Monitoring zdravstvene ispravnosti vode za piće iz vodoopskrbnog sustava Grada Zagreba (Monitoring of Drinking Water Safety from the City of Zagreb Water Supply)

U radu su prikazani rezultati monitoringa zdravstvene ispravnosti vode za piće iz javnog vodoopskrbnog sustava grada Zagreba u razdoblju od 01.01.2005. do 01.09.2006. godine. Zdravstvena ispravnost vode za piće je od velikog javno-zdravstvenog interesa, pa je monitoring vode za piće potrebno provoditi u cjelosti i na nacionalnoj razini

Monitoring zdravstvene ispravnosti vode za piće iz vodoopskrbnog sustava Grada Zagreba (Monitoring of Drinking Water Safety from the City of Zagreb Water Supply)

U radu su prikazani rezultati monitoringa zdravstvene ispravnosti vode za piće iz javnog vodoopskrbnog sustava grada Zagreba u razdoblju od 01.01.2005. do 01.09.2006. godine. Zdravstvena ispravnost vode za piće je od velikog javno-zdravstvenog interesa, pa je monitoring vode za piće potrebno provoditi u cjelosti i na nacionalnoj razini

PRC1‐labeled microtubule bundles and kinetochore pairs show one‐to‐one association in metaphase

In the mitotic spindle, kinetochore microtubules form k‐fibers, whereas overlap or interpolar microtubules form antiparallel arrays containing the cross‐linker protein regulator of cytokinesis 1 (PRC1). We have recently shown that an overlap bundle, termed bridging fiber, links outermost sister k‐fibers. However, the relationship between overlap bundles and k‐fibers throughout the spindle remained unknown. Here, we show that in a metaphase spindle more than 90% of overlap bundles act as a bridge between sister k‐fibers. We found that the number of PRC1‐GFP‐labeled bundles per spindle is nearly the same as the number of kinetochore pairs. Live‐cell imaging revealed that kinetochore movement in the equatorial plane of the spindle is highly correlated with the movement of the coupled PRC1‐GFP‐labeled fiber, whereas the correlation with other fibers decreases with increasing distance. Analysis of endogenous PRC1 localization confirmed the results obtained with PRC1‐GFP. PRC1 knockdown reduced the bridging fiber thickness and interkinetochore distance throughout the spindle, suggesting a function of PRC1 in bridging microtubule organization and force balance in the metaphase spindle

Rast i fotosinteza u vodene leće (Lemna minor L.) izložene kadmiju u kombinaciji s cinkom ili bakrom

