DRIFT DIVE SURVEY REPORT 2015 A summary of drift dives conducted by Fish & Game West Coast Region in the spring and summer of 2014/2015 Rhys Adams, Fish & Game Officer, March 2015 _____________________________________________________________________________________________ Drift Dive Survey Report 2015 Page 1 of 10 DRIFT DIVE SURVEYS REPORT 2015 A summary of drift dives conducted by Fish & Game West Coast in the spring and summer of 2014/2015. Rhys Adams, Fish & Game Officer, March 2015. Summary Drift dives have been conducted in the West Coast Fish & Game Region since 1985. The purpose of these surveys is to give an indication of trout abundance in a particular stretch of river. Where dives have occurred in past years, comparisons can be made. The data and findings of the surveys are intended for internal management purposes only. The spring dives were conducted in December 2014 and the summer dives in February 2015 incorporating Fish & Game staff from the Nelson Marlborough Region, North Canterbury Fish & Game and the West Coast Regional Council. The Mawheraiti River at SH7 Bridge and Mirfins Bridge, the Grey River at Waipuna and Hospital Flat, and the Inangahua River at Blacks Point were dived. Small fish have increase in abundance at all sites except for the Grey River at Hospital Flat. The only consistent and distinct seasonal change in abundance observed in the seasonal dives in the Mawheraiti River is an increase in small fish from spring to summer at the Mirfins Bridge site. Staff recommendations are; Continuation of drift dive programme as a tool for gathering long term data on West Coast trout abundance and continue to assist other neighbouring regions with their drift dive programmes on a reciprocal basis. Introduction Drift diving is now a commonly used method of monitoring trout abundance in clear, small to medium sized rivers throughout the country. The West Coast Fish & Game Region’ database of drift-dive results date back to 1985 when MAF conducted a series of dives for their “100 Rivers” survey. Since then, Fish & Game staff have undertaken up to 10 dives per year if river conditions have been favourable. There is now a large West Coast data set that enables comparison at sites where multiple years have been dived. The data provides a ‘spot’ count of trout abundance on a particular stretch of a river. The West Coast Region performs dives in relation to specific threats or management information needs and sites are not randomised. Therefore, results in this report should not be used to describe catchment level or regional level observations. The Data and findings of the surveys are intended for internal management purposes only. _____________________________________________________________________________________________ Drift Dive Survey Report 2015 Page 2 of 10 Method The method involves a number of snorkelled divers drifting downstream, maintaining a line across the river and counting trout that pass under or between them on one side. Trout are divided into three size groups; Large: Trout over 450mm in length. Medium:Trout less than 450mm and greater than 150mm in length. Small: Trout less than 150mm in length. Fish numbers are recorded by each diver, with the team leader collecting the information from each diver periodically throughout the dive and/or on completion. The Majority of West Coast Rivers are dived specifically for brown trout (Salmo trutta) and unless specifically stated, brown trout are the species referred to as ‘trout’ or ‘fish’ in this report. Dive sites are between 1 and 3 Km in length. This distance is considered the longest possible to avoid fatigue whilst being long enough to give an estimate of the actual population for that stretch of river. Water clarity is measured at the beginning of each dive with a 200mm black disc and tape measured horizontally through the water column. Good water clarity is required for an accurate count therefore diving is not generally undertaken if the visibility is less than 4m. More divers are required if water clarity is low to ensure adequate coverage. The Mawheraiti River was selected to dive due to observations that trout abundance has been notably low in recent years. Two dives were performed, spring and summer to assess if there is seasonal fluctuation in trout abundance as part of 2014/15 workplan project 1115 sports fishery research. The Inangahua River was dived in response to the potential of mining discharge in the catchment to affect the fishery and the application for two hydro power schemes in the