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The First National Communication on Climate Change
NATIONAL CIRCUMSTANCES | GREENHOUSE GAS INVENTORY | POLICIES AND MEASURES TO MITIGATE CLIMATE CHANGE |
4. Greenhouse Gas inventory
Central to any study of climate change is the development of an emission inventory that identifies and quantifies а country’s primary sources and sinks of GHG. The inventory process is important for two reasons: (1) it provides а basis for the ongoing development of а comprehensive and detailed methodology for estimating sources and sinks of greenhouse gases, and (2) it provides а common and consistent mechanism that enables all signatory countries to the United Nations’ Framework Convention on Climate Change to estimate emissions and to compare the relative contributions of different emission sources and greenhouse gases to climate change. Moreover, systematically and consistently estimating emissions at the national and international levels is а prerequisite for evaluating the cost-effectiveness and feasibility of pursuing possible mitigation strategies and adopting emission reduction technologies.
This chapter summarizes the sources and sinks of Ukraine GHG emissions and uptakes. The emission estimates presented here were calculated using the IPCC Guidelines for National Greenhouse Gas Inventories [6, 18], to ensure that the emission inventories submitted to the Framework Convention are consistent and comparable across sectors and among nations. Ukraine has followed these guidelines, except where more detailed data or methodologies were available for major sources of emissions.
4.1 Ukrainian Greenhouse Gas Emissions
Greenhouse gases include carbon dioxide (CO2), methane (CH4), nitrous oxide (N2O), water vapor and ozone (O3) directly contributing to the greenhouse effect.
Chlorofluorocarbons (Cfcs), а family of human-made compounds, its substitute hydrofluorocarbons (Hfcs), and other compounds, such as perfluorinated carbons (Pfcs), are also greenhouse gases. In addition, there are other “photochemically important” gases, such as carbon monoxide (CO), oxides of nitrogen (NOx), and nonmethane volatile organic compounds (Nmvocs) that are not greenhouse gases, but contribute indirectly to the greenhouse effect. These are commonly referred to as “tropospheric ozone precursors” because they influence the rate at which ozone and other gases are created and destroyed in the atmosphere.
Although carbon dioxide, methane, and nitrous oxide occur naturally in the atmosphere, their recent atmospheric build-up appears to be largely the result of human activities. This build-up has altered the composition of the Earth’s atmosphere and may affect future global climate. Since 1800, atmospheric concentrations of carbon dioxide, methane and nitrous oxide have increased by 30, 145 and 15 percent respectively [18].
Use of chlorofluorocarbons is phased out under the 1987 Montreal Protocol on Substances That Deplete the Ozone Layer.
Ukrainian Inventory carrying out in accordance with UN FCCC commitments, touches upon three direct GHG: carbon dioxide (CO2), methane (CH4), nitrous oxide (N2O) and three “photochemically important” gases: carbon monoxide (CO), oxides of nitrogen (NOx), and nonmethane volatile organic compounds (Nmvocs).
The concept of global warming potential (GWP) has been developed to compare the abilities of each greenhouse gas to trap heat in the atmosphere. Carbon dioxide was chosen as the “reference” gas. Gases are presented in units of gigagrams of carbon equivalent (Gg CE). Carbon comprises 12/44 of carbon dioxide by weight.
The GWP of а greenhouse gas is а ratio of global warming - or radiative forcing (both direct and indirect) - from one kilogram of а greenhouse gas to one kilogram of carbon dioxide over а period of time. This report uses the 100-year Gwps recommended by the IPCC (Table 4–1).
Table 4–1. Global Warming Potential of Greenhouse Gases, 100 Years
Gas |
GWP |
Carbon Dioxide |
1 |
Methane |
21 |
Nitrous Oxide |
310 |
The Ukrainian inventory deals with the following five categories of GHG sources and sinks: energy systems (including transportation), industrial processes, agriculture, forestry and land-use change, and wastes.
The current Ukraine Greenhouse Gas Inventory for 1990 is summarized in Table 4–2. The totals presented in the summary tables in this chapter may not equal the sum of the individual source categories due to rounding. For the base year total GHG emissions were 232 882 Gg of carbon equivalent. CO2 emissions were partly offset by an uptake of carbon in Ukrainian forests of 14 175 Gg of carbon equivalent in 1990.
