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Strategic Analysis of the Environmental Challenges for Northwest Russia
4. Sector Specific
Environmental Challenges
This chapter provides an overview of key environmental problems in three sectors, based on
their significance for the people in Northwest Russia and the Baltic Sea environment.
- The water sector (Section 5.1)
- The energy sector (Section 5.2)
- The waste sector (Section 5.3)
4.1 Environmental Challenges in the Water Sector
During the Soviet period Russia maintained as compared to e.g. West Europe
a high service level in urban areas concerning water supply and wastewater
collection and treatment. The problem today is therefore not always lack of access to
these services because of their nonexistence but the poor or non-functioning of systems
mainly due to lack of maintenance. Much of the equipment is broken down or heavily energy
consuming, whereas structures are of sufficient quality or can be rehabilitated.
Therefore, rehabilitation and retrofitting existing plants could be more cost-efficient
and in general be more adequate than investing in new plants. Public utility systems in
the water sector are generally designed for capacities much above required levels and are
thus inefficient.
The following section focuses on problems related to protection of drinking water
resources, water supply and wastewater disposal including collection, treatment and sludge
handling. As signatory of the London Protocol, Russia is committed to address
environmental and health problems related to water simultaneously. However, the
implication of the present problems for public health is outlined first to illustrate the
necessity to intervene now and in a cost-efficient manner.
Wastewater treatment
and drinking water quality are inadequate for about 500,000 residents of the city of
Kaliningrad. While around 160,000 cubic metres of wastewater are generated by the city
every day, the existing more than 50 years old waste water treatment plant can only cope
with 68,000 cubic metres, and the new treatment plant is not expected to be ready until
2005, says the Commission. In total, 150 million cubic metres of untreated industrial and
municipal sewage, containing more than 30,000 tonnes of pollutants, are emitted into the
region's rivers every year. In turn, this flows into the Vistula and Curonian lagoons
which, together with adjoining wetlands, are also listed as pollution hotspots. |
www.helcom.fi, Press Release 27.04.01
4.1.1 Impact on public health
Outbreaks of infectious diseases related to water supply or recreational waters are
frequent in the Russia. According to WHO Regional Office for Europe, Russia had in year
2000 an infant mortality rate of 18 per 1000 live births, more than double of Western
Europe and an under-five mortality rate from diarrhoeal diseases of 9.3, more than 10
times higher than Western Europe.
In 1999, the Harvard School of Public Health conducted a detailed survey of the
relationship between gastrointestinal diseases and microbiological pollution of drinking
water in the City of Cherepovets, Vologda region. The study demonstrated that
approximately 90% of adults had antibodies to cryptosporidium in their blood indicating a
high frequency of exposure to this pathogen14.
In August 2001, the Russian Security Council Commission on ecological security stated
that drinking water quality in Russia is endangering human lives because of its
contamination with industrial waste15 (from
old dump sites).
4.1.2 Drinking water resources
Drinking water resources are contaminated from the following sources:
 | discharge of domestic or industrial wastewater to rivers or lakes |
 | seepage to groundwater from individual sanitation systems |
 | seepage into both surface and groundwater from dump sites of all kinds |
 | seepage or overspill from storage of sludge from wastewater treatment (domestic and
industrial) or from storage of farm manure. |
 | seepage of sewage pipes to water supply systems |
Urban areas generally draw their raw water from surface water sources, whereas rural
areas typically rely on shallow wells. About 60% of the population16 are supplied with water from surface water sources.
According to the national classification of surface water, most Russian rivers and
lakes are classified as "moderately polluted" or "polluted" and less
than 1% can be abstracted without treatment. Within this classification the Neva River,
the main drinking water supply source of St. Petersburg, is characterised as
"polluted"17. In Northwest
Russia 40% of the drinking water does not meet chemical standards and about 25% does not
meet microbial standards18. Poor raw
water quality due to bacteriological and chemical contamination of water sources,
inadequate water treatment facilities and leakages in the distribution systems are seen as
main reasons for not maintaining a safe drinking water supply.

Figure 4.1
Water test from primary sources* not meeting hygienic and sanitary standards
* Including ponds, reservoirs, wells etc. Source: GOSKOMSTAT, 2001
4.1.3 Water supply
The supply of water is facing the following problems:
 | excessive water consumption |
 | excessive water loss |
 | poor water quality |
 | interrupted supply |
 | excessive energy consumption |
 | inefficient water treatment |
As compared to the Soviet period, domestic water consumption in Northwest Russia has
been reduced significantly reaching an average 245 litres /capita/day19. However, this level is still twice the consumption of
western European countries. The major reason for this excessive consumption is an
in-efficient distribution system with a high level of losses, leaking in-house fittings
and wasting of stored water (preventive measure against interrupted supply) as well as an
insufficient tariff structure not providing appropriate incentives for reducing
consumption.

Figure 4.2
Total water consumption* 1990-2000
Source: GOSKOMSTAT, 2001
According to the National Environmental Action Plan for Russia, more than half of the
country's water supply systems, including the central-ised water supply systems in
virtually all cities and towns, need to be renovated or rebuilt. The present water losses
are reported to be 40 -50% of the abstracted amounts of water, which is very high,
compared to the levels of typical Western countries of 5 - 15%.
The poor condition of the supply system is also reducing the water quality when
contaminants are entering the pipe system at low (or negative) pressure. This situation
occurs when the water supply is interrupted either during repair or when pumps are stopped
to save energy.
Intermittent water supply requires people to store water for periods of non-supply.
This leads to risk of contamination during storage and poor hand hygiene as washing hands
become unpractical (when you are used to having a tap). It also leads to wasting of
excessive stored water when fresh supply becomes available.
Pskov City is supplied with
drinking water from the Velikaja River. After treatment the water is distributed through
two major pumping stations into the city network. Due to leakages and frequent bursts in
the network about 50% of the produced and treated water is lost or wasted.
The yearly power consumption in the pumping stations totals about 20
million kWh. Pumps with optimal efficiency and adequate controls would provide savings of
25-30% of the present energy consumption. Reduction of network leakages to a realistically
obtainable level of 20% will result in additional energy savings leading to a total
reduction in power consumption for water distribution of about 50%. |
Source: Danish Environmental Protection Agency project document, 2002
Water treatment plants do not sufficiently address the water quality problems of
microbiological components like cryptosporidium (parasite). These parasites are a
widespread problem in Russian water supply. Another problem encountered in many of
Northwest Russias waterworks, using surface water, is pre-cautionary chlorination in
the process of water purification, which leads to the formation of carcinogenic
chlororganic compounds in drinking water.
4.1.4 Wastewater disposal
Wastewater collection and treatment represent another major environmental challenge for
Northwest Russia. About 55% of the Russian population is serviced by centralised
wastewater collection and treatment systems. The wastewater treatment facilities need
maintenance: Of the 76% of wastewater treated, only about 10% is treated according to
required standards20.
The main problems facing disposal of wastewater are:
 | leaking and collapsing sewers |
 | hydraulic overloading of system from stormwater and infiltrating ground-water |
 | discharge of untreated wastewater |
 | insufficient treatment of wastewater |
 | unsafe disposal and low utilisation of sludge |
 | excessive energy consumption for transport and treatment |
A major source of pollution in the
Baltic Sea is the old (>50 years) and malfunctioning sewage and wastewater treatment
system in St. Petersburg. Since 1992, the amount of untreated wastewater coming from the
sewers has been halved and the amount of phosphate discharged curbed substantially.
Nevertheless, half a million cubic metres of untreated municipal and industrial wastewater
is still washed into the river Neva and its tributaries every day. In addition, 200,000
cubic metres of untreated industrial wastewater are flushed directly into the river from
industrial outlets |
Source: HELCOM Task force hot spots review
Wastewater collection system
The wastewater collection system (sewer network) in Northwest Russia is generally
of a poor quality and has seriously deteriorated due to lack of repair and maintenance
over a considerable span of years. Leaking sewers pose a considerable threat to aquifers
and surface water bodies, endangering the drinking water supply. Sewer pumping stations
face frequent breakdowns, which in combination with sewer blockages result in severe
overflows.
Wastewater treatment
Urban wastewater
Most of Northwest Russia's wastewater treatment plants is designed for mechanical and
biological treatment for removal of organic matter. Generally, there is limited removal of
nutrients like nitrogen and phosphorus. Most of the plants do not comply with required
standards, which result in excessive pollution loads being discharged into receiving
waters with subsequent risk of health hazards, eutrofication and oxygen depletion.
The most widespread pollutants present in discharges into water bodies or catchment
areas are oil products, suspended solids, nitrogen, phosphorus, synthetic surfactants,
zinc and copper compounds, and phenols21.
The treatment technology in Northwest Russian wastewater plants is, generally
speaking, in line with internationally accepted principles as regards the process
configuration. However, the plants suffer from severe lack of maintenance, obsolete and
inefficient equipment and lack of appropriate control systems.