catchment. The Grey River at Hospital Flat was dived to monitor the state of a highly valued section of river near the Grey River Water Conservation Order that has a perceived high angler usage. The Grey River at Waipuna is dived to monitor the middle reaches of one of the West Coast most fished West Coast River catchments (Unwin, 2009). Staff from the West Coast Regional Council, North Canterbury Fish & Game, and Nelson Marlborough Fish & Game Region assisted with dives. Staff provided their time on a reciprocal basis and this ensures diver numbers are adequate. Two seasonal dives were undertaken in the Mawheraiti River in; ‘spring’ on the 16th of December. Summer dives were completed on the 19th & 20th of February, 2015. Unless stated, historic dives were undertaken in summer during the months of January or February. Results _____________________________________________________________________________________________ Drift Dive Survey Report 2015 Page 3 of 10 Mawheraiti River: (Mirfins Bridge site) The Mawheraiti River at the Mirfins Bridge site has been dived on seven occasions within three successive sports fishing seasons. The dives are seasonal with November and December relating to spring, January or February relating to summer and May relating to autumn. The data is presented in the table 1 below. Three years of spring and summer comparisons can be made. The only consistent change in trout abundance seasonally at this site is the increase of small trout from spring to summer. This change is distinct. Seasonal changes for medium and large fish are inconsistent. Table 1.Mirfins Bridge dive site data Large/km Med/km Small/km 2012 (Nov) 7 10 1 2013 (Jan) 11 38 27 2013 (May) 9 17 1 2013 (Nov) 7 15 4 2014 (Feb) 2 2 22 2014 (Dec) 15 25 12 2015 (Feb) 10 21 102 Average 9 22 24 combined 19 76 27 26 26 52 133 54 Mawheraiti River: (SH7 Bridge site) The Mawheraiti River at the SH7 Bridge was dived in spring (December 2014) and summer (February 2015). The spring dive counts were; 8 small/km, 18 medium/km, and 8 large/km. The summer counts were; 54 small/km, 21 medium/km, and 14 large/km (see Chart 1). When comparing spring dives between 2014 and 2015 medium size fish increased in abundance, but small and large fish counts were similar. Compared to summer 2014 the summer dive for 2015 revealed an increased in counts of all fish sizes, most notably small fish. All counts for summer 2015 are below the summer average but are a notable increase on record low combined counts of summer 2014. Seasonal comparisons of abundance can be made between four spring and summer dives. The only consistent change in seasonal abundance between spring and summer is an increase in the count of large trout. The changes are not distinct due to the low numbers of fish counted. For medium trout, seasonal changes in abundance are inconsistent. Three of four comparisons show a slight decrease in abundance from spring to summer. The numbers counted are low so the changes are not distinct. For small trout, changes in abundance are also inconsistent with three out of four comparisons showing an increase in abundance from spring to summer. _____________________________________________________________________________________________ Drift Dive Survey Report 2015 Page 4 of 10 Grey River: (Waipuna site) The 2015 Grey River dives at Waipuna counted 145 small/km, 54 medium/km and 14 large/km. Small fish counts have increased from 2014 levels and are well above average. Medium fish counts have increased from 2014 levels and are only slightly below average. Large fish counts have decreased and sit slightly below average (see Chart 2). _____________________________________________________________________________________________ Drift Dive Survey Report 2015 Page 5 of 10 Grey River: (Hospital Flat site) The 2015 dives at Hospital Flat reveal 8 small/km, 4 medium/km 20 large/km. Small and medium fish are at relatively low levels of abundances, however large trout abundance is above average compared to all ten years dived on this section of river. The counts of small and medium trout are similar to 2014 however counts for large trout have increased (see Chart 3). Inangahua River: (Blacks Point site) The 2015 dives at Blacks Point reveal counts of 170 small/km and 19 medium/km. Small and medium trout abundance has increase from record lows of 2014. Although the increase in medium trout is evident, 2015 counts are below average. Counts of small have increased substantially from 2014 counts but are still below average. The large fish count