Table 4–2. Ukrainian Greenhouse Gas Emissions, 1990, Gg
Gas/source |
Emissions (Full Molecular Weight) |
Emissions (Direct and Indirect Effects; Carbon Equivalent) |
Greenhouse Gases |
||
Net Carbon Dioxide |
648 131 |
176 763 |
Fossil Fuel Combustion |
668 332 |
182 272 |
Industrial processes |
31 775 |
8 666 |
Total |
700 107 |
190 938 |
Forestry (sink) |
-51 976 |
-14 175 |
Methane |
9 453 |
54 140 |
Energy |
6 265 |
35 881 |
Agriculture |
2 254 |
12 909 |
Waste |
934 |
5 349 |
Nitrous Oxide |
23.412 |
1 979 |
Energy |
6.708 |
567 |
Chemistry |
6.160 |
521 |
Waste |
0.132 |
11 |
Forest fires |
0.175 |
15 |
Agricultural soils |
10.237 |
865 |
Photochemically Important Gases |
||
Carbon Monoxide (CO) |
7 481 |
- |
Nitrogen Oxides (NOX) |
1 243 |
- |
Nonmethane Volatile Organic Compounds (Nmvocs) |
656 |
- |
Net Emissions |
|
232 882 |
Figure 4-1 illustrates the relative contribution of the primary greenhouse gases to Ukrainian emissions in 1990. The shares of different sectors in GHG emissions are presented at the Figure 4-2.
Figure 4-1. Greenhouse Gases emissions in 1990, Gg
Figure 4-2. Sources of Greenhouse Gases in 1990 %
Due largely to fossil fuel consumption, carbon dioxide emissions accounted for the largest share - approximately 76 percent. Methane accounted for 23 percent of total emissions, which included contributions from agricultural activities and landfills, among others. The nitrous oxide emissions are less important comprising 1 percent of total emissions.
The emissions of the photochemically important gases CO, NOx and Nmvocs are not included in Figure 4-2, because there is no agreed-upon method to estimate their contribution to climate change. These gases only affect radiative force indirectly.
Statistical data for the development of the National GHG Emission Inventory for 1990 were collected and analyzed according to the IPCC Methodology. Official statistical data from Ukrainian Ministries and Departments were used. Information gaps in several emission source categories have produced а high level of uncertainty in the results. All statistical data used and emission assessments have previously appeared in official Ukrainian publications [14].
The following sections present the anthropogenic sources of greenhouse gas emissions, briefly discuss the emissions pathway, summarize the emissions estimates, and explain the relative importance of emissions from each source category.
4.2 Energy Sector and Transportation
Fuel combustion and fugitive emissions from fuels were considered in category “Energy sector and transportation” as the main sources of greenhouse gases.
After the disintegration of the Union of Soviet Socialist Republics (USSR), the most important problem for Ukraine was dependence from energy import. However, for the last few years, domestic fossil fuel production has been diminishing steadily. Coal production decreased from 164.2 million metric tons (MMT) in 1990 to 130 MMT in 1994; oil production decreased from 5.2 MMT in 1990 to 4.2 MMT in 1993; and natural gas production decreased from 19.8 billion m3 in 1990 to 19.4 billion m3 in 1993 [11,21]. Despite the low level of domestic oil production, Ukraine has large facilities for oil refining, which are capable of processing 60 MMT of oil per year [11,15]. Gas is transported from Russia to а number of European countries through the Ukrainian territory at а rate of more than 100 billion m3 per year.
In 1990 total fossil fuel consumption in Ukraine totaled 9,365.73 PJ (Table 4–3). The main consumers of fuel are electricity and heat production, and industry (Figure 4-3).
Table 4–3. Fossil Fuel Consumption in Ukraine by Sectors
Sector |
PJ |
Percent |
Energy |
4,046.33 |
43.20 |
Industry |
2,834.39 |
30.26 |
Transportation |
791.78 |
8.45 |
Agriculture |
325.14 |
3.47 |
Household & Services |
1,263.31 |
13.49 |
Others |
104.78 |
1.12 |
Total |
9,365.73 |
100 |
Figure 4-3. Fossil Fuel Consumption by Sectors in Ukraine
The 1990 Energy Balance of Ukraine [15] was the main source of statistical data of fuel consumption. However, the types of fuel and sectors included in this document differ from the IPCC Methodology. Therefore special software was designed to reformat the official statistical data according to the IPCC worksheets format; to calculate fuel production, import, export, and other parameters; and to transform the data into the units used by the IPCC.