Metals have a variety of negative outcomes on plants, essential components of any ecosystem. The effects of CdCl2 (5 μmol L-1), ZnCl2 (25 or 50 μmol L-1), and CuCl2 (2.5 or 5 μmol L-1) and combinations of CdCl2 with either ZnCl2 or CuCl2 on the growth, photosynthetic pigments, and photosystem II (PSII) efficiency of duckweed (Lemna minor L.) were investigated. All of the treatments caused growth inhibition and remarkable metal accumulation in plant tissue after 4 and 7 days. In the combined treatments, the accumulation of each metal applied was lesser in comparison to treatments with single metals. After 4 days, all of the treatments generally diminished chlorophyll a content and decreased the maximum quantum yield (Fv/Fm) and effective quantum yield (ΔF/F’m) of PSII. However, after 7 days of exposure to a combination of Cd and Zn, pigment content and PSII activity recovered to control levels. A higher concentration of Cu (5 μmol L-1) as well as Cd in combination with Cu had a prolonged inhibitory effect on photosynthetic features. Our results suggest that growth inhibition was due to the toxic effect of absolute metal quantity in plant tissue. Zn counteracted Cd uptake, as seen from the recovery of pigment content and PSII efficiency in plants exposed for 7 days to the Cd and Zn combination. Cu-induced oxidative stress led to a prolonged inhibitory effect in plants treated both with a higher concentration of Cu (5 μmol L-1) and simultaneously with Cd and Cu. Our findings could contribute to general knowledge on anthropogenic and environmental contaminants that endanger plant communities and significantly disrupt the sensitive balance of an ecosystem by influencing photosynthetic mechanisms.Izloženost metalima može izazvati različite štetne učinke u biljaka. Vodene leće izložili smo solima teških metala CdCl2 (5 μmol L 1), ZnCl2 (25 μmol L 1 ili 50 μmol L 1) i CuCl2 (2,5 μmol L 1 ili 5 μmol L 1) te kombinaciji CdCl2 sa svakom od navedenih koncentracija ZnCl2 i CuCl2. Rast biljaka, količina fotosintetskih pigmenata i učinkovitost fotosistema II (PSII) mjereni su nakon četiri i sedam dana tretmana. Utvrđeno je da su svi tretmani uzrokovali značajnu inhibiciju rasta te akumulaciju metala u biljci. U biljaka koje su bile izložene kombinacijama teških metala količina pojedinog metala u tkivu bila je niža u odnosu na količinu istog metala u biljaka izloženih samo tom metalu. Nakon četiri dana tretmana sva su tri metala, neovisno o tome jesu li bila primijenjena zasebno ili u kombinacijama, uzrokovala smanjenje količine klorofila a i pad vrijednosti maksimalnog (Fv/Fm) i efektivnog (ΔF/F’m) prinosa PSII. Međutim, u biljaka koje su bile istovremeno izlagane kadmiju i cinku, vrijednosti količine pigmenata i učinkovitost PSII vratile su se nakon sedam dana na kontrolnu razinu, a bakar u koncentraciji 5 μmol L 1 te kombinacija kadmija i bakra i dalje su imali inhibitorni učinak. Budući da smanjeno primanje pojedinog metala uočeno u biljaka izloženih kombiniranim tretmanima nije ublažilo inhibitorni učinak na rast, možemo zaključiti da je inhibicija rasta uzrokovana apsolutnom količinom metala primljenog u tkivo. Povećanje količine fotosintetskih pigmenata i učinkovitosti PSII nakon sedam dana tretmana kadmijem i cinkom upućuje na oporavak biljaka, što se može objasniti ublažavajućim djelovanjem cinka na učinak kadmija uslijed smanjenog primanja kadmija u biljku. Suprotno tome, dugotrajni inhibitorni učinak istovremenog tretmana biljaka kadmijem i bakrom te samim bakrom u koncentraciji 5 μmol L 1 može se objasniti oksidacijskim stresom uzrokovanim bakrom. Rezultati ovoga istraživanja pridonose saznanjima o štetnim učincima antropogenih i okolišnih onečišćivača, koji narušavanjem mehanizama fotosinteze ugrožavaju ne samo biljke i njihove zajednice nego i osjetljivu ravnotežu ekosustava

On the Zagreb Indices as Complexity Indices

Two original Zagreb indices, denoted M1 and M2, and introduced in 1972, were symmetry-modified by summing up only degrees (SMM1) or edge-weights (SMM2) of symmetry nonequivalent vertices or edges of graphs. Their dependence on the structural features and symmetry of molecular graphs is studied. They were also compared to eight other complexity indices (RCI, TC, TC1, BT, BI, twc, wcx) on nine graphs (A, B, C, D, E, F, G, H, I) with five vertices that were earlier studied by several research groups. The TC, TC1 and Nt produce exactly the same complexity ordering of nine graphs (I>H>G>F>E>D>C>B>A). The ordering produced by M1 is different from this ordering in that it cannot discriminate E and F, and C and D. Likewise, M2 and twc produce exactly the same ordering and the latter ordering differs from the former only in the reverse order of E and F. Orderings produced by SMM1 and SMM2 differ considerably from orderings given by TC, TC1 and Nt or M2 and twc

Occurrence of P. aeruginosa in Water Intended for Human Consumption and in Swimming Pool Water

Considering the fact that water is a basic need of every living being, it is important to ensure its safety. In this work, the data on the presence of the opportunistic pathogen P. aeruginosa in drinking water (n = 4171) as well as in pool water (n = 5059) in Primorje-Gorski Kotar County in Croatia in the five-year period (2016–2020) were analysed. In addition, the national criteria were compared with those of neighboring countries and worldwide. The proportion of P. aerugino-sa- positive samples was similar for drinking water (3.9%) and pool water (4.6%). The prevalence of this bacterium was most pronounced in the warmer season. P. aeruginosa-positive drinking water samples were mostly collected during building commissioning, while pool samples were from entertainment and spa/hydromassage pools. Outdoor pools showed a higher percentage of positive samples than indoor pools, as well as the pools filled with freshwater rather than sea-water. The highest P. aeruginosa load was found in rehabilitation pools. Cro

Učinak bakra na toksičnost i genotoksičnost kadmija u vodenoj leći (Lemna minor L.)

