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Heterotrophic protists are essential components of the marine ecosystem, yet they are often excluded from monitoring programmes. With limited resources, monitoring strategies need to be optimised considering both scientific knowledge and available resources. In doing so, it is crucial to understand how sampling frequency affects the value of the data. We analysed 11 years of weekly heterotrophic protist time-series data from Station L4 in the Western English Channel to explore how different sampling intervals impact data quality. In the L4 dataset, comprising 55 protist taxa, the reduction of sampling frequency from weekly to four times a year at specific seasons decreased the number of taxa encountered by 38% for ciliates and 29% for heterotrophic dinoflagellates while the mean annual biomass or its mean variation were not affected. Furthermore, when samples were taken only four times a year, biomass peaks of the ten most important taxa were often missed. The primary motivator for this study was furthering the development of the heterotrophic protist monitoring in temperate and subarctic marine areas, e.g. the Baltic Sea. Based on our findings, we give recommendations on sampling frequency to optimise the value of heterotrophic protist monitoring.

The use of citizen science in the collection of surface water marine microplastics (MP) samples with manta trawl was tested in the Baltic Sea, where the collection of surface water samples is often hampered by environmental conditions. Sampling was carried out at 7 locations around the Baltic Sea with a custom-made manta trawl which was operated onboard a sailing boat. The total concentrations of ≥ 0.3 mm MP in the samples ranged from 0.45 to 1.98 MP m−3. Based on the results and experiences from this study, citizen science could be introduced into the toolbox of monitoring large MP. When the common basic constraints of surface water sampling within a regional sea are defined and agreed upon, citizen science could be used for strengthening the power of assessments on the state of the marine environment by increasing the spatial coverage of the monitored area.

Highlights • Microplastics were found in 9% of all sampled fish. • Fish caught within the urban area of Helsinki displayed the highest occurrence of plastic ingestion (27.5%). • No relationship was found between microplastic occurrence in fish and plastic concentration in seawater. • This study is the first assessment on microplastic ingestion by coastal fish in Finland. Microplastic (MP) ingestion by four species of small coastal fish from the northern Baltic Sea was investigated. The digestive tract contents of 424 specimens, caught across eight sampling sites along the Finnish coastline were analysed for the occurrence of MP ingestion. MP were found in 38 fish individuals (9% of sampled fish). Specimens from the urban area of Helsinki displayed the highest prevalence of ingested plastics (27.5%). No relationship was found between the size or species of the fish and the presence of ingested MP particles nor the amount of MP in seawater. The comparison to a previous study conducted using the same research methods indicates that the ingestion of MP is more common in coastal fish than in offshore fish in the northern Baltic Sea.

In the Baltic Sea, water is stratified due to differences in density and salinity. The stratification prevents water from mixing, which could affect sinking rates of microplastics in the sea. We studied the accumulation of microplastics to halocline and thermocline. We sampled water with a 100 μm plankton net from vertical transects between halo- and thermocline, and a 30 L water sampler from the end of halocline and the beginning of thermocline. Thereafter, microplastics in the whole sample volumes were analyzed with imaging Fourier transform infrared spectroscopy (FTIR). The plankton net results showed that water column between halo- and thermoclines contained on average 0.92 ± 0.61 MP m

The ingestion of microlitter by blue mussels (450) was studied at a wastewater recipient area in the Baltic Sea. The mussel soft tissues were digested using enzymatic detergents and the detected litter particles characterized with FT-IR imaging spectroscopy. Microlitter concentration in seawater and WWTP effluent were also measured. Microlitter was found in 66% of the mussels. Mussels from the WWTP recipient had higher microlitter content compared to those collected at the reference site. Plastics made up 8% of all the analysed microlitter particles. The dominating litter types were fibres (~90% of all microlitter), 42% of which were cotton, 17% linen, 17% viscose and 4% polyester. The risk of airborne contamination during laboratory work was lowered when mussels were digested with their shells on instead of dissecting them first. The approach was found applicable and gentle to both non-synthetic and synthetic materials including fragile fibres.

