1732 __ ~~~~voL4 4 ......... R t ., X ~\ r_ M Ls t ' ~~~~~~~~ Japan's Experience in Urban Environmental Management Yokohama A Case Study Metropolitan Environmental .4W Improvement M E I P Program April 1996 Table of Contents Page Table of Contents iii Foreword v Executive Summary vii Chapter 1: Profile of the City of Yokohama 1 The City ofYokohama 1 History of the City 4 Chapter 2: Environmental Protection Measures inYokohama 11 Environmental Pollution inYokohama 11 Environmental Protection Measures inYokohama 15 Organization of Environmental Protection inYokohama City 24 Chapter 3: Key Environmental Conservation Measures, and Organization inYokohama 29 Pollution Control Agreements 29 Kanazawa Reclamation Project and Industrial Relocation 37 Relationships Between Environment and the Economy inYokohama 45 Chapter 4: Environmental Protection Measures in the Private Sector 51 Power Generation: Coal-Fired Electric Power plant 51 Chemical Industry 52 Food Processing Company 56 Small and Medium-sized Electronics Parts Manufacture 60 Chapter 5: Summary And Conclusion 63 Evaluation of Environmental Protection Measures inYokohama 63 Conclusion on Environmental Protection Measures inYokohama 67 Annexes 69 Annexl: Yokohama Automobile Pollution Control Program 70 Annex 2: Changes of Pollution Control Agreement between Yokohama City and Isogo Thermal Electric Power Plant, Electric Development Inc. (Major contents of the agreements) 72 Table of Contents iii Foreword I _ _ d _ d _ munity environmental actions, and links these MEIP: the Context for the Study growing environmental network efforts with gov- MEIP: tlhe Context for the Study ernment policy and investment initiatives. The UNDP-assisted, World Bank-executed Metro- politan Environmental Improvement Program A further focus of MEIP is the exchange of ex- (MEIP) began work in 1990 in five Asian metropoli- perience and sharing of information among MEIP tan areas-Beijing, Bombay, Colombo, Jakarta, and cities. This has been carried out through a series of Metro Manila. In 1993, this intercountry program intercountry workshops that review the city work began its second phase and Kathmandu joined as programs, exchange useful experience, and develop the sixth MEIP city. By 1996, MEIP will enter its third intercountry projects. phase -with multi-donor assistance - and launch new programs in additional Asian cities. MEIP has established the city programs, set in motion a variety of city subprojects, and mobilized MEIP's mission is to assist Asian urban areas the intercountry exchange. MEIP publications are tackle their rapidly growing environmental prob- intended to share insights and experiences devel- lems. The MEIP approach emphasizes the oped from the MEIP process and its projects. The cross-sectoral nature of these problems and the fail- MEIP city programs work independently, with each ure of traditional, sectoral development strategies other, and with international partners to reverse to adequately address urban environmental dete- urban environmental degradation and provide use- rioration or the linkage between industrial and ur- ful and replicable lessons in urban environmental ban development. management. The work program in each city is therefore guided by Steering Committees and technical work- MEIP and Urban ing groups that reflect the cross-sectoral, interagency Envirotmental Management nature of urban environmental issues. The policy ,,, . , a v and technical committees develop Environmerntal Experience i Japan Management Strategies (EMS) for their metropoli- To assist developing countries strengthening insti- tan regions; incorporate environmental consider- tutional capacity to control pollution and manage ations into the work of economic and planning environmental resources, learning from countries agencies; contribute to the strengthening of envi- and cities that have experienced similar problems is ronmental protection institutions, and identify high a particularly effective tool. priority environmental investments. Japan has had a large measure of success in The MEIP city office serves as secretariat to the dealing with environmental problems associated Steering Committee and is managed by a local en- with rapid industrialization and urbanization. As a vironmental professional, the National Program developed country in Asia, its urban environmental Coordinator (NPC) . The NPC coordinates all MEIP management history affords an excellent opportu- activities and is responsible for developing the en- nity to derive lessons and case studies. vironmental network of government, private sec- tor, non-governmental organizations (NGOs), re- This city case study of Yokohama is a compan- search institutions, and communities. MEIP sup- ion piece and source document for the MEIP na- ports workshops, demonstration projects, and com- tional study on Japan. In addition to the city reports Foreword v on Kitakyushu and Osaka, MEIP has published a On behalf of the MEIP team, I would like to ex- national report entitled, "Japan's Experience in Ur- press appreciation to Shunsuke Aoyama and his col- ban Environmental Management." leagues at EX Corporation for their superb efforts in conducting the study. We are especially grateful to the The studies undertake a detailed review of report's principal authors: Shunsuke Aoyoma, Jeremy Japan's experience in urban environmental protec- J.Warford, Kiichiro Sakaguchi, Nahoko Nakazawa, and tion and clean-up. The focus was to elaborate expe- Hiroshi Naito for their exactingwork and careful analy- riences of particular relevance to MEIP cities, and sis. Profound thanks are due to Professor Michio to other cities in Asia and elsewhere in the devel- Hashimoto, Chairman, and to the other members of oping world. the Central Steering Committee, and to Professor K. Saruta, Chairman, and other members of the Some useful conclusions concerning the appli- Yokohama Committee. Finally, we are indebted to the cability of Japan's experience for developing coun- Government of Japan for the support that enabled us tries can be drawn. The studies demonstrate that, to undertake this project and to the unflagging efforts while much of the technology and present manage- of Kazuhiko Takemoto of the Japan Environment ment practice may not be easily transferable, the way Agency and of Katsunori Suzuki, our colleague at in which Japan tackled pressing environmental MEIP-World Bank. problems during the 1960s and 70s is directly rel- evant to the environmental management challenge David G. Williams facing MEIP cities. Program Manager vi Metropolitan Environmental Improvement Program Executive Summary from large factories in the existing coastal indus- Summary of Environmental trial area. Furthermore, it was at that time predicted Protection Measures in that large factories in the new coastal industrial area would discharge the same volume of SOx as in the Yokohama existing coastal industrial area. However, not hav- The City of Yokohama had been a center of trade in ing authority to control pollution directly, the City Japan from the opening of the port in 1859 through of Yokohama only conducted SOx monitoring, and World War II, and an essential part of the Keihin dealt with grievances on a case-by-case basis. Industrial Area. During the post-war period, how- ever, the citywas taken over by US occupation forces Under these circumstances, in 1963, the and financial difficulties were severe. Since the city's Asukata municipal administration came into power, reputation as a center of trade was ruined, major with campaign pledges to improve the quality of industries in commerce, trade, and finance had left life of the citizenry, and to enlist citizens'participa- the city for other areas, primarilyTokyo. In 1951 the tion in city govemrnment. It largely modified the old city introduced methods to attract new factories to policy of Yokohama, which had given major priority the area and a new strategy to promote industrial to creation of industrial infrastructure. With respect development through projects such as the indus- to pollution control measures, the city's own pollu- trial zones in reclaimed coastal areas and investment tion control agreements, which later came to be in infrastructure. called the"Yokohama style", prevented pollution in the new industrial area, and controlled pollution in The population of Yokohama was 620,000 imme- the existing industrial area. Municipal govemments diately after WWII. By the first half of the 1950s, the had no legal authority over pollution control at the city's population, at more than a million, exceeded the time. Under the agreements, the City of Yokohama pre-war level. The downtown area developed in an obtained, based on mutual consultation, pledges unplanned manner, and reconstruction of the old from business enterprises to implement pollution coastal industrial area of the pre-war period was the control measures. Pollution control agreements were means of facilitating industrial and economic revital- also adopted in the existing industrial area. Since ization. In the late 1950s, Japan embarked upon its the latter half of 1970s, the guidelines were also used period of rapid economic growth. Concentration of to generalize the environmental pollution control population and industry inTokyo convertedYokohama agreements. into a dormitory town for Tokyo. The population of Yokohama increased by 100,000 per annum in the Strict controls enforced for large-scale compa- period after 1960.The rapid increase in population and nies under the environmental pollution control industrial activities caused an expansion of the urban agreements were effective since these companies district and haphazard land use. It led to a "dough- possessed enough technological and economic ca- nut"phenomenon in the downtown area and subur- pacity to respond to the measures. On the other ban sprawl. Results included industrial pollution and hand, measures applied to small and medium-sized shortages in public facilities, such as schools, hospi- factories, which were scattered throughout the city, tals, and sewerage. were difficult to enforce, and their implementation lagged behind. Therefore, during the 1980s, In the mid-1960s, about 90% of SOx (a major Yokohama started to relocate these factories to the element of air pollution) in the city was discharged Kanazawa Industrial Complex. Taking advantage of Executive Summary vii factory relocation, the city was able to control pol- lution, rehabilitate and modernize the downtown Evaluation of Environmental area, and rationalize management of the factories . M by promoting collective and cooperative actions and strengthening managerial capacity. Yokohama In this section, we evaluate the environmental pro- In order to control industrial pollution dur- tection measures in Yokohama such as the pollu- ing the high economic growth period, the city tion control agreements and the Kanazawa recla- took a series of measures such as the environ- mation project described in Chapter Three. mental pollution control agreements, various guicdelines, and relocation and cooperative ac- Pollution Control Agreements tions with small and medium-sized factories. These measures were successful and largely im- Overall evaluation The first pollution control proved conventional industrial pollution. agreements inYokolhiama were conceived by an au- tonomous effort of the city during the mid-1960s However, from the 1980s, the focus shifted from when local governments did not have any legal au- industrial pollution to the newer issues of pollution thority over pollution control. Under the agree- related to daily urban living such as that caused by ments, the city obtained, based on mutual consul- automobile traffic, domestic waste water, and neigh- tation, pledges from business enterprises to imple- borhood noise. Yokohama recognized that it was ment pollution control measures. The city took the time to shift its emphasis from exclusive concern initiative in undertaking preventive pollution con- with industrial pollution, and that it was necessary trol measures with the support of citizens' move- to establish the "Yokohama Environmental Basic ments, while allowing companies to establish their Charter"in order to protect and create a good city factories on a selected basis. TheYokohama pollu- environment. The city designed the environmental tion control agreement was different from the fol- management plan (Environmental Plan 21) in 1986 lowing two types of pollution control measures, one to realize the Basic Charter. It was recognized that taken in Yokkaichi and the other in Mishima- it was necessary not only to control industrial pol- Numazu. In the case ofYokkaichi, pollution control lution as in the past, but also to implement a com- measures were pursued only after companies had prehensive and well-planned environmental ad- established their factories and started causing pol- ministration for pollution prevention and creation lution. In the case of Mishima-Numazu, the resi- of a better living environment. This plan became the dents rejected the siting of planned plants by orga- foundation of the new environmental administra- nizing a strong residents' movement. For this rea- tion. son theYokohama Pollution Control Agreement was frequently called "Yokohama style". The initiative Based on the environmental management plan, taken by the Mayor of Yokohama was the main rea- Yokohama has recently handled various environ- son for the inception and success of the"Yokohama mental problems such as environmental pollution style"pollution control agreement, which was nec- by chiemical substances, ecological degradation, essary to protect citizens' health and the living en- large resource/energy consumption, waste disposal, vironment. This was a major break with tradition, global warming, and ozone destruction. for according to conventional ideas, local munici- palities were not allowed to establish their own viii Metropolitan Environmental Improvement Program regulating standards or methods, which would be coastal industrial zone. Residents around the zones stricter than those required according to the struc- formed a residents' organization called "Council for ture of laws and regulations at that time. Conservation of Environmental Hygiene in Naka and Isogo Districts". They appealed to the national, pre- Early pollution control agreements were con- fectural, and city govemments to implement pollu- cluded with large companies in the new industrial tion control measures. Anti-pollution campaigns by area on the coastal reclaimed land in order to con- local residents inYokkaichi and Mishima-Numazu af- trol increasing pollution originating from existing fected this movement. Citizens' movements at that factories. In fact, since pollution originating from time not only promoted pollution control measures the new factories was much less than that from the byYokohama City, but also gave birth to the first pol- existing factories, the pollution control agreements lution control agreement. were very effective. Thereafter, citizens' movements continued to The agreements specified maximum pollution support the city's pollution control measures. This control targets, based on scientific data, and in light was because the city kept residents well informed of present conditions and future prospects of air of the content and results of scientific experiments pollution, and of the level of pollution control tech- conducted by the city and factories, as well as the nology available at that time. Although the agree- content and effectiveness of the agreements. This ments were much stricter than laws and prefectural openness removed anxiety from residents, and the ordinances established later, the companies recog- visual evidence of improvement in environmental nized that scientifically reasonable standards based quality enabled the city to win the residents' un- on large scale monitoring or a wind-tunnel test, derstanding and trust. were being set. The agreements played an effective role in introducing advanced technology and de- Companies' reaction Escalating anti-pollution veloping new technologies such as the country's first demands from the public, and land sales contracts power generation by LNG, and the improvement were the extemal factors that companies accepted in ground concentration of pollutants due to col- in the early pollution control agreements. Since the lective smokestacks. city's investigation and finding were scientifically sound, the companies acknowledged the results and Early pollution control agreements, which first agreed to cooperate. On the other hand, intemal targeted new factories, were later adopted by exist- factors that companies accepted such a strict agree- ing factories. Even after certain legal regulations ment were as follows: were provided, the agreements were still innova- tive. For example, the agreements imposed stricter * Yokohama was blessed with a large consumer control than laws, or introduced total emission tar- market in the outskirts of the capital; gets while existing laws only regulated emission concentrations. * Good economic conditions at that time eased negotiation of the agreements; and Residents'movements From the early 1960s, air pol- lution had become a serious problem in the existing * Having abundant capital and management ca- coastal industrial zone. Residents were anticipating pacity, the large companies were able to cope with alarm the arrival of still more factories in the new with the pollution control costs. Executive Summary ix As a result, the companies were able to pay for avoid a vertical administration, though this is typi- the costs of pollution control investment, and to cal in the Japanese administrative structure, and it maintain industrial competitiveness at the same has maintained its flexibility to effectively handle time. the problems at hand. Since then, the administra- tive structure has basically stayed the same. Staff Later, the city signed other pollution control members were engineers who had received higher agreements with the existing factories. The follow- education, and were highly concerned about pollu- ing factors attributed to the successful agreements: tion issues and approached their task with enthusi- First, the companies understood theYokohama style asm and dedication. Moreover, the city made great when they reached early pollution control agree- efforts to improve its staff's capability and accumu- merits with new factories. In addition, following lated technology in the Bureau. This accumulation increasing anti-pollution demands from the public, of technology, specifically reflected in the conclu- these companies came to realize that, in order to sion of theYokohama pollution control agreements carry out their business in the future, it would be that were based on scientific knowledge and tech- vital for them to obtain a consensus from local gov- nology, and helped the city win credibility and un- emments and residents when building or expand- derstanding from the enterprises which concluded ing factories. It turned out that to take pollution pollution control agreements. control measures is not so costly in the long term and is affordable, though large investments are re- Requirements for effective pollution control quired in the initial stage. Furthermore, from the agreemenits 'he experience ofYokohama city in- factories' point of view, the conclusion of pollution dicates the following requirements for effective pol- control agreements meant a kind of authorization lution control agreements. for pollution control measures fromYokohama City. As a result, the factories were able to build up good 1) The content of the agreements should be de- relationships with the residents. fined from a scientific and technological point of view, and not simply from an abstract and Administrative reaction The city's administrative ethical point of view. structure and staff attitudes and skills for pollution control were key factors. The pollution control agree- 2) A strict and rigid agreement is not always good. ments were successfully implemented through fre- It needs to be adjusted according to the eco- quent monitoring, on-the-spot inspections, and nomic, technical and managerial capacity of the guidance. Such local effort has been an important firm local characteristics. tool to induce effectiveness of the measures and this has been a distinctive characteristic of theYokohama 3) In order to check whether the companies carry administration. The city administration obtained out a comprehensive implementation of the residents' trust and cooperation, and maintained it agreements, it is necessary for the administra- by disclosing pollution information as openly as tion to be aware of best available protection possible. Since the city set targets based on scien- technology. Therefore, it is desirable for the ad- tific data, the companies tended to accept them. ministration to maintain a certain number of qualified staff and train them. Local staff must T'he Bureau of Pollution Control was established have enthusiasm, as well as knowledge of ad- with its 10 staff when the first pollution control vanced technology. agreement was concluded. Yokohama was able to x Metropolitan Environmental Improvement Program 4) It should be recognized that the pollution con- Accordingly, the city decided to locate some trol agreements exist not only for the company small and medium-sized industry in special sections and local govemment administration, but pri- of the Kanazawa Industrial Complex and let them marily for the residents'well-being. discharge effluent to the collective treatment sys- tem after each factory removed some hazardous Kanazawa Reclamation Project and Industrial substances. To have a collective treatment facility is Relocation much more economical than the case where each factory has its own industrial treatment facilities The goal of the Kanazawa Reclamation Project was because the former requires less space for the treat- more than just creating land for industry and port ment facility installation and less operation and as in the past. The ultimate goal was to reclaim land maintenance costs. as a site for redeveloping the downtown area and accommodating small and medium-sized factories. Costs of construction, operation and mainte- Small and medium-sized factories scattered around nance of the collective facilities are borne by the user the city were transferred into the Kanazawa Recla- companies. The facilities were constructed by using mation Land. This facilitated rationalization of fac- a 30-years low interest loan provided by the Japan tory management through cooperation and system- Environment Corporation.Yokohama city subsidized ization. The industrial relocation was also effective a part of the interest. Annual operation and main- as a measure for controlling pollution including tenance costs are settled by the user companies ac- noise, vibration, and offensive odors. cording to a certain formula using contract and ac- tual effluent volume, as well as effluent density. Successes of the Project Collective treatment proved more economical Concern about living environment The reclama- than individual treatment. It also made possible for tion project was formulated with careful consider- Yokohama city to easily monitor the effluents of the ation of environmental aspects and urban planning. user companies, and to give them appropriate guid- The area was divided into the industrial and resi- ance. dential sites by a national road running North-South in the center of the reclaimed land. A 50 m wide Incentives to relocate (land price and financial green tract of land was also constructed as a buffer subsidy) The incentives included the availability zone along the national road.The city secured about of necessary infrastructure on the site, and low cost 10% of total reclaimed land for building a seaside requirement of the relocation. park, a park on the old coastal line, and green buffer zones.The construction of the green buffer zones were The initial sales price of industrial site was funded by the Japan Environment Corporation. 