Rural wastewater
Wastewater treatment in the rural areas is characterised by low coverage by public
utilities. A significant number of people living in rural areas are thus responsible on
their own for handling and disposal of their wastewater. As the financial situation in
rural villages is not favourable, the scope for improving or just maintaining local
facilities is limited.
Disposal of Sludge
Sludge from wastewater treatment constitutes a severe threat to the soil quality
and ground and surface water resources. The sludge is often poorly stabilised and
previously contained large amounts of heavy metals and other toxic or recalcitrent
substances. However, the decrease in industrial production has generally resulted in a
substantial improvement of the sludge quality, thereby reducing the risk of contamination
from sludge presently produced and disposed of.
Where sludge is still stored in lagoons it imposes a risk of contamination of streams
and rivers due to frequent overflows of aquifers and due to pollutants seeping into the
ground.
4.1.5 Energy consumption in the water sector
Energy consumption in wastewater pumping stations is generally excessive due to
inefficient control measures, inadequate pumping equipment and lack of maintenance. The
energy consumption is estimated to be two to three times larger compared to corresponding
western installations of similar capacity and nature. The efficiency of wastewater pumping
stations reaches only 15-20%, and electricity over-consumption for all Russia amounts to
2.5 billions kWh annually22.

Figure 4.3
Wastewater treatment efficiency (expressed as discharge/person equivalent
(PE)/year in treatment plants larger than 30 PE of b) BOD5 (biological Oxygen Demand in 5
days), c) Phosphorous and d) nitrogen. Assessment from 1998 Kaliningrad (Russia), Elblag
(Poland), Pârnu, Ostro-botnia (Finland), Fyn (Denmark) and 1999 Laholm Bay area (Sweden)
and Schleswig-Holstein (Germany)
Source: Strategies for improved Eutrophication Management in the Baltic Sea Region,
Bernet., p.
Energy consumption for groundwater pumping, water treatment and supply exceeds by a
factor 2 to 3 the kWh/m3 needed when using modern pumping equipment combined with
efficient operations control. Investments in pump replacements often have a payback period
of less than 5 years. One reason is that pumping stations in Northwest Russia are not
usually equipped with special devices regulating their output upon demand, and the
regulation of output is carried out by manual operation of valves. As a result, the
efficiency of the pumping station does not exceed 35-40%. For all Russia, the annual
electricity losses amount to 5-5.5 billions kWh due to this reason only.
The mechanical/biological treatment
plant in Novgorod receives wastewater loads corresponding to about 190,000 inhabitants
(calculated as Population Equivalents (PE)). The annual power consumption at the plant is
25 million kWh or 135 kWh/PE*year. Typical figures for Danish treatment plants of a
similar size lie between 30-45 kWh/PE*year.
The excessive energy consumption is mostly attributable to inefficient
aeration systems and poor or non-existing process control. |
4.1.6 Water Sector Financing
The low level of revenue generated from the user charge payments is the core of the
financing problems experienced by the water utilities.
 | Many utilities have not been allowed to raise tariffs to levels that would allow them to
collect enough revenue to cover O&M costs; cross-subsidies between industrial and
domestic consumers remain very high (in average industrial tariffs are about six times
larger than domestic tariffs); the industrial recession and the large industrial tariffs
have forced industries in some Vodokanals to find alternative sources of water; and the
domestic tariffs have not been noticeably increased between 1997 and 1999. |
 | The reduced industrial consumption of water during the 1990s and resulting decline in
payments from industrial consumers have further aggravated the financial status as the
industrial consumers are the main source of revenue. |
The environmental financing
strategy carried out for Pskovs water sector compared estimated expenditure
associated with operating the municipal water services (water supply and wastewater
treatment) and the estimated flow of financing during the period 2000-2020. The situation
in Pskov in the base year 2000 was:
 | a concern regarding drinking water quality due to secondary
pollution in the deteriorated water distribution network
|
 | wastewater treatment appears to be close to or in line with EU
standards, but the operating efficiencies of the plants are low
|
 | the infrastructure for sewage collection is well developed and the
service level better than in many countries with similar income levels, but the sector
suffers from years of underinvestments, lack of systematic maintenance, and the networks
have deteriorated
|
The financing strategy concluded that the requirement for sustainable
operation and maintenance would be RUR 491 million per year. This is the expenditure
required to continue with the present level of service. However, the study of supply of
finance revealed that the level of financing was in the area of RUR 160 million per year.
The strategy therefore highlighted a major financing gap and concluded that supply of
finance needed a major shift upwards in order to sustain the present level of service. |
Source: OECD, Danish Environmental Protection Agency: "Short Justification for
the Municipal Water and Wastewater Financing Strategy, Pskov", 2001
4.1.7 Natural Resource Management
When analyzing the challenges faced in the water sector, there is an urgent need to
understand the interrelationship between these challenges and issues related to
biodiversity and Natural Resource Management.
Problems concerning biodiversity and nature protection include amongst other resource
extraction and pollution, poorly planned and executed commercial forestry, construction
and transport activities, insufficiently regulated hunting. Furthermore, these problems
are aggravated by uncertainty about future ownership of land and resources and low
environmental awareness among administrative staff, decision-makers, and the general
public. Also, regional policies are lacking realistic implementation plans, and common
principles and standards for resources management including overall strategy for
development of protected areas, Ramsar sites etc. The planning is impeded by a lack of
cost effective environmental monitoring systems which are able to provide reliable data
and information for use in planning, management and conservation of natural resources.
There is a need to improve spatial planning/landscape planning tools to adequately
preserve natural resources as eg. water bodies, streams and lakes, incl. ground water
protection. The point of departure should be a holistic approach, with comprehensive
co-ordination and co-operation between relevant regional and local authorities which would
also be a mean to allocate resources more effectively.
Capacity building in North West Russia's environmental administrations with particular
focus on implementation of international conventions and agreements relevant to nature
protection is essential. Networking with other international protected areas should be
encouraged as a mechanism for capacity building of protected areas staff.
4.1.8 Facing the challenges in the water sector
Because of the close interrelationship between wastewater disposal and water supply the
concept of total water management must be empha-sised in Northwest Russia.
Part of this concept is to prioritise investment to ensure the best use of the limited
resources. Proper planning and investigations of perceived problems like groundwater
pollution or a health impact can confirm a problem or on the other side lower the priority
for an intervention.
Furthermore, the total water demand concept demands for efficient water demand
management to ensure lower water consumption and economically and environmentally suitable
management of utilities.
Financing strategies carried out for the regions of Pskov and Novgorod also pointed to
the need for strategic investments in energy saving equipment as well as renovation of the
water supply networks and other water saving initiatives, including lower consumption
levels. Relatively small pilot interventions in this area should be implemented to
effectively demonstrate needed win-win solutions, that brings down operational expenses
and hence have a short payback period.
Finally, the total water management concept demands for:
 | Management strengthening and operational performance improvement initiatives at public
utilities; |
 | Integration of river basin management plans in investment planning; and |
 | Improved monitoring and regulation. |
With regard to rural areas, individual water supply and wastewater disposal systems
should be centralised only when found both financially and environmentally feasible, as
individual systems are not necessarily a prioritised environmental or health problem.
Concerning health issues, there is a need to identify more precisely which infectious
diseases are related to water quality and how they are most efficiently addressed.
Similarly the chemical components that locally are having a potential impact on public
health should be identified and monitored.
As laboratories in Northwest Russia at present can not analyse all drinking water
standards, "problem" components must be identified and subsequent interventions
should be initiated at the most efficient place. Some components must be removed at the
source where others must be removed at treatment plants or prevented from entering supply
systems.
It should be noted that contamination of sludge by heavy metals and other industry
related toxic or otherwise dangerous substances must be handled at source i.e. at the
industries.
The technical solutions for solving the problems and obstacles within water supply,
wastewater collection and treatment are well-known and well-proven technologies exist, for
instance:
 | rehabilitation of sewer system with priority to replacement of pipes in emergency
conditions, either by nodig methods or by replacement of sewer pipes |
 | replacement of pumps in order to reduce the number of breakdowns and to decrease the
present high energy consumption |
 | rehabilitation of existing water supply and wastewater treatment facilities including
implementation of new modern technology for water and wastewater treatment and
installation of new less energy consuming equipment and control and monitoring systems |
 | further investigate groundwater resources as alternative to surface water and where
deemed relevant thorough feasibility studies must be conducted to ensure technical,
economical and financial feasibility |
 | possible environmentally and hygienically sound improved sludge handling and disposal
includes: anaerob or aerobic stabilisation, sludge dewatering by mechanical dewatering
facilities for major plants and sludge drying beds for minor plants, sludge drying and
incineration, utilisation in agricultural and horticultural areas, biological
recultivation of disturbed lands and landfills, and disposal at controlled landfills |
In Jan 2003 the 3rd session of the
Coordination Council for National Action Program "Water of Russia the 21st
Century" was held in Moscow.
Development of the National Action Programme was initiated by the
Ministry of Natural Resources of the Russian Federation with the objectives to overcome
the inter-agency and territorial contradictions in water management and to activate the
relevant economic and legal mechanisms, with the river basin management principle as a
background.