of 7/km is a decreased from 2014 levels but is at levels consistent with several other years (see Chart 4). _____________________________________________________________________________________________ Drift Dive Survey Report 2015 Page 6 of 10 Discussion With the exception of the Grey River at Hospital Flat small fish counts increased from 2014 levels and in some cases by a substantial amount. This is likely to be a reflection of successful spawning seasons in 2013 and 2014 as small fish are considered to be approximately 6 or 18 months of age during the summer dives. Of particular note is that small fish at the Grey River Waipuna site are well above average abundance. When considering all trout sizes as a combined trout count, the summer combined counts at all sites increased from 2014 levels. The combined summer count for 2015 at the Mawheraiti SH7 site is the highest count since 2011 when the fishery declined. The main contributor to the increase is small fish which suggest an improvement in spawning success from previous years in the catchment. The counts are still below average and far from the highest counts. Seasonal dives have been undertaken at the Mawheraiti SH7 Bridge site on four consecutive years, and at the Mirfins bridge site on three consecutive years. From the two sites the only consistent and distinct change in seasonal abundance is that small fish increase in abundance from spring to summer at the Mirfins Bridge site. The only other consistent change is large fish increase in numbers from spring to summer at the SH7 site. The counts of fish are low however, being well below summer averages, and the changes are not distinct. Therefore, further dive data would be necessary in years’ of higher large fish abundance to draw conclusions that the observed changes describes a pattern of changes in seasonal abundance in that particular stretch of river. _____________________________________________________________________________________________ Drift Dive Survey Report 2015 Page 7 of 10 Since 1985, when the MAF initiated the drift diving data set on the West Coast it is evident that trout populations fluctuate in abundance over the years. Climatic conditions are considered to play a major role in governing salmoniid abundance levels in West Coast Rivers (Kelly, 2009). It is reasoned that if large flood events occur more frequently trout abundance will be low. Large Floods have the potential to significantly affect the abundance of trout. Two notable ways a flood can affect abundance is; mortality from physical damage during high flow periods and destruction of spawning redds. These factors combined have the potential to decrease small fish abundance especially in spring during the emergence/ alevin lifecycle stage (Jensen & Johnson, 2002). Large and Medium trout populations have been shown to be negatively affected by large flood events in the Motueka River. Food abundance, water temperatures and low flows may also have an effect on adult trout abundance in the Motueka River (Young et al, unpublished). Staff Recommendations Continuation of the drift dive programme as a tool for gathering long term data on West Coast trout abundance. Continue to assist with neighbouring regions drift dive programmes on a reciprocal basis. That council receives the report. References Jenson A.J. & Johnson B.O. (2002). The functional relationship between peak spring floods and survival and growth of juvenile Atlantic Salmon (Salmo salar) and Brown Trout (Salmo trutta). Functional Ecology 13, 778-785. Unwin, M.J. (2009). Angler usage of lake and river fisheries managed by Fish & Game New Zealand: results from the 2007/08 National Angling Survey. Kelly, D (2009). Drift Dive Surveys. Fish & Game internal report. Young, R.G. et al. Unpublished Cawthron Institute report. Factors controlling adult trout abundance in the Motueka River over 20 years. _____________________________________________________________________________________________ Drift Dive Survey Report 2015 Page 8 of 10 Appendix – Raw data from 2014/2015 reported drift dive sites. RIVER LOCALITY Date GRID REF DIST WIDTH Grey R Hospital Flat 1998 2 20 Grey R Hospital Flat 2 20 Grey R Hospital Flat 2 Grey R Hospital Flat Grey R Hospital Flat Grey R Hospital Flat Grey R Hospital Flat 16/02/2012 Grey R Hospital Flat 30/01/2013 Grey R Hospital Flat 10/02/2014 Grey R Hospital Flat 19/02/2015 320/621-308/614 2431119/5861497 2429994/5860486 2431119/5861497 2429994/5860486 2431119/5861497 2429994/5860486 2431119/5861497 2429994/5860486 