Although the presence of microplastics in marine biota has been widely recorded, extraction methods, method validation and approaches to monitoring are not standardized. In this study a method for microplastic extraction from fish guts based on a chemical alkaline digestion is presented. The average particle retrieval rate from spiked fish guts, used for method validation, was 84%. The weight and shape of the test particles (PET, PC, HD-PE) were also analysed with no noticeable changes in any particle shapes and only minor weight change in PET (2.63%). Microplastics were found in 1.8% of herrings (n = 164) and in 0.9% of sprat (n = 154). None of the three-spined sticklebacks (n = 355) contained microplastic particles.

Effects of household post-consumer plastics and tyre rubber on a Baltic Sea copepod Limnocalanus macrurus were assessed. Fragments of commercial recycled low-density polyethylene vegetable bags and rubber originating from recycled car tyres were incubated in seawater, and the copepods were exposed to the filtrate of the water. L. macrurus experienced erratic swimming behaviour and increased mortality in the filtrate of unwashed vegetable bags, containing elevated concentrations of alcohols, organic acids and copper. Responses of the antioxidant defence system (ADS) were recorded in copepods exposed to rubber treatments containing high concentrations of zinc. Significant responses in the ADS enzymes indicate that reactive oxygen species (ROS) formation was exceeding the detoxification capacity of the ADS which may further lead to prolonged state of oxidative stress. Observed effects of exposure on the biochemical level coincide with impaired swimming activity of the copepods, indicating possible irreversible cellular responses leading to behavioural changes and mortality.

Highlights • The ingestion rate of microplastics (MPs) was 17% for perch and 25% for vendace. • Most of the ingested MPs were smaller than 100 μm. • Imaging FTIR method was developed for the quantification of MPs from fish gut. • Contamination increased the limit of detection especially for small MPs. Despite the ubiquitousness of microplastics, knowledge on the exposure of freshwater fish to microplastics is still limited. Moreover, no standard methods are available for analyzing microplastics, and the quality of methods used for the quantification of ingested microplastics in fish should be improved. In this study, we studied microplastic ingestion of common wild freshwater fish species, perch (Perca fluviatilis) and vendace (Coregonus albula). Further, our aim was to develop and validate imaging Fourier-transform infrared spectroscopic method for the quantification of ingested microplastics. For this purpose, enzymatically digested samples were measured with focal plane array (FPA) based infrared microscope. Data was analyzed with siMPle software, which provides counts, mass estimations, sizes, and materials for the measured particles. Method validation was conducted with ten procedural blanks and recovery tests, resulting in 75% and 77% recovery rates for pretreatment and infrared imaging, respectively. Pretreatment caused contamination principally by small

Microplastics (MPs) are observed to be present on the seafloor ranging from coastal areas to deep seas. Because bioturbation alters the distribution of natural particles on inhabited soft bottoms, a mesocosm experiment with common benthic invertebrates was conducted to study their effect on the distribution of secondary MPs (different-sized pieces of fishing line

The need for harmonized monitoring protocols for marine microplastic has been discussed for many years, but how to reach this goal has not been agreed upon. Important questions addressed when micro ...

Microplastics (MPs) are ubiquitous in the marine environment. High concentrations of MPs are found from seafloor sediments, which have been proposed to act as their final sinks. Because bioturbation is an important process affecting the burial of MPs, a mesocosm experiment was established to study whether sediment infauna may also promote MP return to the sediment surface. Thin layers of frozen sediment containing an environmentally realistic concentration (1300 MPs per kg of dry sediment) of MP fragments in two size classes (500 μm and 100-300 μm) were added to depths of 2 cm and 5 cm in the experimental cylinders filled with sediment. The displacement of these MPs, made of acrylonitrile butadiene styrene (ABS), by a community of common benthic invertebrates in the northern Baltic Sea (clam Limecola balthica, polychaete Marenzelleria spp., gammarid Monoporeia affinis) was studied in a 10-week experiment. After the experiment, the MPs were extracted from each sediment layer and the animals were examined for MP ingestion. The results indicated that the transportation of MPs to the sediment surface by bioturbation was negligible. Thus, in the Baltic Sea, the seafloor may act as a sink for once sedimented MPs, reducing simultaneously the MP exposure of the macrofauna feeding on the sediment surface.

