Teil III: Praktische Erfahrungen mit dem Umweltmanagement in der Landwirtschaft

Zusammenfassung  Im Rahmen praktischer Untersuchungen der Autoren zu Umweltmanagementsystemen in der Landwirtschaft, und hier insbesondere der Umweltprüfung, zeigen sich die Besonderheiten der Agrarwirtschaft im Implementierungsproze?. Einige Bereiche k?nnen relativ einfach umgesetzt werden, andere Aspekte bedürfen einer differenzierteren Methodik als bei anderen Wirtschaftsbereichen. W?hrend sich das Managementaudit durch die übersichtliche Organisationsstruktur landwirtschaftlicher Betriebe meist als unkritisch erweist, werden beim Wirkungsund Rechtsaudit einige bereichsspezifische Probleme erkannt. Das Wirkungsaudit zeigt dem Anwender nach der Einführung einer neuen, speziell auf die Landwirtschaft angepa?ten Methodik der Stoffstrombilanzierung praxisorientierte Handlungspotentiale. Die Ergebnisse k?nnen je nach Bedarf auf Betriebs-, Betriebszweigoder Kostentr?gerebene ausgewiesen relevant, da sie einhohes ?kologischen Gef?hrdungspotential besitzen und bei den praktischen Erhebungen h?ufig Gegenstand von Beanstandungen waren. Diese betreffen vor allem die Lagerung von umweltrelevanten Stoffen (Pflanzenschutzmittel, Diesel, Jauche, Gülle, Festmist oder Sickers?fte) sowie die etwaigen Notwendigkeit und Beschaffenheit eines Waschplatzes. Die Konfliktbereiche werden beschrieben und darauf aufbauend Optionen zur Verbesserung aufgezeigt. Online-Publikationsdatum: 20.12.1999     

Teil II: Lösungsansätze für den landwirtschaftlichen Betrieb bei der Implementierung eines Umweltmanagementsystems

The registration of the present situation regarding environmental investigation is the basis for efficiently proceeding in the course of the implementation of environmental management systems (EMS). The basic analysis is found on the individual elements: reaction audit, management audit and compliance audit. Via an optimal performance of an environmental investigation while implementing an EMS, the basis for a maximum utilization has been created for the user as well for agriculture. Utilization for the company is provided by documentation of the organizational structure showing a transparency of procedures with regard to efficiency. Furthermore, an EMS is useful in the course of external tasks, e.g. public approach, business partners, position to authorities, deregulation or minimization of liability.     

Landfill leachate treatment by immediate one-step lime precipitation,carbonation, and phytoremediation fine-tuning

The high pollutant load of sanitary landfill leachates poses a huge challenge in the search for efficient and environment friendly solutions for their treatment. The objective of this work was to study an integrated solution of environmentally friendly technologies — immediate one-step lime precipitation (IOSLP), carbonation (CB), and phytoremediation (Phyt) — to treat a sanitary landfill leachate. In the leachate sample treatment by IOSLP, the influence of CaO concentration (18.2–33.3 g_CaO L^?1) and stirring time (2–60 min) on the sludge sedimentability and pollutant removal was studied. Organic load and ammonia nitrogen (AN) removal increases with CaO added, as well as sludge volume. Stirring time has a small influence on organic load and AN removal, presenting a minimum for sludge volume. Thus, the best operational conditions were chosen as 27.6 g_CaO L^?1, and 40-min stirring time, with 64% chemical oxygen demand (COD) removal. Sludge humidity was 2.1%, making dewatering needless. IOSLP supernatant was submitted to CB by atmospheric CO₂, and 100% removals in AN and hardness were attained. Effluents from IOSLP and IOSLP?+?CB were utilized in Phyt tests, with Vetiver (Chrysopogon zizanioides (L.) Roberty). The best COD removal (37%) during Phyt was attained for the samples treated by IOSLP?+?CB.

     

Metal composition of arrow squid (Nototodarus sloanii [Gray 1849]) from the Chatham Rise,New Zealand: implications for human consumption

Environmental Science and Pollution Research - Cephalopods are important in the diets of humans and many other apex predators, and can play an important role in the bioaccumulation of metals. In...     

Heavy metals detection in river water with cantilever nanobiosensor

Abstract

Heavy metals can be highly toxic depending on the dose and the chemical form. In this context, sensing devices such as nanobiosensors have been presented as a promising tool to monitor contaminants at micro and nanoscale. In this work, cantilever nanobiosensors with phosphatase alkaline were developed and applied to detect heavy metals (Pb, Ni, Cd, Zn, Co, and Al) in river water. The nanobiosensor surface was functionalized by the self-assembled monolayers (SAM) technique using 16-mercaptohexadecanoic acid, N-(3-dimethylaminopropyl)-N′-ethylcarbodiimide (EDC) and N- hydroxysuccinimide (NHS), and phosphatase alkaline enzyme. The sensing layer deposited on the cantilever surface presented a uniform morphology, at nanoscale, with 80?nm of thickness. The nanobiosensor showed a detection limit in the ppb range and high sensitivity, with a stability of fifteen days. The developed cantilever nanobiosensor is a simple tool, suitable for the direct detection of contaminants in river water.     