30,000 yen/M2. However, it actually increased to 50,000-60,000 yen/m2 due to delays in granting rec- Pollution control measures In order to prevent lamation licenses and soaring construction costs. pollution from occurring in their new neighborhood, There was considerable doubt as to whether the tar- companies implemented the following pollution geted small and medium-sized businesses could control measures after relocation: arrangement of afford for relocation.The city therefore reduced taxes factory location within the industrial complexes, es- for the factories concerned over a limited period, tablishment of treatment facilities, as well as indi- exempting them from property tax, corporation tax, vidual measures within the factories themselves. and the special land holding tax. Executive Summary xi Taking advantage of factory relocation, the city nancial burden of interest payments prevented the tried to reform and rationaLize management of small city from spending more time for the identification. and medium-sized factories by promoting collec- tive and cooperative actions, as well as improving Utilization of vacated sites Yokohama either organization in the factories themselves. Organi- purchased the vacated sites from the relocating fac- zational promotion made it possible for small and tories and constructed public facilities such as parks, medium- sized companies, which were financially or attempted to conclude agreements with the com- weak, to obtain public funds such as the promotion panies regarding the utilization of the vacated sites. fund for small and medium-sized companies and In the latter case, companies were required to have loans from Japan Environment Corporation. prior consultation regarding their disposition, thereby limiting the future uses of the sites. How- Project execution organization The Kanazawa ever, both parties sometimes could not reach an Reclamation Project inYokohama was implemented agreement on sales prices. The city could not con- by inter-departmental effort involving Planning and trol the use of vacated land effectively. Coordination Division, Pollution Control Bureau, and 10 other bureaus of Yokohama city. Officials of those organization formed both the steering and technical committees for the project. Conclusion on Environmental Unsuccessful aspects Protection Measures in Process offactory relocation The city introduced Yokohama criteria to prioritize the districts from which relo- The national emission standard is a minimum stan- cated factories should be drawn. Criteria included dard to be complied with. National emission stan- the presence of residents and industries located in dards are not necessarily adequate for some cities close proximity to each other, existing environmental where pollution problems are serious. For this rea- conditions, and managerial capability. Based on the son, in order to protect local residents' health and results of this investigation, the city selected facto- living environment,Yokohama City found it neces- ries which would require relocation, and then en- sary to implement its own measures through pollu- couraged the process. Although the city initially tion control agreements or guidelines/guidance. wanted to relocate 2,000 out of 6,000 small- and medLium-sized factories, only about 400 factories The experience of Yokohama presents an ex- were actually relocated. Many factories which ample of a local govemment which has successfully caused pollution could not be relocated due to the implemented its own environmental protection lack of relocation funds. Moreover, about 40% of measures. To this end, it requires a comprehensive the factories relocated were previously located in the plan of actions including not only environmental semi-industrial area, and not in the mixed residen- protection but also local economic policy and local tial-industrial area. It may be said that more facto- living environmental policy. ries could have been identified and relocated if the city had identified candidate factories from only resi- TheYokohama experience also demonstrated the dential areas or commercial areas and excluded importance of gaining the trust from local residents semi-industrial areas, and if more time had been and companies. To obtain this, the city: spent for such identification. However, the city's fi- xii Metropolitan Environmental Improvement Program 1) aimed at rational, objective and effective city 5) disclosed environmental and other informa- management; tion including environmental issues as fully as possible. 2) trained special staff in environmental ad- ministration; The City of Yokohama has obtained trust from the residents for its individual measures such as 3) established cooperative relationships with municipal reform and residents'participation.These external specialists and research institutions; efforts made it possible for the city to successfully negotiate with companies about the pollution con- 4) encouraged residents' participation and es- trol agreements and to maintain effective relation- tablished a system to listen to residents' ships with the central government. opinion in the city management; and Executive Summary xiii Chapter One: Proffle of The City of Yokohama ing the high economic growth of the 1960s, and in The City of Yokohama 1978 it overtook Osaka, becoming the second larg- est city in Japan. After that, its population contin- ued to increase and reached 3.22 million in 1990, i.e. approximately tripled over the 30 years. The Introduction population density ofYokohama is 7,393 people per square km, and 95.6% of the city's population lives With a population of 3,220,000, the city ofYokohama in the densely populated core area. is the second largest city in Japan. The city is capital of Kanagawa prefecture and a center of prefectural poll- Among eleven ordinance-designated cities in tics, economics, and culture. However, the city does Japan, only the cities of Yokohama and its neighbor, not have a long history; it is only about 130 years since Kawasaki, have a ratio of day-time to night-time its port was first opened, but since then, the port has population of less than 100. Yokohama's ratio was become the most important and largest in Japan. 88.7% in 1990, indicating that the city had many commuters who lived inYokohama but worked out- Location, Topography, and Climate side of the city in places such as Tokyo. The city of Yokohama, located in the eastem part of Industry Kanagawa prefecture, is 20 to 40 km from the cen- ter of Tokyo.The city lies on the eastem edge of Tama Yokohama has developed as an industrial city with Hill facing Tokyo Bay. Several rivers flow across the high standards of technology and large-scale pro- tableland, forming gentle alluvial plains. Several riv- duction based on its port. Its annual trade volume ers such as the Tsurumi, the Katabira, and the Ooka (sum of imports and exports) is about 10 trillion yen, Rivers flow into Tokyo Bay, while the Sakai and the accounting for 15% of the national total. Kashiwao Rivers flow south and to the Sagami Bay. The tertiary industries account for 69.3% of the Since a large part of the city lies on gentle hill city's total production. In the tertiary industry, ser- and alluvial formations, there is no area which is vice industry in particular has had a major share and high enough to be called a mountain. However, a high growth rate in recent years. The secondary Kamaridani and its vicinity, located in the southern industries account for 30.6%, and the primary in- Kanazawa reclaimed area, present a mountain-like dustries only 0.1% of total output; the primary in- view, owing to the"Kanazawa Ruiso,"which is geo- dustries have in fact been on a continual decline in logically similar to the Miura Peninsula. recent years. The annual average temperature of Yokohama Manufacturing inYokohama is mainly led by the is 15.2°C; the highest temperature is 30.4°C in Au- chemical industry, followed by electrical machinery, gust and the lowest is 1.0°C in January on average. general machinery, transportation equipment, food processing, oil and coal. With respect to business Population establishments, those with more than 300 employ- ees, though accounting for only 4.2% of the total The population of Yokohama was 1.14 million in number of establishments, constitute 59.2% of the 1960. A rapid increase in population took place dur- value of manufactured goods output. Chapter I Figure 1-1: Location of Yokohama Japan Sea Sapporo Kyoto V P Sendai Hiroshima Kobe Kita-kyush< , >i FtLktLoka 4 S \ Tokyo Pacific Ocean Kawasaki Osaka Nagoya Yokohama Sa tam a Tokyo Yananshi Tokyo bay "N Yokohama City - . 60 1955-90 500 s 300 --------- S--- --- - ..... ..30 300 . ...... ~~~~~~~~~~~~~~~~30 2 00 -5=;Sei= -M-20 100 10 0 ~~~~~~~~~~~~~~~~~~~~~~~~~~~~0 55 60 65 70 75 80 85 90 (Yr) It became increasingly difficult for theYokohama in 1991. It grew 1.7 times over the 11 years period. city to find land for final disposal Oandfill) sites.The The largest part of industrial waste is generated by situation got so serious that the mayor declared"War manufacturing industry, followed by electricity, gas, against Waste."The city government constructed a water supply, and construction industry. With re- number of incinerators. In 1990, 97% of the mu- spect to the type of industrial waste, sludge comes nicipal waste collected was incinerated, while the first, followed by construction waste. ratio was less than 30% in 1955. Because of constraints on land acquisition for Treatment of night soil Figure 2-5 indicates the final disposal, waste reduction through recycling and collected night soil amount. It was 256,000 kilo li- waste treatment for reduction is important in ter/year in 1955, and increased because of the de- Yokohama and throughout Japan. Table 2-1 shows crease in agricultural population and the increasing that the final disposal amount was reduced to a difficulty in using night soil for agricultural purpose quarter of waste generation amount in 1991 through due to urbanization. In 1970, the amount reached a recycling and waste treatment such as incineration, peak of 641,000 kilo liter/year, and decreased there- de-watering and drying, etc. Noteworthy is that after. amount of waste reduction through treatment such as incineration has increased remarkably, 169% of Night soil sludge amount was in its peak in the corresponding amount in 1986. 1980, and decreased thereafter because of the de- velopment of the sewage system. In 1970, the night soil sludge was only one-third (1/3) of the night soil coliection amount. However, the current sludge amount is slightly larger than the night soil collec- Environmental Protection tion amount. Measures in Yokohama Industrial wastes The estimated amount of in- This section presents a summary of environmental dustrial waste was 5,840,000 ton/year in 1980, protection measures in Yokohama in each of main 7,610,000 ton/year in 1986 and 9,920,000 ton/year periods described earlier. Chapter 2 15 1986 1991 Table 2-1: 1. Waste Generated 7,610,000 t/d (100%) 9,920,000 t/d (100%) [130%] Recycling and 2. Waste Recycled 2,420,000 t/d (32%) 2,620,000 t/d (26%) [108%] WasteVolume 3. Waste Reduced through Reduction Waste Treatment such as hirough Incineration, Incineration, De-watering & Drying 2,950,000 t/d (39%) 4,990,000 t/d (50%) [169%] De-watering, 4 Waste Disposed of at Landfil Site (1-2-3) 2,240,000 t/d (29%) 2,310,000 t/d (24%) [103%] and Drying, etc. Note: Percentages shown in [] indicate ratios of 1991 amounts to 1986 amounts. of Industrial Wastes Industrial Promotion and Pollution: Countermeasures taken by Kanazawa Countermeasures Based on Ordinances of the prefecture At this time, there were no national Kanagawa Prefecture (195os to mid-1g6os) guidelines on pollution countermeasures.There was no coherent pollution control policy at the prefec- Socioeconomic situiation and pollution Imme- tural level; priority was given to the industrial de- diately after World War II, air pollution often caused velopment, and pollution countermeasures only asthmatic diseases, especially among the US Army took place if they were"in harmony"with economic and families located at the Yokohama base. A US objectives. Army doctor inYokohama disclosed information on this disease, which was later called "Yokohama In this situation, following the"Tokyo Munici- asthma". Public health staff in Kanagawa prefec- pal Pollution Control Ordinance"(1949), which was ture andYokohama jointly researched the problem. the first of its kind enacted by a local government during the post-war times, "Kanagawa Prefecture As noted earlier, the rapid industrial devel- Workplace Pollution Control Ordinance" was en- opment and economic growth which accompa- acted in 1951 in Kanagawa prefecture. According to nied the post-war reconstruction, was attained by this ordinance, the objective of pollution preven- developing and integrating industry in the zone tion was"the harmonization of industrial develop- which had existed from pre-war times inTsurumi ment and the welfare of residents."With regard to and along the Kanagawa coast. Accompanying the content of the pollution regulations, in order to this process, industrial pollution such as land sub- avoid damages on people and property due to noise, sidence due to the pumping of ground water, as vibration, soot and smoke, or drainage water, mea- well as soot and smoke, industrial waste water, sures to adjust factory operations were taken. How- noise, and vibration increased rapidly. The con- ever, there were no specific regulations regarding tent of the damage was similar to the one experi- the discharge of pollutants. Criteria for anti-pollu- enced in the pre-war period. Pollution in this pe- tion measures were often abstract, and no specific riod can be said to be an extension of pre-war obligations were stipulated. The role of the prefec- pollution. Of the twenty-four cases involved in tural administration was merely to advise compa- the pollution disputes in Kanagawa prefecture of nies on pollution control measures when problems 1952, noise was the most frequent problem, fol- arose. It is noteworthy that the administrative re- lowed by air pollution such as soot and smoke, sponsibility for environment management rested on gas, and dust, and water pollution due to waste the Commercial Division of the Economic Depart- water. ment of Kanagawa Prefectural Government. 16 Metropolitan Environmental Improvement Program National countermeasures Belatedly, following in systematizing the measurement of pollution and the pollution control ordinances of the local gov- handling grievances about it. emments, the national government enacted laws for water pollution control, the"Water Quality Conser- Intensification of Industrial Pollution: the vation Law"and the"Factory Effluent Control Law" "Yokohama Style" Response (196os to mid- (1956) and the"Soot and Smoke Regulation Law" 1970s) (1962). These laws included economic harmoniza- tion provisions that could be used to relax the en- Socioeconomnic situation and pollution In order forcement of the law depending on financial condi- to promote industrialization in this period, besides tions of enterprises.Yokohama city was designated the existing coastal industrial zone (the Tsurumi and by the"Soot and Smoke Regulatory Law"in 1963. Kanagawa districts),Yokohama city created factory The emission standards stipulated in the laws were sites by reclaiming other coastal areas such as extremely lax, and these laws were not capable of Negishi Bay, and the Daikokucho and Honmoku ar- effecting adequate pollution prevention. eas, and attracted large-scale factories. Yokohama city began to deal with pollution by Amid these developments, pollution in the exist- commencing basic studies and installation of soot par- ing coastal industrial zones of Tsurunmi and Kanagawa ticle deposit gauges in the coastal industrial zones of increased, and the"red smoke problem"occurred in Tsurumi ward and Kanagawa ward in 1956. From 1958, Tsurumi. This was caused by emission of iron oxide. in addition to measuring dust fall in the entire city, Complaints involved laundry being dyed red, blight- monitoring of sulfur dioxide resulting from the lead ing of garden plants, and the large quantities of dust. dioxide process also began. From 1959, the city itself began to handle all pollution complaint cases, and in In the newly reclaimed areas of the Negishi and thatyear some 657caseswere dealtwith. Furthermore, Honmoku districts where the expansion of corpo- as a result of the revision to the Kanagawa Prefecture rations had begun, from about 1960 petitions from Business Establishments Pollution Control Ordinance local medical associations were made against the of 1961, more environmental responsibilities were damage from soot and carbon black emitted from entrusted to the city from the prefectural government. petroleum refineries. On the occasion of the expan- A pollution official was posted to the Public Hygiene sion of large-scale electricity and gas plants, etc., Division of the Bureau of Hygiene, which was respon- this developed into an organized anti-pollution sible for health and sanitary conditions, and the pro- movement of the local citizenry. cessing of complaints was conducted. Counterneasures taken by Kanazawa In the national laws and prefectural ordinances prefecture of that time, cities were not recognized as having any authority with regard to the regulation of pol- With the abolition of the old ordinance, the lution sources, and could not carry out any direct "Kanagawa Prefectural Pollution Control Ordinance countermeasures. Indeed, the cities themselves of- of 1964" was introduced. The ordinance gave the ten adopted an approach of not revealing pollution mayor the authority for pollution control. Accord- problems in order to attract factories for industrial ing to the ordinance, the regulatory target covered growth. The period from the mid 1950s to the mid not only factory but also general business enter- 1960s was an important one for pollution control. prises; and it introduced a license and notification The measures described above were the initial steps system for target machinery and works. The notifi- Chapter 2 17 cation system was a pioneering innovation. In ad- were predicted to increase to the same level as in dition to the former administrative guidance and the Tsurumi and Kanagawa districts. leadership method, the ordinance emphasized regu- latory aspects, but the "harmony" provision re- The pollution control agreementwas the country's mained. In June 1964,"Pollution Standards Regula- first genuine effort to address environmental problems tions" were established. The regulations required caused by industry. Yokohama, which had no legal objective standards in order to strengthen adminis- authority with regard to pollution regulations at the trative authority, including the power to order a sus- time, used the leverage of one item of the real estate pension of industrial operation. The determination sales contracts, and through discussion brought the of pollution standards according to the major use industrialists to commit themselves to execution of of river water was an important innovation. pollution control measures. Based on scientific data on the present state and estimated future growth of Countermeasures taken by Yokohama City air pollution, the agreement prescribed strict, extremely practical and effective measures which concretely dealt Backcground Air pollution caused by sulfur diox- with pollution prevention measures. Agreements were ide and dustfall was the main form of industrial pol- concluded with petroleum plants which subsequently lution in this period though water contamination located in the reclaimed areas inYokohama, as simi- also existed. Additionally, though the volume of larly done with existing large-scale steel, chemical, sulfur dioxide discharged from the existing coastal petroleum, and electric power enterprises before they industrial area inTsurumi/Kanagawa accounted for constructed or expanded production facilities.The ii- about 90% of the city total, the city had no author- tial pollution control agreements demonstrated that ity to directly regulate the source of pollution or take obtaining consent of the local government and local measures against it. Yokohama city continuously residents when establishing plants was indispensable measured the concentration of sulfur dioxide and for the smooth execution of corporate activities. To dealt with complaints on a case-by-case basis. obtain industries' cooperation, it was also necessary to ensure that the environmental studies were all sci- lJnder these circumstances, in 1963, the reform- entifically sound. These series of pollution control ist Mayor Asukata came into power. He pledged to agreements came to be called the"Yokohama method." implement pollution prevention policies, and the foundations of the pollution prevention policies of The pollution control agreements made possible Yokohama were rapidly laid. In 1964, a pollution sec- to reduce sulfur oxides emissions from the factories tion was established in the Public Health Division, in the Negishi Bay to one-third (1/3) of the level Bureau of Hygiene and was promoted as the Pollu- predicted without agreement. The ambient concen- tion Control Center. tration of sulfur dioxides inYokohama already be- gan decreasing in 1968 when application of K-value Pollution control agreement In 1964, the first (SOx emission concentration) regulation started. Pollution Control Agreements was concluded be- tween Yokohama city and a thermal electric plant Rapid Economic Growth: Strengthening of that was planned to be constructed in the Negishi National Pollution Policy (latter half of 196os Bay reclamation area where there were construc- to 1970s) tion plans of not only this electric power plant but also an oil refinery, and other enterprises. If all these Socioeconomic situiation and pollution In facilities were constructed, sulfur oxide emissions Yokohama as in many other large cities, rapid popu- 18 Metropolitan Environmental Improvement Program lation growth and industrial development in the control was placed at the top of the list of actions period of high level economic development led to for protection of citizens' life. The city expressed its the mixing of commerce, industry, and residences environmental protection goal in easy words instead in urban areas and the phenomenon of sprawl, of using figures so that the citizens could under- bringing about the deterioration of the living envi- stand the environmental goals easily. ronment. Development of pollution control agreements and Countermeasures taken by national government changes in principles and gtidelines The pollu- and Kanazawa prefecture tion control agreements, which targeted large-scale factories, actively progressed in the 1970s. The As pollution intensified, a full-scale response at the agreements were concluded with existing plants, national level began to take shape. In 1967 the when plants moved and when new extensions were "Basic Law for Environmental Pollution Control" undertaken. The pollution control agreements first was enacted. This was a period of strengthening na- targeted air pollution control, mainly control of sul- tional pollution policy, with enactment of the "Air fur oxides and subsequently, targeted water con- Pollution Control Law," the "Water Pollution Con- tamination control and waste control. trol Law of 1970"through the"Pollution Diet" (this Diet session was given this name because the en- With regard to large corporatioris, from the latter tire session concentrated on pollution problem), the half of the 1970s, uniform pollution control policies "Waste Disposal and Public Cleansing Law" and came to be executed based on the experience of mak- establishment of the Environment Agency in 1971, ing pollution control agreements. The next task was etc. In Kanagawa prefecture, the"Pollution Control how to deal with small- and medium-sized enter- Ordinance" was revised. prises. In contrast to the individual handling of large- scale enterprises, it was agreed that the use of rela- Countermeasures taken by Yokohama City tively uniform measures was sufficient, and an ap- proach involving guidance and directives was followed. Expansion of organtizatiott of regulatory The guidelines were prepared based on the previous authority In Yokohama, the Pollution Control pollution control agreements.The reason why the city Center established in the Bureau of Hygiene became used guidelines instead of establishing its own ordi- independent in 1971 as the Pollution Prevention Bu- nance was that it was unnecessary for the city to cre- reau. A good deal of regulatory authority with re- ate a municipal ordinance which complemented the gard to air pollution and water pollution was also prefectural ordinance. The guidelines were generally delegated to the mayor. As a result, the various laws followed by small and medium industries. and prefectural ordinances became the basis of le- gal regulations for pollution countermeasures. Kanazawareclamnationproject Amongthepol- Countermeasures taken byYokohama city include lution control measures inYokohama, strict control monitoring and surveillance of pollution-generat- of large-scale companies were enforced under the ing business enterprises, public waterways, and air environmental pollution control agreements. This quality, along with various types of regulations. turned out to be effective since these companies possessed enough technological and economic ca- In 1973,Yokohama city prepared a comprehen- pacity to respond to the measures. On the other sive city development plan that has a slogan,"Cre- hand, measures against small- and medium-sized ate new town by citizens." In this plan, pollution companies, which were scattered throughout the Chapter 2 19 city, were difficult to enforce, and their implemen- collective organization of small- and medium-sized tation lagged behind. industries and joint use of facilities was promoted and pollution control rneasures were implemented Emission control and promotion of fuel con- with rationalization and strengthening factory man- version by guidelines and directives as stated above agement. were therefore introduced. However, there were still serious pollution problems caused by small- and The reclamation project was formulated with medium-sized enterprises which were located in the careful consideration of environmental aspects and mixed district of housing and factories. Water pol- urban planning. In determining land utilization and lution as well as noise pollution and vibration were segmentation, the city secured about 10% of total caused by traditional local industries such as plat- reclaimed land for building a seaside park, a park ing and textile printing along the Ooka andTsurumi on the original coastline, and green buffer zones. Rivers. The city also developed an urban redevelopment site equipped with anti-pollution facilities, and secured The small- and medium-sized companies were sites for residential buildings and public facilities. limited in their ability to implement pollution con- trol measures in their existing sites in terms of eco- Air pollution control Air pollution countermea- nomic and technical capacity and due to the condi- sures were mainly aimed at providing a monitoring tion of their location. Accordingly, the city