Experimental studies have shown how microplastics are taken up by various aquatic organisms. Most of these studies have been carried out with small ( 200 μm and ABS > 100 μm) in comparison to primary microplastic beads (90 μm). Our results show that fragments of secondary plastics may end up in the food web but only in small amounts, and that the size of the fragments more than their shape is a crucial nominator influencing the numbers of plastics ingested. Future research aiming to resolve the effects of microplastics in the ecosystems should concentrate on environmentally relevant plastics and concentrations.

Microplastic debris is a globally pervasive contaminant, which presents a substantial risk to marine biota, food webs, and ecosystems. Microplastics are heterogeneously distributed, with highest concentrations associated with the oligotrophic subtropical gyres and relatively biologically productive semienclosed seas and coastal waters. Encounter rates between biota and microplastics are driven by their geographic overlap and relative concentrations; the characteristics of the plastic; and the motility, detection capabilities, and feeding strategy of the organism. We identify four main routes via which microplastics can infiltrate marine food webs: ingestion, inhalation, entanglement, and trophic transfer. Drawing upon established research and more recent exposure studies using microplastics, we highlight how plastics can be detected, ingested, processed, and rejected by filter feeders. Finally, we consider how marine organisms can affect microplastics, by incorporating the plastic into biological matrices, through the movement, redistribution, and burial of plastic.

Conventional wastewater treatment with primary and secondary treatment processes efficiently remove microplastics (MPs) from the wastewater. Despite the efficient removal, final effluents can act as entrance route of MPs, given the large volumes constantly discharged into the aquatic environments. This study investigated the removal of MPs from effluent in four different municipal wastewater treatment plants utilizing different advanced final-stage treatment technologies. The study included membrane bioreactor treating primary effluent and different tertiary treatment technologies (discfilter, rapid sand filtration and dissolved air flotation) treating secondary effluent. The MBR removed 99.9% of MPs during the treatment (from 6.9 to 0.005 MP L−1), rapid sand filter 97% (from 0.7 to 0.02 MP L−1), dissolved air flotation 95% (from 2.0 to 0.1 MP L−1) and discfilter 40–98.5% (from 0.5 – 2.0 to 0.03–0.3 MP L−1) of the MPs during the treatment. Our study shows that with advanced final-stage wastewater treatment technologies WWTPs can substantially reduce the MP pollution discharged from wastewater treatment plants into the aquatic environments., final draft, peerReviewed

The cryptomonad Rhinomonas nottbecki n. sp., isolated from the Baltic Sea, is described from live and fixed cells studied by light, scanning, and transmission electron microscopy together with sequences of the partial nucleus- and nucleomorph-encoded 18S rRNA genes as well as the nucleus-encoded ITS1, 5.8S, ITS2, and the 5′-end of the 28S rRNA gene regions. The sequence analyses include comparison with 43 strains from the family Pyrenomonadaceae. Rhinomonas nottbecki cells are dorsoventrally flattened, obloid in shape; 10.0–17.2 μm long, 5.5–8.1 μm thick, and 4.4–8.8 μm wide. The inner periplast has roughly hexagonal plates. Rhinomonas nottbecki cells resemble those of Rhinomonas reticulata, but the nucleomorph 18S rRNA gene of R. nottbecki differs by 2% from that of R. reticulata, while the ITS region by 11%. The intraspecific variability in the ITS region of R. nottbecki is 5%. In addition, the predicted ITS2 secondary structures are different in R. nottbecki and R. reticulata. The family Pyrenomonadaceae includes three clades: Clade A, Clade B, and Clade C. All Rhinomonas sequences branched within the Clade C, while the genus Rhodomonas is paraphyletic. The analyses suggest that the genus Storeatula is an alternating morphotype of the genera Rhinomonas and Rhodomonas and that the family Pyrenomonadaceae includes some species that were described multiple times, as well as novel species.