Among others, the program will comprise the following key components:
 | Meeting the demand for water resources
|
 | Prevention of negative impacts of waters
|
 | Safety of river engineering facilities
|
 | Management of national water resources
|
 | Protection of water bodies against pollution
|
 | Introduction of economic mechanisms in water management
|
The President and the Government of the Russian Federation support the
development of the Program. The Working Group and the Expert Council established by them
for this matter are to make a presentation of the Program for the President. A meeting of
the Working Group is scheduled for Jan 28. |
Source: Press-Service of the Ministry of Natural Resources of the Russian
Federation, Jan 16, 2003.
Areas of particular relevance for international co-operation
Within the water sector, the following international environmental agreements are of
particular relevance to co-operation, as Russia is signatory to all three:
 | Convention on Protection of the Marine Environment of the Baltic Sea area |
 | the UN-ECE Water Convention on Protection and Use of Trans-boundary Water Courses and
International Lakes |
 | The London Protocol on Water and Health |
The international co-operation regarding these three international environmental
agreements has received significant attention in the Russian co-operation already, and
this effort should be maintained or even further improved.
Furthermore, future co-operation in the water sector shall be seen as a building block
in the regional EU Water Initiative (WI) for the EECCA23 region which was agreed on at the World Summit on Sustainable
Development in Johannesburg in September 2002. The new regional TACIS programme has as a
specific objective implementation of the EU WI focussing on water supply and sanitation as
well as integrated water resources management and transboundary waters.
Serious environmental challenges are related to the energy sector in Russia. These
include specific environmental problems caused by air pollution and waste handling (see
chapter 4.3), and excessive natural resource consumption due to inefficient use of energy.
Air pollution causes a wide range of health, environmental and socioeconomic impacts.
While some air pollution problems have local causes and impacts, such as within an urban
area, other problems have regional or global implications.
Table 4.1
Principal anthropogenic sources for major air pollutants.
Source |
Pollutants |
PM10
PM2.5 |
SO2 |
NOX |
VOC |
O3 |
HM &
Toxics |
CO2,
GHG |
ODS |
Energy production |
++ |
+ |
+ |
|
(+) |
+ |
++ |
|
Industrial processes |
++ |
+ |
+ |
+ |
(+) |
+ |
+ |
++ |
Transportation |
++ |
+ |
++ |
+ |
(++) |
+ |
++ |
|
Domestic and commercial |
+ |
+ |
+ |
+ |
|
|
+ |
+ |
Agriculture |
|
|
|
|
|
|
|
|
(+) indicates indirect source
Table 4.2
Overview of impacts of major air pollutants.
Impact |
Pollutants |
PM10
PM2.5 |
SO2 |
NOX |
VOC |
O3 |
HM
& Toxics |
CO2,
GHG |
ODS |
Health effects |
++ |
+ |
+ |
+ |
++ |
++ |
|
|
Agricultural & forest
damage |
|
+ |
+ |
(+) |
++ |
+ |
|
|
Visibility degradation |
++ |
(+) |
(+) |
(+) |
+ |
|
|
|
Acidification |
|
++ |
++ |
|
|
|
|
|
Eutrophication |
|
|
++ |
|
|
|
|
|
Stratospheric ozone depletion |
|
|
|
|
|
|
|
++ |
Global warming |
|
|
|
|
|
|
++ |
|
Material damage |
+ |
+ |
+ |
+ |
++ |
|
|
|
(+) indicates indirect impact
Russia has extensive fossil energy resources. Besides supplying its own consumption
of fuels energy exports, particularly oil and gas, account for the main part of
export income to Russia. In domestic consumption coal accounts for 16% of the fuel
consumption, natural gas for 54% and oil for 19%.
Historically, for various reasons (cheap energy, huge distances, severe climate, large
proportion of energy intensive industries in the national economy) energy consumption in
Russia has always been very high. The Russian economy is dominated by large
energy-intensive industries. Furthermore energy use is in generally inefficient as
compared to international norms due to low energy prices, lack of metering and controls
and lack of market incentives to reduce costs.
4.2.1 Energy-related global and local environmental problems
Global/regional
Global and regional environmental problems related to energy production and conversion
include emissions of CO2 and other green house gasses and emissions of air
pollutants leading to acid rain and eutrophication with transboundary implications, for
instance affecting the environment of the Baltic Sea. Russia has met its international
commitments to reduce its emissions of SO2, NOX, and CO2.
However, the reduction in emissions relates to the decline in the Russian GDP, and the
emission reductions have even been slower than the decline in GDP.
The energy sector contributes with 90% of all green house gasses emissions in Russia.
If Russia ratifies the Kyoto Protocol it commits itself to maintain its emissions of CO2
and other greenhouse gases in 2008-12 at the same level as in 1990. The decline in the
Russian economy following the transition of the economy has already reduced the energy
consumption significantly and the country is expected to be in a position to sell carbon
credits to other countries that are not able not meet their targets domestically.

Figure 4.6
Russian and IEA projection of CO2 emissions
Source: IEA 2002, p. 262
Even though Russia has reduced its emissions they still amounted to 11 tonnes of CO2
per capita in 2000. This is similar to e.g. Denmark, but remarkably high considering that
the GDP/capita is 10-15 times lower in Russia. The low energy efficiency in Russia also
results in high CO2 emissions when compared to other countries.
Major emitters of energy related
CO2 in 1996 |
|
Total emissions tonnes |
Emissions per GDP (tonnes/USD 1000) |
United States |
5325 |
0.84 |
China |
3142 |
0.87 |
Russia |
1517 |
2.20 |
Japan |
1178 |
0.45 |
Germany |
905 |
0.64 |
India |
863 |
0.70 |
UK |
583 |
0.57 |
OECD average |
12117 |
0.66 |
OECD, Environmental Performance
Review, p. 192 |
The energy sector accounts for 50% of all harmful emissions to the atmosphere. In the
figure below emission of different pollutants has been added in order to provide a very
rough indicator for the emissions of pollutants to the air to provide an overview of the
main sources of these pollutants. The figure discloses the electricity sector (including
heat generation) as the main source of emission.

Figure 4.7
Percentage breakdown of emissions by sector in 1999
Emissions include SOx CO NOx Methane, VOCs and Particulate
matter.
Source: "State Report on the Ecology in 1999", Moscow 2000
Source: IEA 2002, p. 245
Details on the individual emissions from the energy subsectors are provided in the
table below.
