE” stands for the Public Administration Institute for Turkey and the Middle East.
3. “Susurluk” is an important symbol of corruption in Turkey. A court in Istanbul issued a verdict that some public officials had set up an illegal crime organization to realize their own personal interests by misusing the public power.


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ASSESSING THE PERCEPTIONS REGARDING THE INSTITUTIONAL EFFECTIVENESS OF STATE ENVIRONMENTAL AGENCIES

ASSESSING THE PERCEPTIONS REGARDING THE INSTITUTIONAL EFFECTIVENESS OF STATE ENVIRONMENTAL AGENCIES


Firuz D. YASAMIS, Ph. D
Associate Professor




Valiler Sitesi A-5 No. 7
Vatan Caddesi, Tuzla, Istanbul 34940
Turkey


fdy@ttnet.net.tr
(90) (532) 3619156
(90) (216) 3953181


Increasing the performance of the state environmental agencies (SEAs) necessitates an effective institutionalization of governmental environmental management functions. There are examples of successful and unsuccessful SEAs in several parts of the world. Analysis and assessment of these cases can deliver useful insights for the institution builders. The objective of this paper is the assessment of the institutional effectiveness of the SEAs in Turkey. A checklist is developed including 16 criteria and 123 sub-criteria to measure the effectiveness of the SEAs. 28 national and international experts have formed a Delphi panel and evaluated the national and local conditions. Results, based upon the perceptions of the experts, indicate that the overall effectiveness of the SEAs far less from satisfactory. Negative consensus has been reached over the effectiveness of 13 out 16 criteria and 95 out of 123 sub-criteria while no consensus has been achieved over the rest of the parameters. The survey has also proven that the Delphi technique can be effectively used for the purpose. Utilisation of checklist method is also useful in diagnosing the ailing components of the SEAs. It is recommended that this approach can be used in similar cases elsewhere.

KEY WORDS: State Environmental Agencies, environmental management, Turkey, Delphi.
1. Introduction

The State Environmental Agencies (SEAs) aim to resolve the undesirable outcomes of environmental pollution and to develop remedies for the needs of environmental quality upgrading, as is the case in Turkey. The SEAs in Turkey have been assigned to similar duties by the Constitution and the main environmental legislation. Article 56 of the 1982 Constitution explicitly mentions the “right of healthy and balanced environment.” According to this Article, the state and the citizens are responsible for upgrading environmental quality, protecting environmental health and preventing environmental pollution. However, according to the Article 65, the State will execute this responsibility within the limits of available financial resources. “The Environmental Code” (Republic of Turkey -RoT- 1983) furnishes similar provisions and principles. It, however, had not contributed to the concept of sustainable development as it is primarily concerned with economic development and the generation of employment. Nevertheless, these two main legal documents have a common denominator: economic development has priority and environmental concerns will be dealt with only if financial constraints permit. Undoubtedly, these provisions are not compatible with the concept of sustainable development. This means that the level of national political will to further protect and to enhance the environmental quality is severely curtailed.
As far as the right to know is concerned, the Environmental Code furnishes the public with a strong, definitive tool. Article 30 of this Code guarantees the right to apply to administrative and legal authorities in order to prevent pollution. Besides this, it establishes a sound basis for the right to sue administrative authorities responsible for environmental protection in the courts in the event that they fail in their respective duties. Therefore, both real and legal persons may petition the authorities to have environmentally detrimental activities terminated. The responsible agency has to reply within 60 days. If it does not, the petition will be taken as rejected and the right to sue will automatically be granted to the plaintiff. New legislation entitled “Freedom of Information” (RoT 2004) has secured the right to know in environmental matters. Through the adoption of other new legislation, “the Penal Code,” (RoT 2004) environmental crimes have been re-defined and new legal sanctions, which include jail sentences for unlawful polluters, have been created. Nevertheless, the possibilities for public participation are limited. For example while “the Regulation for Environmental Impact Assessment” foresees a “public meeting” at the site where new investment is planned, the local inhabitants are merely informed about the project and their opinions simply registered. Only the “7th National Development Plan” (SPO 1998) has explicit and clear-cut provisions on the improvement of institutional set-up. Although, the 7th Plan diagnosed the institutional problems accurately and developed effective solutions, by the end of the plan period only a few of the recommendations had been realized. Moreover, despite the fact that Turkey prepared the “National Environmental Strategies and Action Plan” (NEAP) (SPO 1999), its results have thus far been negligible, too.
It should also be pointed out that the preparation and publication of the “State of the Environment Reports” have become part of neither the daily routines of the Ministry of Environment and Forestry (MoEF) nor the mechanisms of national environmental legislation-making.
A new concern has emerged during the last 25 years in Turkey with respect to the significance of environmental protection. However, it would be rather difficult to state that political will to protect and further enhance the quality of the environment has emerged at the national and local administrative levels. The concerns with rapid economic development and combating the problems of unemployment still have more priority than rendering the development more sustainable and protecting the environment.
While some countries have established successful institutional examples and effectively controlled the negative impacts of environmental and ecologic pollution, others have failed to prevent pollution. New philosophies, strategies, policies and procedures are being developed and implemented in different parts of the world. The diffusion of these trends is creating new and inspiring examples for others (Busch and others 2004). There are several examples worldwide which indicate the changing nature of the SEAs (Wang and others 2000). The first example is the new public management reform initiative in the USA by the introduction of “Governmental Performance and Results Act” (GPRA) of 1993, which had considerable impact on the SEAs, resulting in further enhancing the outcome achieved (US Congress 1993). One of the most visible outcomes of this approach is the “performance partnership agreements” between the EPA and the SEAs, which aims to increase the institutional effectiveness of environmental government organizations. OECD developed similar attempts known as “Environmental Performance Reviews” (EPR), which is further supported by the UNEP and Asian Development Bank and “Public Environmental Expenditure Management” (PEEM), which is a framework for designing successful environmental expenditure programs and choosing the right implementing institutions. The European Union (EU) has developed new approaches to environmental policies such as strategic planning, free access to environmental information and subsidiarity. The World Bank has provided strong support for the establishment of the National Environmental Strategies and Action Plans (NEAPs) and accepted NEAPs as a pre-condition for the eligibility of receiving credits.
The second example is the workshop organized by the International Network of Environmental Compliance and Enforcement (INECE). The results of the workshop and the national papers presented have indicated that there is a need for the development of a commonly acceptable and practicable performance measurement system for environmental compliance and enforcement activities (INECE 2003).
Finally, countries all over the world are trying to improve the performance and institutional effectiveness of their SEAs. For instance, China has developed a new environmental performance assessment methodology in collaboration with the World Bank. Similar attempts are being carried out in several other countries ranging from Newly Independent States to Argentina and to Canada (INECE 2003). These initiatives attempt to develop national remedies to local demands for more institutional effectiveness in the SEAs. A recent OECD study has outlined the differing approaches for the improvement of environmental public service delivery capacities of the SEAs. These approaches are ranging from the rigid and hierarchical ones in which the mandates are limited to the establishment of different environmental departments in other ministries to the establishment of inter-ministerial working groups or cabinet-level committees, commissions of enquiry, task forces and to significantly decentralized systems (OECD 2001).
Therefore, a need comes forward: to establish a framework of the basic requirements of an effective SEA. However, assessment and evaluation of the SEAs either at the national or local level has always been difficult and cumbersome due to the complexity of both the issues involved and ability to measure the institutional effectiveness levels. Development of criteria and the establishment of monitoring systems offer potential to solve the problem. Unfortunately, this is not an easy task and the assessment of the effectiveness of the SEAs has not been satisfactorily done. Such an inability, consequently, leads to deficiencies in both diagnosing the ailing components of the system and developing counter measures for the ineffective and inefficient procedures. However, studies done in this regard are rather limited (Clerici and others 2004).
This study aims at bridging the gap between the felt needs and the emerging obstacles in measuring the effectiveness level of national and local SEAs, thus creating a kind of benchmark for the assessment. In this regard, firstly, a list of effectiveness criteria has been developed, and, then, a field study has been carried out to measure the institutional effectiveness of the national and local SEAs in Turkey.

