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(A) Map showing location of the Belcher Islands in southeastern Hudson Bay, Nunavut, Canada. (B) Air photograph showing the hamlet of Sanikiluaq and the locations of Annak and Imitavik lakes. Air photograph reproduced under license from Her Majesty the Queen in Right of Canada, with permission of Natural Resources Canada. 

(A) Map showing location of the Belcher Islands in southeastern Hudson Bay, Nunavut, Canada. (B) Air photograph showing the hamlet of Sanikiluaq and the locations of Annak and Imitavik lakes. Air photograph reproduced under license from Her Majesty the Queen in Right of Canada, with permission of Natural Resources Canada. 

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Many Arctic communities use lakes as a cost effective method for facultative treatment and disposal of sewage and other liquid wastes. These sites represent ideal locations to study eutrophication processes in Arctic regions, where very little is known about accelerated nutrient fertilization, despite increasing threats from growing populations and...

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... Hermanson (1991,1998) and Herman- son and Brozowski (2005) studied the geochemical and pollution history of Annak Lake (Fig. 1), a culturally eutrophied lake located on the Belcher Islands (Nunavut, Arctic Canada). This lake is an ideal location to study Arctic eutrophication processes because the nearby hamlet of Sanikiluaq has used it for open water season facultative treatment of domes- tic waste since about 1968. Predictably, the lake is currently ...
Context 2
... Lake is located near the hamlet of Sanikiluaq (568 53N, 798 27W) on northern Flaherty Island, the largest of the Belcher Islands, in southeastern Hudson Bay, Nunavut (Figs. 1A, B). The lake is small (surface area = 2 ha) and moderately shallow (Z mean = 1.9 m, Z max = 4.5 m) with a single basin. It has no appreciable input streams other than runoff from its 44.3 ha drainage basin. Based on precipitation data (0.477 m yr -1 ; average measured at Kuujjuaraapik, Quebec, 1981-1990), we estimate the flushing rate of ...
Context 3
... recording thermometer, and an eight-inch diameter Secchi disc. Dissolved oxygen concentra- tions were performed using the Winkler titration method. For comparison purposes, the same variables were also recorded from nearby Imitavik Lake (August data only), a relatively pristine lake that is used as the source for the municipal water supply (Fig. ...
Context 4
... is unlikely that forcing mechanisms other than the sewage inputs could be responsible for the observed changes in Annak Lake. For example, although no long-term climate data exists for Saniki- luaq, temperature records from nearby Kuujjuaraapik (Fig. 1A) show no warming trend over the timeframe of interest (http://www.climate.weatheroffice.ec.gc.- ca/). Catchment disturbances have been minimal, with the only activity being the development of a road that Aquat. Sci. Vol. 69, 2007 Research Article allows the sewage truck direct access to the lake (Fig. 6B). The diatoms were also not ...

