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Spatial distribution and seasonal variation in Undaria pinnatifida ...

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4.1.4. Other Invasive SpeciesOther <strong>in</strong>vasive species recorded dur<strong>in</strong>g coastal surveys are shown <strong>in</strong> Appendix 2. The <strong>in</strong>vasive tunicate Styela Clava wasrecorded at ten of the twenty six coastal sites surveyed. The <strong>in</strong>vasive alga Codium fragile ssp. tomentosoides wasrecorded at two coastal sites <strong>and</strong> the Asian paddle crab Charybdis japonica was also seen two coastal sites. Results for<strong>in</strong>vasive species recorded on mussel farms are shown <strong>in</strong> Appendix 3A. All the mussel farms surveyed had Styela Clavagrow<strong>in</strong>g on the l<strong>in</strong>es <strong>and</strong>/or <strong>in</strong>frastructure. Twenty eight of the thirty one mussel farms surveyed had Codium fragile ssp.tomentosoides present. Styela Clava <strong>and</strong> Codium fragile ssp. tomentosoides were abundant on the moor<strong>in</strong>g l<strong>in</strong>es atTakawhare Bay. Styela Clava, Codium fragile ssp. tomentosoides <strong>and</strong> Charybdis japonica were recorded at the Waikawauboat ramp site <strong>and</strong> at Kirita Bay.4.1.5. Environmental DataSite environmental <strong>in</strong>formation for the spatial survey is shown <strong>in</strong> Appendix 3B. Dur<strong>in</strong>g this survey average sal<strong>in</strong>ityrecorded at mussel farm sites was 34.7 ppt with a range of only two parts per thous<strong>and</strong> recorded across all sites,maximum 35.5 ppt, <strong>and</strong> m<strong>in</strong>imum 33.5 ppt. The average temperature recorded over the survey was 18.7ºC with am<strong>in</strong>imum of 16ºC <strong>and</strong> a maximum of 20.6ºC. Temperatures were measured at different times of day <strong>and</strong> <strong>in</strong> vary<strong>in</strong>gweather conditions so cannot be directly compared between sites. Secchi depths are shown (from northern (left), tosouthern (right) locations) <strong>in</strong> Figure 9. Sites had an average secchi depth of 5.9m across all mussel farm sites with amaximum of 8.5 recorded at Wilson Bay <strong>and</strong> a m<strong>in</strong>imum of 4m at Koputauaki Bay.Figure 9: Secchi depths: <strong>Spatial</strong> survey locationsSeawater nutrient data is shown <strong>in</strong> Figure 10. Very high ammonia read<strong>in</strong>gs seen at Port Charles, Motorua Isl<strong>and</strong>,Koputauaki Bay, Motukopaki Isl<strong>and</strong>, Motukakarikitahi Isl<strong>and</strong> <strong>and</strong> Whanganui Isl<strong>and</strong> were all samples taken <strong>in</strong> November.Differences <strong>in</strong> ammonia levels at the same site can be seen for Port Charles, Motukopaki East <strong>and</strong> Kirita Bay as they wereeach visited <strong>in</strong> November, visit 1 <strong>and</strong> February, visit 2. Nitrite <strong>and</strong> nitrate were relatively variable among sites, with thehighest concentrations recorded <strong>in</strong> Port Charles <strong>and</strong> Manaia Harbour, as well as at one site at Motukopake Isl<strong>and</strong>.Nitrogen concentrations were typically low at the Wilson Bay farm sites. Phosphate occurred at relatively constantconcentrations among sites <strong>and</strong> times. For details on sampl<strong>in</strong>g dates <strong>and</strong> sites see Appendix 3B.16

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