INSERT FIGURE 1

2. Materials and Method

The Delphi technique, (Helmer 1967 a, Helmer 1967 b, Jantsch 1967, 1972, Ament 1973, Enzer 1973, DeLurgio 1998, Martino 1992, Gokhale 2001, Linston and Turoff 2002) being a data collection and forecasting method, aims at removing ambiguity by improving the scientific quality of existing common knowledge through the integration of experts’ ideas. According to some writers (Linstone and Turoff 2002) “Delphi may be characterized as a method for structuring a group communication process so that the process is effective in allowing a group of individuals, as a whole, to deal with a complex problem.” Delphi is the process of constructing reality through the integration of experts’ opinion.
There are 28 panel members in this study, with three of them being international experts working in international organizations (WB, EU and French Water Management Company) and having considerable knowledge about the status of environmental management (EM) in Turkey. The remaining 25 (four university professors, three governors, three sub-governors, two mayors, four provincial directors of Environment, one State Planning Organization -SPO- expert, four NGO directors specialized in environmental matters and four industry managers) are national experts representing the academia and professional fields.
In order to measure the effectiveness of the SEAs, 16 criteria were developed by the author, based upon the analysis made over the SEAs of several countries, which were further broken down into 123 sub-criteria. Questions forming the questionnaire were in the form of stating an idea, opinion or a judgment on the questioned subject, matter, fact or parameter. The same questionnaire was used in all rounds. However, the phrases in the tables below are shortened versions of the statements appearing in the questionnaire. The members of the panel were requested to indicate their decisions by marking an (X) on the most relevant alternative in the list of the answers, ranging from “1-strongly agree” to “5-strongly disagree” (Likert scale), which best reflects the respondent’s opinion and knowledge. In addition, the panel members were asked to state the reasons for their choice. In order to inform the other members, these justifications were conveyed to them in the subsequent rounds, without displaying the name of the respondent. Frequency distributions (FDs), means (Ms), standard deviations (SDs) and members’ opinions were announced in succeeding rounds to other members by the Project Controlling Center. The research was carried on the Internet through e-mails. Three rounds of questions and answers were completed.
It was expected that at the end of each cycle, Ms would approach either side of the scale and SDs (the first standard deviation representing the 68 percent of respondents) would become smaller thus indicating whether or not consensus was achieved amongst the members of the panel with respect to the questioned sub-criterion. Therefore, the computation of the Ms and SDs became vital in understanding and deciding about the level of effectiveness of the sub-criterion. This was followed by the calculation of the mean of the means (MMs) and the mean of the standard deviations (MSDs) for the criteria. Meanwhile, sequence graphs of the Ms and SDs of each round were obtained to observe the changes of the respondents through out the survey and Pearson “r” values were computed for the Ms and SDs of each round to measure the correlation amongst the rounds. Finally, overall MMs and overall MSDs for all 123 questions were calculated to derive a general judgment over the effectiveness of the SEAs in Turkey.
The author predetermined that a negative consensus would be declared for the questioned criterion if 68 per cent of the respondents (first standard deviation) rated the criterion more than the median value (rounded sum of MMs and -/+ MSDs values of the final round is equal to or greater than the median value of 3) and a positive consensus would be declared if the 68 per cent of the respondents rated the criterion less than the median value (rounded sum of MMs and MSDs is less than 3). A non-consensus will be declared if the above-described value were both considerably smaller and bigger than the median value. Therefore, for example, MMs = 4.08 and MSDs = ± 0.79 (3.29-4.87) would be declared as a negative consensus; MMs = 2.05 and MSDs= ± 0.75 (1.30-2.80) would be declared as a positive consensus; MMs = 3.11 and MSD = ± 0.89 (2.22-4.00) would be declared as non-consensus and MMs = 3.60 and MSDs = ± 0.74 (3.60-0.74 = 2.86 ~ 3.0) would also be declared as a negative consensus.

3. Results and Discussion

The criteria of effectiveness and their corresponding sub-criteria are briefly explained below. The results (Ms, SDs and decision) of the survey are also presented in the tables designed for each criterion and sub-criterion. Therefore, the findings of the research for all components of the SEAs are given in the tables.

3.1 Political Will

Existence of political will to assure the right of environment and the sustainable development is necessary for an effective SEA. Furthermore, the right for environment includes three sub-criteria: the right to know, public participation and accessibility to judiciary on environmental matters. The right of environment and sustainability should be regulated in the constitutions or in the main legislation of the country concerned and should also be formulated in national development plans or in the investment plans of local governments. The SEAs should utilize the “State of the Environment Report” system, which is being successfully used by the parliaments in some countries for the justification of budgetary allocations for environmental expenditures. Based upon these facts, the panel members were asked the following questions to assess the willingness at national or local administrative levels for protection of the environment. The Ms and the SDs of the responses are given below in Table 1.

INSERT TABLE 1

The MMs is 3.60 and MSDs is ± 0.79 for 12 questions. Therefore, a negative consensus was achieved on this criterion meaning that political will has not been generated in the country. No positive consensus was encountered for the sub-criteria whereas negative consensus has been achieved over 6 sub-criteria. Consensus was not achieved for the rest of the sub-criteria. The result is discouraging for national environmental will. Local governments’ rating on the issue was even lower than that of the central administration. In this assessment, the expatriate members of the panel were more optimistic than the national members. Among the national experts, those representing industry were more positive than professionals, academicians and NGO representatives. Participation in environmental decision-making and the non-existence of the “State of the Environment Reports” were indicated as the most ailing components of the environmental will in Turkey.