started system based on the Air Pollution Control Law, to consider moving these companies to more ap- achieving the environmental quality standards for propiiate areas, such as industrial complexes. By sulfur oxides, and promoting countermeasures for doing so, the city intended to help promote indus- hydrocarbon and nitrogen oxide. Modernization of trial development by rationalizing factory manage- a monitoring system for ambient air and automo- ment, as well as by reforming and strengthening bile exhaust gas made it possible to monitor pollut- their management.This would also help the city pre- ing factories regularly. Sulfur oxides met the exist- vent and control pollution, as well as organize and ing environmental quality standards in all the city redevelop the city zone. monitoring stations through countermeasures such asYokohama Pollution Control Agreements with the InYokohama city, this measure was realized by large-scale factories in the coastal district from the the construction of Kanazawa Industrial Park in the 1960s; K-value regulations (on SOx emission con- reclaimed land beyond Kanazawa district. The centration) in the Air Pollution Control Law; and Kanazawa Reclamation Project had been formulated total emission control in the Prefectural Ordinance. under the Comprehensive Construction Plan of However, environmental quality standards were Yokohama International Port City of 1966. The rec- then revised in 1974. To meet the new standards, lamation project started in 1971 and was completed Yokohama city formulated administrative guidelines in 1981. The goal of the project was more than just including countermeasures relating to small- and building an industrial site or a port facility as in the medium-sized enterprises and established total past. The ultimate goal was to reclaim land as a site emission control mainly on fuel. Furthermore, since for redeveloping the downtown area and accom- total emission control was carried out based on the modating small- and medium-scale factories scat- Air Pollution Control Law, the new environmental tered around the city, thereby strengthening land quality standard was met from the 1980s and then, utilization and controlling pollution. Alongwith this, air pollution due to sulfur oxides became less of a 20 Metropolitan Environmental Improvement Program national concem. Due to these regulations, annual ing on weather conditions. emissions of sulfur oxides in the city fell to 3,000 tons in 1980, 3% of the peak of 103,000 tons in 1968. Because of the enactment of Air Pollution Con- Trends in dust fall paralleled the reduction in sulfur trol Law with strong objectives, many regulations oxides, and also decreased significantly, particularly were set up during this period and they forced the between 1965 and 1970. industries to take necessary measures. Of course, the implementation was possible because the in- The"Nitrogen Oxides Countermeasures Guide- dustries had enough financial capacity and devel- line"introduced a total emission control. While the oped technology. preventive measures against fixed pollution sources spread, new sources such as air pollution from au- Water pollution control Water pollution control tomobile emissions became a problem. Japan's ob- activities during this period included development jective was to reduce emissions of CO, hydrocar- of a monitoring system based on the Water Pollu- bon, and nitrogen to about 10% of existing levels tion Control Law, tightening the regulations against based on 1970 Amendments of the Clean Air Act. polluting factories to meet the environmental qual- Although this objective was scheduled to be fully ity standards for toxic substances in public waters, implemented in 1976, it was postponed, and a and development of sewerage service. staged upgrading of the standard was legally ac- cepted because of a request from manufacturers. The telemeter monitoring system for water quality was established following the orderly set up Opposed to this national action,Yokohama con- of regular monitoring stations for river and coastal sidered automobile pollution as a common prob- water body. lem among large cities, and joined the "research association on automobile exhaust gas for seven Toxic substances such as cyanogen and mercury large cities" with Tokyo, Kawasaki, Nagoya, Kyoto, continued to pose threats to public waters and, in Osaka, Kobe in July 1974. Research based upon traf- consequence, to human health. The rate of non- fic surveys and cost of new emission standards made compliance with environmental quality standards it clear that regulation by 1976 was technically and relating to toxic substances was 4.8% in 1971. How- economically possible. The association therefore ever, toxic waste decreased due to enforcement of a requested the national government to fully imple- strict regulation against factories, and is now rarely ment the regulation. In the summer of 1975, the found. In this period, due to effective effluent con- city implemented an investigation of NOx and CO trol on large-scale factories in the coastal district, emission from automobiles and used the study re- problems of water contamination with industrial sults to establish the level of regulation. With re- waste water had been much alleviated. On the other spect to hydrocarbons, following the damage due hand, water contamination with domestic sewage to photochemical smog in the city in 1971, the city became increasingly serious in this period. Since investigated photochemical air pollutants from fac- Yokohama city had not yet fully developed a sewer- tories and workplaces, and prepared guidelines for age system, quick development was felt desirable. controlling photochemical air pollutants. The re- ported number of victims in photochemical smog Soil contamination Soil contamination due to reached its peak in 1975 and then, decreased dras- toxic substances became a problem. Soil contami- tically. However, warnings are still issued depend- nation due to mercury and PCB was found on an Chapter 2 21 old chemical factory site in 1973, and since then the daily urban living, energy conservation, and the city has provided guidance to buyers and sellers of demands stimulated by increased incomes for a factory sites on which toxic substances was used. In comfortable living environment. These problems, 1986, the city established the "Guidelines for Soil complicated and diverse as they are, have imposed Contamination Measures in Old Factory Sites" a new challenge to environmental authorities in the which provided instructions with respect to disposal country. of contaminated soil. Countermeasures taken by Yokohama City Solid waste management The volume of waste disposal in Yokohama greatly increased accompa- Environmental mantagement policies Yokohama nied by a rapid increase in population and high eco- recognized during the mid-1980s that it was time nomic growth in the 1960s. It doubled in five years to shift its emphasis from exclusive concern with from 1960, then, almost tripled during the five years industrial pollution, and that it was hecessary to from 1965 to 1970, and increased seven times dur- establish an environmental assessment system in ing the decade of 1970s. parallel with existing measures in order to protect and create a good city environment. Through the The city started construction of modern incin- discussion in the council for control of environmen- erators in 1969. Incinerators constructed by 1970 had tal pollution, the city introduced the"Guidelines for a total capacity of incinerating 40% of the total waste Yokohama Environmental Assessment" in April amount collected by the city. 1980. The guidelines consist of a procedure for en- vironmental assessment and a description of the Acquisition of sites for final disposal became so methodology by which a project proponent can difficult for the city that it declared "War against undertake environmental assessment. Waste" in 1972. Further, Yokohama adopted the "Yokohama Urban Pollution and Energy Conservation: Environmental Basic Charter"in March 1986 which Response to the New Environmental Pollution was intended to form a good city environment for and Creation of a Comfortable Living the 21st century based upon a balance between na-, Environment (latter half of the 1980s) ture and human conduct. Emphasizing that every- body should participate in the creation of a better Socioeconomic situation and pollution During city, the Environmental-Basic Charter had a slogan, this period, the population of Yokohama continued "Yokohama with good environment where the citi- its steady increase. As mountain, forest, and farm zen can live safely and comfortably." Cooperation lands gave way to housing sites, the water reten- between citizenry, business, and administration was tion capability of the land declined. Environmental urged. At the same time, Yokohama designed the resources were strained by demands for recreational environmental management plan (Environmental lake and river facilities, and as household income Plan 21). This plan was expected to realize the envi- increased, the number of automobiles owned in ronmental slogan stated in"Yokohama Plan for the Yokohama also grew rapidly. From the 1980s, there- 21st century," which was prepared in December fore, the importance of conventional industrial pol- 1981. It was recognized necessary not only to imple- lution declined. The focus shifted from industrial ment various environmental measures individually pollution to the newer issues of pollution related to as in the past, but also to implement a comprehen- 22 Metropolitan Environmental Improvement Program sive and well-planned environmental administra- are some upper reaches and branch rivers that need tion from the new standpoint. Environmental Plan more improvement in water quality. A decrease in 21 was earmarked as a foundation of the new envi- water volume in the river is anticipated due to the ronmental administration. development of sewerage system. After having im- proved drinking water quality, the citizens now de- Air pollution control Nitrogen oxides from au- mand the amenities from a clean water environment tomobiles have become a major problem. Although and comfortable access to bodies of water. the city established the "Administrative Guidelines for Nitrogen Oxides Control Measures" aimed at Overall, contamination of coastal waters has achieving total emission control, environmental remained unchanged in recent years. In Tokyo Bay, quality standards have in practice not been met. The red tide due to eutrophication caused by nutrient city has therefore formulated the "YokohamaAuto- salt (nitrogen and phosphorous) still occurs. mobile Pollution Control Plan,"taking various mea- Groundwater pollution due to an organic chlorine sures to address this source of pollution, including chemical substance (trichloroethylene) also raised traffic volume control, road improvements, and so apprehension in the community. The city investi- on (See ANNEX 1). gated the source of this contamination at factories concemed, and prepared"Guidelines for Trichloro- Water polluttion control After having improved ethylene" and "Guidance Manual," and also pro- water quality in terms of health indicators such as vided technical assistance in specific cases. cyanogen and mercury, it became necessary to im- prove water quality in terms of living environment With respect to actions conceming unregulated indicators such as SS and BOD. The relative impor- chemical substances and high-technology pollution tance of domestic pollution increased. River and sea control, the city prepared'Yokohama tentative guid- pollution due to discharges of synthetic detergents ance for environmental protection in connection from households became evident. with high technology industry," and also provided technical supports and advises in specific cases. The quality of the major river in the city has Furthermore, in response to the environmental pol- improved in recent years with the rapid develop- lution caused by use of agricultural chemicals at a ment of the city sewerage system. However, there golf course, the city concluded the"environmental Water Quality (mgl/) Access to Sewerage(%) Figure 2-6: 25 10 0 Water Quality RiVer BOD -inPublic 2 0 _ ... __ . ... .. ..................... ................. ...... ...... ...- 80 W s _d . ................. Aters t Access to 15 ... ..........................--.-......... . .... ......... ....................-60 Sewerage by Residences, 10 - ---- 40 ~~~~~~~~~~~~~~~~1955-90 1 0 ............ -.. ... .......................... .. ... .... ........ .................. .......... ..... '. ................... .< 0......... .4 1S0 - s '.. ,,,,,,",,,,,,,,,Coastal Water C0L) 20 ...ss .................... ....... .... ........ ....... ... ..... . ...... ..I....... . ..... ...... 2 Access to Sewerage ------------- 0 .-.-- 0~~~~~~~~~~~~~~~~----- 55 60 65 70 75 80 85 90 (Yr) Chapter 2 23 protection agreements regarding the use of agricul- there was no division or section with explicit respon- tural chemicals"with five golf courses in 1991. sibility of sewerage which was temporarily set un- der the engineering works division of the Water General amenity The needs of the citizenry are Supply Bureau. not limited merely to pollution control, but have come to include comfortable living and recreation. In the immediate post-war period,Yokohama In today's Yokohama, the upgrading of city parks, could not conduct total city planning because of protection of green areas, and preparation of green the long period of US army occupation, and did buffer zones are being introduced. River facilities not carry out a systematic sewerage development. originally designed for flood prevention are viewed With respect to organizational structure, there also as amenity facility. In reclamation areas, artifi- were sewage sections under the Reconstruction cial beaches are being prepared, and people have Bureau, the Water Supply Bureau, and the Con- begun to re-create the natural environment that was struction Bureau, respectively. In 1949,Yokohama once destroyed. integrated the sections into the Sewerage Divi- sion of the Construction Bureau. In 1950, a flood prevention project started in Tsurumi district as part of full-scale sewerage development scheme (excluding rainwater). Construction of a sewage Organization of Environmental treatment plant for the central distric't started in PinYokohama City 1957. In 1961, the Sewage Division (later renamed as Sewage Works Department) was created un- This section describes the initial establishment and der the Civil Works Bureau, becoming indepen- subsequent evolution of the organization responsible dent and entitled the Sewage Works Bureau in the for environmental protection measures inYokohama. same year. Establishment and Changes in Responsibility The bureaus such as civil works, sanitation, etc. for Sewage, Night Soil, and Waste monitored the quality of public waters since the early 1950s. The sewerage facility division of the construc- Yokohama city had started its basic sanitation de- tion bureau had measured the water quality regu- partmental bureau for water supply, sewerage, night larly between 1957 and 1966. soil treatment, and waste disposal, and provided these services even in the pre-war period. Solid waste Awaste disposal service inYokohama started first with the waste collection and disposal Sewerage system. With respect to its sewerage by private operators in foreign residents areas and, system,Yokohama introduced its first piped drain- downtown areas during the port-opening period. age installation in its foreign district (presently The city began direct operation of solid waste col- Yamashita-cho, Naka-ku) in 1869 right after the lection in 1917 (the Taisho period) and completed Yokohama port-opening. It subsequently built an- its construction of the WasteTreatment Plant in 1931. other drainpipe in its downtown area. However, in This was the largest plant in the Orient at that time. the pre-war period, the city still did not have a com- Since then, the city has gradually expanded solid prehensive drainage system. The Civil Works Bu- waste collection and disposal facilities. In 1946, the reau had primary responsibility for sewerage, but Waste Management Division of the Sanitation Bu- 24 Metropolitan Environmental Improvement Program reau resumed its responsibility and expanded waste of modern incinerators. collection areas. The division was upgraded into a bureau in 1951 after which it developed a full scale The share of solid waste management to the waste disposal system including a series of incin- city's total expenditure was 1.9-2.5% during the erators. 1960s and 4.0-4.8% during the 1970s. The number of staff of the Cleansing Department was about Figure 2-4 shows the amount of waste collec- 1,000 in the middle of the 1960s and increased 3 tion and treatment since 1955.The amount of waste times in 30 years. in Yokohama increased largely along with rapid population growth and high economic growth. Night soil Night soil management service in However, the capacity of incinerators was not Yokohama was originally provided by private op- enough and only 40% of total collected waste in erators. In the port-opening period, these opera- 1970. tors collected night soil and collection fees from households. The night soil was in turn sold to farm- Figure 2-7 shows trends of the city's solid waste ers. After that, the "Waste Disposal and Public management expenditures and of the number of Cleansing Law" imposed a legal restriction on a staff members in the Cleansing Bureau. In the 1960s, night soil management. In some areas private op- the expenditures increased gradually and, since erators were not able to expand their service, fast 1970, increased rapidly mainly due to construction enough to keep up with increases of night soil quan- Figure 2-7: Expenditure (million yen) Number of Staff Solid Waste 4 5, 000 3. 6 0 0 Management: 40, 000 ... ._ ... .. ........-........ . ...........................................20 oedu........................ Exp enditure 3 5.000 . 800 and 3 0, 000 . .--..... 2, 4 0 0 Employment, 25.000 ---- .----------~~~ . -- -- . --- 2.000 ~1955-90 2 5, 0 00 __._...... . ..... ...._._.. ........_ ........ 7.= 2 , 000 20. oo0 - - .......Staff . ...... __. 600 1 5. 0 o o . __ ..... .... .. ... Expend i ture-- _. 2 0 0 I0, 000 . ..-. - _--- .------- ..- --.- . . ....-....... .. .... ... ..--. a- . 800 5, 000 . . ._..... ..... ... . ....... . ... . .. ____ 4 0 0 0 55 60 65 70 75 80 85 90 Asahi Plant pintJL + Kounan Plant Waste Incineration Plant Sakae Plant Jiodogaya Plant Hokubu Plant Chapter 2 25 tities. To cope with the situation, the city started its actions. own collection service in 1924 for public facilities and private houses that applied for the service. Conimencement of environmental measurement Pollution countermeasures in the city first started On the other hand, there was constant conflict with the installation of facilities for dust fall mea- over territorial expansion among private operators surement in 1956 and of sulfur dioxide measure- with the increase of private houses following down- ment by the lead dioxide (PbO2) method in 1958. town. development. The"Kanagawa Public Cleans- Originally, these were research studies on urban ing Regulations of 1933"in the pre-war period in- sanitation in theYokohama Health Institute. These troduced a business license system for night soil were simple measurement methods and did not tar- collection operation and regulated the business. Fol- get a specific pollution source. However, these mea- lowing WWII, private enterprises resumed its op- surements have been useful in identifying long-term eration. The "Public Cleansing Law of 1954" stipu- trends in pollution. Therefore, the city still uses the lated that municipalities were responsible for night 30-year old methods of measurement in addition soil rnanagement. Municipal governments intro- to its modem and expensive, automatic measure- duced a business license system for night soil man- ment system. agement and a uniform fee for collection. They also made clear the operational territory of each night Coniplaint Settlement Systematic actions for en- soil collection company, and thereby facilitated a vironment and pollution in the Yokohama city ad- smooth operation. ministration originated with the creation of a post for a pollution specialist at the Public Health Divi- Institutional Development of Pollution Control sion under the Sanitation Bureau in June 1961. Be- and Environmental Actions cause revision of the Kanagawa Project Site.Pollu- tion Control Ordinance required a transfer of a part Different from the bureau in charge of sewerage, of environmental management responsibility from solid waste, and night soil, another bureau - re- the prefectural govemment to the city, that posi- sponsible for pollution countermeasures - was es- tion was created for settlement of complaints at the tablished more than a decade after WWII. Table 2-2 health center, which was a branch office of the Sani- shows the changes of the number of staff members tation Bureau. The health center was responsible for in charge of pollution control and environmental handling pollution problems. Technically compli- Year Number of Staff Events Table 2-2: 1960 0 The Changes 1961 1 Appointment of pollution specialist at the Public Health Division of the 1964 (April) 7 Deployment of staff in charge of pollution Number of 1964 (December) 10 Establishment of Pollution Control Center Staff 1971 38 Establishment of Bureau of Pollution Control Members in 1973 84 Reorganization of the Bureau Charge of 1976 134 Establishment of Pollution Research Institute Pollution 1980 164 Establishment of Office of Environmental Impact Assessment Control and 1984 168 Establishment of Bureau of Pollution Control Convronmend 1985 170 Environmental 1987 166 Appointment of division chief of Automotive Pollution Control Actions. 