Elevated levels of E. coli bacteria, nitrate-nitrite-nitrogen, total nitrogen and total suspended solids have been identified as the primary water quality issues within the Waitepuia catchment.
These elevated levels of contaminants move into the sensitive receiving environment of the Te Awa o Ngatoroirangi/ Maketū Estuary and may result in unsafe conditions for recreational contact, and impact estuarine health and freshwater wildlife.
Water quality in the Maketū Estuary has already been impacted adversely due to elevated nutrient levels nitrogen (N) and phosphorus (P) and bacterial levels (E.coli) (Park, unpublished (a) and (b)).
Bay of Plenty Regional Council scientists have estimated that to restore the estuary to moderate ecological health, improve safety for shellfish gathering and contact recreation, contaminants will need to be substantially reduced across the catchments that supply water to the estuary.
Past monitoring summary
Surface water quality monitoring
Water quality monitoring was carried out at six sites in the Waitepuia sub-catchment in November 2016 and 2017 as part of a general survey which covered 112 sites in the Kaituna Water Management Area (WMA). This one-off sampling indicated elevated total nitrogen and E. coli bacteria across the sub-catchment, and some isolated occurrences of elevated total suspended solids and total phosphorus. The results from these one-off samples resulted in Bay of Plenty Regional Council (BOPRC) prioritising incentive based funding through its focus catchment programme.
Ecology monitoring
Ecological information for the Waitepuia catchment consists of habitat and fish surveys. These are restricted to the lower parts of the catchment to date. Habitat assessments during the synoptic survey in November 2016 and 2017 indicated poor habitat quality (Carter, Davis & Suren, unpublished). Various fish surveys have been undertaken in the Waitepuia catchment between 1999 and 2016 (NIWA, 2020). Fish Index of Biotic Integrity (IBI), scores range from ‘poor’ to ‘excellent’.
The surveys also identify the presence of diadromous native fish species (shortfin eel, inanga, common bully, banded kōkopu, Galaxias sp., giant bully and redfin bully) as well as the introduced Gambusia sp. (NIWA, 2020). This indicates that these watercourses could be used as a migration pathway for diadromous fish to upper catchments, provided fish passage barriers (physical or chemical) were not an issue.