2.12. Pilot Project: Elaboration of the Process and Logistics Options for the Im-plementation of the System for Collection and Utilization of PCB Wastes and PCB-Containing Equipment in the Russian Arctic
The Project Goal was to develop a mechanism for the implementation of priority projects in the context of the soon to be completed preliminary works for the ratification of the Stockholm Convention by the Russian Federation, including:
The project was implemented by OOO “Research and Production Facility “Centre for Landscaping and Waste Management”. The Project Duration 07 July 2010 to 30 November 2010 The Project Activities
The Project Outcomes In line with the objectives and Action Plan of the National Arctic Policy of the Russian Federation, it will be necessary to establish a comprehensive security system to protect the territory, population, and facilities in the Arctic from the risks of natural and man-made disasters. In the context of environmental safety, it is necessary, in particular, to provide for the disposal of toxic industrial waste and chemical safety in the residential areas. An inventory of waste in the Russian Arctic must serve as the main database for tackling the problem. The Inventory will assess the quantity and composition of wastes, their location, identify the owners of wastes, and, most importantly, will legalize the presence of wastes. The Inventory will help regional administrations to make informed decisions concerning destruction or disposal of wastes. Information obtained as a result of this work will be used in calculating the economic costs of environmental activities such as the procurement of equipment, collection and classification of waste, shipping them to the processing site, etc. The assumed PCB wastes in the Russian Arctic are leftovers from human activity. These are likely to include the remains of buildings, electrical substations, boiler houses with heating systems, tanks, containers, drums with oil residues and Sovol, as well as oils containing polychlorinated biphenyls (PCB). PCB-containing Sovols were used in transformers and other equipment, electrical substations, and in heating systems, as good non-freezing coolant. They have not been manufactured in this country since 1993.
In three nearby Central, Northern, and North-Western Federal Okrugs, there is more than 4,000 ton of PCB in PCB-containing equipment used and stored in the chemical and petrochemical industries, ferrous and nonferrous metallurgy, machinery, forestry sector. The 2000 inventory of PCB and PCB-containing equipment established that there was PCB-containing equipment (transformers and capacitors) in Murmansk Oblast, Yamalo-Nenets Autonomous Okrug, Krasnoyarsk Krai and the Republic of Sakha (Yakutia). In the territories that are part of the Russian Arctic, there is about 1,269 ton of PCB. Almost the entire PCB stock was found in Krasnoyarsk Krai - 990 t (78% of the total) and in the Yamal-Nenets Autonomous Okrug - 235 t (18,5%). It may be assumed that these figures are not very precise, and most likely underreported. It will be necessary to make a comprehensive and detailed inventory and registration of PCB and PCB-containing equipment and their locations in the Russian Arctic. This inventory should serve as a basis for the development of a detailed PCB destruction action plan. The pilot project also conducted an analytical review of the regulatory requirements to safe storage of stockpiles of PCB and PCB-containing wastes in the Russian Arctic, including requirements to a full range of necessary actions for the disposal of PCB-containing equipment: draining PCB, washing the equipment, neutralizing the equipment (including transformers, capacitors and empty PCB containers), and destruction of PCB and PCB-contaminated waste. A very important aspect of PCB waste disposal in the Russian Arctic is to develop special requirements to the system of collection, transportation, storage and destruction of PCB and PCB-containing equipment. There are currently no such requirements. High-temperature processes are used to directly process such toxic chemicals as PCB. Self destruction of polychlorinated biphenyls will be at a temperature that is not less than 1100 ° C and PCB should be in the reaction zone for at least 1-2 seconds. In this way, there will be no secondary dioxins (PCB belongs to dioxins) generated. The pilot project report discussed matters related to the organization of environmental monitoring at those locations in the Russian Arctic where PCB and PCB-containing equipment are operated, stored and disposed of. There is also a review of the regulatory requirements. It is noted that Russia operates only 4 specialized laboratories capable of environmental monitoring of PCBs and dioxins. To ensure the technical capacity of PCB monitoring at the facilities that operate PCB-containing equipment, as well as in the storage and disposal areas, it will be necessary to furnish the existing specialized laboratories with modern analytical instrumentation and to establish new laboratories staffed with skilled professionals. The Report also describes the evidence-based process and logistics proposals as the best application options for the Arctic with due regard for the earlier proposals concerning the collection and utilization of PCB wastes and PCB-containing equipment. They include themes such as the selection of PCB destruction technologies, technologies for the treatment of transformers, treatment or destruction of capacitors, including matters related to the feasibility studies of such activities, performance of individual modules, number of individual installations and selection of sites for the disposal of PCB and PCB-containing wastes. The proposed scheme of preparation for PCB waste thermal disposal of in the Russian Arctic includes:
Another important focus in waste collection is degassing empty PCB containers after PCB has been drained (drums, containers, tanks, etc.). This problem should be dealt with in parallel with the main objectives since the degassing solution must also be thermally destroyed. In order to have a full environmental insight in the process of establishing the PCB inventory, it will be necessary to take soil samples for PCB to decide whether remediation of soil is required. If PCB is found near a water body, PCB water samples must also be taken. The main difficulties in this work will be to obtain information about PCB-containing wastes and select a site for the construction a PCB thermal destruction station. Therefore, good motivation proposals will be needed to address these issues.
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