1991 208 Establishment of Environmental Protection Bureau 26 Metropolitan Environmental Improvement Program cated pollution problems were handled by the Publi" ous experiments in-order to collect data more rap- Health Division of the Sanitation Bureau. The idly. In 1965, the system was replaced by Yokohama Health Institute was involved in the pol- telemetering. This was the first of its kind used in lution issues when necessary. Since there were at Japan. After the Air Pollution Control Law was en- that time no national laws or prefectural ordinances acted, the city in emergency has to seek the coop- to give the city authority to regulate pollution eration of industries to reduce pollution concentra- sources, the Sanitation Bureau in charge of health tion based on the data obtained through regular and sanitation handled complaints. monitoring. Yokohama sets smog warnings on its own initiative based on telemetering data, gives Organizational structure in thie introduction and smog warnings to large corporations before an development period of the "Yokohamna Style" pol- emergency happens, and requests their cooperation lution control agreements Mayor Asukata, who to reduce emissions of pollutants. pledged strong actions against the environmental pollution in his mayoral election, took office in The Bureau of Polluttion Control - a full-scale March 1961 and organized his administration to organization for pollution countermeasures In cope with the pollution. In April 1961 Public Health 1971, the Pollution Control Center became indepen- Division with seven staff members under the Sani- dent from the Sanitation Bureau and was renamed tation Bureau, the Yokohama Pollution Control the Bureau of Pollution Control (38 staff members). Committee and, in December, the Pollution Con- This is becauseYokohama, as an ordinance-desig- trol Center were established. The establishment of nated city was given authority over monitoring and these organizations prepared for full-scale devel- regulating sources of pollution through the enact- opment of pollution control actions. The Pollution ment of the Air Pollution Control Law and the Wa- Control Center had approximately 10 staff mem- ter Pollution Control Law, as well as the Basic Law bers at first, and was responsible for measurement, for Environmental Pollution Control. analysis, training, settlement of complaints, etc. Around this time, Yokohama introduced a more The number of recruited staff greatly increased competitive recruitment system which attracted during the decade following the establishment of higher caliber staff. The Pollution Control Center and the Bureau of Pollution Control. Ten to twenty staff later the Bureau of Pollution Control primarily ex- were recruited annually. This is because the city's pected to receive job applications from engineers actions against pollution were well known and na- with higher education. tional concern about pollution issues was growing at that time. The staff recruited by the Bureau of In its technical aspect, Yokohama started air Pollution Control were highly concemed about pol- quality monitoring at an early stage and has con- lution issues and did their jobs with enthusiasm and tinued to emphasize it. This foundation turned out dedication. to be useful for preparing for pollution control agree- ments. Air pollution is changeable within short pe- Staff of the Bureau of Pollution Control con- riods of time due to fluctuations in pollutants and ducted various types of jobs including measurement, weather conditions. It became necessary therefore analysis, factory guidance and settlement of citizen's to introduce more precise measures. In 1964, complaints, and had been trained to think from the Yokohama introduced regular monitoring by using citizen's standpoint. For this reason,Yokohama was automatic record measurement, and conducted vari- able to avoid a vertical administration, though this Chapter 2 27 is typical in the Japanese administrative structure, vate firms with a public certification will continue to and to maintain its flexibility to easily handle the be essential to the administration's success in promot- problems. Moreover, the city made great efforts to ing pollution countermeasures. improve its staff's capability. Staff participation in seminars and training courses contributed to accu- Organizational expansion for polllution counter- mulation of technology in the Bureau.Yokohama en- measures The Bureau of Pollution Control has con- vironmental pollution control agreements were pre- tinued to expand, and more divisions have been cre- pared based upon the city's accumulated experience ated with precisely designated responsibilities. The and the latest technology. Pollution Research Institute was also established in 1976. Thereafter, pollution problems have been re- Staff have successfully implemented the pollution defined more widely as environmental problems. control agreements and the various guidelines through The organization began expanding and developing frequent monitoringand on-the-spot inspection. Such itself so as to deal with new themes such as envi- local efforts have been an important tool to induce ronmental assessment and environmental manage- effectiveness in measures and these have been a dis- ment. The number of the staff in the Environmental tinctive characteristic of the city.The city has also con- Protection Bureau and the functions in 1992 are tracted out a part of the monitoring work required by shown in Table 2-3. the Air Pollution Control Law and the Water Pollution Control Law to private firms.The development of pri- Table 2-3: Functions Administrative Medical Technical The number Organization Total Affairs Engineering Affairs Skill of staffiand Bureau Chief 1 1 functions of General Affairs Dept. 40 28 7 1 4 the Planning & Coordination Dept. 79 18 28 2 Environmental Pollution Control Dept. 79 8 71 Protection Environmental Science Institute 38 4 34 Bureau Total 206 58 141 1 6 28 Metropolitan Environmental Improvement Program Chapter Three: Key Environmental Conservation Measures and Organizations in Yokohama This chapter shows key pollution control measures ants including sulfurous acid gas as well as soot and taken byYokohama city, through the pollution con- smoke became quite conspicuous.Yokohama's ob- trol agreement and industrial relocation, and dis- jective was to develop as an industrial city. Because cusses the relationship between environment and the existing industrial zone, Tsurumi-Kanagawa, economy in Section C. had already been saturated by mid-1950s, the city planned to promote further industrial development on reclaimed industrial land in the coastal zone. Large-scale reclamation projects started in Daikokucho and Tsurumi districts and in Negishi Pollution Control Agreements Bay. At the completion of the Daikokucho reclama- tion project in 1961, large-scale factories for petro- Pollution control agreements are defined as pacts leum, chemicals, electricity, and food processing or accords which are mutually agreed upon in ad- were built on the new site, induced by a factory in- vance between local govemment and/or commu- vitation act. However, construction of a thermal nity groups and business enterprises whose activi- electric power plant on this site resulted in a further ties present a threat of pollution. These agreements aggravation of air pollution. On the new site cre- reflect measures and steps to be taken by the enter- ated through the Negishi Bay reclamation project prises in order to prevent and control business-re- started in 1959, construction of large-scale factories lated pollution. for petroleum, electricity, steel, machinery, and elec- tricity was planned. During this period, the city ob- Pollution control agreements inYokohama were served substantial industrial development. Volume conceived by an autonomous effort of the city dur- of crude petroleum used in Yokohama increased ing the period when local governments did not have from 0.54 million kilo liter in 1961 to 1.56 million any legal authority over pollution control. In fact, kilo liter in 1964, almost threefold growth in three these were the first major pollution-related agree- years. ments made in Japan. Under the agreements based on mutual consultation, the city obtained pledges Residents' movements In the meantime, air pol- from business enterprises to implement pollution lution had become a serious problem in the exist- control measures. In this section, we discuss the first ing coastal industrial zone of Tsurumi-Kanagawa pollution control agreement inYokohama in 1964, district. Residents along Negishi Bay were antici- its policy process and procedures, its features and pating with alarm the arrival of still more factories. effectiveness, as well as development of subsequent When the petroleum refinery built on the first re- agreements. claimed land in Negishi Bay started its operation in April 1964, citizens started to complain about noise, Situation before the conclusion of the pollution odor, and soiling of washed clothes caused by gen- control agreements erators and plant facilities.This stimulated the rapid evolution of an anti-pollution movement among industrial development and thiegrowthi of pollution citizens. from late-195os throutgh mid-196os Industries in Yokohama rapidly developed after 1950, returning By May of the same year, residents in Negishi to their pre-war level of output by 1955. At the same Bay and the Honmokucho area had formed a time, however, pollution caused by various pollut- resident's organization called"Council on Conser- Chapter 3 29 vation of Environmental Sanitation in Naka and When a local medical association in Negishi Bay Isogo Districts," with 200 executive members se- appealed to the Mayor to formulate pollution con- lected from among managers of various organiza- trol measures in the coastal industrial zone of tions and groups. The council made an appeal to Negishi Bay, the city responded unenthusiastically. the Ministry of International Trade and Industry It sent a copy of the association's request to the (MITI), Ministry of Health and Welfare, Ministry of newly-established companies and asked for their Construction, and the Economic Planning Agency, cooperation. In addition, it promised to the asso- for"a preliminary investigation on pollution in the ciation that it would provide anti-pollution guid- Negishi-Honmoku industrial zone." During the ance under prefectural ordinances, and that it would appeal, the Council adhered to its position that the respond to the issues by establishing a new organi- committee would not only directly make an appeal zation, Committee on Environmental Pollution to government but also directly negotiate with cor- Control Measures of Yokohama. However, the com- porate headquarters in Tokyo, if necessary, and re- mittee was called into session only twice, in 1962 fused any concessions regarding its principle "resi- and in 1964, without delivering any substantive dents could coexist only with enterprises which measures. would conserve living environment." In response, the Ministry of Health and Welfare replied that Conclusion of the first pollution control "while the Ministry would make efforts to improve agreement environmental hygiene, local municipalities would also need to establish an agency respon- Movement in tlte city's administration In 1963, sible for conducting a preliminary investigation Mr. Asukata ran forYokohama Mayor with campaign in the area where serious pollution was foreseen." pledges of "creating a city administration which Based on this reply, the Council requested would care about children,"'"building a city in which Yokohama"to take all possible measures."There- anyone would be attracted to live,"as well as solv- after, the movement played a significant role in ing pollution and other issues. His victory in the bringing about the success of anti-pollution mea- mayoral race gave impetus to environmental efforts sures in Yokohama. in the city. During the same year, a number of other reforming governors and mayors were also elected Attitude of thie city administration Prior to es- in regional elections held nationwide, with similar tablishing pollution control agreements, the city ad- campaign pledges on pollution control. Indeed, ministration had no authority to regulate pollution pollution issues had become a center of public at- either under national laws or under prefectural or- tention across Japan. It was during this period that dinances. While this certainly prevented the city MIT and the Ministry of Health and Welfare inves- from taking direct measures, there was a tacit un- tigated into the pollution situation inYokkaichi and derstanding within the city administration not to proposed a plan for pollution control, and that a stir up pollution issues, in order to achieve indus- construction plan for large-scale industrial com- trial development through invitation of factories. For plexes in Mishima and Numazu was abandoned example, the Basic Plan For International Port City following opposition from local residents. of 1956, under which reclamation projects were in- corporated, emphasized industrial development. In order to implement promises made during However, nothing was mentioned with regard to the campaign, the Yokohama Mayor established a pollution issues. basic policy which emphasized improvements in the 30 Metropolitan Environmental Improvement Program living environment. In addition, with regard to pol- in Negishi Bay, transferring a part of the land from lution issues, the Mayor began building the foun- the Tokyo Electric Power Co. Establishment of such dation for a pollution control structure, by exami- power resources was implemented according to a nation of anti-pollution strategies in consultation basic plan formulated by EPDC. It was the MITI with academic groups as well as by strengthening Minister that had authority to decide on the con- the city's pollution control regime. struction of power facilities based on an electric enterprise law. Therefore, municipal govemments In response to a request made by the council, at that time had no goveming authority over the the city conducted a preliminary investigation of the construction of power resources, except that gover- pollution caused by major factories in Negishi and nors were requested by EPDC to present their ad- Honmoku.The results of the investigation predicted visory opinions. Yokohama city administration that"without taking any aggressive measures against leamed of the plan for the construction of the power air pollution from now on, the center of the city plan through the Govemor only after the plan was would be polluted by the end of the 1970's at the decided. same level as in the existing coastal industrial zone in Kawasaki and Tsurumi districts." Based on the In June of the same year, Tokyo Electric Power data provided by the investigation, the city requested Co. requested that the city grant them a concurrence an academic group to present their advisory opin- in transferring part of their land which had been ions on pollution control measures. The group's developed specifically for the company to EPDC, as Nine-Point Recommendations included measures a construction site for a coal thermal electric power such as reexamination of industrial and urban plan- plant.The company made this request because of a ning, strengthening health administration systems clause in the sales/purchases contract stating that for residents, strengthening the anti-pollution transference of reclaimed land to a third partywould regime, and adherence to the principle of infor- require the city's concurrence. mation disclosure with regard to pollution issues. Taking this land-transfer request as an oppor- Conclusion of the first pollution control agree- tunity,Yokohama started responding to the power- ment with the Isogo Thermnal Electric Power plant issue, not as an isolated issue related only to PlantoftheElectricPowerDevelopmentCo. In EPDC, but as a generic issue that would require May 1964, whileYokohama requested that an aca- comprehensive pollution control measures in the demic group present their advisory opinions, the entire coastal industrial zone. We can conclude that Electric Power Development Coordination Council Yokohama autonomously started dealing with the (EPDC), an advisory body of MITI, decided to con- pollution issues for the first time. struct coal thermal electric power plants in three cities, based on a govemment policy on coal. The In August of the same year, Yokohama estab- three cities were Yokohama, Takehara in Hiroshima lished the Council on Environmental Pollution Con- prefecture and Takasago in Hyogo prefecture. The trol Measures, consisting of citizen's representatives, coal thermal electric power plants scheduled to be scholars and experts, and factory representatives. built in these cities belonged to Electric Power De- The council conducted scientific investigations and velopment Co., a national enterprise funded by the experiments, including an on-site air pollution study government. In Yokohama, construction of the and a wind-tunnel test of electric power develop- power plant was scheduled on the reclaimed land ment, and examined detailed conditions of the Chapter 3 31 power plant such as the density of exhaust fumes own experiments, but also facilitated extensive dis- and the height of smokestacks. cussions between them. Moreover, the city kept resi- dents well informed of the content and process of Having conducted a number of scientific inves- the experiments. The companies respected the tigations on pollution prevention and control, the agreement. As a result, the city won the residents' city could finally establish a method for designing understanding and trust. Furthermore, the agree- pollution control measures. Based on this method, ment required the companies not only to take pol- in December the city requested that EPDC should lution control measures but also to monitor and re- take pollution prevention and control measures pro- port on pollution conditions. The agreement also posed by the city.The company accepted the request, authorized the city to conduct on-site investigations, and signed a formal voluntary agreement on the when necessary. pollution control with the city. This had not been possible earlier under any existing regulations, in- In addition, the city obtained from the Tokyo cluding a construction standard law, a fire preven- Electric Power Co. a written confirmation that it tion law, and a soot and smoke control law. In Oc- would not start constructing a scheduled thermal tober, two months prior to the conclusion of the electric power plant without obtaining the city's agreement, using referral opinions as a basis of ar- approval, and that it would freeze construction for gument, the city asked the MITI to guarantee the three years. enforcement of the pollution control measures against the EPDC and obtained a confirmation note Features of thepollution control agreement Un- from MMI. der the pollution control agreement of Yokohama, the city took initiatives in undertaking preventive Coontent of the agreement The agreement nu- pollution control measures with the support of the merically specified maximum pollution control mea- citizens' movement, while allowing companies to sures based on scientific data and findings, such as establish their factories on a selected basis."I don't present conditions and future prospects of air pol- intend to restrict industrialization. The issue is how lution, and in consideration of the level of pollution municipalities control incoming factories," said control technology available at that time. For ex- Mayor Asukata in a magazine interview at that time. ample, under a soot and smog regulation at that The Yokohama pollution control agreement was time, emission levels of sulfur dioxide at gas-pro- unique and different from the following two types ducing facilities and petroleum refining facilities in of pollution control measures, one taken inYokkaichi Yokohama had been set under 2,200 ppm. Under and the other in Mishima-Numazu. In the case of the new agreement, however, the emission level was Yokkaichi, pollution control measures were pursued reduced to 500 ppm, enforcing drastically stricter only after companies had established their facto- targets. The agreement also set detailed measures ries and started causing pollution. In the case of on air pollution control, including establishment of Mishima-Numazu, construction of factories was dust collectors, height of smokestacks, emission rejected through the strong citizens' movement. speed, exhaust fume temperature, and fuel quality, Because of its uniqueness, Yokohama Pollution as well as provisions for anti-noise measures. Agreement was called"Yokohama style"later. In order to determine the details of the agree- From the companies'point of view, there were ment, the city not only encouraged factories to par- several reasons for accepting the agreement. The ticipate in the experiments and/or to conduct their companies had no other alternatives but to sign the 32 Metropolitan Environmental Improvement Program agreement since the construction of the power fa- In 1965, however, when Tokyo Electric Power cility was based on a sales/purchases contract of Co. planned an expansion of a thermal electric land. The company thought it was necessary for its power plant, the company asked the city for an ad- sustainable business operation to comply with the visory opinion about its pollution abatement plans. residents'request. The company's decision was also The volume of sulfur oxide emissions from this ther- influenced by the MITI' s concem that MM's plan mal plant was the largest in the city, accounting for for future national power development might be 65 percent of total emissions. Taking this opportu- affected by the citizens' anti-pollution movements nity, the city concluded an environmental pollution if it ignored such movements. control agreement with the company. Under the agreement, the company was required to integrate Yokohama's pollution control agreement is con- smokestacks and to follow new emission standards. sidered a major breakthrough in the history of pol- A reason for the electric company to enter the vol- lution as no local government in Japan had power untary agreement is that to conclude such agree- to set its own pollution control standards at that time. ment was a necessary condition for the company to It should be said that theYokohama Mayor played a obtain an approval from the Electric Power Devel- great role in bringing about such breakthrough. opment Coordination Council. Pollution control agreements in early years Following this success, Yokohama signed an (1964-1970) environmental pollution control agreement with Asia Oil Co. in 1968.This agreement originated from Conclusion of the pollution control agreements the exchange of memorandum on"the agreement with newly-established factories Taking the on pollution control cooperation in connection with opportunity at the conclusion of the pollution con- factory expansions"between the company and the trol agreement with the Isogo Thermal Electric city in 1967 when the company requested permis- Power Plant of the Electric Power Development Co., sion for reclamation prior to the actual expansion the city signed another agreement with the follow- of facilities. ing three factories that were planned to be con- structed in Negishi and Honmoku by Nippon Oil The pollution control agreements with the ex- Co., Tokyo Gas Co., and Tokyo Electric Power Co. isting two factories were made based on preceding respectively. Noteworthy is that the city successfully memoranda instead of land sale/purchase contracts made Tokyo Electric Power Co. change the type of that had previously served as a basis for agreements plant from the one which uses crude petroleum to with new factories. The following factors attributed the one which uses only natural gas in view of re- to the successful agreements: First, companies ducing emission of sulfur oxides, which was at the trusted in Yokohama city that made pollution con- center of pollution debate at the time. trol agreements based upon the findings of scien- tific investigation in earlier cases. In addition, fol- Conclusion of agreements with existingfactories lowing escalating anti-pollution demands from the Early pollution control agreements after 1964 con- public, these companies came to realize that, in or- centrated on the emission control of mainly sulfur der to carry out steady business activities, it would oxides and dust fall of new factories planned to be be vital for them to obtain a consensus from local constructed. This implies thatYokohama gave little governments and residents when building or ex- attention at that time to effective measures against panding factories. Furthermore, Yokohama was existing polluting factories. blessed with a large consumer market adjacent to Chapter 3 33 the capital. As a port city, it was also endowed with The recommendations presented the following excellent conditions for the establishment of facto- pollution control measures in the existing industrial ries, which enabled the companies to pay off the zone: (i)development of a comprehensive system, costs for pollution control investment and to main- in which the city would establish principles of pol- tain industrial competitiveness.The fact that the city lution control measures and provide such services possessed virtual authority over matters such as the as evaluation, advice, and guidance in a consistent approval of industrial water supplies also contrib- manner (ii)making factories aware of their social re- uted to the success. Finally, economic conditions at sponsibilities in causing pollution; (iii)searching for that time also contributed to the negotiation of these strategies which would increase the possibility of agreements. During this high economic growth pe- obtaining companies' cooperation; (iv)establishment riod, companies invested actively. With favorable fi- of an organizational system in which companies' nancial and managerial conditions, these large com- efforts could be accurately evaluated. In addition, panies were able to make investments in the pollu- considering the extent to which the pollution con- tion control. trol measures would have an effect, the recommen- dations referred to the relationship between mu- Effectiveness In conclusion, these pollution con- nicipal measures and intermunicipal measures, con- trol agreements greatly contributed to the preven- sideration of long-term planning of the Keihin In- tion pollution aggravation in Negishi district. Ac- dustrial Zone and mutual cooperation with related cording to a projection in 1964, new factories sched- administrative bodies and research institutes. uled in Negishi and Honmoku were expected to emit 300 tons of sulfur oxides per day by 1970. Furthermore, the recommendations indicated Thanks to the pollution control agreements, how- a new approach by which the city would aggres- ever, the actual emission of sulfur oxides was about sively respond to water contamination and indus- 60 tons per day although there was a difference be- trial waste, in addition to air pollution which had tween the initial factory construction plan and what been the center of anti-pollution debate. has been actually constructed. Ambient air quality also improved following the worst peak in 1967. In the meantime, national attitudes toward pol- lution, as well as those of prefectures, had been dras- Pollution control agreements in the middle and tically changed. During a Diet meeting on pollu- later period (197o-1975) tion in 1970, more than fourteen laws and regula- tions were enacted or amended. In addition, under "Ten-Point Recommendations" by an academic the Pollution Control Law of Kanagawa Prefecture group and strengthening of national and prefec- which was newly established in 1971, the city's pol- tura! responses While the pollution generated by lution control authority over existing factories was new factories in Negishi district was successfully further strengthened. This Law authorized the city controlled to a satisfactory level, the Tsurumi- to conduct on-site investigations in all factories and Kanagawa district still was the most heavily polluted offices in the city, and to receive reports from them. area inYokohama in 1970. In order to promote pol- It also required companies to obtain mayoral ap- lution control measures in the existing industrial proval when establishing or modifying their facto- zone of the Tsurumi-Kanagawa district, the city ries and offices. commissioned an academic group to conduct an in- vestigation, and received its Ten-Point Recommen- With these events, pollution control agreements dations in 1970. continued evolving with amendments. 