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1
József SZABÓ (1822 1894)
geologist, foundation member of the Hungarian
Geological Society (tömören, 2-3 sorban az
életmu fejléce).

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For the regionalization of less productive areas
in national scale a functional approach was used
which integrates the knowledge on soil
degradation processes in nationwide level.
Specific soil threats were classified into ranked
categories. Supposing (quasi)uniform distribution
of vulnerability measure along these classes, we
introduced a standardized value as a ratio of
the class order to the maximum class order
expressed in percentage. For the overall spatial
characterization of degradation status, spatial
information was integrated in a result map by
summarizing the degradation specific
standardized cell values. This map in one hand
has been used for the delineation of soil
degradation regions. On the other hand
appropriate spatial aggregation of index values
on geographical and administrative regions is
suitable for their quantitative comparison thus
they can be ranked and this feature can be used
for the identification of less favorable areas.
For the regionalization of less productive areas
in national scale a functional approach was used
which integrates the knowledge on soil
degradation processes in nationwide level.
Specific soil threats were classified into ranked
categories. Supposing (quasi)uniform distribution
of vulnerability measure along these classes, we
introduced a standardized value as a ratio of
the class order to the maximum class order
expressed in percentage. For the overall spatial
characterization of degradation status, spatial
information was integrated in a result map by
summarizing the degradation specific
standardized cell values. This map in one hand
has been used for the delineation of soil
degradation regions. On the other hand
appropriate spatial aggregation of index values
on geographical and administrative regions is
suitable for their quantitative comparison thus
they can be ranked and this feature can be used
for the identification of less favorable areas.
For the regionalization of less productive areas
in national scale a functional approach was used
which integrates the knowledge on soil
degradation processes in nationwide level.
Specific soil threats were classified into ranked
categories. Supposing (quasi)uniform distribution
of vulnerability measure along these classes, we
introduced a standardized value as a ratio of
the class order to the maximum class order
expressed in percentage. For the overall spatial
characterization of degradation status, spatial
information was integrated in a result map by
summarizing the degradation specific
standardized cell values. This map in one hand
has been used for the delineation of soil
degradation regions. On the other hand
appropriate spatial aggregation of index values
on geographical and administrative regions is
suitable for their quantitative comparison thus
they can be ranked and this feature can be used
for the identification of less favorable areas.
For the regionalization of less productive areas
in national scale a functional approach was used
which integrates the knowledge on soil
degradation processes in nationwide level.
Specific soil threats were classified into ranked
categories. Supposing (quasi)uniform distribution
of vulnerability measure along these classes, we
introduced a standardized value as a ratio of
the class order to the maximum class order
expressed in percentage. For the overall spatial
characterization of degradation status, spatial
information was integrated in a result map by
summarizing the degradation specific
standardized cell values. This map in one hand
has been used for the delineation of soil
degradation regions. On the other hand
appropriate spatial aggregation of index values
on geographical and administrative regions is
suitable for their quantitative comparison thus
they can be ranked and this feature can be used
for the identification of less favorable areas.
For the regionalization of less productive areas
in national scale a functional approach was used
which integrates the knowledge on soil
degradation processes in nationwide level.
Specific soil threats were classified into ranked
categories. Supposing (quasi)uniform distribution
of vulnerability measure along these classes, we
introduced a standardized value as a ratio of
the class order to the maximum class order
expressed in percentage. For the overall spatial
characterization of degradation status, spatial
information was integrated in a result map by
summarizing the degradation specific
standardized cell values. This map in one hand
has been used for the delineation of soil
degradation regions. On the other hand
appropriate spatial aggregation of index values
on geographical and administrative regions is
suitable for their quantitative comparison thus
they can be ranked and this feature can be used
for the identification of less favorable areas.
For the regionalization of less productive areas
in national scale a functional approach was used
which integrates the knowledge on soil
degradation processes in nationwide level.
Specific soil threats were classified into ranked
categories. Supposing (quasi)uniform distribution
of vulnerability measure along these classes, we
introduced a standardized value as a ratio of
the class order to the maximum class order
expressed in percentage. For the overall spatial
characterization of degradation status, spatial
information was integrated in a result map by
summarizing the degradation specific
standardized cell values. This map in one hand
has been used for the delineation of soil
degradation regions. On the other hand
appropriate spatial aggregation of index values
on geographical and administrative regions is
suitable for their quantitative comparison thus
they can be ranked and this feature can be used
for the identification of less favorable areas.
For the regionalization of less productive areas
in national scale a functional approach was used
which integrates the knowledge on soil
degradation processes in nationwide level.