Table 4.3
Air pollution emissions from the energy sector 1993-99 (1000 tonnes)
|
1993 |
1994 |
1995 |
1996 |
1997 |
1998 |
1999 |
1993-99 |
Oil sectors emissions |
1.862 |
1.682 |
1.447 |
1.305 |
1.267 |
1.383 |
1.322 |
-29% |
SOx |
16 |
15 |
19 |
20 |
23 |
23 |
23 |
46% |
CO |
618 |
497 |
438 |
490 |
541 |
657 |
627 |
2% |
Nox |
17 |
16 |
17 |
18 |
21 |
22 |
24 |
39% |
Methane |
900 |
886 |
689 |
535 |
439 |
432 |
446 |
-50% |
VOCs |
275 |
326 |
208 |
210 |
202 |
189 |
143 |
-48% |
Particulates |
36 |
32 |
30 |
32 |
41 |
60 |
60 |
64% |
Production (million tonnes) |
352 |
316 |
307 |
301 |
306 |
303 |
305 |
-13% |
|
|
|
|
|
|
|
|
|
Natural gas sector emissions |
717 |
717 |
706 |
541 |
450 |
425 |
453 |
- 37% |
SOx |
47 |
47 |
47 |
48 |
48 |
51 |
61 |
30% |
CO |
248 |
241 |
206 |
200 |
216 |
204 |
213 |
- 14% |
Nox |
62 |
51 |
28 |
24 |
24 |
24 |
25 |
60% |
Methane |
221 |
207 |
404 |
249 |
145 |
132 |
140 |
- 37% |
VOCs |
136 |
168 |
18 |
17 |
13 |
5 |
7 |
- 95% |
Particulates |
4 |
4 |
5 |
4 |
5 |
8 |
8 |
93% |
Production (bcm) |
618 |
604 |
595 |
601 |
571 |
591 |
591 |
- 4% |
|
|
|
|
|
|
|
|
|
Coal sector emissions |
376 |
661 |
620 |
542 |
487 |
467 |
555 |
48% |
SOx |
56 |
55 |
50 |
42 |
33 |
26 |
20 |
- 63% |
CO |
63 |
67 |
64 |
62 |
50 |
42 |
34 |
- 45% |
Nox |
15 |
16 |
16 |
16 |
14 |
11 |
10 |
- 33% |
Methane* |
- |
418 |
403 |
345 |
320 |
326 |
436 |
4% * |
VOCs |
97 |
0 |
0 |
0 |
0 |
0 |
0 |
- 100% |
Particulates |
109 |
105 |
86 |
77 |
69 |
61 |
54 |
- 50% |
Production (million tonnes) |
285 |
273 |
263 |
257 |
245 |
232 |
249 |
- 13% |
|
|
|
|
|
|
|
|
|
Petroleum refining emissions |
1.182 |
997 |
899 |
842 |
810 |
762 |
740 |
- 37% |
SOx |
197 |
181 |
159 |
144 |
148 |
134 |
136 |
- 31% |
CO |
87 |
64 |
59 |
59 |
49 |
50 |
47 |
- 46% |
Nox |
22 |
21 |
21 |
21 |
22 |
21 |
20 |
- 9% |
Methane |
276 |
228 |
209 |
171 |
80 |
78 |
102 |
- 63% |
VOCs |
589 |
494 |
441 |
438 |
502 |
469 |
427 |
- 27% |
Particulates |
11 |
10 |
11 |
9 |
10 |
9 |
7 |
- 3% |
Throughput (million tonnes) |
219 |
181 |
180 |
176 |
178 |
163 |
169 |
- 23% |
|
|
|
|
|
|
|
|
|
Electricity sector emissions |
5.890 |
5.234 |
4.977 |
4.707 |
4.386 |
4.303 |
3.891 |
- 34% |
SOx |
2.498 |
2.255 |
2.134 |
2.006 |
1.833 |
1.818 |
1.618 |
- 35% |
CO |
191 |
219 |
248 |
259 |
254 |
238 |
242 |
27% |
Nox |
1.384 |
1.200 |
1.137 |
1.109 |
1.055 |
1.021 |
961 |
- 31 % |
Methane |
3 |
4 |
4 |
3 |
4 |
6 |
3 |
23% |
VOCs |
1 |
1 |
1 |
1 |
1 |
1 |
1 |
30% |
Particulates |
1.813 |
1.556 |
1.453 |
1.330 |
1.239 |
1.219 |
1.065 |
- 41% |
Production (TWh) |
957 |
876 |
860 |
847 |
834 |
827 |
846 |
- 12% |
|
|
|
|
|
|
|
|
|
Total energy emissions |
10,027 |
9,291 |
8,649 |
7,937 |
7,400 |
7,339 |
6,62 |
- 31% |
SOx |
2,813 |
2,553 |
2,408 |
2,259 |
2,084 |
2,051 |
1,858 |
- 34% |
CO |
1,206 |
1,088 |
1,015 |
1,070 |
1,110 |
1,191 |
1,163 |
- 4% |
Nox |
1,501 |
1,304 |
1,218 |
1,187 |
1,135 |
1,100 |
1,041 |
- 31% |
Methane |
1,437 |
1,742 |
1,710 |
1,302 |
988 |
974 |
1,126 |
- 22% |
VOCs |
1,097 |
899 |
713 |
666 |
718 |
665 |
579 |
- 47% |
Particulates |
1,973 |
1,707 |
1,585 |
1,453 |
1,364 |
1,357 |
1,195 |
- 39% |
* Comparison of coal sector emissions of methane is far 1994-1999.
Source: IEA 2002, p.246
Local/regional
Apart from the global implications on the environment, energy production has other
negative side effects. The establishment of energy plants and the disposal of by-products
from energy production represent an environmental problem for the local environment, but
can also have regional implications as pollution is washed into the Baltic Sea (see
chapter 4.3).
Health Impact
During the first half of the 1990s pollution levels exceeded Russian air quality
standards (maximum allowable concentration) in cities covering 62% of the Russian
population. One-third of the entire population lives in areas with high pollution peaks.
Emission per unit of GDP of SOX, NOX, particulates, CO, VOCs, and CO2
have all increased during the 90s and remain much higher than the OECD average.
Air pollutant
emissions, 1997 |
|
SOX Per
unit of GDP |
NOX per
unit of GDP |
Russia |
6.0 |
2.9 |
USA |
2.3 |
2.8 |
Germany |
1.3 |
1.2 |
OECD Europe |
2.1 |
1.9 |
OECD Environmental performance review, p. 56
The severe air pollution leads to high frequencies of respiratory diseases in Russian
cities24.
4.2.2 Energy consumption and conversion
Excessive energy consumption and losses in energy conversion and supply are at the
core of the energy related environmental problems in Russia. The Russian energy
consumption in 1999 totalled 6.8% of world total25,
making Russia the third largest energy consumer after USA and China. The industrial sector
accounted for 65% of the consumption, the remaining was split evenly between transport and
residential sectors.
Energy consumption
Households heat and hot water consumption are high not only due to Russias
severe climate but to a higher degree due to technical deficiencies and inadequate
behaviour. Consumers cannot control their individual heat consumption, as there are often
no thermostatic valves on the radiators as central heating systems are normally
one-stringed. At the same time they also lack incentive to reduce consumption of heat and
hot water, as billing is often independent of the actual consumption of the individual
household.
Industries in Russia are very energy intensive, which is reflected in an overall energy
intensity of the country of 84 MJ/$ GDP in 2000, compared to for instance 12 MJ/$ GDP in
USA. Energy consumption in industry includes district heating, electricity and primary
fuels. Historically low energy prices paved the road for heavy energy intensive industry
and little awareness to energy efficiency and officially required energy standards.
Inefficient design and control measures, inadequate pumping equipment, leakages and
insufficient insulation of boilers and pipes often result high electricity and heat
consumption in industries. Further more overdimensioning of pipes, valves and pumps often
causes electricity consumption for pumping purposes to be very high compared to western
systems.
Energy networks
District heating networks are gradually deteriorating due to lack of maintenance (e.g.
leakage and poor insulation of pipes) and reinvest-ments, and some 15% of the pipes in
Russia need urgent replacement.
This results in increasing heat and water losses from the networks. The consequence is
heat losses that on the average are assessed to some 30%.
Emissions and leakages from the oil and gas industries are of significant environmental
importance. Emissions of CO2 and leakages of natural gas from production sites
and the pipes of the national gas company Gazprom alone accounted for 11% of the total CO2
emissions in Russia in 199926.
Energy Conversion
Power generation in Northwestern Russia amounts to 5.6% of total power generation in
Russia and is distributed on thermal power production (coal, gas and oil) 33%, hydro 18%,
nuclear 41% and others 9%. Coal is playing an increasing role as fuel for power production
in Russia, and this is expected to continue at the expense of gas and oil as fuel. The
recent economical recovery has resulted in increased electricity consumption in households
and industries.
Most power plants in Northwest Russia are obsolete by Western standards and seriously
need maintenance and upgrading, resulting in low efficiency power plants. If investments
stay at the present low level, 32% of the current generating equipment is forecasted to be
out of commission by 2005, which may give rise to crisis in electricity production and
lead to regional power shortage27.

Figure 4.8
Electric power and Heat generation
Source: Energy Strategy of Russia (1990 index 100)
District heating consumes about 280 million tons of oil equivalents, corresponding to
about 44% of Russia's total fossil fuel demand.
The overall energy efficiency of combined heat and power plants production in Russia is
around 75-80%. When comparing with international best-practise it should be possible to
reach efficiencies in Northwest Russia of not less than 90% which would imply a reduction
in fuel consumption and emissions of at least 25%.
However, rehabilitation of district heating systems and introduction of decentralised
solutions will entail huge investments, which are also needed to remove pollutants from
flue gases of central heating plants and boiler stations.
4.2.3 Energy sector reforms and strategy
In 2001, the Main Provisions of the Russian Energy Strategy to 2020 was approved by the
Russian government. The Strategy provides an overview of problems facing the energy sector
and resolutions needed to support general economic growth and reform. However, due to
criticism as to the reality of the implementation of the Strategy a revised version is
presently under preparation.
Sector reforms within in the oil,
gas, coal and electricity industries have been implemented or are on their way/being
considered.
The oil industry has only had limited foreign investments due to
the unstable investment climate. In order to overcome the uncertainties to investors,
Product Sharing Agreement legislation is being debated in the Russian Parliament as
foreign capital and expertise are needed for the development of the industry. A new
pipeline to the Baltic Sea is under construction to allow for increased oil export.
The gas sector is currently being considered reconstructed in
order to split the monopoly of Gazprom into several up stream production companies and to
allow equal access for gas producers to the transmission network to foster competition on
the Russian market. New pipelines are under construction and the Russian government aims
to increase its export to Western Europe in the next decade.
The coal sector holds the world's second largest coal reserves.
The industry was restructured in the mid 1990s as the state coal company was phased out
and production subsidies were ended. After a period of decline, since 1998 production has
increased and in 2000 reached 281 million tons. Domestic use of coal is given priority in
the Russian governments energy planning in order to allow for larger exports of oil
and gas.
The power sector lacks funds for maintenance and repair. To
improve the performance of the sector and to attract foreign investors the Russian
government in 2001 approved a plan for restructuring of the power sector monopoly UES. The
restructuring will break UES into separate generation and distribution units, and after
2004 the wholesale and retail electricity market will be liberalised. |
4.2.4 Difficulties related to institutional and pricing issues
Organisational and financial difficulties are at the heart of the environmental
problems in the energy sector and need to be addressed. Difficulties arise in the
interface within the energy sector and between energy companies and consumers.