Carbon dioxide (CO2) emissions for 1990 were estimated according to both the "bottom-up" and "top-down" methods. The bottom-up method used data on fuel and energy resources consumed in seventeen sectors of the Ukrainian economy. The top-down method used data on total values of fuel consumption. Carbon dioxide emission factors were taken from the IPCC Methodology [6].
Estimates of emissions from fuel combustion are presented in Table 4–4. NON-CO2 emission assessments were taken from national statistical information [13] for stationary sources.
Table 4–4. GHG Emissions for Fossil Fuel Combustion for stationary sources, Gg
Source |
CO2 |
CH4 |
N20 |
CO |
NOx |
Nmvocs |
Fuel Combustion |
668,332.0 |
35.6 |
6.7 |
3,273.0 |
760.7 |
265.1 |
Methane emission factors for fuel production, transportation, and primary processing were assessed according to Ukrainian experts data and IPCC Guidelines. Table 4–5 presents CH4 emission estimates in Ukraine for 1990, and Table 4–6 - the corresponding emission factors. In order to account Ukrainian circumstances minimum and maximum emissions and emission factors were calculated by national experts.
Table 4–5. CH4 Emissions for the Fuel Production, Transportation, Processing and Storage in Ukraine, Gg
Sources |
Base |
Minimum |
Maximum |
Coal |
2,784.87 |
2,180.35 |
3,610.12 |
Oil and gas |
3,444.52 |
1,696.38 |
4,558.65 |
Total |
6,229.39 |
3,876.73 |
8,168.77 |
Table 4–6. CH4 Emission Factors for the Production, Transportation, Processing, and Storage of Fossil Fuels in Ukraine
Activity |
Units |
Emissions Factor |
Underground mining |
||
Coal mining (Donetsk Basin) |
m3 CH4/t |
25.5 |
Coal mining (Lviv-volyn Basin) |
m3 CH4/t |
12.8 |
Postmining activity |
m3 CH4/t |
2.0 |
Surface mining |
||
Coal mining |
m3 CH4/t |
1.2 |
Postmining activity |
m3 CH4/t |
0.2 |
Oil-refining systems |
||
Prospecting and drilling |
kg CH4/drill-hole |
no data |
Production |
kg CH4/pj |
4,500 |
Transportation |
kg CH4/pj |
745 |
Processing |
kg CH4/pj |
1,000 |
Storage |
kg CH4/pj |
180 |
Natural gas systems |
||
Extraction |
kg CH4/pj |
450,000 |
Processing, distribution, and storage |
kg CH4/pj |
600,000 |
Venting and Flaring |
kg CH4/pj |
14,000 |
There are no published statistical data on GHG emissions from mobile sources in Ukraine for 1990. The main source of emissions is road vehicles, which in 1990 consumed more than 10 MMT of petroleum, 14 MMT of diesel fuel, about 48 thousand metric tons of propane-butane, and 284 million m3 of natural gas [3]. Road vehicles in Ukraine have а very low fuel efficiency; they use 1.4 to 1.5 times more fuel than similar automobiles and buses in developed countries. Consequently, GHG emissions per km are higher. Table 4–7 presents estimates of GHG emissions from mobile sources.
Table 4–7. GHG Emissions from Mobile Sources in Ukraine
Source |
Annual Fuel Consumption |
Aggregate Emission Factors (g/kg) |
Total Emissions (Gg) |
||||
(103 tons) |
CO |
NOx |
Nmvocs |
CO |
NOx |
Nmvocs |
|
Heavy-duty Trucks |
|||||||
Gasoline |
5,184.00 |
400 |
40 |
36 |
2,073.60 |
207.36 |
186.62 |
Diesel |
2,560.00 |
20 |
20 |
5 |
51.20 |
51.20 |
12.80 |
Butane |
31.70 |
150 |
25 |
30 |
4.76 |
0.79 |
0.95 |
Natural gas |
162.40 |
140 |
22 |
25 |
22.74 |
3.57 |
4.06 |
Cars |
|||||||
Gasoline |
3,800.00 |
400 |
40 |
36 |
1,520.00 |
152.00 |
136.80 |
Natural gas |
12.00 |
150 |
25 |
30 |
1.80 |
0.30 |
0.36 |
Buses |
|||||||
Gasoline |
1,301.00 |
400 |
40 |
36 |
520.40 |
52.04 |
46.84 |
Diesel |
320.00 |
20 |
20 |
5 |
6.40 |
6.40 |
1.60 |
Butane |
4.40 |
150 |
25 |
30 |
0.66 |
0.11 |
0.13 |
Natural gas |
29.14 |
140 |
22 |
25 |
4.08 |
0.64 |
0.73 |
Total |
4,205.64 |
474.41 |
390.89 |
4.3 Industrial Processes
Greenhouse gas emissions from industrial processes were calculated according to the IPCC Methodology [6, 18]. The following industrial chemical processes were considered: nitric acid manufacture [2], adipic acid manufacture [9], CO2 production and use (the main source is ammonia manufacture, the main consumer is carbamide manufacturing), cement production (calculations were based on clinker production volume), lime production and use (the main consumers are the sugar industry and construction), limestone use (the main consumers are iron and steel production [20], and glass manufacture), and soda manufacture and use.