34 Metropolitan Environmental Improvement Program Amendmet tofthepollutioncontrolagreeenetts It tion and enacted in 1970, regulations over pollu- is common to amend pollution control agreements tion sources inYokohama were less strict than those when the factory planned an expansion or a change set by theYokohama pollution control agreements, in the original plan, in order to introduce new pol- and not sufficient to achieve environmental stan- lution control technologies and to set new standards dards. For example, sulfur dioxide concentration was based on the level of technologies (See Annex 2). set at K-value of 11.7 (maximum ground level con- centration 0.02 ppm). Taking advantage of flexibil- For example, sulfur dioxide emission standards ity in the pollution control agreements, Yokohama agreed upon between the city and EPDC was based further strengthened its pollution control measures on emission concentration, and was stricter than the against large-scale factories by restricting the level standard under the Soot and Smoke Regulation Law of sulfur in fuel, using kerosene and gas, and con- at that time. This standard based on emission con- verting the standard for sulfur oxides from a maxi- centration was transformed later to a new standard mum ground-level concentration standard to a com- based on landing density, regulating the entire vol- pound ground-level concentration standard. More- ume. Moreover, under an Environmental Pollution over, in order to stimulate factories' awareness of Control Law enacted in 1968, sulfur dioxide stan- social responsibility for pollution control, the city dards inYokohama were set at K-value of 20.4 (maxi- added to the agreement a new clause regarding the mum ground level concentration was 0.035 ppm per cessation of operations in the event of occurrence facility). However, under the Yokohama Environ- of pollution. mental Pollution Control Agreement of 1968, a maximum ground level concentration of sulfur di- Furthermore, the city also consulted with fac- oxide per facility was set below 0.01 ppm, enforcing tories located in the existing industrial zone over more advanced pollution control measures. water pollution control measures during negotia- tion and incorporated the results into the agree- Evolution of pollution control agreemnents Achieve- ments. The city began enforcing definite numeri- ment in Negishi and Honmoku by the early cal standards in 1972, when it reached a pollu- Yokohama-style pollution control agreements soon tion control agreement with Ajinomoto Co. In started to have an impact on the attitude of existing previous agreements, a water pollution control factories inTsurumi-Kanagawa in dealing with pol- item was limited to density of oil content con- lution. These factories started negotiating a pollu- tained in the effluent, except in the case of labo- tion control agreement, despite the fact that they ratory where more items are subject to standards. did not have a sale/purchase contract for land which However, after the agreement with Chiyoda had served as a basis for reaching agreements be- Chemical Engineering & Construction Co. (Labo- tween the city and newly establishing factories. ratory) in 1973, the city established a new clause Public opinion against pollution became so strong which set a concentration of Biochemical Oxygen that the factories tried to get public trust by reach- Demand (BOD) and Chemical Oxygen Demand ing a pollution control agreement with the city. It (COD) under 10 ppm. Moreover, the city intro- could be said that pollution control agreement be- duced another check, namely the ability of fish to came a process through which a factory as whole breed in drainage. would be accepted by the citizens and the city. Development of pollution control agreements Under the Basic Law for Environmental Pollu- and transformation into guidance and tion Control, amended in a Diet meeting on pollu- guidelines (after 1975) Chapter 3 35 Standardization of pollution control agreements guidelines. The content of pollution control agree- Until 1975, details of the pollution control agree- ments had been restricted by the level of pollution ments had been determined in accordance with the control technologies available at the time of mak- state of respective factories with which the agree- ing the agreements. As pollution control technolo- ments had been made, as well as pollution control gies developed, however, it became increasingly fea- technologies available at the time of agreement. By sible to apply uniform emission standards to most 1975, however, as a growing number of agreements factories. Furthermore, under guidelines, the city and amendments were concluded, some items could exercise more precise control and guidance started to commonly appear in their content. These than under prefectural ordinances. Guidelines in- items included evaluation and report, on-site in- cluded measures against sulfur oxides; soot and spection, cost bearing, prior consultation, public smoke; hydrocarbon material; nitrogen oxide; land disclosure, cessation of operations, and subsidence; factory noises; and domestic discharges reconsultation. Most of these became standard items to drainage, as well as directives on factory drain- in the agreements. This standardization was help- age and fish breeding. ful in eliminating impartiality that might possibly arise in the presence of non-standardized pollution There had also been resentment over unfair dis- control agreements, and in strengthening the city's tribution of the burden for pollution control mea- authority for pollution monitoring and for on-site sures among factories which reached agreements investigation, which was further strengthened by and those in the same industries which did not, as later amendments of relevant guidelines. well as among offices which received city's guid- ance through on-site inspections and those which Transformation to guidelines and directives Dur- did not. In order to ease this discontent, the city ing the mid-1970s, major companies implemented horizontally regulated companies under guidelines. pollution control measures based on the pollution con- The guidelines could also be established by the trol agreements. However, there remained problems mayor, and could therefore be introduced promptly concerning the small- and medium-sized enterprises and effectively. It is extremely important to note that in dealingwith pollution control measures.Theircom- there are no legal penalties for failing to observe pliance was necessary in order to meet the sulfur di- the guidelines. Companies always adhere to them, oxide standards of ambient air quality which were re- apart from the accidents, this being a uniquely Japa- vised in 1974. nese characteristic. With regard to small- and medium-sized en- In establishing the guidelines, the city followed terprises, enforcing pollution control measures by the procedure appropriate to the Yokohama-style individual agreement was not efficient because their pollution control agreement, i.e. establishing a ba- emission volume was relatively small although there sis of scientific data and having extensive consulta- were numerous such enterprises. In addition, as the tions with the target factories. For example, in or- contents of the agreements with large-scale enter- der to control sulfur dioxide and nitrogen oxide in prises became standardized, the city came to the the air, the city established regulations based on conclusion that similar measures could be taken for scientific models simulating entire city zones. With small-and medium-scale companies. Accordingly, regard to the guidance approach, the city tried to the city started to control the small-and medium- obtain a consensus from companies by holding re- scale companies, not under agreements, but under gional briefings. 36 Metropolitan Environmental Improvement Program Yokohama did not establish its own by-laws on cation of small and medium-sized companies un- pollution control regulations for several reasons. der Kanazawa Reclamation Project and Kanazawa During the period when the city was not allowed to Industrial Complex. establish regulations more stringent than the Basic Law for Environmental Pollution Control and the Reclamation projects in Yokohama prior to the Water Pollution Control Law, it used pollution con- Kanazawva reclamnation project The reclamation trol agreements, which are more stringent. After the of coastlines in Yokohama had started during the city was permitted to establish its own regulations, Edo period in areas which included Ishizaki, it did not need to do so because the Kanagawa pre- Kanagawa, and Takashima-cho. Today, these areas fectural govemment established regulations stricter are located in the center of the city, constituting the than the national ones, and Yokohama city could commercial district. During the Meiji period, recla- apply them. mation for industrial purposes began. The first ma- jor industrial reclamation was the 495 ha of recla- mation inTsurumi completed in 1931. By this time, Keihin Industrial Zone had been formed by reclaim- ing the major part of the coastline from Tokyo to anaaa Reclamatio rojec Kawasaki and Yokohama. By 1940, industrial out- Kandazn ral Re lation Projec put of the Keihin Industrial Zone had surpassed that and Industrial Relocation of Hanshin Industrial Zone, ranking first across The Kanazawa Reclamation Project had been for- Japan. mulated as a project under the Comprehensive Con- struction Plan of Yokohama International Port City Reclamation continued after the war in order of 1966. The goal of the project was more than just to promote the city's policy of industrialization. With building an industrial site or a port facility as in the the reclamation of 80 ha of industrial land in past.The ultimate goal was to reclaim land as a site Daikokucho in 1955, most of the land suitable for for redeveloping the downtown area and accom- reclamation inTsurumi-Kanagawa district had been modating small- and medium-sized factories scat- reclaimed. In order to foster economic growth at that tered around the city, thereby strengthening land time, the city started a large-scale 613 ha reclama- utilization and controlling pollution. tion project in Negishi Bay and attempted to pro- mote industrial development by inviting large-scale A strict control over large-scale companies was factories to locate there. Due to this reclamation, enforced under respective pollution control agree- however, resort beaches such as Isogo, Byobugaura, ments as stated before. This turned out to be effec- and Sugita, which had been located along the eight tive since these companies had possessed adequate km-long coastal line and enjoyed by theYokohama technological and economic capacity to take neces- citizens, disappeared. Another reclamation project sary measures. On the other hand, pollution con- began in 1963 in Honmoku district and was 340 ha trol of small- and medium-sized companies, which in size. It aimed at building sites for a wharf and were scattered throughout the city, was difficult to Honmoku-related industries. However, given the enforce, and their implementation lagged behind. strong public fear that the reclamation would ob- struct a view of the famous Japanese garden, This section discusses pollution control mea- Sankeien, about 11 ha of parks and green tract of sures achieved through the organization and relo- lands was arranged. Nevertheless, these green tracts Chapter 3 37 of land constituted only three percent of the total Local pollution caused by small- and medium- reclaimed land. sized companies in their neighborhoods became a serious problem. These companies had been estab- 'We can conclude that the major goal of coastal lished during the period when little attention was reclamation projects inYokohama was to build in- paid to urban planning, and they were located in dustrial sites and port facilities. As a result, the areas where residential buildings and factories were coastal area was formed as a place separated from mingled together. These small- and medium-sized the daily life of the citizens. factories faced the challenge of streamlining and modemizing production facilities and equipment Planning of Kaanazazwa reclamation project while preventing and controlling pollution mainly Kanazawa district inYokohama was located in the due to noise and vibration. However, there was a southernmost area of the city, and possessed the limit to the extent these issues could be solved at only natural coastline remaining in the city at that existing factory locations. time. Three fishery cooperatives possessed rights to fishing in this area. There were people who Accordingly, the city started to consider relo- made a living by seaweed farming, trawler net cating these companies to an appropriate area such fishing, net fishing, or pole-and-line fishing. as industrial complexes. By doing so, the city in- Around 1955, when the reclamation projects in tended to help promote industrial development by Daikokucho and Negishi Bay were being formu- rationalizing factory management through coopera- lated and implemented, a reclamation plan was tion and organization of small- and medium-sized also being formulated by private companies for companies, as well as by reforming and strength- Kanazawa area, which was the only reclaimable ening their management. This would also help the land left inYokohama. The goal was to utilize the city prevent and control pollution, as well as orga- area for industrial promotion during the high eco- nize and redevelop the city zone. nomic growth period at that time. The"Yokohama Basic Comprehensive Plan for Constructing an In- However, in order to obtain the concurrence ternational Port City"in 1957 also aimed at stimu- of small- and medium-sized factories located in lating industry through the Kanazawa reclama- the area where residential buildings and facto- tion. ries were mingled, the city had to provide them with incentives to relocate. The incentives in- However, during the decade following 1955, a cluded low relocation costs and an assurance that rapid increase in population, and a rapid expansion relocation sites would be provided with infrastruc- of industry resulted in unplanned city development, ture. Since it was almost impossible to secure an and destruction of farmlands and forests. As a re- inexpensive site suitable for large-scale industrial sult, residential buildings and factories mingled to- complexes in the inland of Yokohama, there was gether in the narrow, crowded city zone, causing no alternative but to reclaim coastal land in order environmental problems such as odor and noise. A to create sites suitable for relocating small- and dramatic increase in road traffic also caused serious medium-sized companies. problems such as air pollution, noise, and traffic jams. Use of the coastal areas to alleviate these wors- With the growing perception of the sea's role ening urban conditions was thought to be an obvi- in the natural environment and recreational use, the ous solution. city reviewed coastal development projects. From the mid-1960s, the value of the coastal areas in the 38 Metropolitan Environmental Improvement Program city began to be reexamined. More generally, the Project development Asukata administration in 1963 published the "White Paper on Citizen's Life", which emphasized The project moved into an important implementa- the balance between industrial development and the tion stage with the city council's resolution in 1968. quality of life of the citizens; and from this view- point, the White Paper said that policy for inviting Institutional structure The Kanazawa Reclama- large industries should be reexamined. tion Project inYokohama was implemented by in- volving many departments including the Planning Moreover, in October 1965, the publication en- and Coordination Division, Pollution Control Bu- titled A Future Yokohama Created by its Citizens fun- reau, Waste Incineration Bureau, Economic Bureau, damentally reexamined the"Comprehensive Basic Planting Bureau, Road Bureau, Sewerage Works Plan for Constructing aYokohama International Port Bureau, Water Works Bureau, City Development City" and gave a different orientation from the Bureau, and the Kanazawa ward. Steering and tech- former one specifically with regard to reclamation nical committees were organized and staffed by of- in the Tomioka/Kanazawa district. The old type of ficials of those departments. reclamation aimed at siting heavy chemical indus- try, while a new type of reclamation aimed at the Funding plan The city found it difficult to secure improvement of urban environmental conditions by financial sources since it could not expect to receive relocation factories located in the downtown. It also advanced income, such as deposits, which had been aimed at construction of recreation facilities that the paid by the newly established companies in the pre- citizens can enjoy along coastal line, an important vious reclamation projects for industrial sites. Of property for the public. The city had a sense of re- 41.3 billion yen required for the total project expense gret about the planned reclamation of Tomioka/ from 1968 to 1972, the city planned to finance 28.8 Kanazawa areas because the areas had natural billion yen of future investment by issuing bonds. coastal line which did not exist in any other places The rest was to be financed by the sale of the re- inYokohama. However, the reclamation with main claimed land upon completion. However, since the emphasis on the city's environmental improvements city could not finance such a large amount of funds was judged to bring about better overall results for by issuing domestic bonds alone, it also planned issu- the citizens in the end. ance of foreign bonds denominated in German marks. In 1966"Comprehensive Construction Plan of Settingthesellingpriceforreclaimedland Origi- theYokohama International Port City"was prepared. nally,Yokohama planned to sell reclaimed land at a This plan combined the city's infrastructure devel- constant unit price throughout the whole Kanazawa opment plan and welfare plan. area. The selling price was to be based on the cost of reclamation, including all construction costs, in- As a part of the"Comprehensive Construction cluding the sea park. However, such a policy turned Plan of the Yokohama International Port City", out to be unprofitable, due to delays in granting rec- Kanazawa Reclamation Project was formulated aim- lamation licenses and soaring construction costs. ing at both solving urban issues and promoting in- The city, therefore, introduced a pricing formula dustrial development. This was a new approach be- which took account of inflation. cause in the previous time, sea reclamation in Yokohama aimed at industrial development alone Specifically, Yokohama established an initial by inviting large industries. sales price in October 1975; the price of industrial Chapter 3 39 sites being 48,000 yen/m2 in the second half of 1975. three sections: 1) a wood industry and shipyard site, Thereafter, the city increased prices at a rate of 4.4% 2) wholesale and transportation industry site and per year. By 1978, therefore, the price of an indus- 3) a manufacturing. Kanazawa Industrial Complex trial site was 53,300 yen/m2. It meant that the unit is one of the largest industrial parks in Japan. There sales price (160,000 to 200,000 yen/tsubo' ) had al- are presently about 400 enterprises in the Kanazawa most doubled from the original estimate of about industrial park. 100,000 yen/tsubo at the beginning of the plan in 1971. Although this price was still less than the av- The public facility site was used for building erage price (210,000 yen/tsubo) of "Ha' district in schools, bicycle roads, and pedestrian roads, and the Negishi reclaimed land which had come into also for a sewage treatment plant, an incineration the market a little earlier, there was considerable plant, loading area, and a heliport. doubts as to whether the targeted small- and me- dium-sized businesses could afford to relocate. The Significance of the Kanazawa reclamation project city therefore reduced taxes for the factories con- in environmental conservation The reclamation cemed over a limited period, exempting them from project was formulated with careful consideration property tax, corporation tax, and the special land- of environmental aspects and urban planning. In holding tax. determining land utilization and segmentation, the city secured about 10% of total reclaimed land for Utilization of reclaimed land building a seaside park, a park on the original coast- line, and green buffer zones, developed an urban The total area of land reclaimed in the Kanazawa redevelopment site equipped with anti-pollution fa- reclamation project is 660 ha. With regard to land cilities and equipment, and secured sites for resi- utilization, 258 ha are used as industrial sites, 253 dential buildings and public facilities. ha for public facilities, 82 ha as residential sites, 67 ha as a sea park site. The residential site is sepa- Pollution control measures through rated from the industrial site by a national road run- organization and rearrangement of small- and ning north-south in the center of the reclaimed land. medium-sized companies in the Kanazawa A 50m-wide green tract of land was also constructed Industrial Complex as a buffer zone along the national road. This buffer zone was constructed by the city using a loan pro- Relocation to the Kanazawa Industrial Complex, as vided by the Japan Environment Corporation. Trees well as organizing and rationalizing small- and were planted in the buffer zone to block out the sight medium-sized companies, were the first major ef- of traffic, reduce noise, and clean the air. It divides forts to solve factory/residence mixture problems the reclaimed land into two sites: the residential and and to strengthen their company management- the industrial sites. although the city had a similar experience of recla- mation and industrial relocation in much smaller The residential site was used for building 10,000 scale before this major effort. During implementa- housing units for employees of the factories which tion, the city conducted a detailed investigation had been scheduled for construction on the indus- about factories, and tried to strengthen the man- trial site. agement basis of small- and medium-sized com- panies by improving their organization, simulta- The Kanazawa industrial site (258 ha) that can neously paying careful attention to pollution con- accommodate about 600 enterprises is divided into trol measures at the relocation site. 40 Metropolitan Environmental Improvement Program Process offactory relocation panies applied in total, only 40% of the factories which required relocation actually registered. Registration, relocation plannting, and guidance About 10% of the factories that desired reloca- Since available space for industrial relocation in the tion did not eventually register due to a lack of reclaimed area was limited, the city had to set criteria relocation funds or a fear of losing customers to prioritize the districts from which factories should through relocation. be moved. Criteria included the need for a complete rehabilitation and reconstruction of a particular area Process of transfer In 1979, the city publicly invited rather than a piecemeal approach, disaster prevention factories to transfer to Kanazawa Industrial Complex planning and the presence of residences and indus- and received applications from 462 companies. The tries located in dose proximity to each other. city then investigated the companies which applied for land in light of a number of criteria, including fi- In order to better understand the actual situa- nancial capacity, the pollution associated with their tion of the companies considered for relocation, the factory operations, and the environmental condition city investigated the factories that should be relo- of their existing neighborhoods. The decision on cated from viewpoint of pollution control. Based on whether to permit or reject factories was examined by the results of this investigation, the city selected facto- the Council on Selection of Relocating Companies, cre- ries to be relocated, and then encouraged the process. ated under a city ordinance. Following this, 372 com- panies from various manufacturing industries were Types of pollution caused by pre-relocating fac- selected. Figure 3-1 shows the breakdown of 372 com- tories are as follows: panies by type of business. Considering the fact that many of them were already located near the Karazawa (1) Noise and vibration associated with press and Industrial Complex, factors such as the proximity of rolling operations (about 60% of the relocating the factories to their customers seemed to play a ma- factories); jor role in the selection. (2) Odor and dust particles caused by painting and As shown in Table 3-1, 372 enterprises actu- metalworking (about 30%); ally relocated themselves to the Kanazawa Indus- trial Park, 81% of enterprises that applied for re- (3) Effluent-related pollution associated with location in 1979. Of the 372 enterprises th,at ac- washing of oil drums, plating, and food pro- tually relocated, 108 enterprises (29% of 372) had cessing (the remaining 10%). been identified by the City as requiring reloca- tion, and the remaining 264 enterprises (71 % of About 50% of the incoming factories were origi- 372) relocated though not identified by the City nally located in residential areas, 40% in industrial/ as requiring relocation. residential mixed areas, and the remaining 10% in commercial areas. There were 108 enterprises (38% of 28'5) that had been identified by the City as requiring reloca- Based on the results of this investigation, the tion. The difference, 177 enterprises (285 - 108) did city conducted a registration of factories which not relocate though identified by the City as requir- desired relocation to the Kanazawa Industrial ing relocation. Reasons for the 177 enterprises not Complex, including those which the city had tar- having relocated though recommended by the City geted for investigation. In 1977, while 497 com- are listed as follows: Chapter 3 41 Figure 3-1: Breakdown of Ce'rami cs 1 . 3 Others theRelocated ~~~~Text ilIe 3. 1 4. 5 Companies Wooden Furniture X ) I byType of K Bsns existing locations:27Printing 3 f6 cilties 4)~ ~ ~ ~ ~ev Reloate Macthehplneser Recycle Res5 twn of int Enterprises Foodstuff Type of Smlusd e 6. 