Since its first reported appearance in the Baltic Sea in 2007, there has been a little research on the role of the Arctic ctenophore Mertensia ovum in this ecosystem. We provide results from the first feeding experiments of M. ovum from the northern Baltic Sea. Experiments were conducted with various prey types; picocyanobacteria Synechococcus bacillaris, ciliates Mesodinium rubrum, nauplii of mixed copepod species and copepodites of Eurytemora affinis. Molecular gut content analyses were also used to measure in situ feeding of M. ovum on the picocyanobacteria. The observed clearance rates on M. rubrum (< 9.0 mL predator(-1) h(-1)), and S. bacillaris (

Species identification based on morphological characteristics has caused misidentifications and led to twisted views of abundances and roles of ctenophores. Based on extensive field studies from 2007 to 2010, the occurrence of the arctic ctenophore Mertensia ovum was genetically verified in the southern, central and northern Baltic Sea, and its egg production, distribution and abundance were studied in relation to physical factors. Genetic analyses indicate that M. ovum is by far the most abundant small ctenophore in the Baltic Sea. Specimens from a 20 yr old ctenophore collection were also genetically identified as M. ovum, contrary to their previous morphological identification as another ctenophore species, Pleurobrachia pileus. Thus, earlier reports on P. pileus in the Baltic Sea may actually refer to M. ovum. The abundance of M. ovum was regulated by both salinity and temperature, with highest abundances found in sea areas and water layers at temperatures 5.5 and oxygen levels >4 ml l-1. During summer, the highest abundances of ctenophores and their eggs were found near the halocline, while the distribution was more uniform throughout the water column during winter. Only ctenophores >3.5 mm (oral-aboral length) produced eggs in the experiments, with an average rate of 2.2 eggs ind.-1 d-1. Finally, comparison with published data from the 1980s (assuming that those data refer to M. ovum) indicates that the present-day ctenophore abundance is ~80% lower in the north and ~55% higher in the southern parts of the Baltic Sea, due to reasons yet to be established.

Article, Wastewater treatment plants (WWTPs) can offer a solution to reduce the point source input of microlitter and microplastics into the environment. To evaluate the contributing processes for microlitter removal, the removal of microlitter from wastewater during different treatment steps of mechanical, chemical and biological treatment (activated sludge) and biologically active filter (BAF) in a large (population equivalent 800 000) advanced WWTP was examined. Most of the microlitter was removed already during the pre-treatment and activated sludge treatment further decreased the microlitter concentration. The overall retention capacity of studied WWTP was over 99% and was achieved after secondary treatment. However, despite of the high removal performance, even an advanced WWTP may constitute a considerable source of microlitter and microplastics into the aquatic environment given the large volumes of effluent discharged constantly. The microlitter content of excess sludge, dried sludge and reject water were also examined. According to the balance analyses, approximately 20% of the microlitter removed from the process is recycled back with the reject water, whereas 80% of the microlitter is contained in the dried sludge. The study also looked at easy microlitter sampling protocol with automated composite samplers for possible future monitoring purposes., published version, peerReviewed

During the last few decades the role of citizens in environmental monitoring has changed remarkably in Finland. In this chapter, we briefly describe this change by using examples of both traditional and modern monitoring systems. According to our findings, there are at least four important drivers challenging traditional monitoring systems. First, the monitoring is undergoing a rapid process of globalisation and e.g. the systems that earlier focused on national problems are today controlled by European legislation or influenced by international problems, agreements and practices. Second, public obligations for monitoring have grown much more rapidly than economic resources and it requires the monitoring systems to have a new kind of ability to adapt to changes. Third, the migration of people from rural areas to towns has reduced the potential of a voluntary workforce. The forth driver is the aging of the volunteers. All drivers, without new monitoring strategies, challenge both the performance and geographical coverage of monitoring systems. We expect that a combination of new technologies, such as remote sensing, the Internet of Things and Big Data, can empower new groups of volunteers and increase the social impact and effectiveness of voluntary monitoring to fulfil our national and international obligations.

