Krasnodar GRES Project Volume I11 Environmental Assessment
Krasnodar GRES Project Volume I11 Environmental Assessment Krasnodar GRES Project Volume I11 Environmental Assessment
' - European feather grass Anapa, Laba river. Included in the list of rare and extinct species of the Russian Federation) - Jacob's rod (from the Laba river to Pyatigorye. Included in the list of protected flora species of the Russian Federation) These species are not found within the construction site or transmission line corridors. Impacts on environmental systems of the Caucasus biosphere reserve. The northern boundary of the reserve is 48 km from the construction site. Water quality impacts, electromagnetic field impacts, and noise will not reach the reserve. The existing NOx background concentration within the biosphere reserve is 0.008 mg/m3. The estimated NOx emissions attributable to the Krasnodar GRES is 0.001 1 mg/m3. Therefore, the combined NOx level within the biosphere reserve is estimated to be 0.0091 mg/m3 which is well below the MPC of 0.04 mg/m3. Nitrogen oxide concentration increases in the atmosphere of the reserve are within measurement accuracy limits and will show a minor difference from the background values. MPC for the reserve are much lower (see section 2.1 .I) compared to MPC for populated areas. Environmental impact on the reserve can be caused only through acid rains. In Russia there is no established methodology to predict acid rains. Therefore, this type of impact is considered to be an unregulated impact. Mathematical modeling of acid rains conducted for a previous site study indicate that: 1. With existing wind velocities and directions, nitrogen oxides, given their 30 to 70 hour atmospheric residence time may reach the reserve; 2. Majority of acid fallout shall fall on north-western stepped part of the Krasnodar Territory; 3. Probability rate of the oxides fallout in the reserve is 0.01 and that of acid rains is even less. In accordance with the International convention on trans-boundary transfer, acid rain mitigation measures include a decrease of total emissions of sulfur oxides and nitrogen oxides (tons per year). According to the Environmental Report of the Krasnodar Territory in 1994 the Territory met the Convention requirements as of 1993. Decrease rates of total emissions are ahead of schedule by 23.8 %, i.e. USAID/KRASEIA/OFFICIAL/EIACHS.DOC 3/26/96 PAGE 5-28
e 4.79 tons per year (page 23 of the Report). With commissioning of the power plant NOx emissions shall increase up to 2.58 tons per year, i.e. total emissions level for the Territory shall remain within the Convention requirements. However, with commencement of power plant operation reconstruction of the units of the existing Krasnodar City thermal power plant and switching to modern combined cycle mode shall become possible with consequent cessation of use of sulfur containing fuels which will contribute to a decrease of total nitrogen and sulfur oxides emissions and will improve the acid rain situation. With the power plant commissioning, the probability rate of acid rain in the reserve shall be decreased. The Environmental Report of the Krasnodar Territory in 1994 (see page 105) points out "increasing impact on biota of the reserve by chemical and radiological pollution associated with global transboundary transfer of pollutants, however the consequences of this process require further study". 5.2.1.6 lmpact on Human Health Impact on human health is rendered through air, potable water, water reservoirs, soil, labor conditions and living standards. Water quality shall be improved due to commissioning of a new subchannel water intake at Andryuki. Water reservoir quality shall not be deteriorated because waste water shall be processed at the treatment plant, and withdrawal of fresh water shall be minimized due to use of dry cooling towers. Silty and toxic industrial waste is not discharged to water reservoirs but held within the power plant site in special vessels. There will be no soil pollution or degradation (see section 5.2.1.7). Due to construction of the residential compound, recreation center, school, asphalt covering of the streets, central heating, lighting of the streets, and other planned infrastructure development projects, living conditions will improve. Medical care shall improve due to construction of a new clinic. Air quality shall be nominally impacted but will remain within permissible concentrations. Previously conducted mathematical modeling (accounting for changes of meteorological conditions disregarded by OND-86 methodology) states that more than 90 % of the time, above ground concentrations of air pollutants in adjacent populated areas shall not differ from the background values (see Table @ 5.11). PAGE 5-29 i \ '.F'
- Page 114 and 115: @ In terms of the leaching extent,
- Page 116 and 117: Form of Use Arable land Perennial p
- Page 118 and 119: @ River Laba Malaya Laba 4.4.1 Land
- Page 120 and 121: Name Administration of Mostovskoy 1
- Page 122 and 123: N 1 2 3 4 5 6 7 8 9 10 11 12 13 14
- Page 124 and 125: a The average annual increase of pl
- Page 126 and 127: Data on record keeping of ungulate
- Page 128 and 129: divided into separate massifs by th
- Page 130 and 131: a 4.5.2.1.3 Animal Kingdom The Cauc
- Page 132 and 133: the Southern slope. European minks
- Page 134 and 135: 4.6.1.3 Labor and Occupation Market
- Page 136 and 137: Total Disease of circulation organs
- Page 138 and 139: and waste with negative impacts on
- Page 140 and 141: Existing Environment Conditions Lan
- Page 142 and 143: 5.1.2.5 River Crossing by Transmiss
- Page 144 and 145: 5.2 Operation Stage Figure 5.1 is r
- Page 146 and 147: Maximum concentration of nitrogen o
- Page 148 and 149: Distance From the Power Plant, km 1
- Page 150 and 151: probability is 7.14 m3/sec and this
- Page 152 and 153: Underflooding of the power plant te
- Page 154 and 155: Water pollution at the water intake
- Page 156 and 157: Biological pollution and chemical p
- Page 158 and 159: Noise range in the engine room fall
- Page 160 and 161: Reference points 002 through 004 ar
- Page 162 and 163: use of individual noise reduction m
- Page 166 and 167: Populated Areas Mostovskoy Pereprav
- Page 168 and 169: 1 2 3 4 5 6 7 8 9 # Table 5.1 2 Est
- Page 170 and 171: In accordance with the district Adm
- Page 172 and 173: during oil transportation. The othe
- Page 174 and 175: are then directed to an oillwater s
- Page 176 and 177: Biological reclamation - bogging an
- Page 178 and 179: - direct impact on vegetation, fore
- Page 180 and 181: 5.2.3.2 Transmission Lines 5.2.3.2.