3.2 Environmental Aims and Targets

“Aim” is the idealistic end-point of any process whereas “target” is a tangible, quantifiable, measurable and discrete end-point. Environmental aims are usually determined as planning the risks involved; assessing, managing and enhancing the carrying capacity and improving the quality of life in the area concerned. Integrating environmental and developmental decision making procedures at all levels, preventing environmental pollution and nuisances, prioritizing environmental planning and coordination issues, protecting scarce resources, institutional development of environmental impact assessment and reporting schemes, creating environmental databanks and inventories and establishing administrative focal points are also adopted as the aims of the SEAs in several cases.
However, environmental targets are different than aims. An effective administration should monitor and measure the quality for each environmental medium as well as for each specific area and should set targets to be achieved in a given period. These targets can be stated in the quality standards or in the environmental master plans or in the site-specific or pollution-specific optimization plans.
In addition to the GPRA of the USA, Sweden has adopted a new legislation on “target”- based public environmental management recently, which is comprised of principles, objectives, interim targets, strategies, and follow-up mechanisms. The overall aim of the initiative is to develop efficiency in environmental policies (Edvardsson 2004).
In Turkey, the aims of the SEAs are specified in the laws and regulations. Additionally, some certain standards for emissions and discharges are specified in the legislation.
The questions and the results are given in Table 2.

INSERT TABLE 2

Negative consensus was achieved over this criterion meaning that environmental aims and targets have not been determined satisfactorily. The analysis indicated that while the expatriate members and members representing the industry of the panel are evenly divided into opposing ideas, the other members were quite clear on the insufficiency of the environmental aims and targets. Consensus has not been achieved over the national political will when it has been taken as an individual sub-criterion. Negative consensus has been achieved over the sub-criterion of local governments’ will. Therefore, the situation is worse in local governments compared to central government.

3.3 EM Strategies of the SEAs

EM, which is solely used from the SEAs’ point of view in this research, can be defined as “control in the use of natural resources and the implementation of measures to ensure their conservation, the protection of habitats and the control of hazards” (Markandya and others 2002). EM strategies, as carried out by the national and local SEAs, can be divided into three main categories: command-and-control, voluntary EM and market-based instruments (Smith 2000).
A command-and-control strategy relies on environmental rules, standards and sanctions. A voluntary EM strategy tries to eliminate the sanctions and encourages people to voluntarily share environmental targets. The “ISO 14000 series of International Environmental Management Standards (IEMS),” the “Eco-Management and Auditing Regulation (EMAR)” of the EU, the “President’s Excellence and Leadership Program” and “Common Sense Initiative” of the US EPA and voluntary agreements between industry and the SEAs are the examples of this strategy. Market-based instruments of EM intend to assure the internalization of negative externalities caused by the polluters and thus impose effective financial and economic sanctions on the polluters to correct environmentally inappropriate practices, habits and actions. All of these strategies have somehow found place in Turkey. However, the scope of implementation remains limited when compared to the country’s needs and the status of practice in other countries.
Table 3 gives the questions asked and obtained results.

INSERT TABLE 3

Negative consensus was achieved for this criterion. The results indicate that the SEAs in Turkey have not satisfactorily developed or implemented EM strategies. Negative consensus was achieved on 5 sub-criteria; consensus failed to be obtained on the rest of the sub-criteria. The respondents rate conditions in local governments even less favorably.

3.4 Environmental Policies

Reports of the Organization for Economic Cooperation and Development on Turkey (OECD 1992, 1999) indicate that discrete and material foundations have not been identified in environmental policies. Development plans, the NEAP and the national and local Agenda 21s support this contention. The rhetoric of these documents has not been satisfactorily translated into action. The survey asked panel members several questions pertaining to policies and got the following results.

INSERT TABLE 4

Negative consensus was achieved on the adequacy of environmental policies in Turkey. Out of a total of six criteria having to do with environmental policies, two (activities of the MoEF and the SPO) sub-criteria achieved no consensus while negative consensus was achieved over the rest of the sub-criteria. Local policy development is even less favorable than that at the national level. The merger of the ministries of Environment and Forestry has not changed the pessimistic outlook of the panel members. NGOs were the most critical sub-group for environmental policies of both national and local SEAs.

3.5 Environmental Functions and Procedures

The functions of the SEAs can be technical, administrative, legal, economic or financial in nature. Some functions and procedures should be available to environmental managers and to those who are responsible for compliance management. At a minimum, these functions ought to include the ability to determine the extent of pollution in the environmental media. These include level of emissions, discharges, and dispersion of pollutants, and recording changes over time and space. Standards for measurement, analysis and calibration, as well as appropriate sampling and sound laboratory practices are also crucial. An effective environmental impact assessment and reporting procedure is an essential part of the SEAs. Permit and licensing procedures that can control operations, discharges and emissions should not be ignored. This goes for the development of legal procedures, too. A means through which rule-breakers are prosecuted is also an indispensable part of a workable SEA system. This can include the creation of legal sanctions like fines, imprisonment or partial, total, temporary or permanent closure of plants that are in violation of regulations. Still other functions of the SEAs are the prevention of pollution, risk assessment and reduction, improvement of science for environment, research and technology, provision of environmental education to the masses, regulatory development, enforcement, strategic planning and budgeting, funding, managing human resources, training for environment, information resources management, free public access to information, establishing data networks and sharing the data. The load of external and international relations of the SEAs should not be underestimated. The questions directed to the panel members and the obtained responses with respect to the sufficiency and effectiveness of environmental procedures are given below.

INSERT TABLE 5

Negative consensus (MMs = 3.97 and MSDs ± 0.74) was achieved on national environmental functions and procedures. This results was also confirmed by the answers given to a summary judgment: “The effectiveness and competency levels of the functions and processes … as performed by all responsible ministries, the Ministry of Environment (and Forestry) and “the Specially Protected Areas Administration” and by their field organizations till now since the establishment of these institutions within the context of national SEAs are good and positive.” The M of the answers given to that judgment was 3.79 with a SD of ± 0.74. The proximity of this value to the value of the MMs and MSDs is striking. 22 sub-criteria were measured. Negative consensus was achieved on 20 sub-criteria. No consensus was achieved only on two sub-criteria and there was no positive consensus.

INSERT TABLE 6

Results of the survey on the effectiveness of the local environmental functions and procedures are provided in Table 6. A stronger negative consensus was achieved on local environmental activities. The MMs obtained for this question was 4.08 with a MSDs of ± 0.72. Negative consensus was achieved on all sub-criteria. Again the proximity of the MMs and MSDs to the value of summary judgment should be noted. The summary judgment was as follows: “The effectiveness and competency levels of the functions and processes as listed in the questions … and as performed by the local governments within the context of local SEAs are good and positive.” The M was 4.07 and SD was ± 0.60 for this question. This basically indicates a strong but negative consensus having been achieved amongst the panel members, with the institutional effectiveness of the local governments being graded even less compared to central government.

3. 6 Environmental Criteria and Standards
Environmental standards are the most crucial inputs of a “command-and-control” strategy. What the public cares about and what it wants has to be determined under the given characteristics of the ambient environment. This then must be translated into numerical and tangible values. By enforcing these standards, public agencies will pave the way for better environmental quality and the creation of a more protective shield for groups at risk. Environmental standards have also been promulgated in Turkey. In order to measure their effectiveness and sufficiency, the following questions were asked.