Emission estimates for carbon dioxide and nitrogen oxides (Table 4–8 and Table 4–8) are based on statistical data on production volumes [14] and national emission factors obtained from stoichiometric equations for chemical reactions.
Table 4–8. CO2 Emissions from Industrial Processes in Ukraine, Gg
Source |
Emissions |
Cement production |
8,745.31 |
Lime manufacture and use |
4,531.40 |
Soda manufacture and use |
987.41 |
Limestone and Dolomite use |
10,968.95 |
CO2 use and production |
6,543.38 |
Total |
31,776.45 |
Table 4–9. NOx Emissions from Nitric and Adipic Acids Production in Ukraine, Gg
Source |
Emissions |
Nitric acid manufacture |
7.51 |
Adipic acid manufacture |
0.82 |
Total |
8.33 |
Table 4–10 contains CO, NOX Nmvocs emissions estimations for а number of industrial processes. Production volumes were obtained from the national statistics, and emission factors were taken from industrial emission standards for the former USSR.
Table 4–10. Indirect Greenhouse Gas Emissions from Industrial Processes
Production |
Volume 1000 tons |
Emission Factors, kg/t |
Emissions, Gg |
||||
CO |
NOx |
Nmvocs |
CO |
NOx |
Nmvocs |
||
Blast-furnace Sinter |
60,926.50 |
32.80 |
0.40 |
- |
1,998.49 |
24.37 |
- |
Iron-ore Pellets |
27,916.80 |
0.27 |
0.31 |
- |
7.54 |
8.65 |
- |
Coke |
34,666.80 |
3.11 |
0.30 |
- |
107.81 |
10.40 |
- |
Rolled Ferrous Metal Produce |
38,600.00 |
1.63 |
0.41 |
- |
62.92 |
15.83 |
- |
Steel Pipes |
6,500.00 |
1.63 |
0.41 |
- |
10.60 |
2.67 |
- |
Steel |
52,600.00 |
2.35 |
0.62 |
- |
123.61 |
32.61 |
- |
Pig-iron |
44,900.00 |
- |
0.09 |
- |
- |
4.04 |
- |
Nitric Acid |
2,780.20 |
3.19 |
- |
- |
8.87 |
- |
- |
Ammonia |
5,149.59 |
1.06 |
0.77 |
- |
5.46 |
3.97 |
- |
Phosphate Fertilizers |
593.00 |
0.21 |
0.04 |
- |
0.12 |
0.02 |
- |
Oil, primary refining |
58,981.30 |
0.03 |
0.001 |
0.90 |
1.77 |
0.06 |
53.08 |
Clinker |
17,500.00 |
20.00 |
2.28 |
- |
350.00 |
39.90 |
- |
Lime |
8,677.00 |
59.30 |
3.19 |
- |
514.55 |
27.68 |
- |
Soda Ash |
1,119.50 |
7.02 |
0.15 |
- |
7.86 |
0.17 |
- |
Acetic Acid |
156.34 |
24.76 |
- |
59.58 |
3.87 |
- |
9.32 |
Formaline |
205.21 |
2.97 |
- |
0.42 |
0.60 |
- |
0.09 |
Total |
2105,998 |
170.37 |
62.49 |
4.4 Agriculture
The main sources of GHG emissions in the category “Agriculture” were enteric fermentation and manure management in domestic livestock, rice cultivation and nitric fertilizers use. Crop residue burning is not widely used in Ukraine, so this source of emissions was not considered.
Initial data for the inventory of GHG emissions from agricultural activities were taken from statistics [14] and documents of the Ukrainian Agrarian University.