- Page 182 and 183: 5.2.3.2.2 Impacts on Bird Migration
- Page 184 and 185: Positive lmpacts Additional facilit
- Page 186 and 187: 6.0 WORKER HEALTH AND SAFETY Health
- Page 188 and 189: In the course of practical training
- Page 190 and 191: knowledge of power generator's safe
- Page 192 and 193: @ Urgent instruction is carried out
- Page 194 and 195: - preventive maintenance of the equ
- Page 196 and 197: Governing Standard: "Regulations in
- Page 198 and 199: The Plant Substation; Fenced-off ar
- Page 200 and 201: CONTAMINANT RUSSIA CO NO2 SO2 Parti
- Page 202 and 203: urn agricultural wastes for fuel, t
- Page 204 and 205: production and the large land area
- Page 206 and 207: Interconnection to the existing tra
- Page 208 and 209: 7.6 Alternative Water Supplies and
- Page 210 and 211: 4. "Report No. 256". Krasnodar Terr
- Page 212 and 213: Target of Impact ENVIRONMENTAL Air
' - European feather grass Anapa, Laba river. Included in the list of rare and<br />
extinct species of the Russian Federation)<br />
- Jacob's rod (from the Laba river to Pyatigorye. Included in the list of<br />
protected flora species of the Russian Federation)<br />
These species are not found within the construction site or transmission line<br />
corridors.<br />
Impacts on environmental systems of the Caucasus biosphere reserve. The<br />
northern boundary of the reserve is 48 km from the construction site. Water<br />
quality impacts, electromagnetic field impacts, and noise will not reach the<br />
reserve.<br />
The existing NOx background concentration within the biosphere reserve is 0.008<br />
mg/m3. The estimated NOx emissions attributable to the <strong>Krasnodar</strong> <strong>GRES</strong> is<br />
0.001 1 mg/m3. Therefore, the combined NOx level within the biosphere reserve is<br />
estimated to be 0.0091 mg/m3 which is well below the MPC of 0.04 mg/m3.<br />
Nitrogen oxide concentration increases in the atmosphere of the reserve are within<br />
measurement accuracy limits and will show a minor difference from the<br />
background values. MPC for the reserve are much lower (see section 2.1 .I)<br />
compared to MPC for populated areas. <strong>Environmental</strong> impact on the reserve can<br />
be caused only through acid rains.<br />
In Russia there is no established methodology to predict acid rains. Therefore, this<br />
type of impact is considered to be an unregulated impact. Mathematical modeling<br />
of acid rains conducted for a previous site study indicate that:<br />
1. With existing wind velocities and directions, nitrogen oxides, given their 30<br />
to 70 hour atmospheric residence time may reach the reserve;<br />
2. Majority of acid fallout shall fall on north-western stepped part of the<br />
<strong>Krasnodar</strong> Territory;<br />
3. Probability rate of the oxides fallout in the reserve is 0.01 and that of acid<br />
rains is even less.<br />
In accordance with the International convention on trans-boundary transfer, acid<br />
rain mitigation measures include a decrease of total emissions of sulfur oxides and<br />
nitrogen oxides (tons per year). According to the <strong>Environmental</strong> Report of the<br />
<strong>Krasnodar</strong> Territory in 1994 the Territory met the Convention requirements as of<br />
1993. Decrease rates of total emissions are ahead of schedule by 23.8 %, i.e.<br />
USAID/KRASEIA/OFFICIAL/EIACHS.DOC 3/26/96 PAGE 5-28