INSERT TABLE 7

The results given in Table 7 indicate that there was no consensus on environmental standards in Turkey (MMs = 3.32, MSDs = ± 0.99) amongst the members of the panel. Likewise, no consensus was achieved on five out of six sub-criteria and only one negative consensus was achieved for the sub-criterion of standardization of standard making. There was no positive consensus for any sub-criterion. However, the inclination towards the ineffectiveness of the environmental standards should be noticed. The cross tabulation analysis showed that the international members of the panel and the members coming from the industry were more satisfied compared to other subgroups. The academicians and the provincial directors of the Ministry of Environment became the most critical subgroups in this category.
3.7 Environmental Planning

Along with the performance management, strategic planning was the most essential component of a management system. Strategic planning requires objectives, targets, strategies, policies, actions, timing and placing for any action in concern. It also requires both internal and external assessment, measurable targets, priority development, internal consensus and an environmental observatory to monitor both the developmental activities and changes in environmental parameters. Furthermore, strategic planning must assess the critical issues involved, such as human resources, financial resources, data resources, strengths and weaknesses, present strategy, organizational structure, organizational culture, opportunities, environmental trends, political economic and social trends, stakeholders, threats, and trends in technology, statutory constraints and public opinion. The planning process begins with preliminary work designed to define regional characteristics. Demographic, geographic, topographic, economic and urban parameters are among the many parameters that must be included. Later, a methodology should be determined for data gathering and retrieval in terms of monitoring networks, minimum data required, data processing and data banks. The obtained data should be analyzed, mean parametric values as well as maximum and minimum values calculated, FDs obtained, trends identified and pollution indices developed. The succeeding stage should be simulation and modeling and developing solution alternatives. An ideal environmental planning process should include the following: determining the status of environment; assessing the availability of natural resources, minerals and human resources in the area; assessing the present pollution loads in the area; developing an integrated environmental planning considering the assimilative and supportive capacities of the environment.
This approach has best been defined by the GPRA of 1993 in the USA. The EPA formulated its own version of environmental planning under the guidance of GPRA and requested the development of “strategic planning,” “goal planning,” “annual performance plans,” “performance results,” “cost accounting” and “the planning, budgeting, analysis and accountability” (PBAA) system from the SEAS.
In Turkey, planning conducted in public agencies mainly consists of land-use schemes and is hierarchical in orientation. The top plan in the hierarchy is the 5-year “development plans” which are conducted by the SPO and based upon the concept of sector planning. The second level is supposed to be the “regional plans” both for land-use and sector development. Institutional responsibility again belongs to the SPO. However, with the exception of Southeastern Anatolia Plan, no such a plan has yet been prepared. The next level is called the “environmental order plan.” The content of this plan is controversial. The Ministry of Public Works (MoPW) looks at this plan as a “land-use plan” whereas the MoEF approaches it in more ‘environmental’ terms. Then there are the urban plans, which are further subdivided into implementation plans. Additionally, such environmental regulations as “Air Quality Protection,” “Water Pollution Prevention,” “Noise Prevention” and “Solid Waste Control” also mention the concept of planning without actually defining and describing the content and the methodology. These environmental plans have never been prepared by any public agency despite the fact that nearly 20 years have passed since the promulgation of these regulations.
The questions prepared under these considerations are seen in Table 8.


INSERT TABLE 8

Negative consensus was achieved over the sufficiency of environmental planning activities in Turkey (MMs = 3.86, MSDs = ± 0.65). Correspondingly, negative consensus was obtained over four out of five sub-criteria. No consensus was achieved over the private environmental auditing companies’ contributions to the solution of industrial environmental problems.

3.8 Institutional Set-up: Old and New Organization Models

EM requires an organization to manage and oversee the environment. However, the task of establishing an effective and efficient SEA necessitates delicate handling of the problem from the perspective of political preferences, interagency relations, funding opportunities, creating and reflecting political will and securing public support. Determining the mission of the organization, defining the major environmental problems that need to be tackled, understanding how these problems are already being taken care of, which existing agencies are assuming responsibility, and the way in which these agencies derive powers; setting up the legal framework, understanding the formal procedure of establishing a new public organization; determining who will make the ultimate decisions; deciding on the format of the agency to be established; and specifying the administrative functions of the new organization as well as the relations between the central government and the local governments will be the main issues to be tackled. As far as interagency relations are concerned, determining the environmental programs in effect and the managing role of existing agencies for them; understanding the strengths and weaknesses of existing interagency relations; and forecasting the need for cooperation are the major issues to be addressed. As far as funding and financing issues are concerned, there are several other concerns that have to be dealt with. These include the determination of priorities, selection of decision-makers, expansion of the role and the share of the private sector, and methods by which money to be spent from the budget is allocated (Ryding 1992). Once decided upon, the internal organizational structure should be established for the operation of core functions such as budgeting, planning, facility management, personnel administration, information management, external affairs, legal counseling and policy development. Additionally, the focal points of each environmental media should be established to set standards, to monitor compliance, to prevent pollution, to assess risks and to take remedial action.
The organizational structure of the Turkish SEAs is given in Figure 1. The system is divided into two main branches: central government agencies (including field organization) and the local governments. In the central government, in addition to the main institution of the MoEF, there are several other ministries taking part in the system. In the MoEF, in addition to the central ministerial organization, a special unit has been formed to manage the Specially Protected Areas. Two funds have been established for both organizations. However, these funds are not operational at the moment. There are two different types of municipalities in the country: the two-tier metropolitan municipalities and the single tier municipalities. The municipalities also have significant responsibilities. The following sub-criteria tried to be measured.

INSERT TABLE 9

Negative consensus was achieved over the effectiveness of the institutional set-up of the SEAs of Turkey at the national and local level (MMs = 3.79, MSDs = ± 0.79). Negative consensus was also achieved on seven out of nine sub-criteria.

INSERT TABLE 10

Turkey has recently witnessed an organizational shake up, mainly upon the advice of the EU experts. Under this reorganization, the ministries of the Environment and Forestry were merged. Through this unification, both the central and the field organization of the both ministries were modified. The panel members were asked to predict the future success of this modification. Negative consensus has been achieved over the chance of success of the new model.