29Rw 9') Cnstructlion/ ,j/ 1) Could not determine to relocate: 68 actions among participating companies are in- 2) Lack of fund for relocation: 37 creased; and 3) investments can be reduced by hay- 3) Took pollution control measures on ing common facilities such as common effluent the existing locations: 27 treatment facilities. 4) Relocated to other places: 23 5) Judged later by the City as not Initially, parrticipating firms were classified into requiring relocation: 15 twenty groups by type of industry, but eventually in 6) Out of business: 7 fifteen groups after integration and coordination. Total: 177 The Funds for Advancement of Small and- Me- Guiidaince on organization Taking advantage of dium-Sized Companies were used for a group of factory relocation, the city tried to reform and ratio- medium-sized companies for construction of a de- nalize the management of small- and medium-sized tached industrial complex, based on the factory col- factories by promoting collective and cooperative lectivization project; for a group of small-sized fac- actions, as well as improving organization in the fac- tories, and for construction of a factory apartment tories themselves. The creation of the collective with a view based on the factory cooperation project. management system has the following advantages: For the remaining seven organizations, a coopera- 1) govemment low-interest loans are made avail- tive factory was constructed, assisted by the Japan able for this purpose; 2) sales and purchase trans- Environment Corporation. 42 Metropolitan Environmental Improvement Program \Numnber of Enterprises a. Enterprises applied for relocation (1979) 462 Table 3-1 b. Enterprises actually relocated (1979) 372 (b/a = 81 %) Number of c. Enterprises identified by the City as requiring relocation and 108 (c/b = 29 %) Enterprises applied for relocation (e - d) (1977) (c/e = 38 %) in connection d. Enterprises identified by the City as requiring relocation, but did not apply 177 with for relocation (e - c) (1977) (d/e 62 %) Relocation e. Enterprises identified by the City as requiring relocation (c+d) (1977) 285 f. Enterprises not identified by the City as requiring relocation but actually relocated (b - c) (1977) 264 (f/b = 71 %) Financing and assistance with relocation as neighborhood pollution. Nevertheless, in or- der to prevent secondary pollution in their new For companies relocating their factories, securing neighborhopds, the companies took the follow- funds became the most critical issue, since a large ing pollution control measures after relocation: amount of funds was needed to finance various ac- arrangement of factory location within the indus- tivities including obtaining factory sites, construct- trial complexes, and establishment of common ing factories, landscaping, and establishing pollu- treatment facilities, as well as individual mea- tion control facilities and equipment. These reloca- sures, within the factories. tion expenses imposed a particularly heavy burden on small and medium-sized factories which were Arrangenment of factory locations within the facing recession after the first oil shock. comnplex. In planning factory locations within the industrial complex, the city designated zones based In order to encourage relocation,Yokohama in- on type of industry. After locating light industries troduced long-term, low-interest public funds, gave close to residential sites, the city located general preferential tax treatment, and promoted advance- manufacturing industries, followed by industries ment and collectivization of the small- and medium- causing loud noise and odor in the section near the sized factories involved in the relocation. seashore, far away from the residential site. In or- der to alleviate environmental impacts on the neigh- The city not only actively utilized govemmental boring area, measures were also taken to arrange financial systems, such as the Fund for Advancement the location and the combination of buildings. of Small- and Medium-Sized Factories and funds from Japan Environment Corporation, but also provided In addition, the city grouped together factories loans for companies which did not qualify for govem- which would use common treatment facilities. These mental funds. In addition, the city subsidized a part of grouped factories were located near the common loan interest to be paid by companies as noted earlier. facilities to make economical piping arrangements. The city also gave tax breaks over a limited period in Furthermore, measures were taken to maintain connection with property tax, the special land hold- amenity by preserving the landscape within the in- ing tax, and the corporation tax. dustrial complex and by establishing green buffer zones along public roads and coastlines. Pollution control measures Collective wastewater pretreati7nen tfacilities A Companies were relocated to the Kanazawa In- form of pollution caused by factories in areas where dustrial Complex in order to solve problems such they were in close proximity to residences was ef- Chapter 3 43 fluent containing hazardous substances which was Maintenance and management services of the discharged from small- and medium-sized compa- facility are provided by the water and sewage de- nies in the fields of press dyeing, dyeing, surface partment of theYokohama city. Centralization of fac- treatment, and plating. While the number of these tory effluent treatment enabled the city to efficiently incidents was not large, the city had been encour- monitor and guide companies. Maintenance and aging small- and medium-sized companies to main- management expenses consist of the costs of labor, tain and manage hazard-removing facilities within chemical supplies, repairs, and electricity. Annual each factory through visits and guidance. However, operation/maintenance expenses are about 0.16 bil- it was not only inefficient for the city but also it was lion yen in 1991, and paid fully by user companies. difficult for the small- and medium-sized compa- Cost-sharing among users is determined by a for- nies that lacked economic and technological capaci- mula which includes the contract volume of efflu- ties to maintain and upgrade hazard-removing fa- ent, the actual volume, and effluent density. The cost cilities to meet discharge standards, which became per factory ranges from 0.8 to 40 million yen/year. more and more stringent. More than ten years have now passed since the Accordingly, the city decided to locate some collective pretreatment facility was constructed. Re- small- and medium-sized companies in special sec- pair costs began to increase significantly in recentyears, tions of the Kanazawa Industrial Complex, and let and the facility has required partial replacement. Full- them discharge effluent to collective treatment sys- scale replacement will become necessary in the future, tem after each factory removed specified hazardous and this will be an extremely costly exercise. substances. Pollution control measures for individual To have collective treatment facility is much factories In order to prevent the Kanazawa In- more economical than the case where each fac- dustrial Complex from becoming a new pollution. tory has own individual treatment facilities be- source, besides taking prevention and control mea- cause the former requires less space for facility sures under the regulations targeted at individual installation and less operation/management costs. factories, the city required the following pollution The collective pretreatment facilities treat the fol- control measures and facilities, as a condition for lowing five types of substances: high-density cy- their relocation: anogen, low-density cyanogen, chrome, acid, al- kali, press dyeing, and dyeing. After removing * Industrial heat sources were limited to elec- hazardous substances, waste is discharged into tricity or gas; the public sewerage system. Sludge, which is pro- duced during the treatment process, is also * Thecityestablishedminimumstandards,such treated. Currently, thirty two companies use the as limiting types of building structures and collective pretreatment facility. Although materials to reinforced concrete, concrete Yokohama city actually built these facilities, nec- blocks,andsteel-frameslatesinordertocombat essary expenses were borne by user companies. noise and vibration-related pollution, mainly caused by metal processing industries such as The Japan Environment Corporation provided 30- forging and pressing, and by transportation; year loans (nornally such loans are for 20 years) to the companies for construction costs, and the city paid * The city required construction and recycling a part of interest to ease companies'financial burden. industries to construct buildings on more 44 Metropolitan Environmental Improvement Program than 30% of the factory site, and, as a gen- among residents over the utilization of vacated land. eral rule, prohibited outdoor work; Some of the sites were purchased to construct pub- lic facilities such as parks. Companies were required to plant trees on more than io% of the factory site (13% for In utilizing the vacated sites, the city established factories of which sites larger than 1,ooo m2). a Managing Committee for Vacated Sites of the Kanazawa Relocating Companies, as well as a Further, with respect to the above pollution con- Special Inter-Departmental Committee for Controls trol measures, the city required the companies to of Utilization ofVacated Sites.This facilitated smooth submit a planning document, which facilitated the guidance and control over purchases of vacated sites enforcement of comprehensive pollution control and private development. measures. It also required pre-consultation by each company planning relocation and establishment, so that companies could not apply for a construction permission without consulting the city. Relationship Between .. . . ~~~~Enviroinment and the Economy Utilization of vacated sites Yokohama either E purchased the vacated sites from the relocating fac- in Yokohama tories and constructed public facilities, or concluded This section addresses the relation between economic agreements with the companies on the utilization development and the environment in Yokohama in of the vacated sites. In the latter case companies recent years. Fig.3-2 shows a trend of industrial out- were required to have prior consultation regarding put (expressed in terms of value added) and of am- their disposition, thereby controlling the future uses bient SOx concentration. The trends of energy con- of the sites. Active discussions were sometimes held sumption and SOx emission load are shown in Environmental Concentration Industrial Output Figure3-2 (mg-SO3/100cm2Id) (100 billion yen) SCx 1. 2 1 2 0 Concentration ^ / ~ \ . . and l . o ......... ......... ....................................... ......... :..................... .... .................................... . .. ................ . ...... . I o 0I d u st \\ 1. ~~~~~~~~~~~~output Envir,onmental, Concentration . (Value Added), 1960-90 0. 6 . ........... .... . _ _ _ . ... .. 60 . ~~~~~~,_- Inadustrial Oitput ° ' 4 -'''''''-'-''-.... ...... .................... .o ...... ..''' -'''-' '''7.... ... . ....................... .. -'''''-..................'--''--'- ----------'''---7-*'-'--'-- 40° 0.4 .o . .. . .. ,= ..... . ........ ... .--....... 20 0 0 60 65 70 75 80 85 90(Yr) Chapter 3 45 Figure 3-3: Heavy Oil Conversion (thousand kl/yr) Fuel Consumption 6 H , 000[ byType, V// g as 1960-90 5. 0 0 ................... 00..............(Yr liquid 2, 0 060 65-70 75x 80.. 85 9ty 1st Coal1.-Bur-a ...... _ Ining Poer Gnsutrideli orea . E ~ ~ ~ ~ ~Ui Opesiation Started '0okohama, ~ ~ ~ ~ ~~ Tky Elcti -o- Stre it Operatio ooata 1960 1st .oal-Burning )linarni-Yokohaa Thermoelectric Power0 lant Emissions in .~~~~~~~~~~~~~~~~~~.. ~~~~~ Kinner 1ndusutriaLArea~~~~~~~~~~~~~~~~~.......... 60 60 70 . 75 80Inds90ire |~~~~~s Regul-BurnngLw I Power I Guideline s for SOxOadoo Unlti Oprtonto Stre o| Elect|(reaide Collutarte Eitsio Operuation) o |~~~~~~~~~s Coasogoin MiaThYloam ermoelectric||I * Powero otolAreetwihNX(aa Plant) L Power Unnt|It *ArPluio oto a Figure~~~~~ ~ ~~~~~~ 3*4 Soluxo Emissio Loadnn (thosah toyoElyrirC. Emissions inn .In-----Em TerndusutrialP.Arean N Yokohama, *~e PluinCnrlArentwt ooEeci,Co.,ooastalTemeeti oe ln LG _ ' 1960-Metropoli06n E 75 80 Ordinance on * A~~-'isirg PoatlltoCntlLa Pollution Control I (AreawIndeuolutralt Aeaiso euain 6 olto Coto0eiino i olto oto Agreoet an th (aSxpnmnofMaosAuhriis • songaw Phrmefecturic aoltinC ntro Agremet wiuthermea JapnuSeel POwrd Plante on Air Pollution Control Law PollutionConPolutiorConrolAgreement willthn Foisson Regtulation) Isogo Thermo-amjYoohmaThrmelectric Powlto oto g ermn PlathNK (Japn Stel Pollution Control Agreement with Tokyo Electric,Co.,Yokohama Thermoelectric Power Plant (LNG) 46 Metropolitan Environmental Improvement Program Figure 3-5: Location of Industrial Area -\? V $ Tokyo Bay O~ Inner Inidustrial Area E New Coastal Industrial Area £1Existing Coastal Industrial Area (The above three areas constitiute the entire administrative area of Yokolhama.) Fig.3-3 and Fig.3-4 respectively. Relation between lation between industrial output and ambient con- those environmental indicators and industrial out- centration of SOx. Since concentration of SOx var- put (value added) is shown in Fig.3-6, 3-7 and 3-8. ies by location of monitoring station and by weather conditions, the correlation in Figure 3-6 is less sig- Economic and environmental indicators nificant than that between actual emissions and in- dustrial value added. From 1960 to 1965, the corre- Relation between industrial output (value added) lation was basically positive; as industrial value and SOx concentration Figure 3-6 shows the re- added increased, the concentration of SOx also in- Chapter 3 47 creased. Since 1968, although industrial value added Relationt betwveen industrial value added and en- continued to increase, the concentration of SOx de- ergy contsumnption Figure 3-8 depicts the relation creased. This reflected the impact of SOx counter- between industrial value added and energy con- measures. Conversion of SOx to low sulfur fuel, as sumption. In the high economic growth period from well as the use of taller stacks contributed to the 1961 through the mid-1970s, the correlation was lowering of the SOx concentration. positive; as output value increased, energy con- sumption also increased but at a slower rate. Relation between industrial value added and SOx emissions Figure 3-7 presents the relation Since the latter half of the 1970s, industrial value between industrial value added and SOx emissions. added has continued to increase, but energy con- Fronm 1960 to 1968, as industrial value added sumption has actually declined.The second oil shock increased, so did the emissions of SOx. The of 1979 brought about a significant decrease in en- correlation is more positive than that for ambient ergy consumption. Consumption of energy in 1982 values. Following the peak of SOx emission in 1968, was approximately 20% less than that consumed in it started decreasing though the economic growth 1979. While the energy conservation and the effi- continued. The use of low sulfur fuel is the major ciency improvement has been a major explanation reason for the dramatic decrease in the SOx of this trend, changes in industrial structure, includ- emission. ing the growth in importance of less energy-inten- Figure 3-6: Environmental Concentration Industrial (Mg-SO3 /100cm2 /d) Value Added 1.2 . 6 and SOx Concentration, 1960-80 1.0. .. - - - . - - ..-.- .... .. .64 69 70 0.8 , . - 71 0.6 .. 6 ................. .72 - .. . - - 73 0. 4..- . 0 . 4 ................... .. ............ . ..... .... ........................... ............ ...... ... ............ ...... ..... 75 74 76 78 0.2 80 77 79 0 10.0 20.0 30.0 40.0 S0.0 60.0 Industrial Value Added (100 billion yen) 48 Metropolitan Environmental Improvement Program SO. Emission Figure 3-7: (thousand t/yr) SOx 110 Enmssions . 68 . . and Industrial 10t0 oo~ ~ q - ~-- ~-- - -.-.-- - ...r - ---6---- --- - 69 ..... _ Value Added, 1960-80 s o ... ........ .. -.- . 7. ... .......... ............... .. . .... ... 6 0 .............. ... ......... ..... . --- -6 . ............... ..... .- - . .... .... .... ......... ................. 5 0 . ...... .......... ... ...... ...... .. ... ....... .. ........ ... .. ............... s o ... .. ... ..... ........................ ... ..... . . ... . ......... ........ .... ...... . .... 900 . .-* / .70 74 72 40 20 -......... o0 _* .-. - -- 7&5R 78-79.80 0 10 20 30 40 50 60 Industrial Value Added (100 billion yen) sive industry, has also contributed to the trend. Cur- in the second period being almost 0.2-0.3 mg/day! rently, total energy consumption in Yokohama ap- 100 cm2 lower than that in the earlier one. How- pears to be fairly constant, or increasing very slightly ever, actual emission levels were the same in both from year to year. Annual energy consumption periods. The explanation for this is that ambient (measured in terms of heavy oil) is currently about quality, as measured by monitoring stations on the 1 million kilo liter/year less than that in the peak ground appeared to improve due to the introduc- year of 1972. tion of taller stacks.This brought ab.out an improve- ment in local air quality that apparently was greater Relation between SOx emissions and amnbient than any additional background SOx pollution origi- contcentration. Figure 3-9 shows the relation be- nating in neighboring cities such as Tokyo and tween SOx emissions and ambient concentration Kawasaki. To make a judgment about trends in am- of SOx. Two distinct periods may be observed. In bient quality, a regional rather than a city-wide ap- 1960-67, ambient concentration increased rapidly proach must obviously be used. but subsequently declined. Ambient concentration Endnotes 1. One"tsubo"= 3.945 sq. yards Chapter 3 49 Figure 3-8: Energy Consumption (Heavy Oil Conversion) Vndusteal (thousand kl/yr) and Energy .71 72 73 78 Consumptior 6, 000.4 1960-80 . . .77 7 5. 000.. ....... 7.... ..............--..- 80 4, 0 00 .... ... . . . .. . ..69 3,.000 X. - * ~~~67 ;66 2 , 0 0 ........ ... ...- ....... .. .... ..6 2 6 3 ...... ......................... ...... ............ . ... ..................... 61 6 60 1.000 .' o0 . ,''. . ,. . . . . . . . . . . . . . . . . . . . . . .. 0 10 20 30 40 50 60 Industrial Value Added (100 billion yen) Figure 3-9: SOx Environmental Concentration Emission and (Mg-S03/1OOcm2/d) Environmental 1. 2 Concentration, 62 6 67 68 1960-80 1960-80~~~~~~~~~~~~~~~~~~~~ ... . .. . .. . . . . . . .... . ................ . . ........... .. . . . . . . . . . . . . . . . . . .. . . .. . . . . . . . . . .. .0 64 65 t 7 63 :69 06...................7.......... 7 0_ o. 8 .... .......... ... ........... ................... .......... ..... .............. .......... .777 027 6... . . . . . . .. .. .. . ..... .... ...... 80 - 9 ...... . ............... 0 10 .0 20.0 30.0 40.0 50.0 60.0 70.0 80.0 90.0 100. 0 110. 0 SO . Emission (thousand t/yr) 50 Metropolitan Environmental Improvement Program Chapter Four: Environmental Protection Measures In the Private Sector This chapter focuses on environmental protection Soot and Smoke Regulation Law, the standard of measures taken by the private sector inYokohama. 500 ppm established in the Yokohama Pollution Four examples are presented. These are large scale Control Agreement was extremely stringent. Since business establishments in electricity (coal-fired 1968, K-value regulation has been adopted in the electric power plant), chemical industry Air Pollution Control Law. It should be noted that, (acrylonitrilo production), food industry (food oil in general, the application of K-value regulation and production), and a medium-sized business estab- dilute dispersion made it possible for factories hav- lishment in the electronics industry (electronic parts ing high stacks to comply with the K-value regula- plating). The first two firms (electric power com- tion even with more SOx emissions. pany and chemical company) have pollution con- trol agreements, which have been an important fea- Installation of Stack Gas Desulfurization ture of Yokohama's environmental history. The elec- Equipment tronic parts manufacturer relocated itself to the Kanazawa Industrial Park described in Chapter 3. The power plant installed stack gas desulfurization The food processing firm reduced its emission of equipment and started its operation in March, 1975. waste by improving its production process instead The plant adopted the wet limestone-plaster of installing new treatment equipment. It also in- method for desulfurization, which treated all ex- troduced energy and labor saving measures based haust gas discharged from the plant. upon its own cost-benefit analysis. Reasonsfor taking measures There were a num- ber of reasons why the company took these mea- sures. The main external factor was growing con- cern and pressure for strengthening of pollution Power Generation: Coal-Fired regulation at the national level. There were a num- Electric Power Plant ber of internal factors as well. Located in a large city, the company was concerned about its social This power plant is the first plant in Japan that made responsibility to provide pollution control measures. a pollution control agreement with the city in 1964. Moreover, subsidies for installing stack gas desulfu- Major SOx countermeasures include the use of low rization equipment - a new technology that could SOx coal and installation of stack gas desulfuriza- treat exhaust gas from coal-fired power plants - tion equipment. were provided by the national government in view of the promotion of use of domestic coals. Use of Low-sulfur Coal Effect of measures The positive effects of these SOx countermeasures, from the start of operations measures were as follows: 1) the plant was able to in May 1967 to 1975, have depended upon the use meet the SOx emission standard set out in the of low-sulfur coal. Figure 4-1 shows the shift in a Agreement; 2) it helped to meet domestic fuel sup- sulfur content ratio, and emission standards for ply needs and also made possible to control pollu- burned coal under the Soot and Smoke Regulation tion even with the use of high sulfur coal, thereby Law, Air Pollution Control Law, theYokohama Pol- alleviating the overall fuel supply problem; 3) des- lution Control Agreement, and the Yokohama ulfurization also reduced the emission of soot and Guidelines for SOx countermeasures. Compared dust; 4) it produced a useful, by-product, plaster. with the earlier standard of 2,200 ppm under the As Figure 4-1 indicates, the sulfur content of coal Chapter 4 51 was C'.29% before the installation of the stack gas desulftrization equipment. However, it became pos- Chemical Industry sible to use coals of 0.6% sulfur content (this is a maxirnum; generally it is 0.4%) after the installa- This is the case where a large-scale chemical manu- tion of the stack gas desulfurization equipment. On facturer producing various kinds of chemical prod- the negative side, use of the equipment contributed ucts took water pollution countermeasures, includ- to water pollution: waste water with high COD loads ing both modification of its production process as was generated. It was also costly to install and op- well as investment in an effluent treatment facility. erate, resulting in higher electricity bills. Although the company entered a pollution control Figure 4-1: Enactment of Air Pollution Control Law Change in SOx Concentration Source SOx (ppm) Regulation of Total Emissions Emissions Disignation of Area at the Coal- under the Soot and Stricter K-value fired Power Smoke Regulation Law Regulation Plant, 1962-78 Sulfur Content 2.0 0 0 ....... 09 2,..... .o ..... ... ............. ... .......... .............. ......... ............... ........ ........... .... .. ............. ... ... Emission Standard under! ,Emission Standard under, the Soot.and,Smoke ! the Air Pollution Control Law Regulation.Law ! 1. 5 00 Standard...... content..... 0.6 1. 50 ..................................... ..........._ '.... . .. ................ .............. .............. ..........j ._._....O.6 . . . , . . .. ~Sulfur Content / . Enissior. Standard,.__ .,.i. under, the Pollution . . 1.000 - control-Agreement ........ ............ ..-..,. o 3 Stack Gas 'Desulfuriza tion 1st MLachine Operation ' Facility 5 00 -___--- --- Actual Emission Concentration , -.. 