The report presents results from a study on the role municipal sewage treatment plants (STPs) have as entrance routes for microplastics and other microlitter particles to the marine environment. Mi ...

Two methods for marine microlitter sampling were compared in the Gulf of Finland, northern Baltic Sea: manta trawl (333μm) and a submersible pump (300 or 100μm). Concentrations of microlitter (microplastics, combustion particles, non-synthetic fibres) in the samples collected with both methods and filter sizes remained

The aim of the work was to study the effects of a decaying cyanobacteria bloom on nutrient dynamics, plankton community development and production rates of bacteria and primary producers. It was hypothesised that the system would turn more heterotrophic following the decay of the bloom. A 10-day outdoors mesocosm experiment was performed in early June in a brackish-water environment. Non-toxic filamentous cyanobacteria Aphanizomenon flos-aquae were added to the treatment, whereas the control lacked cyanobacteria. A. flos-aquae decayed rapidly, and was absent from the units by day 2. Significantly higher bacteria abundances, lower nanoflagellate densities and higher ciliate abundances were found, suggesting a bottom-up regulated process in the treatments bags. N:P ratios were low (6–12), suggesting N-limitation. Bacteria correlated negatively with numbers of heterotrophic nanoflagellates (HNF), suggesting grazing on bacteria by HNF. Primary production correlated positively with irradiance, chlorophyll a and inorganic nutrients in all units. The rapidly decaying A. flos-aquae biomass imposed a significant bottom-up regulation in the treatment mesocosms, and the system turned from autotrophic into more heterotrophic with time. The rapid decay also caused some similarities and parallel changes between the treatment and the control.

Dense localized blooms of the toxic dinoflagellate Alexandrium ostenfeldii are a recent phenomenon in the low salinity waters of the Baltic Sea. This study reports results from laboratory experiments investigating the interaction between PSP toxin producing strains of A. ostenfeldii and two copepod species, Eurytemora affinis and Acartia bifilosa, from the northern Baltic Sea. Copepod grazing rates were studied by incubating the copepods with mixed cultures of A. ostenfeldii isolated from a bloom area. The effect of A. ostenfeldii on copepod condition and behavior was studied by exposing copepods to the mixed cultures and cell-free filtrates. Grazing on A. ostenfeldii cells was negligible for both copepod species. The 24 h incapacitation incubations indicated that the condition of both copepod species was negatively affected by the presence of A. ostenfeldii. The behavioral changes observed took place during the first hours of exposure to A. ostenfeldii cells, and little or no change was observed in the condition of the copepods after 6 h compared to 24 h. Similar observations were made for E. affinis incubated in cell-free filtrates of A. ostenfeldii, while the response of A. bifilosa was less pronounced. Our study shows that the copepods do not graze on A. ostenfeldii due to rapid behavioral disturbance and incapacitation by the algal cells and their exudates. This represents the first observation of a negative effect of the A. ostenfeldii on co-occurring biota in the northern Baltic Sea.

Marine litter is one of the problems marine ecosystems face at present, coastal habitats and food webs being the most vulnerable as they are closest to the sources of litter. A range of animals (bivalves, free swimming crustaceans and benthic, deposit-feeding animals), of a coastal community of the northern Baltic Sea were exposed to relatively low concentrations of 10 μm microbeads. The experiment was carried out as a small scale mesocosm study to mimic natural habitat. The beads were ingested by all animals in all experimental concentrations (5, 50 and 250 beads mL− 1). Bivalves (Mytilus trossulus, Macoma balthica) contained significantly higher amounts of beads compared with the other groups. Free-swimming crustaceans ingested more beads compared with the benthic animals that were feeding only on the sediment surface. Ingestion of the beads was concluded to be the result of particle concentration, feeding mode and the encounter rate in a patchy environment.