3.9 Legal Infrastructure

An effective SEA requires well-founded legal rules, norms and sanctions. Negative externalities create disputes and result in conflict of interests between rival parties requiring the intervention of impartial judges as well the implementation of sanctions to wrongdoers. The history of legal developments for the protection of the environment is rather long in Turkey. Pertinent legislation goes back to establishment years of the new Republic. In the Code Civil (RoT 1926, 2003) “responsibilities of the owner” and “the rights of neighbors” have been regulated thus paving the way for better environmental relations amongst the private individuals. In the domain of public law, “the Code on Provincial Administration” (RoT 1949), authorized the provincial governors and district sub-governors to act, as they deemed fit to deal with ecological and environmental problems. The Municipal Code (RoT 1930), empowered municipalities to take every possible action to control and upgrade the urban sanitation. Another code dated same year, the Code of Public Health (RoT 1930 a), gave considerable power and authority to protect public health. Several other regulations, which are still in force, were prepared and put into effect based upon two above-mentioned codes regulating the urban sanitation and civic law-and-order.
The 1982 Constitution, a cornerstone in environmental law, specified “the right to healthy and balanced environment” as a human right. With the new constitution, a series of environmental legislation came into effect. Later, Turkey adopted the approach of creating special management zones for some areas having critical ecosystems. “The Decree on Specially Protected Environmental Zones” (RoT 1985) has been put into implementation.
Several regulations have been prepared to manage environmental quality in such areas as air, water, noise and domestic and hazardous solid wastes. Recent legislation on public administration and local government reform increased the role of local governments in environmental matters. New penal code has developed new definitions and sanctions for environmental crimes. Moreover, the courts, including the administrative courts and the Constitutional Court, have made binding decisions on environmental quality, and in the process have interpreted, consolidated and further developed the legal content. Turkey has also become a partner of or signatory to more than 50 multinational agreements on environment.

INSERT TABLE 11

No consensus was achieved on either the criterion of sufficiency of legal powers or the three sub-criteria.

3.10 Institutionalization of Environmental Impact Assessment (EIA)

EIA has become the most effective tool of the SEAs during the last 30 years, especially in the developed world. Principally, EIA requires forecasting and analysis of the potential impacts of any undertaking before the site selection; final commitment of financial resources and final decision over the technical process to be employed for the proposed investment is made (Yasamis 1997). Turkey decided to establish such a system in 1983 with the enactment of the Code of Environment. Though the code states that details would be spelled out in a regulation to be issued within one-year, it took more than ten years for that regulation to be prepared, becoming effective only as of January 1st, 1994. Since then, the regulation has gone through three major modifications. The sites and projects subject to EIA have been delineated on two different lists. The first list, called “full-EIA,” requires EIA for important and large-scale projects and infrastructures. The second list, called “preliminary-EIA,” identifies the small projects subject to EIA. Management responsibility of both lists belongs to the MoEF now. However, the management responsibility for the second list has been delegated to governors. The panel members were asked the questions with answers statistically evaluated and summarized in Table 12.

INSERT TABLE 12

No consensus was achieved on either the criterion of effectiveness of EIA or two sub-criteria related to full-EIA and preliminary-EIA.

3.11 Technical Infrastructure

An effective SEA requires expensive and sophisticated technical equipment to monitor, diagnose and understand the environmental phenomena over time and space. Furthermore, pollution and wastes needs to be treated and disposed of safely. Although there are some hopeful indications of new investments in this regard, such as the construction of wastewater treatment plants in bigger cities, so far only 20 per cent of the urban wastewater is being treated and only less than three per cent of the municipalities have sanitary and secure landfills and disposal systems for solid wastes.


INSERT TABLE 13

Negative consensus was achieved on (MMs = 4.31, MSDs = ± 0.63) the criterion of sufficiency of infrastructure and the four sub-criteria as indicated in Table 13.

3.12 Market-Based Instruments

The market-type financial end economic tools are being applied more globally. Although there are some “quasi” economic tools of EM in Turkey, they have not gained considerable momentum. The wielding of economic and financial tools ought to have the effect of changing the unacceptable behavior of polluters. For this to work, however, the tax rate should be at least equal to the marginal cost of abatement, treatment or disposal. The concept of marketable pollution quota has not yet been introduced. Deposit and refunding systems exists but are not effective. Developmental subsidies are predominant. Environmental subsidies have also been introduced into the national subsidy scheme recently. Environmental funds are neither sufficient nor used rationally and sensibly. Waste markets have not yet been established. Waste collection systems similar to “green points” are only exemplary in nature but not effective or widespread. Environmental accounting principles have not yet introduced at either the macro or micro level. Neither is there an environmental risk insurance system set up at the moment. Consequently, the development of financial and economic tools of EM should be one of the most important priorities in Turkey. Having them would allow for more effective EM in the upcoming years.

INSERT TABLE 14

The adequacy of economic and financial tools in Turkey with the exception of effectiveness of pollution emission charges/fees sub-criteria was another area of the survey in which the panel members achieved negative consensus (MMs = 4.17, MSDs = ± 0.68).

3.13 Environmental Education and Human Resources Management
An effective SEA should aim at changing the people’s environmentally undesirable mode of behaviors towards environment through enlightening and informing the people on the environmental matters, developing expertise and know-how on environmental technology and training professionals for future employment opportunities. Since environmental management is a composite discipline combining branches of science, it requires a well-balanced and well-designed manpower planning.

INSERT TABLE 15

Another negative consensus was achieved on the criterion of sufficiency and effectiveness of the environmental training and human resources management for environment in Turkey. Negative consensus also was achieved on all of the six related sub-criteria.
3.14 Management Concepts
The very last criterion in the checklist is devoted to the science of management. Contemporary management science is basically related to the concept of “target.” The overall philosophy of today’s management understanding concentrates mainly on the “results achieved.” The mutual relation between the science of environment and the science of management is very strong and both have a strong common denominator: “target”. Management tries to realize set targets. Through monitoring, environmental management information systems and appraisal components it intends to take corrective actions as a continuous and iterative cycle. In this regard, the SEAs should set future environmental quality targets by developing programs and action plans to realize the desired and intended outcomes. This approach has been realized as a major management reform in the US by the introduction of GPRA, which requires strategic plans, performance plans, and annual performance reports.
In Turkey, however, under the obtained results of the panel, it is not possible to say that such an understanding of management is prevalent at the SEAs. The results are given in Table 16.

INSERT TABLE 16

The panel members achieved a strong consensus on the non-existence of modern management techniques in the environmental enforcement and compliance management institutions at both national and local levels.

4. Findings

The findings of the research for all sub-criteria are provided in the tables above. An overall summary of the survey (MMs and SDs for each criteria) is also given in Table 17. Thus, the effectiveness of each sub-criterion was decided. This was followed by the decisions for every criterion on the list. Finally, the overall effectiveness of the SEAs was determined.

INSERT TABLE 17

To sum:
1. None of the measured criteria or sub-criteria obtained positive consensus. The panel members achieved negative consensus on 13 out of 16 criteria and on 95 sub-criteria out of total of 123. Only on three criteria (environmental standards, legal powers and the EIA system) was no consensus at all achieved. Therefore, results indicate a firm negative evaluation of the institutional effectiveness of the SEAs in Turkey. This basic fact indicates a need for a radical shake-up of the existing mode of practices of the SEAs at national and even more, at the local levels. This finding is line with other studies on the issue. A recent study (Sezer and others 2003) concluded that limited financial input is not the sole reason for the ineffectiveness of the SEAs. On the contrary, it found that the main reason was related to weak capabilities of policy implementation and enforcement in Turkey.
2. The opinion of the experts on the overall effectiveness of the SEAs is negative. Also in the three successive rounds of expert views showed a tendency towards consensus. The overall MMs of 123 questions was 3.42 in the first round, which became 3.87 in the second round and 3.85 in the final round. Therefore, negative perceptions increased amongst the members of the panel as the rounds proceeded. The calculated MMs of 3.85 in the final round is rather remarkable and points to an overall dissatisfaction of the experts with the system. The sequence graph of Ms of each question is given below. The discrepancy between the first round and the subsequent second and third round is clear.