0- -0.3 62 64 66 68 70 72 74 76 78 1 t t (Yr) Pollution Control Revision of / Further Revision Agreement the Agreement of the Agreement (Desulfurization) Yokohama Gidelines for SOx Countermeasures 52 Metropolitan Environmental Improvement Program Figure 4-2: External Factors Internal Factors Factors Leading to . - ~~~~~~~~~~~~~~~~~~~~~~~the Leegalleatory Managerial tai Clear direction for stricter regulation on * Corporate responsibility (corporations Installasonof pollution located in large cities) Stack Gas * Guidelines for SOx countermeasures in Technical Desulfurizon Yokohama * From the beginning of the 1970s, the Equipment in * Revision and reinforcement of the technical development of desulfurization a Coal Fired Pollution Control Agreement equipment, which can treat all exhaust Power Plant, * Air Pollution Control Law - gas from the coal-fired thermal power andItsEffects reinforcement of K-value regulation plant, began. * Air Pollution Control Law - an Economic introduction of the regulation of total * The government provided subsidy for emission installing stack gas desulfurization Socio-Economic according to the 5th national coal policy. * National policy for promotion of use of domestic coal Technical * In the early 1970s, desulfurization equipment which could treat all exhaust gas from heavy oil thermal power plants was introduced. ___ _ Installation of stack gas desulfurizationequipmentl Positive Effects Negative Effects Technical Economic Effect * The migratory restriction in fuel supply * Investment and operating costs of the (The use of mixed coal with a relatively equipment led to higher prices for high content of sulfur became possible.) electricity * The reduction of soot and dust emission Other Pollution due to the equipment * Drainage with persistently high COD Economic was discharged * 100% use of plaster (by-product) for cement matenial * A decrease in the contribution for the S coutereasresfo Pollution Health Damage Compensation Sdrcir countrerrneasures for Prevention Association ._drainage treatment__ Other * Technological accumulation - later, it helped in overseas technological cooperation Chapter 4 53 agreement with the city, the agreement, merely about 100,000 m3/d at the end of the 1960s. Cool- meant a goal for the company to be achieved in- ingwater accountedformore than90%, the remain- stead of regulations to be imposed. der being used for boilers, materials, washing, and personal use. Effluent were largely of two types: The chemical plant began its operation in 1936 as a fertilizer factory, producing ammonia, sulfuric acid, * Highly concentrated acrylonitrile effluent am:monium sulfate, urea, and acrylonitrilo. It currently Acrylonitrile was produced by an ammonia oxi- produces dry ice, methylamine, acrylamide, and other dation method that a catalyst oxidized ammo- products. In the latter half of the 1960s, air pollution nia and then synthesized propylene. As a side and water pollution caused by the plant became in- reaction, cyanogen was produced. Highly con- creasingly serious. This plant used to emit such pol- centrated acrylonitrile effluent was a dark brown lutants as SOx from various sources, as well as a sul- effluent with a pH value of 7-8, and contained fide ore, calcinar, nitrogen oxides from the production about 1,000 ppm cyanogen. The company did of sulfuric acid, and offensive odors from organic syn- not treat it in the factory, but dumped it into thetic compounds. In the early 1970s, the plant was the ocean once a month (equivalent to 500m3/ restiuctured; this restructuring involved the disman- d). The cost to the firm of ocean dumping was tling of the ammonia and related facilities and ten about 0.1 billion yen per year. boilers, which were used for air separation, ammonia synthesis, and fertilizer production, were gradually * Effluent from ordinary processes phased out. The need for air poNlution control coun- Polluted waste water from processing of mate- termeasures was then significantly reduced. However, rials and direct cooling were discharged into the water pollution due to factory effluents containing cy- sea after it being treated by coagulation, sedi- anogen and originating from acrylonitrilo production, mentation, and filtration. a major product of the company, continued to create a problem. The next section describes environmental In the early 1970s, when pollution regulations control measures taken by the company to address became stricter, the City of Yokohama introduced this problem. emission/effluent control guidelines for air and water, and the company then took various mea- Measures to Reduce Effluent Load sures, including improved processes, and instal- lation of effluent treatment equipment. Moreover, Reason for taking measutres Although the plant after several discussions with the city, the com- continued to expand its capacity, it did not for sev- pany entered a pollution control agreement in eral years expand its pollution control facilities at January, 1974. the same rate. Waste water treatment was unsys- tematic. For example, it had six drainage channels Prior to the pollution agreement, the company in 27ha sites, but discharged cooling water, rain wa- had treated highly concentrated acrylonitrile efflu- ter, and polluted effluent together. Many factories ent in its treatment facility. The volume of effluent operating in the coastal district were not even aware from ordinary processes was 15,000 m31d, its COD of the pollution they were causing since effluents being 270ppm after treatment, the effluent load of were diluted in a large volume of sea water. COD was 4t/d. Since the effluent standard for this plant was set at COD 60ppm by Kanagawa Prefec- The plant used public water, industrial water, tural Ordinance, waste water was diluted by sea and sea water. The total volume of water used was water before its discharge. 54 Metropolitan Environmental Improvement Program The contents of the agreement were: 1) reduc- The reduction of effluent load by 99% suggests tion of the COD effluent load from 4t/d to less than that the pollution control agreement was extremely 40 kg/d (i.e. a 99% reduction); 2) separate use of strict. However, this figure was not an immediate tar- drainage channels for rain water/cooling water and get, but a future goal. It was immediately possible to polluted water; 3) unification of the drainage chan- reduce effluent to about 1/4, i.e. 4,000 m3/d. Also, to nels and drainage exits; and 4) substitution of indi- keep effluent concentration at the level of lOppm by rect for direct use of cooling water, and water re- treatment was the basis for achieving a 40kg/d efflu- duction and recycling measures. ent load. An effluent concentration of 10 ppm was in- Effluent Volume (thousand t/day) Figure 3: COD Load (t/day) CODLoad COD (ppm) and National Investments h'ater Pollution Control Law Measures inChemical (Regulation of Effluent Concentration) Plant, 1971-81 Pollution Control Agreement Accumulated Investment .' . . < t t(100 million yen) 30.0 20- 400. 40 22. 5 15 - 30C .... .. . ......... - _ O ........ ....... .... ...........................--. . ._ ._.. 30 iacity Investmen \~~~~~~~~~~~~~~~~~~~~~~.. ... s. ........ .... ....... . 15.0 10- 20 ... -------- 20 Effluent Volume'-." A~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~.... , ,... .<* ......... .7.5 5 10C - ......................0...... . .- . 10 . 0 . 0 0 -~~~~~~~~~~~~~ _ _ _ _ ~~~~~~~~~~.. _ _ ..... .... .. . a / ~~~~~COD! Loadi .0.0j 0 0 71 72 73 74 75 76 77 78 79 80 81 , I , t , (Yr) Plant c) Ordinary Processes Effluent I Technique in Active Sludge Treatment e) Improvement of Process b) Highly Concentrated Effluent (Installation in Wet Oxidation Treatment of Reboiler) a) Improvement of a Quick Cooling Process d) Catalyst Development Chapter 4 55 tended to achieve consistency with other companies During the period 1972-1977, investments for which also entered the agreement. Although the ef- pollution control facilities were 2.68 billion yen for fluent from the chemical industry contained toxic sub- water pollution and 1.70 billion yen for air pollu- stances such as cyanogen and other chemicals and was tion. This added to the production costs. These were generally difficult to treat, 10 ppm was technically pos- financed by the company itself, by raising the price sible with tertiary treatment. Since other business es- of its main product, acrylonitrile, by 17.5 yen/kg, or tablishments had adopted a 10 ppm target, it was dif- about 20%. During this time, COD load decreased ficult for the factory alone to adopt 20 or 30 ppm. by about 92%, i.e. from 19t/d to 1.56t/d. Actual methods In the end, however, implementation of the above pollution abatement measures turned out to The following measures, which include process im- be difficult for economic reasons, primarily the provement, were implemented in order to reduce slump in acrylonitrile demand due to structural de- the effluent load. (These are also summarized in pression The company discussed with the city about Figure 4-3). the possibility of a more gradual implementation of the agreement. In 1983, due to heavy competition Catalyst development The company developed its from other factories producing acrylonitrilo and re- own catalyst, which was capable of converting propy- lated products, 2/3 of the factory site was sold. lene (material) to acrylonitrile, and of absorbing resi- due in acrylonitrile production process. This process reduced non-reactive substances and impure by-prod- ucts (primarily cyanogen) and a great deal of COD load in the effluent process. This measure reduced Food Processing Company COD effluent load by about 33%, i.e. from 4t/d to 2.7t/d. This case is one in which a large-scale food pro- The company installed a boiler at its distillation cessing company took measures to reduce air/wa- towers with a direct steam blow method. This de- ter pollution, offensive odors, and solid wastes. The creased effluent by separating steam from polluted characteristics of environmental pollution control effluents, and the steam was reused for condensa- measures in this case were: 1) reduction in effluent tion. This measure reduced COD effluent load by load was achieved by process improvement rather about 44%, i.e. from 2.7t/d to 1.5tld. than by installation of end of pipe treatment equip- ment, 2) the measures took account of saving in en- The company also installed new drainage chan- ergy and labor costs, and 3) the measures were nels that made possible to separate effluent from implemented based on a cost-benefit analysis. rain/cooling water, and reduced volume of effluent to be treated. The number of drainage channels re- This company started operation in 1963. It pro- duced from six to three. duces food oil and related food processing prod- ucts. All materials such as beans, rapeseed, cotton- Effect of measures seed and sesame are imported. The company pro- duces salad oil, margarine, sesame oil, etc. by press- Although COD effluent load decreased from 4t/d ing, extracting, and refining. Figure 4-4 shows the to 0.98t/d (75%), the effluent load standard (40 kg/ process flow in the production of vegetable oil from d) set by the agreement was not achieved. beans or rapeseed. 56 Metropolitan Environmental Improvement Program manufactured good Figure 4-4: materials pressing exrcn e =-i _ Process Flow: Production of soy beans press o tracte o for brewing Vegetable Oil others cmncifugal clay treament wax removal vaccuum treatment seperpion method The factory is located in the Negishi reclama- Summary of measures tion area. In recent years, high-rise apartments have been built in an area close to the factory site. a. The remodeled large boiler included a NOx re- duction combustion technique. Membrane wa- This company has a corporate policy which ter pipes were built in the boiler and a two-stage emphasizes social responsibility and product qual- combustion burner decomposes the NOx pro- ity, as well as the speed and cost of production. It is duced in the main burner. especially concerned about its responsibility for en- vironmental protection and food sanitation. Costs b. Computerization for optimum load distribution incurred to implement the measures described be- control in the boiler has improved its efficiency. low were offset by other savings, rather than by rais- Also, the rotational frequency control in a forced ing product prices. In fact, the company imple- ventilator was remodeled and saved energy. mented the measures only after it determined their Investment in this facility was 290 million yen. rationale based on its own cost-benefit analysis. Effect of measures Air Pollution Control Measures (NOx Countermeasures) As a result of these countermeasures, NOx emissions amount and concentration decreased by 25% respec- Reasonfor taking measures The company exam- tively. The introduction of an auto-control system in ined the case for remodeling its NOx reduction sys- the bo iler made operational management and infor- tem in its large boiler of C heavy oil (high sulfur mation processing easier and replaced four operators. content) in order to respond to theYokohama NOx countermeasures guidelines. At the same time, Air Pollution Control (SOx Countermeasures) boiler control was computerized, thereby saving and Energy-saving (Fuel Conversion) energy and labor. Prior to its implementation, the company had made a cost-benefit calculation, in Reason for taking neasuires As a NOx counter- which benefits (savings) amounted to 100 million measure, the company installed stack gas desulfur- yen/year, due to a decrease in fuel/labor cost, and ization equipment in its large C heavy oil boiler. Be- energy-saving. Capital costs amounted to 70 mil- cause it was difficult to maintain the quality of low lion yen/year. The analysis indicated that the com- sulfur heavy oil, the company agreed, under the pany would achieve a net reduction in costs of 30 guidance of Yokohama city, to install a stack gas million yen/year. Therefore, the company decided desulfurization. However, local residents com- to undertake the proposed NOx countermeasures. plained about re-evaporated steam (wet flue-gas Chapter 4 57 desulfurization equipment lowers temperature NOx emissions decreased by 5%. Five heavy oil stor- around the emission exit and produces steam). age tanks were now used for plant oil after clean- up. The economic calculation indicated that oper- Kanagawa prefecture and the city of Yokohama ating costs would increase by 10% but decrease by subsequently provided guidelines for fuel conversion 75% when the co-generation system is introduced. in order to reduce SOx emissions. The company, at that time, was using two kinds of fuel: A, heavy oil Water Pollution Control Measures - (ower sulfur content) at four small boilers and C, heavy Phosphorous oil (high sulfur content) at its large boiler. Reason for the measures The company had some Following the new guidelines, as a comprehen- effluent treatment facilities from its earliest days: sive means of addressing NOx, SOx, soot and dust, pressurized flotation for industrial process effluent, etc., the company planned to change fuel from heavy and activated sludge for household effluents. It had oil to city gas, and therefore remove flue-gas des- no problems with COD effluent concentrations or ulfurization. Then, considering the fuel conversion loads. However, the effluent from salad oil produc- as a first step, the company planned to reduce total tion contained highly concentrated phosphorous. energy cost by introducing a co-generation system Because the pressurized flotation method could not (installation is scheduled in April 1995). The remove phosphorous, its concentration in the plant's company's decision was based on an economic cal- effluent was 60 ppm. Yokohama city requested culation which indicated that, although operating eutrophication countermeasures under its admin- costs will temporarily increase, in the long run there istrative guidelines for improving the quality of ef- will be operating cost savings. fluents discharged into public waters. Summary of measures The company was determined to introduce a new treatment facility equipment and strengthen Investment in fuel conversion cost 300 million yen. the process rather than to improve the old facility, It was implemented as follows: and considered how to develop the needed tech- nology. A cost-benefit analysis of this measure in- a. The company remodeled combustion dicated net economic advantage will be 100 million equipment in its large boiler and converted fuel from yen per year. The analysis is as follows: C heavy oil to city gas. A charcoal-saving machine was also installed in the boiler to save energy from Merit 240 million yen/year: exhaust gas.The old flue-gas desulfurization equip- a cost reduction in chemical use and efflu- ment was removed. ent treatment, an improvement of produc- tion speed, etc. b. The company remodeled combustion equipment in four small boilers and converted fuel Demerit 140 million yen/year: from A, heavy oil to city gas. capital cost and cost of electric power, etc. Effect ojf measures Actial methods In the salad oil production pro- cess, the company reduced the phosphoric lipid As a result of these measures, NOx emission con- content of crude oil by improving its pressing pro- centration of its large boiler decreased by 30% and cess, then reduced phosphoric acid consumption by 58 Metropolitan Environmental Improvement Program deoxidization, thereby reducing the phosphorous ing process. Vacuum generation equipment origi- content of the final effluent. The total cost of equip- nally used a large amount of sea water. The waste ment was 572 million yen. Specific measures were water from this process was contaminated and cre- as follows: ated a large pollution load. Consequently,Yokohama city regulated the volume of effluent discharged a. Improvement of the pressing process under its administrative guidelines for improving the quality of effluent discharged into public waters. The extract expander equipment (an extruding grain machine) which crushes, mixes, kneads, and The company conducted research with an makes pellets was introduced after the pre-treat- equipment manufacturer, aimed not only at reduc- ment process (a pressed process). The company ing the amount of waste water, but also at improv- found that this process inactivated oxygen of mate- ing the efficiency of the production process. New rials by pressing oxygen and adding steam.This pre- cooling technology was developed. Water cooled by vented hydrate phosphoric lipid from changing to a freezer was used for vacuum generation equipment, non-hydrate one and reduced the phosphoric lipid and recycled cost-benefit analysis indicated that this content in crude oil. measure would be economically advantageous: cost saving due to reduction in the use of steam was b. Intensification of gum removal equipment in greater than cost of using additional electricity for the deoxidization process the new technology. The deoxidization process originally only re- Effects of the mneasures As a result of the mea- moved gum from extract oil. However, new equip- sure, the vacuum condition in the deodorization ment was installed to remove gum from all pressed process became rigid and the operation became oil, which improved the rate of oil production. stable, leading to increases in the efficiency. The measure decreased steam use by 70-80% and also c. Effects of measures decreased specific effluent (sea water) by 85% by recycling the industrial water which was converted Eighty percent of phosphorous lipid content from the sea water. The clean up of scum in water was removed from crude oil, 75% of phosphoric acid pipes became unnecessary because of the conver- consumption in the deoxidization process, and 50% sion to industrial water. The overall process became of the phosphorous content of the final effluent. cleaner. The company obtained a patent for this However, the effluent concentration was still high technology and sold the equipment to four Japa- at about 30 ppm. In light of probable future trends nese plants and three foreign plants in the same in effluent standards for phosphorous, the company industry. is now considering more phosphorous removal techniques, such as anaerobic treatment. Offensive Odors Water Pollution Control Measures - Polluted Reasonfor takingmeasure In the process of pro- Cooling Water ducing salad oil, after the oil from crude oil was pressed, the oil sludge treatment process dried and Reasonfor taking measures Salad oil is deodor- cooled, producing offensive odors. The residents ized with high temperature (270 degree centigrade) who lived around the factory complained, and the and high vacuum (3-5 Torricelli) in the final refin- city of Yokohama advised the company to reduce Chapter 4 59 the offensive odors. The company's own view was all waste disposal process was inefficient. Conse- that it should secure a proper work environment for quently, the company examined the case for replac- its labor force. The approach taken was to control ing the dehydration equipment in order to decrease offensive odors by applying a recycling and closed the water content of newly generated sludge and to system in the production process, and also to re- reduce treatment costs by stabilizing the activated cover heat from exhaust gas. sludge process, and reducing the volume and weight of sludge. A cost-benefit analysis indicated that such a measure would yield a small economic gain. Costs Cost-benefit analysis indicated that this mea- of the project were about 33 million yen/year, in- sure, involving an investment of 56 million yen, cluding both investment and additional operating would yield a slight economic gain. Annual costs of costs. The energy savings due to reduction in use of the project (investment costs plus energy costs) were steam were 35 million yenlyr. 5 million yen. Savings were 16 million yen/year, comprised of a reduction in the cost of sludge treat- Acttal method and effect The company invested ment and disposal, including labor cost savings. 113 million yen in the system to control offensive odor generation. This consisted of a closed system Actual method The company introduced a belt which recycles exhaust gas from the sludge drying press using electric osmosis, which operated 24 process. The exchange gas from a heat exchange hours a day, and also introduced a measuring and machine is showered in the cooling tower and re- monitoring system to reduce water content, as well turned again to the dryingprocess.At the same time, as to increase efficiency. The figure of facility invest- the company undertook an energy-saving measure ment was 56 million yen. (use of recovered showering drainage water as aux- iliary heat source for operating machines) . The con- Effects of the measure The measure resulted in a centration of offensive odors treated by the deodor- reduction in the water content of dehydrated cake ization equipment met regulatory emission stan- from 85% to 65%. This decrease corresponded to a dards. 60% reduction in the generation of dehydrated cake. Also, it made use of fertilizer easier. Moreover, it Industrial Waste Measure (Reduction in the reduced the load of sedimentation of 24-hours-op- Volume of Sludge) erating activated sludge facilities. It also decreased the work load of operators by introducing remote Reason for taking measures The original acti- control and improving the working environment. vated sludge effluent treatment facility treated do- mestic waste water except oil bearing effluent. The extra dehydrated sludge was given to farmers to apply to agricultural land. Originally, since the wa- ter content of the sludge which was dehydrated by Small and Medium-sized five belt presses was in fact high and variable, the E system always required operators to be aware of Electronis Parts Manufacture changes in weight and volume and to react accord- This case refers to a medium-sized electronics parts ingly. Also, although the treatment system operated manufacturer which specializes in metal plating. The continuously, the belt press system only operated factory moved from a mixed residential/industrial during the day time. This discontinuity in the over- area to the Kanazawa Industrial Park during the 60 Metropolitan Environmental Improvement Program period 1980-83. Upon relocation to the new site, products required the company to modernize its the company renewed its production process, used production facilities. The situation also demanded the joint effluent treatment facility, and recycled its that the company discard its old metal plating im- effluent. age and create a modem and clean working envi- ronment for its labor force. The firm, which currently has 130 employees, actually started operation in 1950. It originally pro- Decision-making process and relocation duced a special small resistance bulb or a heat coil for a vacuum pipe, etc. and then shifted its produc- Decision-making and relocation The company tion to electronics parts and materials.The company concluded that the old factory could not deal with now specializes in electroplating precious metals the new situation and should be relocated. It was such as gold and silver, as well as high value-added expected that the sale of the old factory site would electronics components.This product diversification generate about 50% of the total relocation cost.The required new production facilities and raised major reason for moving the factory to the Kanazawa In- funding issues. dustrial Complex was that the Complex had the in- frastructure for controlling pollution and was a Relocation to the Kanazawa Industrial Park project which the city of Yokohama supported by providing subsidies to relocating firms. An impor- Reason for tle relocation In 1960, the factorywas tant factor was that factories in the Park could make located in a ruralYokohama suburb, which was in a use of the joint effluent treatment facility. valley with springs and pine tree forests. The City Planning Law then designated the site as a residen- Relocation When the company decided to relo- tial district and its neighboring district as a category cate in 1979, the city of Yokohama was already reg- I exclusive residential district. In summer time, the istering prospective relocation companies.The com- residents complained about night noise. Because the pany belatedly became a member of a metal plat- factory was located in a residential district, it was ing trade association. The company later became a impossible to even construct a building for a renewal representative firm of the association. or an extension of the production facility or a re- newal of an effluent treatment facility. This factory Cost-sharing The total cost of relocation including was located in an area designated and promoted land, buildings, and production facilities was about 3 for relocation by the Factory Regulatory Law. billion yen. The purchase price of the new land was 55,400 yen/m2. About 2.3 billion yen out of the total One of the problems the factory had at that time cost was provided by a loan from the Japan Environ- was that the old effluent treatment facility became ment Corporation, which charged a 7.35% interest rate obsolete, and its treatment capacity had not kept and a twenty year repayment period. Grants covering up with the increase in production. The facility re- interest and relief from the special land holding tax quired more space and repairs would incur addi- and corporation tax provided by the city ofYokohama tional major costs. It was clearly preferable at this over a limited period were also effective. Yokohama time to invest in a new facility than to repair the old city proposed to buy the old factory site, but could not one. Moreover, the company was expecting a rapid agree on a price. In the end, a private company bought growth in demand for its products because of the it for 200,000 m2 or about 3.5 times higher than the overall growth of the electronics industry in Japan. land price in the Park.An apartment buildingwas built Accelerating demand for high quality electronics at the old site. Chapter 4 61 Effect of relocation the park and enjoyed the improved technologies of those companies. Relocation to the new site enabled the company to improve the quality of its products. The company could satisfy its clients' demands with a better pro- duction environment, therefore obtaining new cli- ents. With regard to technical aspects, the wider fac- Effluent Treatment tory floor made it possible to introduce a sophisti- cated surface analyzer such as a scanning electron microscope. Metal plating techniques could also be Collective industrial wastewater treatment improved and technological innovations, including facility the rnost precise IC products, were introduced. In- vestment in the production increased production Summarij of the measure The Sewerage Bureau and profitability. The number of employees at the facilitated the use of the collective wastewater treat- time of relocation was about 120, but increased to ment facility (industrial wastewater treatment fa- 180 as production expanded. With respect to pollu- cility at the Fukuura factory). The construction cost tion countermeasures, vibration and noise were no of the facility and the maintenance cost were longer problems. Night work no longer resulted in charged to the companies that used them. citizens' complaints. Effect of measures The company decided not to As to other effects, the company could now install a wastewater treatment facility at its own site, obtain more labor supply from the Miura and but to use the collective wastewater treatment fa- Yokosuka areas in addition to the Kanazawa area. cility. Economies of scale in the collective facility Location in a high-technology environment also meant that the firm could dispose of its waste much yielded benefits. For example, the company estab- more cheaply than if it had to install and operate its lished business relations with other companies in own treatment facility. 