Jellyfish are effective predators on mesozooplankton and release large amounts of dissolved organic matter. Nevertheless, jellyfish initiated trophic cascades and bottom-up influences impacting lower trophic levels have received limited attention. We conducted a mesocosm experiment to quantify simultaneous top-down and bottom-up effects of a common jellyfish, Cyanea capillata, in a natural plankton community during autumn. Treatments were 0, 2 or 5 jellyfish per 2.5 m3 mesocosm, four replicates each, with initial additions of inorganic nutrients. Primary and bacterial production, species abundance and composition of several trophic levels and nutrient and carbon dynamics were followed during the 8-day experiment. Multivariate statistics and generalized additive mixed modelling were applied to test whether jellyfish carbon concentration (0–1.26 mg jellyC L−1) in the mesocosms affected the variables monitored. Unexpected negligible predatory impact of jellyfish on mesozooplankton was observed, potentially related to jellyfish senescence. Community compositions of bacteria, phytoplankton and mesozooplankton changed with time, but did not differ between treatments. However, nutrient regeneration by jellyfish was evident, and jellyfish had a positive impact on total and specific bacterial production, total primary production and the >10 µm chlorophyll a fraction. Bottom-up influences from abundant jellyfish could thus stimulate productivity in nutrient depleted autumnal surface waters.

Ecosystem-based management (EBM) is promoted as the solution for sustainable use. An ecosystem-wide assessment methodology is therefore required. In this paper, we present an approach to assess the risk to ecosystem components from human activities common to marine and coastal ecosystems. We build on: (i) a linkage framework that describes how human activities can impact the ecosystem through pressures, and (ii) a qualitative expert judgement assessment of impact chains describing the exposure and sensitivity of ecological components to those activities. Using case study examples applied at European regional sea scale, we evaluate the risk of an adverse ecological impact from current human activities to a suite of ecological components and, once impacted, the time required for recovery to pre-impact conditions should those activities subside. Grouping impact chains by sectors, pressure type, or ecological components enabled impact risks and recovery times to be identified, supporting resource managers in their efforts to prioritize threats for management, identify most at-risk components, and generate time frames for ecosystem recovery.

This study deals with a recently found phenomenon in the northern Baltic Sea: the occurrence of the dinoflagellate Dinophysis acuminata in the deep water below the thermocline. This was first observed in July 2001 at the station BY 15 in the Gotland Deep, where a sharp and intensive chlorophyll fluorescence signal was encountered at 77 m depth. The fluorescence peak was due to a dinoflagellate community dominated by Dinophysis acuminata (approximately 18 000 cells l −1 ). The survival of this community was followed in laboratory incubations in low light (20 μE m −2 s −1 ) and low temperature (+5 °C). After 5 weeks incubation, 67–84% of the initial cell abundance was lost, while few D. acuminata cells survived up to 24 weeks in the original sample. During the incubation, the fluorescence signal of the cells became fainter and the chloroplasts smaller and aggregated. On two occasions a D. acuminata cell was found attached to a smaller cell by a thin cytoplasm strand, possibly indicating mixotrophic behavior. During the following summer (2002), the photosynthetic efficiency of D. acuminata collected from thermocline layers of few stations and from the nitracline (75–80 m) at one station was studied in photosynthesis irradiance ( P–E ) incubations. Photosynthetic activity occurred in all populations, with differences in their photosynthetic carbon uptake rates. Photosynthesis of D. acuminata populations was saturated between 250 and 500 μE m −2 s −1 ; maximum cell-specific carbon uptake rates ( P m ) ranged from 160–925 pg C cell −1 h −1 . The P m -rates in populations originating below the thermocline and in an artificially darkened population were markedly lower than in populations from upper water layers. The varying maximum photosynthetic rates of these populations may reflect their history, e.g. time spent in different light environments.

