The north–south coordinate was a strong explanatory variable both for species numbers and species composition. This is not surprising because, compared to the sites north of the lake, the area around lake Mälaren is both climatically favourable (Raab and Vedin 1995) and has a high density of sites with old trees. Mälaren has been identified as a diversity hot-spot for saproxylic beetles (Ehnström and Waldén 1986), with the western part of Mälaren regarded as being especially species-rich. This was only weakly supported by the results of the present study, as the variable RT90E (west–east

coordinate) had low explanatory power. Practical implications The high conservation value of parks for saproxylic insects shown in this study is dependent on the retention of old trees. Thus, the total rejuvenation of trees, which is considered in some parks, would be fatal this website to the resident fauna. However, all trees will sooner or later die, or they have to be removed for safety or aesthetic reasons. If they individually and continuously are replaced when they die there will be a Selleckchem Alvocidib continuous supply of new trees growing into the ancient-tree age class which in turn means a continuous supply of suitable habitat for the saproxylic insects. On a short term a good measure is to retain trees, or parts of trees, that are cut Idasanutlin mw or fallen in a “tree-graveyard”

situated in a remote part of the park, where it does not conflict with the aesthetic values. Such graveyards is both a chance for insects to finalise their development and a habitat patch that can be colonised (Aulén and Franc

2008). However, compared to the management aiming at a long term continuous supply of old trees, this is of minor importance, both because its’ short term effect and because most of the valuable contributions to the graveyard emanate from the old trees. As almost all lime trees in MYO10 parks, and many lime trees in the more natural sites, were originally pollarded, they are at risk of breaking apart when the shoots from the last pollarding are allowed to grow into large trees. This was observed on several of the sites in this study. The risk of breakage is especially great in re-grown sites where the closer canopy gives less light to the trees, which in turn decreases the production of carbohydrates needed for building a stable trunk. For keeping these old trees alive it is important to continue pollarding. However, old trees that has not been managed for a long time need careful treatment when management is resumed (Slotte 1997; Wisenfield 1995). A strong reduction of the crown by cutting all large branches may be fatal. As pollarding is an expensive measure, it is important that it should only be done on sites where there is the potential to retain the associated fauna and flora, i.e. where one can forecast a continuous supply of old trees in the future. Most of the parks in the present study do have this potential due to the continuous replacement of trees that die.