INSERT FIGURE 2

3. The MSDs narrowed down from 1.07 in the first round to 0.91 in the second round and to 0.78 in the final round. This reduction is a statistically important finding of the survey and proves the dependability of the Delphi technique in creating a consensus over such confused and vague issues as judging environmental success in a country. The sequence graph of the SDs of each round is given in Figure 3. Again the discrepancy between the first and the subsequent rounds is easily visible.

INSERT FIGURE 3

The correlation tables of the Ms and SDs are given in Table 18 below. The correlation of Ms of each round with other rounds was found to be significant at the 0.01 level, which indicates the consistency amongst the rounds. The correlation of SDs between the second and the third round was found to be significant at the 0.01 level, which indicates the consistency between these two rounds.

INSERT TABLE 18


5. Conclusions and Recommendation

Two important conclusions are drawn from the survey.

1. The results given above support the hypothesis of the research: through the developed checklist and the Delphi technique it is possible to assess the effectiveness of the SEAs at national and local level.

2. Analysis of answers helps to diagnose the ineffective, inefficient and ailing components of the existing system at the criteria (13 out of 16) and sub-criteria levels (95 out of 123) thus paving the way to plan and implement the corrective actions to be taken for a better performance in the future. This also proves that such an approach can be used in places where detailed appraisal is not easy due to the lack of data and information.
The realization of an effective SEA either at the national and local level is a complicated and difficult job. Even so, countries are still attempting to establish environmental bodies. A dependable, well-structured and scientifically proven approach can help these countries in their struggle to increase the institutional effectiveness of national and local SEAs.
Despite the growing number of the SEAs and inherent difficulties in establishing such an organization, technical consultancy and guidance provided to them so far remained limited, and unsatisfactory in many countries. An attempt has been made in this paper to fill this gap. The above given results of the survey indicate that the survey have achieved its objectives. It is shown that the assessment of the effectiveness of the SEAs through the Delphi technique is possible.
Therefore, it is recommended that the method and the checklist developed in this survey can be used for similar purposes elsewhere.
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Yasamis, F. D. 1997. Environmental impact assessment. Ankara, 336 pp. In Turkish.










FIGURE 1
THE SEAs IN TURKEY
LOCAL GOVERNMENTS
CENTRAL GOVERNMENT
Greater Municipality/Mayor
Municipality/Mayor
Provincial Special Administration
/Governor/Elected Members
Village/Headman
CENTRAL ORGANIZATION
FIELD ORGANIZATION
Ministry of Environment and Forestry
Other ministries/SPO
Specially Protected Areas Administration
Fund: Environmental Protection
Fund: Specially Protected Areas
Provincial Governor

Provincial Director

District Sub-governor

District Director
Provincial Foundation of Environment/Governor
Higher Council of Environment

Council
of Environment
Provincial Local Council of Environment / Governor

























FIGURE 2
MEANS IN ALL ROUNDS












FIGURE 3
SD VALUES IN ALL ROUNDS












TABLE 1
EXISTENCE OF NATIONAL AND LOCAL WILL
SUBCRITERIA
M
SD
CONSENSUS
1. Political will in Turkey at the national level
3.57
0.79
NEGATIVE
2. Political will in Turkey at the local government level
3.82
0.67
NEGATIVE
3. “The Right of Environment”-central government
3.46
0.84
NONE
4. “The Right of Environment”-local government
3.79
0.50
NEGATIVE
5. Participation in the central government
4.14
0.59
NEGATIVE
6. Participation in the local government
4.04
0.58
NEGATIVE
7. Accessibility to judiciary
3.36
0.78
NONE
8. The Turkish Constitution and the “Sustainable development principle”
3.46
1.07
NONE
9. “Sustainable development principle” and the basic legislation
3.11
1.13
NONE
10. “Sustainable development principle” and National Development Plans and the annual investment programs
3.11
1.07
NONE
11. “Sustainable development principle” and the “National Environmental Strategies and Action Plan”
2.71
0.98
NONE
12. Existence of “State of the Environment Reports”
4.64
0.49
NEGATIVE
Overall
3.60
0.79
NEGATIVE













TABLE 2
SETTING ENVIRONMENTAL AIMS AND TARGETS
SUBCRITERIA
M
SD
CONSENSUS
1. Development of “aims” and “objectives/targets” of national environment management
3.61
0.96
NONE
2. Development of “aims” and “objectives/targets” of local environment management
4.00
0.54
NEGATIVE
Overall
3.81
0.75
NEGATIVE




















TABLE 3
DEVELOPMENT AND IMPLEMENTATION OF ENVIRONMENTAL STRATEGIES
SUBCRITERIA
M
SD
CONSENSUS
1. Sufficiency of “the command and control strategy” by the central government and by its field organizations
3.89
0.63
NEGATIVE
2. Sufficiency of “the command and control strategy” by the local governments
4.07
0.60
NEGATIVE
3. Adequacy of “voluntary compliance strategy”
4.29
0.85
NEGATIVE
4. Effectiveness of “ISO 14001” system
3.46
0.88
NONE
5. Effectiveness of “the market-based instruments of EM”
4.36
0.56
NEGATIVE
6. Success of the central government in developing and implementing strategies
3.43
1.00
NONE
7. Chance of success of the recently formed “The Ministry of Environment and Forestry”
3.50
1.07
NONE
8. Success of the local governments in developing and implementing strategies
4.18
0.55
NEGATIVE
Overall
3.90
0.77
NEGATIVE






















TABLE 4
ADEQUACY OF ENVIRONMENTAL POLICIES
SUBCRITERIA
M
SD
CONSENSUS
1. Success of MoE in developing national environment policies
3.21
0.92
NONE
2. Success of the State Planning Organization in developing environmental policies
3.54
0.96
NONE
3. Success of “The Administration of Specially Protected Areas” in developing policies
3.64
0.78
NEGATIVE
4. Success of the Central Government’s “High Environment Committee” in developing policies
4.18
0.72
NEGATIVE
5. Success of the local governments in developing local environmental policies
4.18
0.61
NEGATIVE
6. Chance of success of the new model of “the Ministry of Environment and Forestry”
3.79
0.79
NEGATIVE
Overall
3.76
0.80
NEGATIVE























