Spatial, temporal and experimental: Three study design cornerstones for establishing defensible numeric criteria in freshwater ecosystems

摘要

Abstract Nutrient over‐enrichment increasingly threatens global water resources. Stressor‐response studies specifically designed to identify levels of nutrients strongly associated with undesirable ecological conditions are needed to inform numeric nutrient criteria that protect inland waters. Diatoms are important components of aquatic life, which support higher trophic levels and are sensitive to nutrient enrichment. We tested a framework that relies on stressor‐response modelling of phosphorus (P) enrichment and stream diatom assemblages across many field locations, multiple years and seasons within years, and under controlled experimental conditions to inform nutrient criteria development. Diatom species composition was nonlinearly correlated with total phosphorus (TP) throughout the 2‐year field study. This occurred despite temporal shifts in species composition between two hydrologically distinct years and over eight seasons. Species assemblages on rocks transplanted from a low P stream to mesocosms representing a P enrichment gradient (8, 20 and 100?μg/L) shifted into two groups over time. Species composition on rocks in low (20?μg/L) and high (100?μg/L) P mesocosms was consistent with assemblages at P‐enriched field sites, whereas rocks in control (8?μg/L) mesocosms had significantly different species composition, consistent with low P field sites. Species composition on rocks transplanted from high P streams did not shift as dramatically and were not significantly different after exposure to different P treatments in mesocosms. Threshold Indicator Taxa Analysis identified syn