Elucidation and short-term forecasting of microcystin concentrations in Lake Suwa (Japan) by means of artificial neural networks and evolutionary algorithms
Introduction
The shallow eutrophic Lake Suwa is being studied for decades with regards to its distinctive patterns of high abundances of Microcystis species and high concentrations of microcystin during summer (e.g. Harada et al., 2001; Park et al., 1993, Park et al., 1998). In situ measurements of limnological variables of Lake Suwa from 1992 to 2003 provided precious information about complex relationships between water quality, meteorology and Microcystis population dynamics.
Non-supervised artificial neural networks (ANN) have been demonstrated to be useful tools for ordination, clustering and visualisation of complex data such as of water treatment plants, stream and lake habitats (e.g. Hong et al., 2003; Park et al., 2003; Recknagel et al., 2006). Supervised ANN and evolutionary algorithms (EA) have successfully been applied to facilitate early warning of sudden outbreaks of toxic blue-green algae in freshwater lakes and rivers by time-series modelling (e.g. Recknagel et al., 1997, Recknagel et al., 2002; Cao et al., 2006; Jeong et al., 2006). However there is no example yet known for ordination, clustering and forecasting microcystin concentrations in natural water bodies using water quality time-series data.
The present study utilised non-supervised ANN and hybrid EA for unravelling complex ecological relationships in the database of Lake Suwa, and forecasting of microcystin concentrations by means of water quality and meteorological data. The study aimed at following research questions: (i) can non-supervised ANN determine seasonal relationships amongst water quality data, Microcystis species and microcystin concentrations with regards to rainfall patterns, (ii) can hybrid EA forecast 3-days ahead the timing and magnitudes of extra-cellular microcystin concentrations, and (iii) can hybrid EA discover rule sets to describe conditions for microcystin occurrence in Lake Suwa.
Section snippets
Study site and data
The study site of this research was Lake Suwa located in central Japan. Lake Suwa is a shallow, hypertrophic lake with occasional weak thermal stratification in summer between April and October and frequent ice cover in winter between December and February. Lake Suwa is mainly used for recreational activities, but a small proportion of lake water is also used for aquaculture, irrigation and industrial purposes (Park et al., 1998).
Microcystis blooms in Lake Suwa have been reported every summer
Ordination and clustering of water quality data by non-supervised ANN
The ordination and clustering of water quality data of Lake Suwa by means of non-supervised ANN has been conducted according to Fig. 1, Fig. 2 distinguishing between typical dry years (1992 and 1994) and wet years (1999 and 2000).
Results in Fig. 4 indicate distinctive differences both in magnitudes as well as seasonal occurrences of Microcystis abundances between dry and wet years. Whilst maximum cell numbers peak in the dry years at 515,000 cells/mL in autumn (September and October), they peak
Ordination and clustering
Non-supervised ANN have unravelled complex relationships between Microcystis species and microcystin concentrations for different seasons and rainfall intensities. The big differences in the abundance of Microcystis and therefore microcystin concentration between typical dry and typical wet years seem to reflect the impact of the Asian monsoon in summer. As reported by Ahn and Jones (2000) extreme cyanobacterial blooms are unlikely to develop in Korean freshwaters during summers with intense
Conclusions
Non-supervised ANN successfully revealed the seasonal succession of Microcystis species and microcystin dynamics in relation to different rainfall and environmental conditions of Lake Suwa. Hybrid EA assembled rule sets that proved to be valid for both prediction and explanation of microcystin dynamics. Outcomes of this research can facilitate early warning of high microcystin concentrations in Lake Suwa.
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