The functional response of a planktonic ciliate, Strombidium sp. feeding on the dinoflagellate Pfiesteria piscicida non-toxic zoospores (NTZ) was experimentally studied with four different prey concentrations (43–3153 cells ml−1). Data from direct observations (NTZ inside individual Strombidium sp.) was used to calculate predator–prey specific ingestion and clearance rates. The ingestion rates varied between 0.68 and 14.26 NTZ ind−1 h−1, and with the predator–prey specific handling time of 2.83 min the Umax was 21.18 NTZ ind−1 h−1. The increase in the prey concentration between approximately 700 and 3000 NTZ ml−1 did not increase the uptake of prey, and at the lowest Pfiesteria NTZ concentrations the feeding efficiency of Strombidium sp. was lowered, possibly indicating a situation of threshold feeding. When data from direct observations of ingested Pfiesteria NTZ were compared with values of total NTZ loss from the experimental water during the experiment, ingestion was found to represent only a fraction of the total NTZ loss in the presence of ciliates. This discrepancy was concluded to be due to other grazer related factors than actual ciliate grazing. The control of the initial growth of Pfiesteria community, in a pre-bloom situation, would require only a small ciliate abundance (less than 5 ml−1), but when the Pfiesteria NTZ are scarce, relatively more ciliates are needed to limit the population growth of the dinoflagellate community because of the apparent feeding threshold. It is concluded that the formation of non-toxic P. piscicida blooms require periods of low grazing pressure or a means to escape grazing.

Samples for studying the ciliate communities of the open Baltic Sea were taken on 2 transects from the Kattegat to the entrance of the Gulf of Finland during 1988 and 1990. The abun- dance of HCIL (heterotrophic ciliates) was highest close to the surface, the maximum values ranging from ca. 7000 (entrance of the Gulf of Finland in 1988) to ca. 20 000 cells l -1 (Arkona Basin in 1990). The dominating HCIL groups were small strobilidiids, strombidiids, or prostomatiids. The photo- autotrophic ciliate Mesodinium rubrum was most abundant in the surface water of Arkona Basin in 1990 (ca. 26 000 cells l -1 ) but was also found at a high concentration in deeper layers during both cruises in daytime (down to 80 m in 1988). Large ciliates dwelling in the oxic/anoxic boundary layer at ca. 100 m depth were found in both years, the highest numbers being ca. 1000 cells l -1 (1988). HCIL community grazing was estimated by using a biovolume-dependent, mostly experimentally derived exponential function. We estimated that in 1988 the ciliate community cleared close to 50% of the water volume per day, whereas in 1990 the highest values reached up to 125% cleared d -1 . In both years, small (≤ 30 µm ESD) ciliates dominated the communities and were also responsible for most of the estimated grazing. Three distinct ciliate associations were revealed from the data of both years by correlation analysis. A deep-water association characterized by large ciliates was found at the oxic/anoxic water interface at the 2 deepest stations, Bornholm and Gotland Basins, in both years, whereas the other associations found were found closer to the surface. Some of these groups may rep- resent true feeding guilds bound together by utilization of same resources, while others could be united by abiotic factors or internal dynamics (e.g. predator-prey relationships) of the association.

The control of silicate, nitrogen and zooplankton was studied with a special emphasis on the planktonic food web on spring bloom on the coastal area of the Baltic Sea in a laboratory experiment. Samples of 150 l of surface seawater were manipulated in transparent plastic laboratory tanks for 3 weeks atin situtemperature (+2 °C) with additions of nitrate and silicate (NO3–N, SiO4–Si), as well as removal of mesozooplankton by filtration through a 100 μ m mesh-sized plankton net. A diatom bloom developed in the experimental tanks within 7 days together with maxima in both picoplanktonic eukaryote and heterotrophic nanoflagellate abundances, during which time inorganic nitrogen and phosphorus were exhausted. Despite the clear response of phytoplankton to the silicate and nitrogen additions, the remainder of the food web was not stimulated by the nutrients. The production and abundance of picoplanktonic algae and bacteria were low and probably controlled by low temperature and bacterial substrates. Maximum growth rates of the organisms varied between 0·1 and 1·2 day−1, being the highest among diatoms and the lowest amongAcartiacopepods. The removal of mesozooplankton through prefiltration enhanced the growth of ciliates with a weak cascading effect through the microbial food web. Most of the biomass and production in the community was concentrated in the net phytoplankton, clearly indicating that in a diatom-dominated spring bloom community in the Baltic sea, only a minor fraction of carbon flow is channelled through the heterotrophic food web. Moreover, increased inputs of silicate and nitrogen to the coastal area before the spring bloom will be channelled to the production of net phytoplankton, therefore not stimulating the heterotrophic food web.