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... There are notable, albeit rare taxa with high nutrient optima, which are consistent with biotic nutrient introductions, such as Fistulifera saprophila in D012, A135, and A085 ( Figure 4). This taxon was found in Resolute sewage ponds (Stewart et al., 2014) and Annak Lake on Belcher Islands, also with high nutrient concentrations from sewage inputs (Michelutti et al., 2007). ...
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... Another example is Annak Lake [13][14][15][16][17], a lake also used for sewage discharge since the 1960s by the community at Sanikiluaq situated on the Belcher Islands (Nunavut). It has a well dated 210 Pb profile, that is further constrained by stable geochemical metals and other proxies linked to human sewage in the core profile, anchoring and corroborating the 210 Pb dates (as described in the cited papers). ...
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... Another example is Annak Lake [13][14][15][16][17], a lake also used for sewage discharge since the 1960s by the community at Sanikiluaq situated on the Belcher Islands (Nunavut). It has a well dated 210 Pb profile, that is further constrained by stable geochemical metals and other proxies linked to human sewage in the core profile, anchoring and corroborating the 210 Pb dates (as described in the cited papers). ...
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... Bottom-up increases in chl a and decreases in hypolimnetic oxygen were more rapid than the response of higher trophic levels, as expected, but there was some resistance to change even in DO and chl a, which had time lags of one to several years. Resistance to disturbance from anthropogenic or experimental nutrient inputs to arctic lakes can be very low (i.e., an immediate response; Schindler 1974;Lienesch et al. 2005;O'Brien et al. 2005) or moderate, with response lags of two to many years (Welch et al. 1989;Michelutti et al. 2007;Stewart et al. 2018). The cause of such muted responses is thought to be related to the extreme environment and long ice cover in arctic lakes (Douglas and Smol 2000;Stewart et al. 2018), although we note here that the strength of nutrient addition is also likely important. ...
... The cause of such muted responses is thought to be related to the extreme environment and long ice cover in arctic lakes (Douglas and Smol 2000;Stewart et al. 2018), although we note here that the strength of nutrient addition is also likely important. For example, low resistance occurs with strong, experimental, or anthropogenic additions (Schindler 1974;O'Brien et al. 2005;Lienesch et al. 2005), while moderate resistance is observed with lower-level fertilization (this study; Welch et al. 1989;Michelutti et al. 2007;Stewart et al. 2018). ...
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... Eutrophication of Arctic lakes is not a novel problem: in fact, there are several examples of nutrient enrichment as a result of sewage inputs and municipal wastes (Schindler et al., 1974;Michelutti et al., 2007;Stewart et al., 2014), including Niven Lake from Yellowknife (Stewart et al., 2018). In the past, however, biological responses to eutrophication were somewhat mitigated by the cold climatic conditions (Douglas and Smol, 2000;Michelutti et al., 2007;Antonaides et al., 2011) and nuisance cyanobacterial blooms, a common repercussion of nutrient enrichment in temperate and tropical regions, were not previously reported (Schindler et al., 1974). ...
... Eutrophication of Arctic lakes is not a novel problem: in fact, there are several examples of nutrient enrichment as a result of sewage inputs and municipal wastes (Schindler et al., 1974;Michelutti et al., 2007;Stewart et al., 2014), including Niven Lake from Yellowknife (Stewart et al., 2018). In the past, however, biological responses to eutrophication were somewhat mitigated by the cold climatic conditions (Douglas and Smol, 2000;Michelutti et al., 2007;Antonaides et al., 2011) and nuisance cyanobacterial blooms, a common repercussion of nutrient enrichment in temperate and tropical regions, were not previously reported (Schindler et al., 1974). Hence, the recent blooms of Planktothrix spp. at Jackfish Lake can be considered a novel response to the combined effects of eutrophication and climatic changes within the context of northern lakes. ...
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... Most Fistulifera species have lightly silicified frustules with inconspicuous margins and few features discernible using light microscopy (LM). Though small, their global range is broad and includes the Arctic (Michelutti et al. 2007), temperate (Gevrey et al. 2004, Vouilloud et al. 2005, and subtropical (this study, Hustedt 1962) regions. Within these regions, Fistulifera has wide ecological occurrence, inhabiting fresh (Lewin 1955, Stancheva et al. 2007), brackish (Bella et al. 2007), saline and marine (Hustedt 1962, Matsumoto et al. 2014) waters, and terrestrial environments (see Navicula JB12 Genbank #KF791556; Qiao & Liu, unpub.). ...
... Within these regions, Fistulifera has wide ecological occurrence, inhabiting fresh (Lewin 1955, Stancheva et al. 2007), brackish (Bella et al. 2007), saline and marine (Hustedt 1962, Matsumoto et al. 2014) waters, and terrestrial environments (see Navicula JB12 Genbank #KF791556; Qiao & Liu, unpub.). Furthermore, the genus is found in a spectrum of trophic states including oligotrophic, eutrophic, and even hypereutrophic (Krammer & Lange-Bertalot 1986, Michelutti et al. 2007). ...
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... values between~15 cm and the top of the sediment core may indicate dilution of 210 Pb unsupp. by increased sedimentation of organic material caused by eutrophication and increased production (e.g., Michelutti et al., 2007). This is supported by enhanced sedimentary contents of TN and TC, respectively, and enriched δ 15 N signals in these sediment layers. ...
... Overall, environmental stressors played a limited role in structuring the diatom community of Lake Yuxian, possibly due to that the dominance of generalist diatoms exhibited a high degree of tolerance and resilience capacity in this nutrient-poor lake (cf. Michelutti et al., 2007). ...
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... Also the increase in A. minutissimum has been related to climate warming in several Arctic records (Antoniades et al. 2004;Keatley et al. 2006;Lim et al. 2008;Paul et al. 2010), but it is also found in mossy habitats (Griffiths et al. 2017) suggesting that the lake-catchment area has become more productive. The recent increase in Nitzschia spp. is also likely related to increase in nutrients, as previously recorded from the Canadian Arctic (Michelutti et al. 2007). In all, the recent changes in diatom assemblages are likely related directly (e.g. ...
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Benthic diatoms are commonly used for palaeoenvironmental reconstruction in Arctic regions, but interpretation of their ecology remains challenging. We studied epilithic diatom assemblages from the shallow margins of 19 lakes from three areas (coast-inland-ice sheet margin) along a climate gradient in Kangerlussuaq, West Greenland during two periods; shortly after ice-off (spring) and in the middle of the growth season (summer). We aimed to understand the distribution of Arctic epilithic diatoms in relation to water chemistry gradients during the two seasons, to investigate their incorporation into lake sediments and to assess their applicability as palaeoenvironmental indicators. Diatoms were correlated with nutrients in the spring and alkalinity/major ions in the summer, when nutrients were depleted; approximately half of the variance explained was independent of spatial factors. When categorised by functional attributes, diatom seasonal succession differed among regions with the most obvious changes in inland lakes where summer temperatures are warmer, organic nutrient processing is prevalent and silicate is limiting. These conditions led to small, motile and adnate diatoms being abundant in inland lakes during the summer (Nitzschia spp., Encyonopsis microcephala), as these functional attributes are suited to living within complex mats of non-siliceous microbial biofilms. Seasonal succession in silica-rich lakes at the coast was less pronounced and assemblages included Tabellaria flocculosa (indicating more acidic conditions) and Hannaea arcus (indicating input from inflowing rivers). The nitrogen-fixing diatom Epithemia sorex increased from the coast to the ice sheet, negatively correlating with a gradient of reactive nitrogen. The presence of this diatom in Holocene sediment records alongside cyanobacterial carotenoids during arid periods of low nitrogen delivery, suggests that it is a useful indicator of nitrogen limitation. Nitzschia species appear to be associated with high concentrations of organic carbon and heterotrophy, but their poor representation in West Greenland lake sediments due to taphonomic processes limits their palaeoenvironmental application in this region. Proportions of epilithic taxa in lake sediment records of coastal lakes increased during some wetter periods of the Holocene, suggesting that snowpack-derived nutrient delivery may offer diatom taxa living at lake margins a competitive advantage over planktonic diatoms during the “moating” ice melt period. Thus, further research investigating linkages between epilithic diatoms, snowpack and nutrient delivery in seasonally frozen lakes is recommended as these taxa live on the ‘front-line’ during the spring and may be especially sensitive to changes in snowmelt conditions.