We investigated interactions between copper (in the concentrations of 2.5 μmol L-1 and 5 μmol L-1) and cadmium (5 μmol L-1) in common duckweed (Lemna minor L.) by exposing it to either metal or to their combinations for four or seven days. Their uptake increased with time, but it was lower in plants treated with combinations of metals than in plants treated with either metal given alone. In separate treatments, either metal increased malondialdehyde (MDA) level and catalase and peroxidase activity. Both induced DNA damage, but copper did it only after 7 days of treatment. On day 4, the combination of cadmium and 5 μmol L-1 copper additionally increased MDA as well as catalase and peroxidase activity. In contrast, on day 7, MDA dropped in plants treated with combinations of metals, and especially with 2.5 μmol L-1 copper plus cadmium. In these plants, catalase activity was higher than in copper treated plants. Peroxidase activity increased after treatment with cadmium and 2.5 μmol L-1 copper but decreased in plants treated with cadmium and 5 μmol L-1 copper. Compared to copper alone, combinations of metals enhanced DNA damage after 4 days of treatment but it dropped on day 7. In conclusion, either metal given alone was toxic/genotoxic and caused oxidative stress. On day 4 of combined treatment, the higher copper concentration was more toxic than either metal alone. In contrast, on day 7 of combined treatment, the lower copper concentration showed lower oxidative and DNA damage. These complex interactions can not be explained by simple antagonism and/or synergism. Further studies should go in that direction.U svrhu istraživanja interakcija između bakra kao esencijalnog elementa te kadmija kao neesencijalnog i toksičnog metala, vodenu leću Lemna minor L. uzgajali smo na podlogama s kadmijem (5 μmol L-1) odnosno s bakrom (2,5 μmol L-1 i 5 μmol L-1) te s njihovim kombinacijama. Unos metala u biljke povećavao se s trajanjem pokusa, a kod kombinacije metala u biljkama je izmjerena niža količina kadmija nego u onima uzgajanima samo na kadmiju. U biljkama tretiranim pojedinačnim metalom došlo je do povećanja sadržaja malondialdehida (MDA) te aktivnosti katalaze i peroksidaze u odnosu na kontrolne biljke. Također, primijećeno je oštećenje DNA iako kod bakra tek sedmog dana tretmana. Količina MDA i aktivnost obaju enzima dodatno se povećala na tretmanu kombinacijom kadmija i bakra (5 μmol L-1) nakon četvrtog dana pokusa, dok se količina MDA smanjila nakon sedmog dana kod kombinacije kadmija i 2,5 μmol L-1 bakra. U tim biljkama primijećena je i veća aktivnost katalaze, dok je aktivnost peroksidaze porasla na tretmanu kadmijem i 2,5 μmol L-1 bakrom, ali se smanjila na tretmanu kadmijem i 5 μmol L-1 bakrom. Oštećenje DNA koje je bilo veće kod kombinacije metala nakon četvrtog dana, osobito u usporedbi sa samim bakrom, smanjilo se nakon sedmog dana pokusa. Iz ovih rezultata može se zaključiti da su oba metala u istraživanim koncentracijama toksična i genotoksična za vodenu leću i da uzrokuju oksidacijski stres. Kadmij u kombinaciji s bakrom više koncentracije bio je toksičniji od pojedinačnih metala nakon četvrtog dana pokusa, dok su u biljaka tretiranih kombinacijom kadmija i bakra niže koncentracije toksični učinci bili manji. Budući da su primijećene interakcije vrlo kompleksne i ne uključuju samo antagonizam odnosno sinergizam potrebna su daljnja istraživanja