The importance of nitrogen, silicon and grazing for the development of the planktonic spring bloom of the transition area between the Baltic Proper and the Gulf of Finland was studied in a laboratory experiment. Water for this experiment was collected prior to the onset of the spring bloom in early April 1991. At this time, inorganic nutrient concentrations were still at their annual maxim. In the experiment, conducted in plastic tanks, the nitrate level was doubled and silicate level tripled by single and combined additions. One tank was filtered with a 100 μm net to exclude large grazers of phytoplankton. Two unmanipulated controls were used. The tanks were maintained at +2 °C for a 3 week period in 12 h of daylight (60 μE m −2 s −1 ), during which time their nutrient and phytoplankton dynamics were followed. All added inorganic nitrogen was swiftly taken up inducing rapid phytoplankton growth; consequently, available phosphorus must have met the needs of growth. The results showed the limiting nature of nitrogen on the maximum primary productivity and chlorophyll a concentration. Silicate additions affected the structure of the phytoplankton assemblage by promoting specifically the growth of the diatom Chaetoceros holsaticus Schutt, which produced resting spores at later stages of the bloom, while Chaetoceros wighamii Brightwell was the dominant diatom species in other tanks. The absence of large grazers had no effect on phytoplankton dynamics.

Experiments were carried out with different Baltic Sea zooplankton taxa to scan their potential to ingest plastics. Mysid shrimps, copepods, cladocerans, rotifers, polychaete larvae and ciliates were exposed to 10 μm fluorescent polystyrene microspheres. These experiments showed ingestion of microspheres in all taxa studied. The highest percentage of individuals with ingested spheres was found in pelagic polychaete larvae, Marenzelleria spp. Experiments with the copepod Eurytemora affinis and the mysid shrimp Neomysis integer showed egestion of microspheres within 12 h. Food web transfer experiments were done by offering zooplankton labelled with ingested microspheres to mysid shrimps. Microscopy observations of mysid intestine showed the presence of zooplankton prey and microspheres after 3 h incubation. This study shows for the first time the potential of plastic microparticle transfer via planktonic organisms from one trophic level (mesozooplankton) to a higher level (macrozooplankton). The impacts of plastic transfer and possible accumulation in the food web need further investigations.

Increasing biomasses of gelatinous zooplankton presumably have major implications for the structure and function of marine food webs at large; however, current data on lower trophic levels are scarce, as most studies have focused on the immediate effects on zooplankton and fish larvae only. We examined the short-term impact of larvae and adults of the invasive ctenophore Mnemiopsis leidyi on a summer planktonic food web in the estuarine southern Baltic Sea, with special emphasis on the microbial loop. Grazing by M. leidyi reduced the mesozooplankton biomass, followed by increased dinoflagellate biomass in treatments with M. leidyi. While chlorophyll a increased most in the treatments with M. leidyi, small phytoplankton and ciliates decreased in all treatments. M. leidyi had a slight effect on bacterial abundance, but not on bacterial production, ectoenzymatic activities, or community composition. Undetectable levels of phosphate and a gradual accumulation of dissolved organic carbon during the experiment suggested a malfunctioning microbial loop scenario. The experiment shows that direct and indirect short-term effects of M. leidyi on the estuarine food web are limited to higher trophic levels and indicates that top-down and bottom-up consequences of M. leidyi expansions on the microbial loop will likely depend on local nutrient conditions. 2017-07-24