Fuel prices
Low fuel and energy prices have a long history in Russia and this has negatively
influenced incentives for heat and power plants, industries and public utilities to
increase energy efficiency.
Tariffs
In the Energy Strategy, tariffs were planned to increase to cover longterm costs by
2010. In reality, however, the tariffs recently approved by government on gas and
electricity as well as the planned increases announced for 2003-2005 fall significantly
behind the tariffs envisaged by the Energy Strategy.
Table 4.4
Selected tariffs and fuel prices
|
2002 |
Forecast 2010 |
Russia |
European average |
Russia |
Electricity, US c/kWh |
1,311 |
6-12 |
3,6 |
Natural gas, USD/1000 m3 |
18 |
100 |
30-55 |
Crude oil USD/toe |
47 |
220 |
100 |
Steam coal USD/toe |
30 |
|
54-60 |
1. Average for households and industry in Russia
Sources: Energy Strategy of Russia, EIA 2002, p.209, and data collected by COWI
Moscow
The tariffs on electricity for Russian industries are higher than for households and
traditionally large cross subsidies have been provided from industry to the residential
sector.

Figure 4.9
Residential and industrial electricity tariffs in Russia
Source: IEA 2002, p. 209
Lack of funding
Similar to the public utilities in the water sector, energy companies lack funds to
finance maintenance and investments. Tariffs typically only cover operational costs, i.e.
fuel, operation and limited maintenance costs.
The District Heating distribution
systems in Russia are old and worn out. 25 % of the capital assets have fully exceeded
their service lifetime, and breakdowns in the heating networks have increased
significantly during the last 10 years.
Another problem is that the District heating networks have poor
thermal insulation and often significant leakages resulting in major heat loss and
groundwater pollution. Loss of heat is far higher than the norm and represents
approximately 30% of the produced heat.
Preventive maintenance is downscaled due to lack of funds, though,
emergency and rehabilitation works cost 2-2.5 times more than the planned maintenance of
the same facilities. |
4.2.5 Environmental nuclear challenges
15% of Russias energy production originates from 9 nuclear power plants with 29
reactors in total. While European countries as Sweden, Germany, Belgium and the
Netherlands are aiming at a downscaling their present levels of nuclear power production,
Russia is expanding its nuclear power production capacity.
Russia is currently planning to upgrade/renovate a number of reactors and plans to
construct five new reactors in the coming 5 to 7 years and additional 10 reactors in the
following 10 years28. The realisation
of these very ambitious plans is threatened by lack of financial resources. Minatom
receives limited revenue for the electricity delivered (65% in 2000) and consequently the
investments are only 20% of what was originally planned. The major non-paying consumers
are mainly state-owned companies.
It is the declared objective of the Minister of Minatom that Russia should be an
important player on the international market in relation to nuclear issues. Russia exports
nuclear power plants to, amongst others, China, India, Iran, and exports uranium and
electricity and has lately started to receive used nuclear fuel for storage.
International support
A long range of countries have on a bilateral basis been involved in tackling the
nuclear problems Russia faces and e.g. the US has contributed with 7 Billion USD since
199229. The EU and Russia are currently
negotiating on the terms for a "Multilateral Nuclear Environmental Pro-gramme in the
Russian Federation (MNEPR)" which is supposed to become the framework for donors who
seek to contribute to the nuclear stability and safety in Northwest Russia. However, it
has not yet been possible to conclude this agreement.
In the summer 2002, the Northern Dimension Environmental Program-me pledged Euro 62
Million earmarked for nuclear projects in Northwest Russia including handling of spent
nuclear fuel (see chapter 4.3.6). However, the implementation of these projects is
dependent on the successful signing of the Multilateral Nuclear Environmental Programme in
the Russian Federation.
Safety
The 1986 Chernobyl disaster is a clear illustration of the risks connected to old and
worn-out nuclear power plants. Today, 16 years later nuclear generated power still
represents an important part of Russias energy production and although the
safety-conditions in the Russian nuclear power plants have been considerably improved
during the 1990s they still give rise to concern30.
The Leningrad Atomic Energy Station
is located 70 kilometres west of St. Petersburg in Sosnovy Bor. The Leningrad Atomic
Energy Station has 4 RBMK-1000 Chernobyl-style reactors and produces app. 50% of the
energy in the St. Petersburg region. The first generation reactors were constructed in the
late 1960s and the second generation reactors in 1979 and 1981. The construction of two
new MKER-800 reactors (a modernised version of the old RBMK reactor), which will replace
the first generation reactors, has started.
Since 1991, more than Euro 65 Million have been invested by foreign
donors in safety equipment in the Leningrad Atomic Energy Station. Nonetheless, the safety
is highly criticised and critics claim that the first generation RBMK reactor type is
amongst the most unsafe in the world due to outdated technology. The International Atomic
Energy Agency (IAEA) is of the opinion that the RBMK reactors should be shut down. |
www.bellona.no
4.2.6 Facing the challenges in the energy sector
Reduced energy consumption and increased efficiency in energy production and supply are
the most efficient ways and must be pursued to reduce the environmental and
health problems caused by the sector. This calls for establishing an institutional and
financial set-up that provides these means and incentives.
Tariff setting must reflect the real longterm cost of producing and supplying energy
and natural gas. This requires that:
 | not only fuel cost but also operational and maintenance cost and depreciation of capital
and equipment are allowed to be included in tariffs |
 | the regional regulatory boards approving tariffs must operate on an arm length and be
independent of local government also in practical terms, and that transparency in tariff
setting is ensured |
 | social concerns for low income families are dealt with not through tariffs but for
instance through direct subsidies or other means |
In the heat sector, installation of control equipment, meters and billing according to
consumption should be introduced both in the domestic, industry and service sectors. This
calls for:
 | huge investments in thermostatic valves and other control equipment, as well as the
required adjustments of existing heating installation, so that the families and consumers
are enabled to control their heat consumption |
 | installation of heat and hot water meters in households and service sector |
 | billing of heat and hot water according to consumption |
Most energy plants in Northwest Russia are in a serious state of disrepair. It is
pivotal that sufficient financial resources be allocated to this sector to avoid more or
less permanent regional power shortages in the coming years, which would have significant
negative impact on the economical activities in Northwest Russia.
Tremendous spills and leakages from pipelines losses further aggravate the situation
and preventive measures should be taken. Furthermore, increasing oil export on tankers
through the Baltic Sea poses a higher risk of accidents and oil spills if no additional
measures are taken. This demands for:
 | Increased minimum requirements to contingency plans and safety equipment and quality of
oil tankers passing through the Baltic Sea |
 | Increased monitoring of the Baltic Sea region to spot oil spills and identification of
guilty parties and subsequent enforcement of the polluter pays principle. |
With regard to nuclear energy, replacement of first generation RBMK reactors is
urgently needed as these are classified as being amongst the most unsafe in the world due
to outdated technology. Also contingency plans and more efficient monitoring systems
should be developed.
Areas of particular relevance for international co-operation
Co-operation could include preparatory work still needed for Russia's signing of the
Kyoto Protocol e.g. technical support, awareness raising and demonstration activities
Furthermore, the scope for Joint-Implementation activities should be pursued.
Finally, Russia should further strengthen its international alliances and efforts
toward fulfilling the obligations of being signatory to the Geneva Convention on
Long-Range Transboundary Air Pollution as well as the Vienna Convention on Protection of
the Ozone Layer, specifically the Montreal Protocol and its amendments.
There are several critical environmental impacts linked to the practises for handling
waste in Northwest Russia. Deficient waste management has a major bearing on the state of
the environment in the Baltic Sea and on issues related to water quality, soil pollution,
and human health. A number of the HELCOM hot spots in Russian territory are in fact
related to waste issues, and are attributable directly to waste management plants or
industries discharge of various hazardous substances.
4.3.1 Municipal solid waste
In Northwest Russia, municipal solid waste31
is almost exclusively disposed of in landfills that do not meet requirements and are
subject to growing capacity constraints. There is very little focus on waste minimi-sation
and recycling.
The legal framework for activities related to municipal solid waste was established
during the Soviet period. Most Acts and Ordinances adopted before 1991 are still in force.
For instance, sanitary norms and rules (Sa-nPin), State Standards (GOST) established
requirements to the Municipal Solid Waste landfills and municipal services involved in
waste collection. In order to promote a new legal basis, the Federal Law "On waste of
production and consumption" was approved in 1998. Based on this Law a number of new
governmental Acts must be adopted.
Waste collection
Urban solid waste collection equipment and transfer stations work fairly well in the
sense that main streets are generally kept clean. However, there are suburban and rural
areas, which are not serviced by regular collection services, which mean that residents
must resort to illegal dumping of waste. There are problems related to an outdated system
of waste collection and storage within and near houses, which requires a lot of manual
labour for waste handling, creates unsanitary conditions within multistorey apartment
houses and around collection points because of odour and contamination of surroundings by
waste. As a result of improper management, waste is readily accessible to rodents, flies
and other insects, which creates a nuisance and risk for human health.
