Portrait of Franz Trolldenier; Employee of Mendelssohn Bank, Berlin Portraits Men

"11.4.1889 Franz Trolldenier geb. 5.12.1866"

Portrait of Georg Heinrich; Employee of Mendelssohn Bank, Berlin Portraits Men

"15.4.1889 Georg Heinrich geb. 12.5.1863. pens. 31.12.1927"

Portrait of Friedrich Brandes; Employee of Mendelssohn Bank, Berlin Portraits Men

"25.7.1891 Friedrich Brandes geb. 11.4.1867 pens. 31.12.1927"

Portrait of Moritz Romberg; Employee of Mendelssohn Bank, Berlin Portraits Men

"1.10.1891 Moritz Romberg geb. 4.6.1870"

Portrait of August Rothschild; Employee of Mendelssohn Bank, Berlin Portraits Men

"1.10.1891 August Rothschild geb. 14.11.1870"

Portrait of Otto Pieper; Employee of Mendelssohn Bank, Berlin Portraits Men

"1.10.1893 Otto Pieper geb. 11.2.1868"

Portrait of Heinrich Ruhrmann; Employee of Mendelssohn Bank, Berlin Portraits Men

"15.11.1893 Heinrich Ruhrmann geb. 1.1.1863 pens. 31.12.1927"

Portrait of Richard Mueller; Employee of Mendelssohn Bank, Berlin Portraits Men

"2.12.1895 Richard Mueller geb. 1.3.1853 pens. 31.12.1927"

Portrait of Franz Koch; Employee of Mendelssohn Bank, Berlin Portraits Men

"15.8.1896 Franz Koch geb. 14.9.1860 gest. 21.10.1927"

Portrait of Max Fonrobert; Employee of Mendelssohn Bank, Berlin Portraits Men

"1.6.1897 Max Fonrobert geb. 5.12.1866"

Portrait of Otto Pfeiffer; Employee of Mendelssohn Bank, Berlin Portraits Men

"1.12.1897 Otto Pfeiffer geb. 23.10.1873"

Heb. U. (Hebrew University) - Grad. (Graduation) '32 - High Commissioner

Digital image

Soil seed bank dynamics in response to an extreme flood event in a riparian habitat

A significantly increased water regime can lead to inundation of rivers, creeks and surrounding floodplains- and thus impact on the temporal dynamics of both the extant vegetation and the dormant, but viable soil-seed bank of riparian corridors. The study documented changes in the soil seed-bank along riparian corridors before and after a major flood event in January 2011 in southeast Queensland, Australia. The study site was a major river (the Mooleyember creek) near Roma, Central Queensland impacted by the extreme flood event and where baseline ecological data on riparian seed-bank populations have previously been collected in 2007, 2008 and 2009. After the major flood event, we collected further soil samples from the same locations in spring/summer (November–December 2011) and in early autumn (March 2012). Thereafter, the soils were exposed to adequate warmth and moisture under glasshouse conditions, and emerged seedlings identified taxonomically. Flooding increased seed-bank abundance but decreased its species richness and diversity. However, flood impact was less than that of yearly effect but greater than that of seasonal variation. Seeds of trees and shrubs were few in the soil, and were negatively affected by the flood; those of herbaceous and graminoids were numerous and proliferate after the flood. Seed-banks of weedy and/or exotic species were no more affected by the flood than those of native and/or non-invasive species. Overall, the studied riparian zone showed evidence of a quick recovery of its seed-bank over time, and can be considered to be resilient to an extreme flood event.

Evaluation of restoration of vegetation infested with cat's claw creeper vine (Dolichandra unguis-cati): soil seed bank response to herbicide and physical removal

Cat’s claw creeper vine, Dolichandra unguis-cati (L.) L.G.Lohmann (formerly known as Macfadyena unguis-cati (L.) A.H.Gentry), a Weed of National Significance (WoNS), is a structural woody parasite that is highly invasive along sensitive riparian corridors and native forests of coastal and inland eastern Australia. As part of evaluation of the impact of herbicide and mechanical/physical control techniques on the long-term reduction of biomass of the weed and expected return of native flora, we have set-up permanent vegetation plots in: (a) infested and now chemically/physically treated, (b) infested but untreated and (c) un-infested patches. The treatments were set up in both riparian and non-riparian habitats to document changes that occur in seed bank flora over a two-year post-treatment period. Response to treatment varied spatially and temporally. However, following chemical and physical removal treatments, treated patches exhibited lower seed bank abundance and diversity than infested and patches lacking the weed, but differences were not statistically significant. Thus it will be safe to say that spraying herbicides using the recommended rate does not undermine restoration efforts.

Seed bank longevity and age to reproductive maturity of Calotropis procera (Aiton) W.T. Aiton in the dry tropics of northern Queensland

Understanding the reproductive biology of Calotropis procera (Aiton) W.T. Aiton, an invasive weed of northern Australia, is critical for development of effective management strategies. Two experiments are reported on. In Experiment 1 seed longevity of C. procera seeds, exposed to different soil type (clay and river loam), pasture cover (present and absent) and burial depth (0, 2.5, 10 and 20 cm) treatments were examined. In Experiment 2 time to reach reproductive maturity was studied. The latter experiment included its sister species, C. gigantea (L.) W.T. Aiton, for comparison and two separate seed lots were tested in 2009 and 2012 to determine if exposure to different environmental conditions would influence persistence. Both seed lots demonstrated a rapid decline in viability over the first 3 months and declined to zero between 15 and 24 months after burial. In Experiment 1, longevity appeared to be most influenced by rainfall patterns and associated soil moisture, burial depth and soil type, but not the level of pasture cover. Experiment 2 showed that both C. procera and C. gigantea plants could flower once they had reached an average height of 85 cm. However, they differed significantly in terms of basal diameter at first flowering with C. gigantea significantly smaller (31 mm) than C. procera (45 mm). On average, C. gigantea flowered earlier (125 days vs 190 days) and set seed earlier (359 days vs 412 days) than C. procera. These results suggest that, under similar conditions to those that prevailed in the present studies, land managers could potentially achieve effective control of patches of C. procera in 2 years if they are able to kill all original plants and treat seedling regrowth frequently enough to prevent it reaching reproductive maturity. This suggested control strategy is based on the proviso that replenishment of the seed bank is not occurring from external sources (e.g. wind and water dispersal).