TABLE 5
SUCCESS IN CENTRAL ENVIRONMENTAL
FUNCTIONS AND PROCEDURES
SUBCRITERIA
M
SD
CONSENSUS
1. Determining pollution
3.86
0.80
NEGATIVE
2. Measuring the environment quality of environmental media, emissions and discharges of pollutants and spatial and temporal diffusion patterns of the pollutants
3.82
0.61
NEGATIVE
3. Developing standards for monitoring, measurement, sampling, analyzing, calibration and good laboratory practices
3.75
0.65
NEGATIVE
4. Effective implementation of “permitting” and “licensing” systems/procedures for work place operations and for the emissions and discharges of the pollutants and the wastes
3.64
0.78
NEGATIVE
5. Prevention of pollution
3.93
0.60
NEGATIVE
6. Environmental risk assessment, planning, management and reduction activities
4.00
0.72
NEGATIVE
7. Scientific researches and technology development studies for environment
4.04
0.84
NEGATIVE
8. Insuring sufficient budget and financial resources for environmental activities
4.32
0.61
NEGATIVE
9. Managing environmental funds in a way that contributes to environmental protection activities
4.50
0.84
NEGATIVE
10. Establishing human resources planning and management system for environment
4.18
0.55
NEGATIVE
11. Fulfilling the international obligations and responsibilities on environment
3.39
0.79
NONE
12. Environmentally sound land use planning
4.04
0.64
NEGATIVE
13. Establishing economic incentive schemes for environmental protection and enhancement
4.36
0.56
NEGATIVE
14. Establishing measurement and monitoring systems
3.96
0.58
NEGATIVE
15. Providing clean-fuel and raw materials to producers to protect the environment
3.93
0.86
NEGATIVE
16. Establishing environmental insurance system against the environmental risks and accidents
4.36
0.87
NEGATIVE
17. Abating/combating/cleaning up the pollutions
3.93
0.86
NEGATIVE
18. Establishing wastewater treatment facilities is good and positive
3.71
0.81
NEGATIVE
19. Establishing secure land filling and disposal sites for solid wastes
4.00
0.67
NEGATIVE
20. Establishing re-cycling and re-use facilities for recoverable solid wastes
4.11
0.88
NEGATIVE
21. Taking precautions/measures against noise
4.00
0.86
NEGATIVE
22. Taking precautions/measures against air pollution
3.54
1.00
NONE
Overall
3.97
0.74
NEGATIVE


















TABLE 6
SUCCESS IN LOCAL ENVIRONMENTAL FUNCTIONS AND PROCEDURES
SUBCRITERIA
M
SD
CONSENSUS
1. Determining pollution
4.11
0.74
NEGATIVE
2. Measuring the environment quality of environmental media, emissions and discharges of pollutants and spatial and temporal diffusion patterns of the pollutants
4.11
0.79
NEGATIVE
3. Developing standards for monitoring, measurement, sampling, analyzing, calibration and good laboratory practices
4.11
0.74
NEGATIVE
4. Effective implementation of “permitting” and “licensing” systems/procedures for work place operations and for the emissions and discharges of the pollutants and the wastes
3.93
0.54
NEGATIVE
5. Prevention of pollution
4.11
0.69
NEGATIVE
6. Environmental risk assessment, planning, management and reduction activities
4.25
0.70
NEGATIVE
7. Scientific researches and technology development studies for environment
4.29
0.76
NEGATIVE
8. Insuring sufficient budget and financial resources for environmental activities
4.25
0.70
NEGATIVE
9. Managing environmental funds in a way that contributes to environmental protection activities
4.43
0.69
NEGATIVE
10. Establishing human resources planning and management system for environment
4.32
0.55
NEGATIVE
11. Fulfilling the international obligations and responsibilities on environment
4.18
0.90
NEGATIVE
12. Environmentally sound land use planning
4.00
0.54
NEGATIVE
13. Establishing economic incentive scheme for environmental protection and enhancement
4.36
0.68
NEGATIVE
14. Establishing measurement and monitoring systems
3.96
0.74
NEGATIVE
15. Providing clean-fuel and raw materials to producers to protect the environment
3.86
0.89
NEGATIVE
16. Establishing environmental insurance system against the environmental risks and accidents
4.21
0.88
NEGATIVE
17. Abating/combating/cleaning up the pollutions
3.86
0.80
NEGATIVE
18. Establishing wastewater treatment facilities is good and positive
3.68
0.61
NEGATIVE
19. Establishing secure land filling and disposal sites for solid wastes
3.79
0.79
NEGATIVE
20. Establishing re-cycling and re-use facilities for recoverable solid wastes
4.11
0.79
NEGATIVE
21. Taking precautions/measures against noise
4.11
0.57
NEGATIVE
22. Taking precautions/measures against air pollution
3.79
0.79
NEGATIVE
Overall
4.08
0.72
NEGATIVE















TABLE 7
SUFFICIENCY OF ENVIRONMENTAL STANDARDS
SUBCRITERIA
M
SD
CONSENSUS
1. Suitability and sufficiency of the ambient environment quality standards
3.07
1.21
NONE
2. Suitability and sufficiency of the standards for polluted air emission and wastewater discharges
2.96
1.17
NONE
3. Suitability and sufficiency of the standards relating to production materials/inputs
3.43
0.69
NONE
4. Suitability and sufficiency of the fuel standards
3.11
0.99
NONE
5. Suitability and sufficiency of the implementation status and conditions of ISO 14000 series “International Environment Management Standards”
3.39
0.92
NONE
6. Standardization of environmental standard making procedures
3.93
0.98
NEGATIVE
Overall
3.32
0.99
NONE





















TABLE 8
SUCCESS IN ENVIRONMENTAL PLANNING
SUBCRITERIA
M
SD
CONSENSUS
1. The national environmental planning activities
4.11
0.57
NEGATIVE
2. The local environmental planning activities
4.25
0.59
NEGATIVE
3. Satisfaction over “The National Agenda 21” of Turkey
3.68
0.61
NEGATIVE
4. Success of the activities in relation to “The Local Agenda 21”
3.71
0.66
NEGATIVE
5. Satisfaction over the private environmental auditing companies’ contributions to the solution of industrial environmental problems
3.57
0.84
NONE
Overall
3.86
0.65
NEGATIVE
























TABLE 9
EFFECTIVENESS OF INSTITUTIONAL SET-UP
SUBCRITERIA
M
SD
CONSENSUS
1. Organizational success and effectiveness of “the Turkish Ministry of Environment”
3.86
0.93
NEGATIVE
2. Success of the “Environment Protection Fund”
4.11
0.69
NEGATIVE
3. Organizational success and effectiveness of the Administration of Specially Protected Areas
3.43
0.69
NONE
4. Success of “The Fund of Specially Protected Areas”
3.68
0.61
NEGATIVE
5. Organizational success and management effectiveness of “the Provincial Environment Directorates”
3.75
0.70
NEGATIVE
6. Organizational success and management effectiveness of” the Provincial Environment Foundations”
3.96
0.92
NEGATIVE
7. Lack of environmental organization at the sub-provincial level
3.82
1.36
NONE
8. Success of “The Local Environment Committees”
3.61
0.69
NEGATIVE
9. Organizational success and management effectiveness of “the Greater Municipalities and Municipalities”
3.93
0.54
NEGATIVE
Overall
3.79
0.79
NEGATIVE