There is a widespread lack of organised collection and treatment of Household Hazardous
Waste (e.g. used accumulator batteries, PVC, mercury lamps etc.). Consequently, these
categories of waste are either not collected, or disposed at unauthorised dumps or at
municipal facilities not equipped to handle this waste segment properly.
Recycling
Modern waste management practices such as separate collection, recycling and
recovery are almost non-existent in Northwest Russia. In St. Petersburg approximately 15%
of the solid domestic waste is recycled32.
Landfill capacity
Many Northwest Russian landfills operate close to their maximum capacity and the
environmental quality of the facilities is low. Many dumpsites are poorly situated both
geologically and geographically. They are not properly designed, constructed and operated:
 | Most disposal facilities are constructed without synthetic liner, many dumpsites have
not even a natural clay lining on the bottom. |
 | leachate is usually not collected and treated at municipal solid waste facilities. |
 | most of the disposal facilities lack a run-on/run-off control system |
 | Ground water quality is not monitored |
 | Fires and open burning on landfill is common. |
 | Limited capacity / access leading to illegal dumping |
The poor condition of Municipal Solid Waste disposal facilities contributes to negative
environmental impacts such as soil, surface and groundwater contamination, air pollution
(including dioxin production), odour and damage to landscape.
More than 400,000 tonnes of
domestic and industrial waste generated every year in the Kaliningrad region and only a
small fraction is recycled. As a result, roughly 15 million tonnes of solid waste have
accumulated in municipal landfills, which do not meet the requirements for environmental
protection. These sites represent a major source of air, ground and particularly water
pollution.
The solid waste disposal site in the city of Kaliningrad is a combined
open landfill dump for municipal and industrial waste, situated not far from some of the
drinking water reservoirs of Kaliningrad. The landfill, constructed in 1978 as a temporary
site, was not provided for environment protection measures. It is, however, still in use
and occupies an area of 13.5 hectares. The landfill is located on a swamp and there is
high water penetration and thus a high risk of ground water pollution. In addition, storm
water flows from the landfill and into the river of Pregolya, which drains into the
Vistula Lagoon and, ultimately, the Baltic Sea. |
Source: Proceedings, EcoTech, Sweden, September, 1999
Northwest Russias treatment facilities do not comply with international or
Russian Standards. St. Petersburg has two treatment plants, which treat approximately 30%
of the domestic waste. An example of the waste problems is insufficient quality of the
compost produced, which contains too high levels of plastic and glass material. At one of
the St. Petersburg treatment plants 7 years of production is accumulated on the site33.
Unauthorised dumping
Insufficient waste collection systems lead to a high level of unauthor-ised
dumping. In St. Petersburg City and Leningrad Oblast there are approximately 75 registered
landfills but also approximately 1,000 unau-thorised dumps of various size34.
Lack of control of waste streams
There is a lack of continuous (from top to bottom) control of the waste streams
from their places of origin to final operations on their disinfecting and recycling. The
main causes of these shortcomings are a weak institutional and legal framework combined
with a widespread lack of co-operation both between the subjects of Northwest Russia and
between the various municipalities.
Privatisation
Even though a privatisation process has been pursued, a de facto monopoly situation is
still the case in many places in the waste sector, even if private enterprises have taken
over provision of most of the service. These companies are either owned by the public
authorities or privately owned (or a combination) and it appears that open tender
procedures based on real competition is not common.

Figure 4.4
Main problems of the St. Petersburg region in the solid waste management
sphere.
Source: St. Petersburg Research Centre "Single Policy in Solid waste Management in
St. Petersburg and in St. Petersburg City.
4.3.2 Industrial hazardous waste
Waste Generation
The most urgent environmental concerns in Northwest Russia are related to industrial
hazardous waste. In spite of the general decline in industrial production during the
1990s and specifically the economic crisis in 1998, annual industrial hazardous waste
quantities are not reported to have fallen during the period. The Russian industry
generates more hazardous substances in the industrial processes than European industries.

Figure 4.5
Industrial production* and generation of toxic waste. Northwest Russia
* Industrial production in real prices, using the consumer price index for the
area as deflator
Source: GOSKOMSTAT, 2001
Waste disposal
In the former USSR the problem of hazardous waste was usually solved in a very simple
way, i.e. by disposing such wastes in special landfills. Many of these hazardous waste
landfills still exist and in many cases they are the only place where it is officially
allowed to bring hazardous wastes.
Between 1970 and 1990 a number of hazardous waste incineration plants were built all
over the Soviet territory. Such incineration plants were usually constructed near e.g.
major industries and big chemical plants and were only capable of treating liquefied
wastes. Moreover, none of them were designed for PCB destruction. After 1991, most
incineration plants were closed down for economic reasons, though some are still in
operation. However, nearly all of them require fundamental modernisation and upgrading to
meet international environmental standards.
In Northwest Russia, there are also cases of hazardous waste being dumped at disposal
sites for municipal solid waste although they are not equipped for this purpose
because no proper site for hazardous waste is available. Also, industries often do not
separate and treat their hazardous waste according to the environmental requirements. In
such cases the hazardous substances are discharged with industrial waste-water into
surface waters.
St. Petersburg is located at the
nexus of an immense ecological system. Lake Ladoga, the largest freshwater lake in Europe
and the primary source of drinking and industrial water for St. Petersburg and the
autonomous republic of Karelia, which lies just outside St. Petersburg. Thirty-two rivers
flow directly into Lake Ladoga (whose reservoir basin spans a total area of 280,000 square
kilometres), and only one river, the Neva, flows out.
The city of St. Petersburg is located at the Neva delta which drains
into the Gulf of Finland. Lake Ladoga is rapidly losing its ability to absorb and disperse
the harmful effects of pollutants, presumably because of the sheer volume of pollutants
dumped into the lake and its ecosystem.
It is estimated that the greatest pollution to Lake Ladoga comes from
effluent waste from pulp and paper plants (like the Priozersk and Syas plants), which
contains more than 300 toxic substances, from agricultural enterprises (which cause
epidemiological risks through their concentration of microbes and parasites), and from the
concentration of phenols from timber which is floated and allowed to sink in the lake. The
key means to save Lake Ladoga from environmental degradation at the hands of municipal and
industrial pollutants is to adopt more stringent waste treatment measures for existing
enterprises. |
Source: TEC Case Study, Courtney M. Nero (May 1999)
Large accumulations
Capacities of recovery and disposal facilities for hazardous waste in Northwest Russia
are by far sufficient to cover the present needs. Therefore, large accumulations of
industrial and hazardous waste are growing at industrial sites, particularly in the
metallurgical and power generation industries. By the year 2000, it is estimated that more
than 120 million tonnes of hazardous waste have accumulated in Northwest Russia35.
As a comparison, the facility serving the entire territory of Denmark, i.e. more than 5
million people, treated about 110,000 tonnes of hazardous waste in 2000. The accumulated
amount of hazardous waste in Northwest Russia, hence, constitutes more than 1,000 times
the annual treatment capacity of this facility36.
Improper storage
The industrial hazardous waste accumulated at industrial sites or deposited at old
hazardous waste landfills in Northwest Russia represent a major environmental problem as
the waste is seldom stored in an environmentally safe manner. Hence, there is a risk of
dangerous substances seeping into, or being washed out from storage sites and polluting
the soil and ground and surface waters, thereby endangering drinking water resources and
human health.
In the Leningrad region, the official hazardous waste disposal site does not meet
environmental requirements (see Box 3.1). Around 800,000 tonnes of unprocessed industrial
hazardous waste, such as chlorinated substances and heavy metals are improperly stored in
open pits37. This implies a serious
risk of soil and ground water contamination, and stormwater may cause substances to wash
into the Neva River and thereby the Gulf of Finland.
Krasny Bor Hazardous Waste
Disposal Site
The hazardous waste disposal site Krasny Bor near St. Petersburg
is among the HELCOM hot spots. Since the opening thirty years ago, it has received more
than 1.5 million tons of industrial toxic wastes. It is the main dumping point for
industrial and toxic waste for factories located in the city and the surrounding Leningrad
region. It has also received waste from other regions in Northwest Russia, but is now
running out of capacity, and hazardous waste from other Oblasts or regions may only be
accepted on the basis of a special resolution (permission).
The existing scheme of hazardous wastes disposal at the landfill
provides inadequate environmental protection, which means that the landfill is a potential
source of pollution affecting the St. Petersburg water supply system as well as the Baltic
Sea basin.
In 1995 the Russian Federation Government supported the initiative of
Leningrad Oblast Administration and St. Petersburg Administration to build an incineration
plant for hazardous waste at the Krasny Bor but then decision was made to construct an
experimental toxic waste treatment plant instead. It is planned to finalize the
construction of the first line of the plant with the capacity of 18,000 tones and put it
into operation in 2003. Furthermore, recently Toxic Waste Emergency Clean-up Programme
aiming at upgrading and cleaning up the site has been launched with the support of the EU,
bilateral donors and International Financing Institutions. |
Source: Committee of natural resources, environmental protection and environmental
safety of St. Petersburg administration, DEPA project documents 2000- 2002
Kaliningrad has similar problems related to storage and processing of hazardous
waste, however, on a smaller scale. Today 6,000 tons of hazardous industrial waste is
deposited in temporary storage houses that were not designed for this purpose. The risk of
hazardous substances leaking into the ground is considered very high38.