2431119/5861497 2429994/5860486 2431119/5861497 2429994/5860487 2431119/5861497 2429994/5860488 2431119/5861497 2429994/5860489 2431119/5861497 2429994/5860489 Grey R Waipuna 1994 Grey R Waipuna 1995 Grey R Waipuna Grey R Waipuna Grey R Waipuna Grey R Waipuna Grey R Waipuna Grey R Waipuna 15/02/2012 Grey R Waipuna 31/01/2013 Grey R Waipuna 11/02/2014 Grey R Waipuna Inangahua R Inangahua R B. Disk L M S TOTAL 10 5 4 19 6.2 34 14 21 69 20 8.4 30 32 89 151 2 20 9.5 45 25 64 134 2 20 9 56 34 155 245 2 20 4.3 46 25 127 198 2 20 11 28 6 3 37 2 20 10.6 30 10 31 71 2 20 12.8 26 6 16 48 2 20 10.8 40 8 17 65 085/735-064/748 3 40 55 557 140 752 085/735-064/748 3 40 39 129 21 189 1996 085/735-064/748 3 40 43 154 92 289 2005 3 40 6.7 20 239 185 444 3 40 7.8 51 238 604 893 3 40 7.3 24 101 65 190 3 40 8.1 31 89 181 301 3 40 10.3 65 89 190 344 3 40 9.1 38 67 56 161 3 40 8 52 44 175 271 20/02/2015 085/735-064/748 2408562/5873429 2406221/5874826 2408562/5873429 2406221/5874826 2408562/5873429 2406221/5874826 2408562/5873429 2406221/5874827 2408562/5873429 2406221/5874828 2408562/5873429 2406221/5874829 2408562/5873429 2406221/5874829 3 40 14 41 161 434 636 Blacks Point 1991 179/962-176/973 1.7 18 7 283 174 464 Blacks Point 1992 179/962-176/973 1.7 18 7 287 774 1068 Inangahua R Blacks Point 1993 179/962-176/973 1.7 18 11 145 674 830 Inangahua R Blacks Point 1994 179/962-176/973 1.7 18 9 127 452 588 Inangahua R Blacks Point 1995 179/962-176/973 1.7 18 25 293 339 657 Inangahua R Blacks Point 1996 179/962-176/973 1.7 18 10 204 396 610 Inangahua R Blacks Point 1997 179/962-176/973 1.7 18 72 392 356 820 Inangahua R Blacks Point 2001 179/962-176/973 1.7 18 4.5 15 93 264 372 Inangahua R Blacks Point 2003 179/962-176/973 1.7 18 6 33 198 683 914 Inangahua R Blacks Point 2004 179/962-176/973 1.7 18 5 26 335 1021 1382 Inangahua R Blacks Point 2005 179/962-176/973 1.7 18 3.5 16 250 623 889 Inangahua R Blacks Point 16/02/2012 179/962-176/974 1.7 18 5.8 13 83 205 301 Inangahua R Blacks Point 30/01/2013 179/962-176/975 1.7 18 7.6 10 77 243 330 Inangahua R Blacks Point 10/02/2014 179/962-176/976 1.7 18 6.5 27 18 46 91 Inangahua R Blacks Point 19/02/2015 179/962-176/976 1.7 18 6.4 12 33 Mawheraiti Bridge 1994 043/892-033/878 1.7 20 43 75 Mawheraiti Bridge 1995 043/892-033/878 1.7 20 106 379 Mawheraiti Bridge 1996 043/892-033/878 1.7 20 72 357 Mawheraiti Bridge 1997 043/892-033/878 1.7 20 35 207 _____________________________________________________________________________________________ 289 334 36 154 193 678 523 952 44 286 Mawheraiti R Mawheraiti R Mawheraiti R Mawheraiti R Drift Dive Survey Report 2015 Page 9 of 10 Mawheraiti R Mawheraiti Bridge Mawheraiti Bridge Mawheraiti Bridge Mawheraiti Bridge Mawheraiti Bridge Mawheraiti Bridge Mawheraiti Bridge Mawheraiti Bridge Mawheraiti Bridge Mawheraiti Bridge Mawheraiti Bridge Mawheraiti Bridge Mawheraiti Bridge Mawheraiti Bridge Mawheraiti Bridge Mawheraiti Bridge 043/892-033/886 1.7 20 5.6 24 27 92 Mawheraiti R Mirfins Bridge 1/11/2012 005/810-999/798 1.4 20 5.1 10 14 2 26 Mawheraiti R Mirfins Bridge 30/01/2013 005/810-999/799 1.4 20 5.6 15 53 38 106 Mawheraiti R Mirfins Bridge 10/05/2013 005/810-999/800 1.4 20 6.3 13 24 1 38 Mawheraiti R Mirfins Bridge 20/11/2013 005/810-999/801 1.3 20 4.5 9 20 5 34 Mawheraiti R Mirfins Bridge 11/02/2014 005/810-999/801 1.3 20 4.9 2 3 29 34 Mawheraiti R Mirfins Bridge 16/12/2014 005/810-999/801 1.3 20 4 19 33 15 67 Mawheraiti R Mirfins Bridge 19/01/2015 005/810-999/801 1.3 20 4.4 13 27 133 173 Mawheraiti R Mawheraiti R Mawheraiti R Mawheraiti R Mawheraiti R Mawheraiti R Mawheraiti R Mawheraiti R Mawheraiti R Mawheraiti R Mawheraiti R Mawheraiti R Mawheraiti R Mawheraiti R Mawheraiti R 2001 043/892-033/878 1.7 20 4.6 16 39 68 123 2003 043/892-033/878 1.7 20 4.6 102 181 272 555 2004 043/892-033/878 1.7 20 4 76 364 167 607 2005 043/892-033/878 1.7 20 5.1 45 307 342 694 2009 043/892-033/878 1.7 20 4.7 44 121 322 487 11/02/2011 043/892-033/878 1.7 20 3.8 29 36 264 329 20/12/2011 043/892-033/879 1.7 20 3.9 19 20 30 69 15/02/2012 043/892-033/880 1.7 20 4.6 22 24 46 92 17/04/2012 043/892-033/881 1.7 20 5.8 31 15 6 52 1/11/2012 043/892-033/882 1.7 20 5.1 21 14 10 45 31/01/2013 043/892-033/883 1.7 20 5 22 7 30 59 10/05/2013 043/892-033/884 1.7 20 6.3 27 11 4 42 20/11/2013 043/892-033/885 1.7 20 4.2 13 10 15 38 10/02/2014 043/892-033/886 1.7 20 5 15 8 5 28 16/12/2014 043/892-033/886 1.7 20 4.2 14 30 13 57 134 20/02/2015 _____________________________________________________________________________________________ Drift Dive Survey Report 2015 Page 10 of 10