TABLE 10
OPTIMISM ABOUT THE NEW ORGANIZATIONAL MODEL
SUBCRITERIA
M
SD
CONSENSUS
1. Appropriateness of merging the Ministry of Forestry and the Ministry of Environment
3.96
1.07
NEGATIVE
2. Chance of success of the new model in future
3.89
0.88
NEGATIVE
3. Chance of success of the new field organization model (the Provincial Directorate of Environment and Forestry)
3.86
0.93
NEGATIVE
Overall
3.90
0.96
NEGATIVE




















TABLE 11
ADEQUACY OF LEGAL POWERS AND AUTHORITIES
SUBCRITERIA
M
SD
CONSENSUS
1. Sufficiency of legal powers/authorities
3.32
1.02
NONE
2. Effectiveness of environmental penalties/sanctions
3.18
1.16
NONE
3. Lack of environmental police
3.50
1.20
NONE
Overall
3.33
1.13
NONE






















TABLE 12
SUCCESS OF EIA
SUBCRITERIA
M
SD
CONSENSUS
1. Effectiveness of the Environmental Impact Assessment practices of the central government
3.43
1.00
NONE
2. Effectiveness of the preliminary environmental impact assessment practices of provincial governorates and the Local Environment Committees
3.32
0.90
NONE
Overall
3.38
0.95
NONE
























TABLE 13
ADEQUACY OF ENVIRONMENTAL INFRASTRUCTURE
SUBCRITERIA
M
SD
CONSENSUS
1. Adequacy of urban and industrial wastewater treatment centers
4.39
0.57
NEGATIVE
2. Effectiveness and adequacy of air quality monitoring systems
4.18
0.77
NEGATIVE
3. Adequacy of sanitary/secure solid waste disposal/land filling sites and solid waste recycling facilities
4.61
0.50
NEGATIVE
4. Adequacy of environmental analysis laboratories
4.07
0.66
NEGATIVE
Overall
4.31
0.63
NEGATIVE
























TABLE 14

EFFECTIVENESS OF MARKET BASED TOOLS
SUBCRITERIA
M
SD
CONSENSUS
1. Effectiveness of environmental tax system
4.64
0.62
NEGATIVE
2. Effectiveness pollution emission charges/fees, wastewater discharge charges/fees and user charges/fees systems
3.57
1.03
NONE
3. Effectiveness of indirect environmental taxes on changing consumers’ environmentally negative behaviors in a way that contributes the protection of environmental quality
3.89
0.79
NEGATIVE
4. Development of marketable pollution quota system
4.50
0.64
NEGATIVE
5. Success of the “deposit fee” and “quota”
4.00
0.72
NEGATIVE
6. Success of the system of waste markets
4.00
0.72
NEGATIVE
7. Success of the Green Point system
4.11
0.57
NEGATIVE
8. Success of the environmental accounting system
4.50
0.51
NEGATIVE
9. Effectiveness of the environmental insurance system
4.36
0.49
NEGATIVE
Overall
4.17
0.68
NEGATIVE























TABLE 15
EFFECTIVENESS OF EDUCATION FOR ENVIRONMENT
AND HUMAN RESOURCES MANAGEMENT
SUBCRITERIA
M
SD
CONSENSUS
1. Effectiveness of formal education institutions
4.14
0.36
NEGATIVE
2. Effectiveness of the education for environment given by the higher education institutions
4.11
0.50
NEGATIVE
3. Effectiveness of informal education institutions
4.36
0.56
NEGATIVE
4. Sufficiency of professional training programs.
3.86
0.65
NEGATIVE
5. Sufficiency of in-service training provided by the Ministry of Environment for the employees
3.89
0.74
NEGATIVE
6. Effectiveness of the human resources management
4.21
0.57
NEGATIVE
Overall
4.10
0.56
NEGATIVE














TABLE 16
EFFECTIVENESS OF MODERN
MANAGEMENT TECHNIQUES IN THE SEAs
SUBCRITERIA
M
SD
CONSENSUS
1. Effectiveness of the contemporary management methods and techniques at the national SEAs
4.07
0.60
NEGATIVE
2. Effectiveness of the contemporary management methods and techniques at the local SEAs
4.43
0.57
NEGATIVE
Overall
4.25
0.59
NEGATIVE

















TABLE 17

SUMMARY OF SURVEY RESULTS
CRITERIA
MMs
MSDs
CONSENSUS
NATIONAL AND LOCAL WILL
3.60
0.79
NEGATIVE
ENVIRONMENTAL AIMS AND OBJECTIVES
3.81
0.75
NEGATIVE
ENVIRONMENTAL STRATEGIES
3.90
0.77
NEGATIVE
ENVIRONMENTAL POLICIES
3.76
0.80
NEGATIVE
CENTRAL ENVIRONMENTAL FUNCTIONS AND PROCEDURES
3.97
0.74
NEGATIVE
LOCAL ENVIRONMENTAL FUNCTIONS AND PROCEDURES
4.08
0.72
NEGATIVE
ENVIRONMENTAL STANDARDS
3.32
0.99
NONE
ENVIRONMENTAL PLANNING
3.86
0.65
NEGATIVE
INSTITUTIONAL SET-UP
3.79
0.79
NEGATIVE
NEW ORGANIZATIONS
3.90
0.96
NEGATIVE
LEGAL POWERS AND AUTHORITIES
3.33
1.13
NONE
ENVIRONMENTAL IMPACT ASSESSMENT
3.38
0.95
NONE
ENVIRONMENTAL INFRASTRUCTURE
4.31
0.63
NEGATIVE
ECONOMIC AND FINANCIAL TOOLS
4.17
0.68
NEGATIVE
ENVIRONMENTAL EDUCATION AND HRM
4.10
0.56
NEGATIVE
MODERN MANAGEMENT TECHNIQUES
4.25
0.59
NEGATIVE
OVERALL
3.85
0.78
NEGATIVE
























TABLE 18

MEANS AND STANDARD
DEVIATIONS
CORRELATION OF EACH ROUND

MEANS
STANDARD
DEVIATIONS
R1
R2
R3
R1
R2
R3





ROUNDS

R1
Pearson Correlation
1.000
.496*
.490*
1.000
.056
.112
Sig. (2-tailed)
.
.000
.000
.
.539
.216
N
123
123
123
123
123
123

R2
Pearson Correlation
.496*
1.000
.917*
.056
1.000
.780*
Sig. (2-tailed)
.000
.
.000
.539
.
.000
N
123
123
123
123
123
123

R3

Pearson Correlation
.490*
.917*
1.000
.112
.780*
1.000
Sig. (2-tailed)
.000
.000
.
.216
.000
.
N
123
123
123
123
123
123














* Correlation is significant at the 0.01 level (2-tailed).