4.3.3 Persistent Organic Pollutants (POPs)
Effects of POPs
Of all the pollutants released into the environment every year by human activity, POPs
are among the most dangerous. They are highly toxic, causing an array of adverse effects,
notably chronic diseases, and birth defects among humans and animals. This report will
briefly describe the 3 categories of POPs: POP pesticides, PCBs (industrial POP) and
Dioxin.
Characteristics of the POPs
These highly stable compounds can last for years or decades before
breaking down. They circulate globally through a process known as the "grasshopper
effect". POPs released in one part of the world can, through a repeated (and often
seasonal) process of evaporation, deposit, evaporation, deposit, be transported through
the atmosphere to regions far away from the original source.
In addition, POPs concentrate in living organisms through another
process called bioaccumulation. Though not soluble in water, POPs are readily absorbed in
fatty tissue, where concentrations can become magnified by up to 70,000 times the
background levels. Fish, predatory birds, mammals and humans are high up the food chain
and so absorb the greatest concentrations. When they travel, the POPs travel with them. As
a result of these two processes, POPs can be found in people and animals living in regions
such as the Arctic, thousands of kilometres from any major POPs source.
Fortunately, there are alternatives to most POPs, though, in Northwest
Russia a lack of public awareness and the absence of appropriate infrastructure and
technology often prevent their adoption. |
POP pesticides
Northwest Russia has large stocks of POP pesticides to be dealt with in the future
(estimated 21,000 tonnes), though exact figures are not available.
PCBs
Another important POP is the PCBs, which were produced by two factories in the former
Soviet Union. From 1939 to 1993, the factories produced a total of about 180,000 tonnes of
PCB39.
It is estimated that some 17,000 tonnes can be found in transformers and 7,000 tonnes
in capacitors.
Amap estimates in its report "PCB in the Russian Federation" that between
1000 and 2000 tonnes of PCB is stored in PCB containing equipment in the Northwest Russian
territory40.
From the point of view of collection or substitution, the transformers are probably the
application areas offering the highest "cost-benefit" ratio with the present
plans for incineration41.
Dioxins and Furans
Dioxin and Furans are by-products of e.g. incineration of POP pesticides, PCB and waste
in general. A large scale US-Russian project provides estimations of dioxin emissions by
different sources. According to the inventory, total annual dioxin emission to the air
from Russian sources was estimated to be within the interval of 6900 to 10900 g I-TEQ
(International
Toxic-equivalent)42.
The most urgent problems regarding dioxins in the Russian federation have until now
been pollution within and around chemical plants producing chlorinated and brominated
compounds. When considering 3 of the most polluting chemical plants, each of them have an
emission about 10 times higher than the entire Danish emission (all sources included).
In Russia domestic waste is primarily deposited at landfills, often together with
industrial wastes. Smoking landfills can be seen in many Russian regions all year round.
Often landfills are set on fire in order to reduce the volumes of waste. No quantitative
estimates of Dioxins and Furans formation from burning landfills are available but there
are reasons to believe that such formation is not less hazardous than emissions from the
waste incineration plants and the burning of landfills represents thus an environmental
challenge that should be dealt with.
4.3.4 Financial challenges in the waste sector
Tariffs
The waste sector in Northwest Russia is in dire need of heavy investment in order to
overcome the challenges indicated in the above sections and establish an environmentally
sustainable waste management system.
Tariffs are collected by the Municipalities/City administrations, but there are a
series of problems related to the collection of tariffs which is similar to those
identified in the water sector (see section 4.1).
The Danish Environmental Protection
Agency has financed the development of an environmental Financing Strategy within the
waste sector in Novgorod Oblast. The Environmental Financing Strategy is a tool for
establishing realistic plans for future investments encompassing amongst other expected
revenue generated from user charges, Operation & Maintenance costs, future investments
needs, required service levels etc. The financing strategy, developed with the aid of
FEASIBLE, a newly developed computer modelling tool, concluded that:
 | There are both motives and possibilities for increase of the waste
collection coverage in the oblast;
|
 | There are both motives and possibilities for development of
recycling systems, starting in the larger cities;
|
 | There is an urgent need to replace current inappropriately located,
designed and operated dumpsites with proper landfills;
|
 | The construction of waste incineration plant in the oblast is not
expedient considering the high costs and the long transport distances;
|
 | There are both motives and possibilities for an increased
inter-municipal co-operation on development and operation of regional landfills;
|
With regard to financing issues the report concluded that:
 | The revenues of municipal waste management enterprises cover, in
general, costs related to their activities in all considered cases in the larger cities.
With the exception of Novgorod, this is explained by that the minimal expenditures on
sub-standard dumpsites;
|
 | The revenues for waste collection and treatment are in many cases
cross-subsidizing sanitary cleansing activities;
|
 | In the larger cities, the envisaged developments in collection
coverage and developments of the regional landfills can be financed with parallel
increases tariffs. However, in the smaller towns, oblast subsidies will be required for
the envisaged developments.
|
 | New modes of financing, such as through property taxes, could prove
beneficial;
|
 | During years of implementation of large facilities, such as new
landfills, there is a need to identify sources of capital investments financing.
|
|
4.3.5 Waste problems related to the energy sector
Oil spills and leakage
The Russian oil and gas industries are responsible for spills and leakages that
contaminate soil and waters in many areas. Environmental standards are not enforced and
international petroleum standards are not yet in place. Spills arise from pipeline
leakages, accidents and tanker spills.
Additional refinery capacity has been established in St. Petersburg and the export of
Russian oil products through the Baltic Sea is planned to triple within the coming years.
Consequently, the risks of accidents and of oil spill will increase if measures to reduce
these risks are not taken.
In total, more than 39 thousand ha of Russian land are contaminated with oil products
of which military sites accounts for more than 70 per cent43. It is estimated that over 3 billion roubles (2001 prices)
or more than USD 100 million are required only for the priority clean-up activities.
A significant part of these military sites are located in Northwest Russia, though,
more detailed studies are needed to assess the full volume of this problems and the impact
on the environment in particular on the ground water, local and regional water bodies.
Similar to other industries in
Russia the military sites are supposed to be operated according to environmental permits.
By 2002, less then 50% of the sites within the federal subordination have got the permits.
Extensive environmental studies at military sites are now being
carried out with international assistance within the general demilitarisa-tion process in
Russia assuming their conversion to civil land use. The studies have already revealed a
number of crucial environmental management issues:
 | Of total reported 39.2 thousand ha of areas contaminated with oil
products in Russia, more than 27 thousand ha are within military sites. It is estimated
that over 3 billion roubles (2001) are required only for the priority clean-up activities.
|
 | About 25% of wastewater from military sites is discharged without
treatment. Only 15% of wastewater discharged from military vessels and harbour facilities
are treated to the level meeting existing environmental norms.
|
 | There are no solid waste treatment facilities at the majority of
military sites. About 14.5 thousand tonnes of mixed waste from the sites per year are just
dumped. The total area of the dumps is 171 thousand ha (2000).
|
 | Over 350 old navy vessels (with total deadweight of 220 thousand
tonnes) are accumulated in navy harbours with practically no pretreatment.
|
|
Source: National Report on Status of the Environment, Russian Federation, 2001
Waste from energy production
Concrete examples of waste problems related to establishment of energy plants and the
disposal of by-products from energy production in Northwest Russia are:
 | High dust and fly ash emission (from coal fired power plants and boiler stations in
Kaliningrad oblast, Pskov oblast, from oil shale recovery in Leningrad oblast); |
 | Wastewater discharge (from the Kirishi oil refinery, cooling water from power plants
from open-type district heating systems with supply water partly used as hot tap water); |
 | Pollution of groundwater and soil by petroleum products (from the Kirishi oil refinery
and oil storage tanks). |
Construction of several new refineries, pipelines and oil terminals in the region in
order to be able to ship out more crude oil and oil products in the Baltic Sea and the
Barents Sea constituting increased risks of oil spills and adverse impacts on sensitive
habitats.
4.3.6 Spent Nuclear Fuel (SNF)
Storage and reprocessing of used fuel
Apart from the safety issues relating to the nuclear power plants there are a series of
problems relating to storage and reprocessing of Spent Nuclear Fuel and other contaminated
wastes.
The only facility for reprocessing used fuel is the Mayak plant which is situated in
the southern part of the Urals. Thus, the used fuel is transported from all over Russia to
this plant which has severe security related implications.
However, Mayak is not capable of treating all types of used fuel elements produced in
various nuclear powered generators and nuclear power plants. Furthermore, long-term
storage facilities are not available and approximately 14,000 tonnes of spent nuclear fuel
is stored at Mayak and at various plants44.
OECD estimates that approximately 1 billion tons of high and low level radioactive waste
is stored in Russia. However, the larger part is related to low-level radioactive waste
from uranium and thorium mining and processing.