The emission factors for livestock were taken from the IPCC Guidelines [6]. The factors for manure were based on the fact that the Crimean region has а warm climate, other regions of the Ukraine have а temperate climate. For example, the emission factor for swine manure management is а weighted average based on the percent of total swine in the Crimean region in 1990 (2.4%) and the Eastern Europe emission factor for а warm climate, plus the percent of total swine in other regions (97.6%) and the Eastern Europe emission factor for а temperate climate: (0.024 x 11) + (0.976 x 7) = 7.10 (Table 4–11).
Table 4–11. Emissions Factors for Ukrainian Livestock
Source |
Enteric Fermentation (kg CH4/ head/year) |
Animal Wastes (kg CH4/ head/year) |
Nondairy cattle |
56 |
13.36 |
Dairy cattle |
81 |
19.40 |
Goats |
5 |
0.17 |
Sheep |
5 |
0.16 |
Swines |
5 |
7.10 |
Horses |
5 |
0.61 |
The IPCC Methodology was used for estimating GHG emissions from rice cultivation. Three regions in Ukraine (the Crimean, Herson, and Odessa regions), have small areas under rice cultivation. The total harvested area in 1990 was 0.0281 Mha. The emission factor was defined using an average temperature of 25°C. The average growing period is 103 days.
Table 4–12 presents CH4 emissions from agriculture in Ukraine in 1990.
Table 4–12. CH4 Emissions from Agriculture in Ukraine, 1990
Source |
CH4 Emissions, Gg |
Enteric Fermentation |
1,702.63 |
Manure Management |
536.40 |
Rice Cultivation |
15.17 |
Total |
2,254.20 |
Assessments of N2O emissions from nitric fertilizers were based on the IPCC Methodology and national statistics and totaled 10.237 Gg.
4.5 Forestry and Land-use Change
In forestry and land-use change, CO2 is mainly emitted as а result of the decay of damaged aboveground biomass and the burning of biomass at harvesting; and forest fires. Forests also sequester carbon (C) in the process of photosynthesis.
Several activities included in the IPCC Methodology for the forestry and land-use change category do not play any significant role in Ukraine. These include conversion of forest to agricultural land, conversion of grasslands and pastures, and abandonment of managed lands, excluding the abandonment zone in the Chernobyl region.
Emissions and uptake of CO2 from forest management and afforestation of Chernobyl zone were estimated according to the IPCC Methodology [6]. For the calculation of the aboveground biomass growth rate, the C ratio in dry matter, and the wet-to-dry wood-weight ratio, data from national statistical publications were used [7, 8, 10, 19].
A method similar to the IPCC for forest clearing was used to estimate CO2 emissions from forest fires. The difference between brush fires, which primarily destroy forest floor, and top fires, which destroy the tree layer, was taken into account. Average CO2 emissions and uptake estimates were obtained for 1990 through an analysis of forest fires during а 9-year period (1986-1994).
Table 4–13 shows the estimates of CO2 emissions and uptake from forestry and land-use management.
Table 4–13. CO2 Emissions and Removals in the Category “Land Use Change and Forestry”
Source |
CO2 Emissions and Removals, Gg |
Forest Managed |
-72,321.3 |
Harvests |
20,683.7 |
Forest Fires |
81.8 |
Abandonment of Lands |
-420.6 |
Total |
-51,976.4 |
4.6 Waste
The IPCC Methodology [6] was used to determine CH4 emissions from solid and liquid wastes.
One of the most important ecological problems in Ukraine is MSW management, annual increment of solid wastes totals 1.5 to 2% [16, 17]. According to national statistics, MSW was estimated to be 11 million tons in 1990, about 8% of which was treated on incineration plants in Kyiv, Kharkov, and Sevastopol. Methane was not recuperated from landfills in Ukraine in 1990 and CH4 emissions from MSW totaled 885.5 Gg.
N2O emissions from solid waste incineration were estimated according to IPCC methodology. The volume of incineration totaled 880 thousand tons, emission factor was taken as the average value of 26-270 grams of N2O per ton of waste. N2O emissions from waste incineration totaled 0.13 Gg in 1990.
Under Ukrainian conditions, rural wastewater decomposes under aerobic conditions. Therefore only urban wastewater was taken into account. In 1990, 3,684 million m3 of municipal wastewater were made in Ukraine, of which 3,597 million m3 (97%) were processed in sewage disposal facilities [12]. Wastewater treated under anaerobic conditions accounts for 15% of the total wastewater in Ukraine. To calculate CH4 emissions from municipal wastewater, biochemical oxygen demand (BOD) in municipal wastewater was defined as 0.05 kg/person/ day. Applying the IPCC CH4 emission factor of 0.22 Gg CH4/gg BOD, emissions from municipal wastewater were estimated as 40.7 Gg CH4. Taking into account recuperation of 6.24 Gg CH4 on sewage disposal facilities in Kyiv and Kharkov [4], methane emissions from liquid wastes totaled 34.46 Gg.