62 Metropolitan Environmental Improvement Program Chapter Five: Conclusion regulating standards or methods, which would be Evaluation of Environmental stricter than those required according to the struc- Protection Measures in ture of laws and regulations at that time. Yokohama Early pollution control agreements were con- In this section, we evaluate the environmental pro- cluded with large companies in the new industrial tection measures in Yokohama such as the pollu- area on the coastal reclaimed land in order to con- tion control agreements and the Kanazawa recla- trol increasing pollution originating from existing mation project described in Chapter Three. factories. In fact, since pollution originating from the new factories was much less than that from the Pollution Control Agreements existing factories, the pollution control agreements were very effective. Overall evaluation The first pollution control agreements inYokohama were conceived by an au- The agreements specified maximum pollution tonomous effort of the city during the mid-1960s control targets, based on scientific data, and in light when local governments did not have any legal au- of present conditions and future prospects of air thority over pollution control. Under the agree- pollution, and of the level of pollution control tech- ments, the city obtained, based on mutual consul- nology available at that time. Although the agree- tation, pledges from business enterprises to imple- ments were much stricter than laws and prefectural ment pollution control measures. The city took the ordinances established later, the companies recog- initiative in undertaking preventive pollution con- nized that scientifically reasonable standards based trol measures with the support of citizens' move- on large scale monitoring or a wind-tunnel test, ments, while allowing companies to establish their were being set. The agreements played an effective factories on a selected basis. The Yokohama pollu- role in introducing advanced technology and de- tion control agreement was different from the fol- veloping new technologies such as the country's first lowing two types of pollution control measures, one power generation by LNG, and the improvement taken in Yokkaichi and the other in Mishima- in ground concentration of pollutants due to col- Numazu. In the case ofYokkaichi, pollution control lective smokestacks. measures were pursued only after companies had established their factories and started causing pol- Early pollution control agreements, which first lution. In the case of Mishima-Numazu, the resi- targeted new factories, were later adopted by exist- dents rejected the siting of planned plants by orga- ing factories. Even after certain legal regulations nizing a strong residents' movement. For this rea- were provided, the agreements were still innova- son theYokohama Pollution Control Agreement was tive. For example, the agreements imposed stricter frequently called "Yokohama style." The initiative control than laws, or introduced total emission tar- taken by the Mayor ofYokohama was the main rea- gets while existing laws only regulated emission son for the inception and success of the"Yokohama concentrations. style"pollution control agreement, which was nec- essary to protect citizens' health and the living en- Residents' novements From the early 1960s, air vironment. This was a major break with tradition, pollution had become a serious problem in the ex- for according to conventional ideas, local munici- isting coastal industrial zone. Residents were an- palities were not allowed to establish their own ticipating with alarm the arrival of still more facto- Chapter 5 63 ries in the new coastal industrial zone. Residents As a result, the companies were able to pay for around the zones formed a residents'organization the costs of pollution control investment, and to called"Council for Conservation of Environmental maintain industrial competitiveness at the same Hygiene in Naka and Isogo Districts.'They appealed time. to the national, prefectural, and city governments to implement pollution control measures. Anti-pol- Later, the city signed other pollution control lution campaigns by local residents inYokkaichi and agreements with the existing factories. The follow- Mishima-Numazu affected this movement. Citi- ing factors attributed to the successful agreements: zens' movements at that time not only promoted First, the companies understood theYokohama style polluttion control measures byYokohama City, but when they reached early pollution control agree- also gave birth to the first pollution control agree- ments with new factories. Second, following in- ment. creasing anti-pollution demands from the public, these companies came to realize that, in order to Thereafter, citizens' movements continued to carry out their business in the future, it would be support the city's pollution control measures. This vital for them to obtain a consensus from local gov- was because the city kept residents well informed emments and residents when building or expand- of the content and results of scientific experiments ing factories. It turned out that to take pollution conducted by the city and factories, as well as the control measures is not so costly in the long term content and effectiveness of the agreements. This and is affordable, though large investments are re- openness removed anxiety from residents, and the quired in the initial stage. Furthermore, from the visual evidence of improvement in environmental factories' point of view, the conclusion of pollution quality enabled the city to win the residents' un- control agreements meant a kind of authorization derstanding and trust. for pollution control measures fromYokohama City. As a result, the factories were able to build up good Companties' reaction Escalating anti-pollution relationships with the residents. demands from the public, and land sales contracts were the external factors that companies accepted Administrative reaction The city's administrative in the early pollution control agreements. Since the structure and staff attitudes and skills for pollution city's investigation and finding were scientifically control were key factors.The pollution control agree- souncd, the companies acknowledged the results and ments were successfully implemented through fre- agreed to cooperate. On the other hand, internal quent monitoring, on-the-spot inspections, and factors that companies accepted such a strict agree- guidance. Such local effort has been an important ment were as follows: tool to induce effectiveness of the measures and this has been a distinctive characteristic of theYokohama * Yokohama was blessed with a large consumer administration. The city administration obtained market in the outskirts of the capital; residents' trust and cooperation, and maintained it by disclosing pollution information as openly as pos- * good economic conditions at that time eased sible. Since the city set targets based on scientific negotiation of the agreements; and data, the companies tended to accept them. * having abundant capital and management ca- The Bureau of Pollution Control was established pacity, the large companies were able to cope with its ten staff when the first pollution control with the pollution control costs. agreement was concluded. Yokohama was able to 64 Metropolitan Environmental Improvement Program avoid a vertical administration, though this is typi- 4) It should be recognized that the pollution con- cal in the Japanese administrative structure, and it trol agreements exist not only for the company has maintained its flexibility to effectively handle and local government administration, but pri- the problems at hand. Since then, the administra- marily for the residents' well-being. tive structure has basically stayed the same. Staff engineers who had received higher education were Kanazawa Reclamation Project and Industrial highly concemed about pollution issues and ap- Relocation proached their task with enthusiasm and dedica- tion. Moreover, the city made great efforts to im- The goal of the Kanazawa Reclamation Project was prove its staff's capability and accumulated technol- more than just creating land for industry and port ogy in the Bureau. This accumulation of technol- as in the past. The ultimate goal was to reclaim land ogy, specifically reflected in the conclusion of the as a site for redeveloping the downtown area and Yokohama pollution control agreements that were accommodating small- and medium-sized factories. based on scientific knowledge and technology, and Small- and medium-sized factories scattered around helped the city win credibility and understanding the city were transferred into the Kanazawa Recla- from the enterprises which concluded pollution con- mation Land. This facilitated rationalization of fac- trol agreements. tory management through cooperation and system- ization. The industrial relocation was also effective Requirements for effective pollution conttrol as a measure for controlling pollution including agreements The experience of Yokohama. city in- noise, vibration, and offensive odors. dicates the following requirements for effective pol- lution control agreements: Successes of the Project 1) The content of the agreements should be de- Concernabout living environment Thereclama- fined from a scientific and technological point tion project was formulated with careful consider- of view, and not simply from an abstract and ation of environmental aspects and urban planning. ethical point of view. The area was divided into the industrial and resi- dential sites by a national road running North-South 2) A strict and rigid agreement is not always good. in the center of the reclaimed land. A 50 m wide It needs to be adjusted according to the eco- green tract of land was also constructed as a buffer nomic, technical and managerial capacity of the zone along the national road.The city secured about firm local characteristics. 10% of total reclaimed land for building a seaside park, a park on the old coastal line, and green buffer 3) In order to check whether the companies carry zones. The construction of the green buffer zones out a comprehensive implementation of the were funded by the Japan Environment Corpora- agreements, it is necessary for the administra- tion. tion to be aware of best available protection technology. Therefore, it is desirable for the ad- Polluttion control measures In order to prevent ministration to maintain a certain number of pollution from occurring in their new neighborhood, qualified staff and train them. Local staff must companies implemented specific pollution control have enthusiasm for, as well as knowledge of, measures after relocation, namely, arrangement of advanced technology. factory location within the industrial complexes, Chapter 5 65 establishment of treatment facilities, as well as in- afford for relocation. The city therefore reduced taxes dividual measures within the factories themselves. for the factories concerned over a limited period, exempting them from property tax, corporation tax, Accordingly, the city decided to locate some and the special land holding tax. small- and medium-sized industry in special sec- tions of the Kanazawa Industrial Complex and let Taking advantage of factory relocation, the city them discharge effluent to the collective treatment tried to reform and rationalize management of system after each factory removed some hazardous small- and medium-sized factories by promoting substances. To have a collective treatment facility is collective and cooperative actions, as well as im- much more economical than the case where each proving organization in the factories themselves. factory has its own industrial treatment facilities Organizational promotion made it possible for because the former requires less space for the treat- small- and medium- sized companies, which were ment facility installation and less operation and financially weak, to obtain public funds such as the maintenance costs. promotion fund for small- and medium-sized com- panies and loans from Japan Environment Corpo- Costs of construction, operation and mainte- ration. nance of the collective facilities are bome by the user companies. The facilities were constructed by using Project execution organization The Kanazawa a 30- year low interest loan provided by the Japan Reclamation Project inYokohama was implemented Environment Corporation.Yokohama city subsidized by inter-departmental effort involving Planning and a part of the interest. Annual operation and main- Coordination Division, Pollution Control Bureau, tenance costs are settled by the user companies ac- and 10 other bureaus of Yokohama city. Officials of cording to a certain formula using contract and ac- those organization formed both the steering and tual effluent volume, as well as effluent density. technical committees for the project. Collective treatment proved more economical Unsuccessful aspects than individual treatment. It also made possible for Yokohama city to easily monitor the effluents of the Process offactory relocation The city introduced user companies, and to give them appropriate guid- criteria to prioritize the districts from which relo- ance. cated factories should be drawn. Criteria included the presence of residents and industries located in Incentives to relocate (land price and financial close proximity to each other, existing environmental subsidy) The incentives included the availability conditions, and managerial capability. Based on the of necessary infrastructure on the site, and low cost results of this investigation, the city selected facto- requirement of the relocation. ries which would require relocation, and then en- couraged the process. Although the city initially The initial sales price of industrial site was wanted to relocate 2,000 out of 6,000 small- and 30,000 yen/m2. However, it actually increased to medium-sized factories, only about 400 factories 50,000-60,000 yen/m2 due to delays in granting rec- were actually relocated. Many factories which lamation licenses and soaring construction costs. caused pollution could not be relocated due to the There was considerable doubt as to whether the tar- lack of relocation funds. Moreover, about 40% of geted small and medium-sized businesses could the factories relocated were previously located in the 66 Metropolitan Environmental Improvement Program semi-industrial area, and not in the mixed residen- The experience of Yokohama presents an ex- tial-industrial area. It may be said that more facto- ample of a local government which has successfully ries could have been identified and relocated if the implemented its own environmental protection city had identified candidate factories from only resi- measures. To this end, it requires a comprehensive dential areas or commercial areas, and excluded plan of actions including not only environmental semi-industrial areas, and if more time had been protection but also local economic policy and local spent for such identification. However, the city's fi- living environmental policy. nancial burden of interest payment prevented the city from spending more time for the identification. The Yokohama experience also demonstrated the importance of gaining the trust from local resi- Utilization of vacated sites Yokohama either dents and companies. To obtain this, the city: purchased the vacated sites from the relocating fac- tories and constructed public facilities such as parks, 1) aimed at rational, objective and effective city or attempted to conclude agreements with the com- management, panies regarding the utilization of the vacated sites. In the latter case, companies were required to have 2) trained special staff in environmental adminis- prior consultation regarding their disposition, tration, thereby limiting the future uses of the sites. How- ever, both parties sometimes could not reach an 3) established cooperative relationships with ex- agreement on sale prices. The city could not control temal specialists and research institutions, the use of vacated land effectively. 4) encouraged residents' participation and estab- lished a system to listen to residents' opinions in the city management, and Conclusion on Environmental 5) disclosed environmental and other information Protection Measures in including environmental issues as much as pos- Yokohama sible. The national emission standard is a minimum com- The City of Yokohama has obtained trust from pliance standard. National emission standards are the residents for its individual measures such as not necessarily adequate for some cities where pol- municipal reform and residents'participation. These lution problems are serious. For this reason, in or- efforts made it possible for the city to successfully der to protect local residents' health and living en- negotiate with companies about the pollution con- vironment, Yokohama City found it necessary to trol agreements and to maintain effective relation- implement its own measures through pollution con- ships with the central govemment. trol agreements or guidelines/guidance. Chapter 5 67 ANNEXES ANNEX 1: Yokohama Automobile Pollution Control Program Contents of the Program automobile exhaust monitoring stations did not in- crease. However, comparing with national level, the The City ofYokohama made a comprehension pro- higher concentration is observed especially trunk gram, "Yokohama Automobile Pollution Control roadsides, and many monitoring stations cannot Program" in 1987 in order to prevent any further meet environmental standard. automobile pollution and improve roadside envi- ronment. The program includes various counter The main reason for this high NO2 concentra- measures such as pollution source control, rational- tion is the rapid increase of car ownership and the ization of material and people's flows, roadside traffic volume in the city. The number of cars regis- measures, etc. The system of the countermeasures tered exceeded 1,275,000 in 1990 which is two and in this program is summarized in Figure A-1. a half times as many as that in 1975. Effects and Problems of the Program As a result of these countermeasures taken based on the program, NO2 concentration measured at 70 Metropolitan Environmental Improvement Program x Measures covering fo polto Reduction of air pollutants and noise from motor Iall over the city l sources lvchiicles by strictcr regulation, motor vehicle inspection, etc: f Promotion of the development and introduction of cleaner cars such as electric cars a for eitrfing Amrranement of largeandcflwb m nediu-saled publfic btcontuol aecontrol systems and systematized traffic lights, for trafic volme Conprsomot the puselof thesetransportationsytm of efficient delivery tnethods of comoity etc. _ Measures applied to|Promotion of hifghly efiietf colmlercta uel the cty' ae a Promotion of highly efficient transportation system of large trucks for harbors and factories Arrangement of largc and medium-scale public bourilot-up area! transportation systems and station squares to . ~~~~~~~~~~~~~~~~~~~~~promote the use of these transportation systems areas | ..... developing areasJ blcrltion PubLi reaintotectzs,othcmpis for car poll u tion5,control ANNEX 2: Changes of Pollution Control Agreement between Yokohama City and Isogo Thermal Electric Power Plant, Electric Development Inc. (Major contents of the agreements) December 1964 July 1967 February 1972 March 1976 (New Construction) (Extension) Air Pollution Dust collector Removal rate should be Removal rate should be Removal rate should be Removal rate should be more than 98% more than 98% by more than 98% by more than 98% by electric dust collection electric dust collection electric dust collection Smoke stack 120m in height More than 140m in height More than 140m in height More than 140m in height Velocity of emission 30m/sec More than 30m/sec More than 30m/sec More than 30m/sec Emission amount Less than 490Nm3/h (SOx) Less than 490Nm3ih (SOx) Emission temperature More than 130C More than 130C More than 130C More than 130C Fuel Low sulfur and low ash Low sulfur and low ash Low sulfur and low ash Less than 0.13% (Sulfur content of heavy oil equivalent) Soot & Smoke Less than 0.6g/Nm3 Less than 0.6g/Nm3 Less than 0.4g/Nm3 Less than 0.05g/Nm3 S02 Less than 500ppm Less than 500ppm Less than 350ppm Less than 60ppm * Installation of blue gas desulfurization facility * Reduction of fuel consumption of afterbumer * Measures to be taken in case of desulfurization facility failure NOx Reduction through * Improvement of improvement of combustion method combustion method * NOx reduction through research on stack gas denitration facility Water Effluent treatment * completely equipped * completely equipped * completely equipped * Compliance with effluent Pollution with treatment facilities with treatment facilities with treatment facilities standard * Sea water pollution * Sea water pollution * Sea water pollution * Improvement of waste control by oil separator control by oil separator control by oil separator water quality to the level of fish living * Recycling of waste water, etc. December 1964 July 1967 February 1972 March 1976 (New Construction) (Extension) Cooling water Stop use of liquefied Stop use of liquefied chlorine chlorine Waste Dust collected * Prevention of * Prevention of * Prevention of * Prevention of dispersion dispersion dispersion dispersion Industrial waste - * Treatment responsibility -Agreement on waste disposal, if necessary Coal management * Prevention of * Prevention of * Prevention of * Prevention of spontaneous ignition spontaneous ignition spontaneous ignition spontaneous ignition * Prevention of dust * Prevention of dust * Prevention of dust * Prevention of dust Noise Noise Less than 40dB Less than 40dB Less than 40dB Less than 40dB Others Measurement * Regular * Regular * Regular * Regular measurement measurement measurement measurement * Reporting upon * Reporting upon * Reporting upon * Reporting upon City's request City's request City's request City's request on-the-spot inspection on-the-spot inspection on-the-spot inspection on-the-spot inspection by-the City by the City by the City by the City Cost to be borne Cost for pollution Cost for pollution Cost for pollution Cost for pollution control should be borne control should be borne control should be borne control should be borne by the company by the company by the company by the company Suspension of - * According to the City's business decision Others - * Guidance to the related industries * Development of planting N nuili. ond Asia Technical Department Environment & Natural Resources Division (ASTEN) The World Bank 1818 H Street, NW Washington, DC 20433 USA Telephone: 202-458-2726 Fax: 202-522-1 664