At Leningrad Atomic Energy Station
the spent nuclear fuel elements are stored in a storage facility on the site right next to
the Gulf of Finland. The storage facility is in a bad condition. Reportedly, there are
cracks in the wall and in the roof. Rainwater enters and contaminated water runs out. All
storage facilities are utilised to the maximum capacity, and RMBK fuel elements will not
be reprocessed. |
www.bellona.no
The naval nuclear decommissioning
Northwest Russia is awash with laid-up nuclear powered submarines and ice-breakers
waiting to be decommissioned. Out of the 248 nuclear submarines built by the Soviet Union
and Russia for the Northern and Pacific fleets, 191 are laid-up. 115 of these are located
in Northwest Russia, of which only 32 have been dismantled. Only 10 submarines have been
defuelled and 71 are laid-up with spent nuclear fuel onboard45.
The tempo at which spent nuclear
Fuel is transported an process at Mayak Plant has slowed drastically during the last
decade. As of 1991, Mayak Chemical Combine has required full coverage of its expenses.
The Russian Navy lacks funds to pay for the service of the Mayak Plant
for reprocessing, which still constitutes the most important reason for the drop in the
rate at which spent nuclear fuel is reprocessed.
Thus there is a sharp increase in the amount of spent nuclear fuel
that is stored at naval bases in Northwest Russia, including fuel that remains in reactors
of laid up submarines.
Specialists and Commanders of the Russian Northern Fleet are both
greatly concerned about this situation, for in theory it will be impossible to transport
all this fuel to Mayak over the course of the next 30 to 40 years.
Finally, experts believe that 10 per cent of the fuel assemblies
accumulated at the Northern Fleet bases and shipyards cannot be reprocessed at Mayak. |
Source: The Russian Northern Fleet: Handling of Spent Fuel Assemblies, Bellona, 2002
Another source of nuclear waste is spent strontium-90 fuel used to power lighthouses in
the northern region. This method of powering lighthouses was also tested in the west but
abandoned since it was difficult to ensure the safety of such large sources at remote and
isolated locations. The source from lighthouses no longer in use is now taken care of with
international assistance46.
4.3.7 Facing the challenges in the Waste sector
Russia should continue the work towards creating an efficient legal and institutional
framework for the waste sector. Russias waste handling strategies should relate to
internationally recognised principles for waste management i.e. the "waste
hierarchy" (highest priority given to prevention, followed by recovery and lowest
priority to safe disposal).
Within these principles, special efforts in Northwest Russia should be given to:
 | Waste minimisation through public awareness campaigns and increased recycling and reuse.
Introduction of waste selection practice and construction of sorting stations initially in
large cities where one can expect sufficient volume of sorted waste to make the business
commercially attractive; |
 | Mapping and controlling the waste streams. This would improve the understanding the
needs and force the various municipalities and Oblast into development and operation of
regional landfills. |
 | Tariffs should reflect the cost of the service provided and full cost recovery has not
yet been achieved. |
 | Capacity building and institutional strengthening especially with regard to waste
management planning, financial and operational management and best practices. |
The technical challenges related to the waste sector are extensive but not
insurmountable in the sense that well known and more or less technology intensive
solutions are available.
 | There is a need for increasing both urban and rural waste collection coverage (e.g.
sorting stations and types of vehicle) for both municipal and industrial waste. This would
reduce illegal dumping of both Municipal and Industrial waste on unauthorised dumpsites. |
 | Waste collection equipment need to be upgraded to allow more focus on recycling and
include household hazardous waste needs in the overall waste collection system. |
 | There is an urgent need for replacing current inappropriately located and designed
landfills. |
 | Waste treatment procedures at landfills need to be environmentally optimised. |
 | The Soviet "heritage" in terms of accumulated waste needs to be dealt with.
E.g. priority should be given to collecting the POPs that still pose a serious threat to
the environment. |
 | The nuclear waste in Northwest Russia must urgently be handled in a safe manner. |
Areas of particular relevance for international co-operation
As signatory to the Basel Convention Russia should continue pursuing that a)
transboundary movement of hazardous waste should be reduced to a minimum, b) hazardous
waste should be treated and disposed of as close to their source of generation as
possible. c) hazardous waste generation should be reduced and minimised at the source.
Furthermore, Russia participated in the preparation of the 1998 protocol to the
Convention on Long-range Transboundary Air Pollution on Persistent Organic Polluters, but
has not signed it. One reason is the requirement to phase out PCB use by 2005, which is
causing difficulties. The 1999-2001 "National Environmental Action Plan" does
not consider Persistent Organic Polluters elimination (among air pollution problems,
phase-out of leaded petrol is given the highest priority). Russia should continue working
towards ratification of the Stockholm Convention on Persistent Organic Pollutants (POPs).
Examples of specific activities envisaged within the preparatory process are:
 | Contribution to the Arctic Monitoring and Assessment Programme project concerning PCB
products (feasibility studies, preparation of pilot projects for elimination/phasing out
of PCBs); |
 | Development and demonstration of strategies for reduction of dioxin releases in
Northwest Russia; |
 | Inventories and development of action plan regarding stockpiled obsolete pesticides (in
co-operation with UNEP and the United States Environmental Protection Agency). |
According to Russian targets set in the Partnership and Co-operation agreement with the
EU Russia should approach various EU regulations as e.g. The EU Waste Management Strategy
(COM (96) 399) and the EU Landfill Directive (1999/31/EC).
Finally, safe handling of nuclear waste demands for close international co-operation,
as Northwest Russia apparently is not able to handle the situation. Dependent on the
successful signing of the Multilateral Nuclear Environmental Programme in the Russian
Federation, Euro 62 Million have been earmarked for nuclear projects in Northwest Russia
under the Northern Dimension Environmental Programme.
14 |
Level of antibodies to cryptosporidium is an
often used indicator of the general drinking water quality.
|
15 |
Health impact from chemical toxics is seldom
acute (like for infectious diseases), but chronic diseases can develop over time.
|
16 |
GOSKOMSTAT, Annual report on the state of the
environment, Russian Federation, 2001
|
17 |
Department of Natural Resources of Northwest
Region, Report on the State of Environment in Northwest Region in 2000
|
18 |
OECD Environmental Performance Review
|
19 |
OECD Environmental Performance Review
|
20 |
OECD Environmental Performance Review, p. 83
|
21 |
Department of Natural Resources of Northwest
Region, Report on the State of Environment in Northwest Region in 2000
|
22 |
OECD Environmental Performance Review
|
23 |
Eastern Europe, Caucasus and Central Asia.
|
24 |
OECD, Environmental Performance Review, p. 58
|
25 |
EIA Country Analysis Brief, November 2002
|
26 |
Russia Environmental Issues. EIA August
2001
|
27 |
EIA Country Analysis Brief, November 2002, p.9
|
28 |
International Kernekraftstatus 2001,
Forskningscenter Risø, Roskilde, April 2002
|
29 |
www.bellona.no article EU-Russia
Committee discusses Russian Nuclear Safety
|
30 |
EIA, Russia Energy Survey, 2002
|
31 |
Waste can be divided into hazardous and municipal
solid waste. Hazardous waste is waste, which is characterised as toxic, poisonous,
explosive, corrosive, flammable or infectious. This includes, for example clinical waste,
chemical waste as well as waste resulting from a number of industrial processes. Most
hazardous waste origins from the industrial sector. Municipal solid waste is non-hazardous
waste from households, commercial enterprises, industry, etc. See www.basel.int for more
information.
|
32 |
St. Petersburg research Centre "Single
Policy in solid waste management in St. Petersburg and in Leningrad Oblast", St.
Petersburg 2000
|
33 |
DEPA project document 2002, Waste Management Plan
for St. Petersburg City
|
34 |
Department of Natural Resources of Northwest
Region, Report on the State of Environment in Northwest Region in 2000
|
35 |
GOSKOMSTAT. 2001
|
36 |
The Russian classification of hazardous waste is
stricter than western standards. 37. HELCOM, 2001
|
37 |
HELCOM, 2001
|
38 |
www.helcom.fi, press release 24.04.2001
|
39 |
As is also the case for POP pesticides,
estimation of PCBs and dioxin emissions in Northwest Russia are very approximate and need
more detailed research
|
40 |
Amap, "PCB in the Russian Federation,
Inventory and proposals for Priority Remedial Actions - executive summary"
|
41 |
Dancee, Status report on POPs in the Russian
Federation
|
42 |
It should be noted that the emission from the
main source - incineration of waste - is calculated on the basis of emission factors from
the UNEP toolkit for dioxin inventories.
|
43 |
Source: National Report on Status of the
Environment, Russian Federation, 2001.
|
44 |
EIA, Russia Energy Survey, 2002
|
45 |
www.bellona.no - Article 28th November 2002 - EU
Russia Committee discusses Russian nuclear safety
|
46 |
Overview of the sources of spent nuclear fuel and
radioactive waste in Northwest Russia, EBRD, 22/4-2002. |
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