Table 4–14 presents the results of the emissions assessment for industrial wastewater.
Table 4–14. CH4 Emissions Assessment for Industrial Wastewater in Ukraine
Industry |
Annual Wastewater, million m3 |
Wastewater Treated at Disposal Facilities, million m3 |
CH4 Annual Emission, Gg |
Iron and steel |
1,790.0 |
755.0 |
1.08 |
Nonferrous metals |
25.9 |
11.1 |
0.02 |
Fertilizer |
537.5 |
320.1 |
1.94 |
Food and beverages |
197.4 |
68.7 |
5.08 |
Pulp and paper |
102.1 |
93.6 |
1.04 |
Petrochemical |
26.5 |
14.9 |
0.41 |
Textiles |
31.8 |
31.5 |
0.94 |
Miscellaneous* |
85.8 |
3.60 |
|
Total |
1,380.70 |
14.11 |
* Microbiologic industry, transport, construction, and building materials production are accounted.
4.7 References
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- Atroshchenko V. I., and S. I. Kargin. 1980. The Nitric Acid Technology. Chemistry, Moscow.
- Bykov, G. A., I. N. Karp, and A. I. Pyatnichko. 1993. The concept of balanced production and liquid and gaseous hydrocarbonic motor fuels consumption in Ukraine. Journal of Ecotechnologies and Resources Saving 4:9-13.
- Horudgy, P. D. 1993. Exploitation of Water Supplying Systems and Sewer System. Science, Kyiv.
- IPCC (Intergovernmental Panel on Climate Change). 1992. Climate Change 1992, The Supplementary Report to the IPCC Scientific Assessment. Cambridge University Press, Cambridge. 200.
- Ipcc/oecd (Intergovernmental Panel on Climate Change/ Organization for Economic Cooperation and Development) Joint Programme. 1994. IPCC Draft Guidelines for National Greenhouse Gas Inventories. Ipcc/oecd Joint Programme, Paris. 3 Volumes.
- Ministry of Forestry. 1989. Forestry of Ukrainian SSR. Kyiv.
- Molchanov, A. A. 1971. Productivity of Forest Biomass for Different Zones. Science, Moscow. 276.
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- Regulative and Reference Materials for Taxation of Forestry of Ukraine and Moldova. 1987. Harvest, Kyiv.
- Shpack, P.p., and B.l. Krupsъky. 1995. Oil and gas supplying problems in Ukraine. Journal of Energy Conservation Problems 1:15-20.
- State Committee For Water Resources of Ukraine. 1991. The Report on Water Resources in Ukraine for 1990. Kyiv.
- State Statistical Committee of Ukraine. 1991a. Atmospheric Air Protection in Ukraine for 1990. Kyiv.
- State Statistical Committee of Ukraine. 1991b. Economy of Ukraine in 1990. Kyiv.
- State Statistical Committee of Ukraine, 1991c. Energy Balance of Ukraine for 1990. Kyiv.
- State Statistical Committee of Ukraine. 1991d. The National Report on Environment of Ukraine. Kyiv.
- State Statistical Committee of Ukraine. 1991e. Ukrainian Production. Kyiv.
- UNEP, OECD, IEA, IPCC (United Nations Environment Programme, Organization for Economic Cooperation and Development, International Energy Agency, Intergovernmental Panel on Climate Change). 1995. IPCC Guidelines for National Greenhouse Gas inventories. IPCC, Bracknell. 3 Volumes.
- Usolъtsev V. A. 1985. Structure and Dynamic of Phytomass of Timber Stands. Forestry, Krasnoyarsk.
- Vegmon, E.f. 1989. Metallurgy of Iron. Metallurgy, Moscow.
- Zabigajlo, V.e. 1995. Ukrainian coal industry development. Journal of Energy Conservation Problems 1:3-7.
- Country study on Climate Change in Ukraine: Development of Greenhouse Gas Emissions Inventory. Final Report. Agency for Rational Energy Use and Ecology, Kyiv, 1995.
- Country study on Climate Change in Ukraine: Development of Greenhouse Gas Emissions Inventory. Final Report. (Supplement). Agency for Rational Energy Use and Ecology, Kyiv, 1995.
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