Remediation potential of caffeine,oxybenzone, and triclosan by the salt marsh plants <Emphasis Type="Italic">Spartina maritima</Emphasis> and <Emphasis Type="Italic">Halimione portulacoides</Emphasis>

Pharmaceuticals and personal care products (PPCPs) have attracted increasing concern during the last decade because of their widespread uses and continuous release to the aquatic environment. This work aimed to study the distribution of caffeine (CAF), oxybenzone (MBPh), and triclosan (TCS) when they arrive in salt marsh areas and to assess their remediation potential by two different species of salt marsh plants: Spartina maritima and Halimione portulacoides. Experiments were carried out in the laboratory either in hydroponics (sediment elutriate) or in sediment soaked in elutriate, for 10 days. Controls without plants were also carried out. CAF, MBPh, and TCS were added to the media. In unvegetated sediment soaked in elutriate, CAF was mainly in the liquid phase (83%), whereas MBPh and TCS were in the solid phase (90% and 56%, respectively); the highest remediation was achieved for TCS (40%) and mainly attributed to bioremediation. The presence of plants in sediment soaked in elutriate-enhanced PPCPs remediation, decreasing CAF and TCS levels between approximately 20-30% and MBPh by 40%.. Plant uptake, adsorption to plant roots/sediments, and bio/rhizoremediation are strong hypothesis to explain the decrease of contaminants either in water or sediment fractions, according to PPCPs characteristics.     

Life cycle assessment and sustainable engineering in the context of near net shape grown components: striving towards a sustainable way of future production

Technical product harvesting (TEPHA) is a newly developing interdisciplinary approach in which bio-based production is investigated from a technical and ecological perspective. Society‘s demand for ecologically produced and sustainably operable goods is a key driver for the substitution of conventional materials like metals or plastics through bio-based alternatives. Technical product harvesting of near net shape grown components describes the use of suitable biomass for the production of technical products through influencing the natural shape of plants during their growth period. The use of natural materials may show positive effects on the amount of non-renewable resource consumption. This also increases the product recyclability at the end of its life cycle. Furthermore, through the near net shape growth of biomass, production steps can be reduced. As a consequence such approaches may save energy and the needed resources like crude oil, coal or gas. The derived near net shape grown components are not only considered beneficial from an environmental point of view. They can also have mechanical advantages through an intrinsic topology optimization in contrast to common natural materials, which are influenced in their shape after harvesting. In order to prove these benefits a comprehensive, interdisciplinary scientific strategy is needed. Here, both mechanical investigations and life cycle assessment as a method of environmental evaluation are used.     

Impact of agglomeration and different dispersions of titanium dioxide nanoparticles on the human related in vitro cytotoxicity and genotoxicity

The published results on nanoparticles cytotoxicity and genotoxicity such as titanium dioxide nanoparticles (TiO(2) NPs) are inconsistent, and often conflicting and insufficient. Since different parameters may have impact on the toxicity results, there is need to lay stress on detailed characterization of NPs and the use of different testing conditions for assessment of NPs toxicity. In order to investigate whether dispersion procedures influence NP cytotoxicity and genotoxicity, we compared two protocols giving TiO(2) NP dispersions with different stability and agglomeration states. Detailed primary and secondary characteristics of both TiO(2) NP dispersions in culture media were carried out before toxicological testing; TK6 human lymphoblast cells, EUE human embryonic epithelial cells and Cos-1 monkey kidney fibroblasts were used to assess cytotoxicity (by trypan blue exclusion, proliferation activity and plating efficiency assays) and genotoxicity (by the comet assay). DNA strand breaks were detected by the alkaline comet assay. DNA oxidation lesions (especially 8-oxo-7,8-dihydroguanine, 8-oxoG) were measured with a modified comet assay including incubation with specific repair enzyme formamidopyrimidine DNA glycosylase (FPG). The TiO(2) NPs dispersion with large agglomerates (3 min sonication and no serum in stock solution) induced DNA damage in all three cell lines, while the TiO(2) NPs dispersed with agglomerates less than 200 nm (foetal serum in stock solution and sonication 15 min) had no effect on genotoxicity. An increased level of DNA oxidation lesions detected in Cos-1 and TK6 cells indicates that the leading mechanism by which TiO(2) NPs trigger genotoxicity is most likely oxidative stress. Our results show that the dispersion method used can influence the results of toxicity studies. Therefore at least two different dispersion procedures should be incorporated into assessment of cyto- and genotoxic effects of NPs. It is important, when assessing the hazard associated with NPs, to establish standard testing procedures and thorough strategies to consider the diverse conditions relevant to possible exposures.