Core Indicator |
Metrics |
Status |
Trends |
Estuarine Waters |
| Hypoxia |
Dissolved oxygen levels |
Interannual variability due to weather and tides; follows N/S gradient; most severe in Providence-Seekonk River and Greenwich Bay; documented for Upper Bay and some embayments. |
Ten years of data in Upper Bay and embayments; severity dependant on weather, tides and river flow. |
| Chlorophyll |
Chlorophyll and macroalgae |
Used as indicator of primary productivity. Highest levels in upper bay; also high in Greenwich Bay/Lower Taunton River. |
Annual bloom has shifted from winter/spring to summer in mid/lower Bay. |
| Beach Closures |
Enterococci |
Dependent on rainfall levels and local stormwater impacts. |
Closures tend to follow rain events; closures affected by local conditions and stormwater runoff. |
| Shellfish Restrictions & Closures |
Fecal coliform bacteria |
Reflects N/S gradient and local stormwater impacts; affected by weather/rainfall; operational changes allow some conditional openings. |
Closure rates predicted to decrease as CSO abatement projects come online. |
Fresh Waters |
| Fresh Waters Impaired by Bacteria |
Enterococci and fecal coliform bacteria |
Not all waters assessed. Of those assessed, 40% RI river miles and 52% MA river miles impaired; 4% RI lake acres and 0.2% MA lake acres impaired. |
Dependent on rainfall and wildlife populations. |
| Fresh Waters Impaired by Dissolved Oxygen |
Dissolved oxygen levels |
Not all waters assessed. Of those assessed, 5% RI river miles and 57% MA river miles impaired; 10% RI lake acres and 5% MA lake acres impaired. |
Affected by nonpoint source inputs and, on major rivers, by point sources; varies by location; temperature; physical conditions. |
| Fresh Waters Impaired by Nutrients |
Nirogen and phosphorus |
Not all waters assessed. Of those assessed, 4% RI river miles and 25% MA river miles impaired; 15% RI lake acres and 6% MA lake acres impaired. Neither state has numeric standards for nutrients in rivers. |
Affected by nonpoint source inputs; varies by location; temperature; physical conditions. |
| Chloride in Lakes |
Chloride (RI lakes data since 1988; not available for MA lakes) |
No RI lakes violate criteria. |
Concentrations in RI lakes increasing since 1993. |
| Low Flow |
Water levels; changes in riverine fish communities |
Several RI rivers exhibit extreme low flow conditions; some impacts to fish populations documented; affected by user demand/drought conditions; MA fisheries staff observed no flow conditions in sime Dighton brooks. |
Existing data limited for many waters; large river stream gauge data show summer flow declines over time; Aug. flows in one Blackstone river basin declined 55% since 1979. |