Responses of Different Test Objects to Experimental Soil Contamination with Crude Oil

Russian Journal of Ecology - Responses to contamination of several soil types with crude oil were comparatively analyzed in organisms of different trophic groups. Samples of soddy podzolic, light...     

Influence of destructive bacteria and red clover (trifolium pratense L.) on the pesticides degradation in the soil

Environmental Geochemistry and Health - Lindane and DDT (1,1,1-trichloro-2,2-bis(4-chlorophenyl)ethane) are pesticides from the group of persistent organic pollutants. These compounds, due to...     

The Role of Micromycetes in the Phytotoxicity of Crude Oil-Polluted Soils

The microbe–plant interaction in soil under crude oil pollution was studied in Perm oblast, the Cisural Region. In the rhizosphere of plants growing in the oil-polluted soil, an increased abundance of nonsymbiotic saprotrophic micromycetes was recorded. Under conditions of crude oil pollution, the development of these microorganisms in the rhizosphere proved to have a strong adverse effect on the plants due to production of mycotoxins.     

Nitrous oxide emission fromagricultural lands in Russia

Nitrous oxide (N₂O) atmospheric emission from differentagricultural soil types in Russia was evaluated based on published data onsingle input of nitrogen (N) fertilizers. For most of experiments the rates offertilization varied from 40 to 75 and from 160 to 264 kg/ha in activematter and they were considered separately. The higher rates ofsynthetic fertilizers (160 to 264 kg/ha) reduced relative gaseous loss ofN as N₂O (N₂O-N). Evidently, if nitrate (NO₃) concentrationswere high, the low content of organic carbon (C) and oxygen (O) restricted soilmicrobiological activity and consequently formation of N₂O. Themajority of gaseous loss of N₂O-N occurred within 140 days afterthe input of fertilizers. The N₂O emission factors derived forchernozem and soddy podzolic soil are 0.0126 and 0.0238 kgN₂O-N/kg N respectively. In 1990, the use of N fertilizers innational agriculture caused the release of 53 Gg N₂O-N thatconstituted 6% of global N₂O emission. Later on, the emissiondropped because of decreased use of N fertilizers, and in 1998 itwas almost 21% of the 1990 level.     

Environmental issues in the post-communist Ukraine

The Ukraine, which gained independence in 1991, faces serious problems related to environmental degradation. Environmental problems contribute to a deterioration in human health and a negative trend in population growth. Both form part of a raft of socio-economic problems encountered during the country's transition to a free market economy. The most serious problems are found in cities and areas near the Black and Azov Seas, the Dnipro river basin and in the Polissya region. This paper provides an overview of the situation. Social and managerial implications of environmental management are considered alongside associated environmental and human health problems in the country. It is concluded that a desired change in the mindset of policy makers and, indeed, the population at large, is required in parallel with legal and technocratic instruments, while real improvements can only be achieved through economic development, which can be facilitated by Western assistance.     

Approaches to standardization of atmospheric pollution undergoing long-range and transboundary transport

The authors consider some possible ways of regulating three types of atmospheric emission of pollutants:

1. emission of substances causing pollution of the natural environment on the global scale (global pollutants);
2. emission of substances causing pollution on a regional scale, most often including territories of several countries (international pollutants);
3. emission of substances causing negative effects in a relatively limited region, for example within border area of two adjoining countries.

Substances (gaseous, as a rule) of a long life-time in the atmosphere that can contaminate natural media on a global scale irrespective of the place of emission refer to the first class of pollutants that are subject to emission regulation at an international level and to quota establishement for individual countries. They are carbon dioxide, freon, krypton-85. Various approaches to determining permissible emission and to quota establishing are discussed in the paper. The second group includes substances of a limited, yet rather long, life-time whose emission intensity makes a notable contribution to environmental pollution of a large region including territories of several countries. Here it is needed to regulate internationally not the atmospheric emission as it is but pollutant transport over national boundaries (sulphur and nitrogen oxides, pesticides, heavy metals). The third group includes substances of relatively short time of life producing local effects. Emission regulation in such cases should be based upon bilateral agreements with due account of countries' mutual interests.     

On the Assessment of Sulphur Deposition on Forests Growing Over the Areas of Industrial Impact

A method of calculation of sulphur deposition values on forests subjectto long-term industrial influence is presented. Investigations wereconducted in the vicinities of nickel smelters of Kola peninsula. Sulphurdioxide (SO₂) is the major phytotoxicant emitted by theseenterprises. Depositions of sulphur were calculated on the basis of ground air layer pollution. To determine it a mathematical model was applied.Field surveys of forest ecosystems response to air contamination werecarried out and areas of different forest damage degree were identified.More than 4300 km² of the territory of Kola peninsula isunder the impact of nickel enterprises. Average SO₂concentration over the area of slight damage to forests is about 20µg/m³. It corresponds to the critical level proposed for forest ecosystems (UN ECE, 1993). Sulphur deposition over thearea of slight damage varies from 0.6 to 1.0 g/m²yr^-1 for coniferous forests. For deciduous forests it isabout 1.0 g/m² yr^-1. These values are close totarget loads for highly sensitive ecosystems (Nilsson et al., 1991), but they exceed critical loads for the northern regions of Europe (Downing etal., 1993).