Considering the increasing role of cities throughout the world and in Europe, the European Union regulations on cohesion policy that are binding in the 2014–2020 programme period have foreseen the need to introduce a separate intervention dedicated to cities and their functional areas. However, the implementation of these solutions did not come without certain problems. They referred both to the process of institutionalising co-operation and to the realisation of projects. Also in Poland, Integrated Territorial Investments have not gone beyond co-operation for the absorption of EU funding so far, which demonstrates doubtlessly that their potential still remains unexploited. Thus, a discussion on both the positive and negative aspects of the implementation of ITIs is necessary. Poland, as the largest beneficiary of the Cohesion Policy, has a wide experience, which might provide valuable information on that matter. The aim of the paper is to present these experiences and to provide conclusions for the regional policy.
Today’s cities tend to “pour out” beyond their administrative boundaries. This phenomenon is related to the settlement of people “from the city” in neighboring municipalities, or taking up jobs in cities by people living in neighboring municipalities. This has been recognized in the European Union, which has introduced appropriate legal instruments for cohesion policy. Integrated Territorial Investments were introduced to the EU cohesion policy for the fi rst time in the 2014-2020 fi nancial perspective. Their goal was to intensify cooperation between cities and their functional areas. Unfortunately, the emerging information about diffi culties in implementing ITIs often become the basis for considering this idea ineff ective. The purpose of the work is qualitative and quantitative verifi cation of the operation of ITU based on selected data, so that it is possible to answer the question about the validity of the existence of this instrument.
The paper presents an impact of the metallurgical wastes dumping site on the following parts of the environment: air, soil and surface waters. Some of the methods used to prevent wastes interactions were showed. The results of the metallurgical wastes leachate samples research, in which toxic metal ions have been found, are presented results of examinations performed on water extracts derived from two types of metallurgical wastes were given. The chemical analysis of water extracts indicate exceeded concentration of toxic metals, such as: lead, arsenic, barium and others. Preliminary results of some metals elimination from the water extracts with PUROLITE ion-exchangers were also presented. The utilised acidous cationit with Na+ groups exchanges the Ba2+ ions in almost 90%, similar to S 930 ionit with chelating groups (Table 5 and 7). Whereas the anionit with hydroxyl groups removes the arsenic ions(V) from the solution with the 60% efficacy (Table 7).
A vertical cut at the mid-depth of the 15-ton forging steel ingot has been performed by curtesy of the CELSA – Huta Ostrowiec plant.
Some metallographic studies were able to reveal not only the chilled undersized grains under the ingot surface but columnar grains and
large equiaxed grains as well. Additionally, the structural zone within which the competition between columnar and equiaxed structure
formation was confirmed by metallography study, was also revealed. Therefore, it seemed justified to reproduce some of the observed
structural zones by means of numerical calculation of the temperature field. The formation of the chilled grains zone is the result of
unconstrained rapid solidification and was not subject of simulation. Contrary to the equiaxed structure formation, the columnar structure
or columnar branched structure formation occurs under steep thermal gradient. Thus, the performed simulation is able to separate both
discussed structural zones and indicate their localization along the ingot radius as well as their appearance in term of solidification time.