Specific soil threats were classified into ranked
categories. Supposing (quasi)uniform distribution
of vulnerability measure along these classes, we
introduced a standardized value as a ratio of
the class order to the maximum class order
expressed in percentage. For the overall spatial
characterization of degradation status, spatial
information was integrated in a result map by
summarizing the degradation specific
standardized cell values. This map in one hand
has been used for the delineation of soil
degradation regions. On the other hand
appropriate spatial aggregation of index values
on geographical and administrative regions is
suitable for their quantitative comparison thus
they can be ranked and this feature can be used
for the identification of less favorable areas.
For the regionalization of less productive areas
in national scale a functional approach was used
which integrates the knowledge on soil
degradation processes in nationwide level.
Specific soil threats were classified into ranked
categories. Supposing (quasi)uniform distribution
of vulnerability measure along these classes, we
introduced a standardized value as a ratio of
the class order to the maximum class order
expressed in percentage. For the overall spatial
characterization of degradation status, spatial
information was integrated in a result map by
summarizing the degradation specific
standardized cell values. This map in one hand
has been used for the delineation of soil
degradation regions. On the other hand
appropriate spatial aggregation of index values
on geographical and administrative regions is
suitable for their quantitative comparison thus
they can be ranked and this feature can be used
for the identification of less favorable areas.
For the regionalization of less productive areas
in national scale a functional approach was used
which integrates the knowledge on soil
degradation processes in nationwide level.
Specific soil threats were classified into ranked
categories. Supposing (quasi)uniform distribution
of vulnerability measure along these classes, we
introduced a standardized value as a ratio of
the class order to the maximum class order
expressed in percentage. For the overall spatial
characterization of degradation status, spatial
information was integrated in a result map by
summarizing the degradation specific
standardized cell values. This map in one hand
has been used for the delineation of soil
degradation regions. On the other hand
appropriate spatial aggregation of index values
on geographical and administrative regions is
suitable for their quantitative comparison thus
they can be ranked and this feature can be used
for the identification of less favorable areas.
For the regionalization of less productive areas
in national scale a functional approach was used
which integrates the knowledge on soil
degradation processes in nationwide level.
Specific soil threats were classified into ranked
categories. Supposing (quasi)uniform distribution
of vulnerability measure along these classes, we
introduced a standardized value as a ratio of
the class order to the maximum class order
expressed in percentage. For the overall spatial
characterization of degradation status, spatial
information was integrated in a result map by
summarizing the degradation specific
standardized cell values. This map in one hand
has been used for the delineation of soil
degradation regions. On the other hand
appropriate spatial aggregation of index values
on geographical and administrative regions is
suitable for their quantitative comparison thus
they can be ranked and this feature can be used
for the identification of less favorable
areas. For the regionalization of less productive
areas in national scale a functional approach was
used which integrates the knowledge on soil
degradation processes in nationwide level.
Specific soil threats were classified into ranked
categories. Supposing (quasi)uniform distribution
of vulnerability measure along these classes, we
introduced a standardized value as a ratio of
the class order to the maximum class order
expressed in percentage. For the overall spatial
characterization of degradation status, spatial
information was integrated in a result map by
summarizing the degradation specific
standardized cell values. This map in one hand
has been used for the delineation of soil
degradation regions. On the other hand
appropriate spatial aggregation of index values
on geographical and administrative regions is
suitable for their quantitative comparison thus
they can be ranked and this feature can be used
for the identification of less favorable areas.
For the regionalization of less productive areas
in national scale a functional approach was used
which integrates the knowledge on soil
degradation processes in nationwide level.
Specific soil threats were classified into ranked
categories. Supposing (quasi)uniform distribution
of vulnerability measure along these classes, we
introduced a standardized value as a ratio of
the class order to the maximum class order
expressed in percentage. For the overall spatial
characterization of degradation status, spatial
information was integrated in a result map by
summarizing the degradation specific
standardized cell values. This map in one hand
has been used for the delineation of soil
degradation regions. On the other hand
appropriate spatial aggregation of index values
on geographical and administrative regions is
suitable for their quantitative comparison thus
they can be ranked and this feature can be used
for the identification of less favorable areas.
For the regionalization of less productive areas
in national scale a functional approach was used
which integrates the knowledge on soil
degradation processes in nationwide level.
Specific soil threats were classified into ranked
categories. Supposing (quasi)uniform distribution
of vulnerability measure along these classes, we
introduced a standardized value as a ratio of
the class order to the maximum class order
expressed in percentage. For the overall spatial
characterization of degradation status, spatial
information was integrated in a result map by
summarizing the degradation specific
standardized cell values. This map in one hand
has been used for the delineation of soil
degradation regions. On the other hand
appropriate spatial aggregation of index values
on geographical and administrative regions is
suitable for their quantitative comparison thus
they can be ranked and this feature can be used
for the identification of less favorable areas.
Bridging the Centuries 1909 2009
Hungary B u d a p e s t 1617 September,
2009 www.mta.hu/soil2009 soil2009_at_szie.hu
Bridging the Centuries 19092009