September 1 2023
Lake Otamangakau opens today
What an absolutely smashing beautiful fine day for the opening a month earlier than in previous years, so expect many anglers heading out through the remains of the surrounding forest after it was shredded by the Cyclone about six months ago. First is DOC’s (Department of Conservation are the managers of the Taupo fishery) latest report with trap results from Lake O. They confirm the status as our trophy lake.
Then below is TRM’s previous blog to reflect anglers’ impressions and for DOC’s explanation – the report by Taupō fishery scientist Dr Michel Dedual summarises a body of research and sets out potential management options for the future of this iconic trout fishery and why it was closed for February…
DOC REPORT
There’s good news for stillwater anglers, with the fishing season at Lake Otamangakau due to kick off on Friday 1 September. In this newsletter you can read about the latest information from the Te Whaiau fish trap, located on the main spawning tributary for Lake Otamangakau – an ideal opportunity to whet your appetite for the new fishing season.
Tight lines.
James Barnett
Editor
The latest fish trap data confirms the fishery is doing well – both brown and rainbow trout have a high average size and condition factor. The focus on protecting large trout should generate even more trophy fish for anglers to target this season.
We will closely monitor how the new regulations continue to bed-in, with data from the Te Whaiau spawning trap providing a valuable insight. A short summary of the latest analysis is provided below.
Te Whaiau fish trap.
The fishing season at Lake Otamangakau is about to open, so it is timely to present a short summary of the latest data captured from the Te Whaiau fish trap.
The Te Whaiau Stream is the main spawning location for trout in Lake Otamangakau. This winter the trap was operational for two months (June and July) which allowed us to capture the back end of the brown trout run along with a significant proportion of the rainbow trout run. This is the second consecutive year the trap has been operational following a 5 year break.
A total of 321 rainbows and 50 browns were processed through the upstream pen, which included 9 trophy sized fish (exceeding 4.9kg or 10lbs). The biggest trout was a rainbow jack that measured 730mm and thumped the scales down to an impressive 5.5kgs or 12.1lbs.
To make a meaningful comparison with previous years (where the trap was operational for five months at a time) we need to apply an adjustment to the figures. We know June and July accounts for more than 95% and 88% variations in the total run of rainbow and brown trout, respectively. These formulas were applied, and information presented. (Fig.1).
The increase in spawning run size was associated with a marked decrease in average weight for both browns and rainbows especially between 2007 and 2013 when the numbers of browns and rainbows exceeded 3,000 trout in total. The increase in spawning biomass was particularly large for rainbow trout which increased from 997kg in 1994 to 7,116kg in 2010 compared to an increase from 790kg to 2,504 kg for brown trout during the same period (Fig.2).
The numbers of trout recorded may be down, but the average weight and condition factor is much improved. The rainbows trapped during 2023 averaged 618mm and 3kg (6.6lbs) with an average condition factor of 45. Overall, they were the third heaviest behind the peaks of 3.1kg observed during winters 1995 & 1996 (Fig.3). There were 8 trophy sized rainbows recorded, which is the highest number since 2005. It is also encouraging to note that a further 16 rainbows weighed between 4kg and 4.4kg (8.8lbs and 9.7lbs) suggesting they will reach the magic double-figure mark over the coming season.
Although the browns were the longest on record, only 1 trophy sized fish was physically trapped; an impressive hen tipping the scales at 4.95kg or 10.9lbs and measuring 665mm. However, it is worth noting that June and July is the tail-end of the brown trout run so it is likely that more trophy sized browns ran earlier in the season before the trap was operational. Anglers reported catching trophy sized browns in Lake Otamangakau during last summer and so it is likely some of these browns spawned in the Te Whaiau Stream earlier in the winter or in the neighbouring Papakai Stream. The presence of some notably large brown unclipped kelts this year in the downstream pen would further suggest that these fish ran earlier. The average length and weight of trapped brown is still impressive compared to previous years (Fig.4).
Trout fishery modelling results suggest a maximum size limit is the best approach to preserve trophy-sized fish. The current maximum size limit of 550mm which came into effect on 1 September 2022, combined with a February closure, has certainly had an immediate impact on the number of trophy trout present in this winter’s run and this bodes well for anglers next summer wishing to target the larger trophy trout in this unique fishery.
More technically minded anglers may be interested in a more detailed analysis of the Te Whaiau trap data, which we plan to publish shortly. Look out for details.
‘How to fish’ Lake Otamangakau.
An oldie but a goodie – if you are new to still water trout fishing or just need an insight into the techniques used to successfully catch trout at Lake Otamangakau, then this video clip is for you. Check out our YouTube clip – ‘Lake O on the fly
TRM’S PREVIOUS REPORT:
Lake O closure arguments continue…
The closure of Lake O (Lake Otamangakau) for February has been an interesting hot discussion amongst anglers. As the January days were running out, the “for & against” issues and arguments did not go away. Instead, they intensified. Lake O is an iconic trophy lake for the Taupo region and is therefore subject to much scrutiny by both anglers and fisheries management.
SWMBO (She Who Must Be Obeyed is the Manager of everything at TRM but would never usually dare to advise on the more important issues like fishing) intuitively suggests perhaps this was a natural human nature response to the 2023 fishing not being quite as good as in previous years, so the anglers needed something to grizzle and bitch about… Seems a reasonable deduction. Perfectly understandable.
As previously posted in TRM’s fb reports, most TRM inmates are against the new regulations for a number of reasons. When we hear one or two dissidents we might take note but that is all. Anglers never agree on much anyway. But when they go on about an issue for weeks then it may be more serious and we are obliged to report further. Consider the argument about which is the best boat for fishing Lake O? Everyone claims they have the perfect compromise. On a good day they are all correct. On a quiet day, who cares… That is when their attention is distracted by changes in the fishing regulations (repeated below).
But this issue of closing the lake for February has really got them all bewildered and wound up.
One extremely important consideration appears to have been deliberately overlooked in all the fb posts and correspondence and in DOC’s analysis and reports. This was explained to TRM by a particularly experienced fishy inmate who has been addicted to Lake O ever since it was formed as part of the Tongariro Hydro catchment scheme. He believes it is the key to the increased level of trout mortality during the last couple of seasons – which appears to have been the trigger that started off all the panic and concerns from DOC. Surprisingly they did not mention it either. Or did they prefer not to factor it into their decision-making process for commercial reasons?
Anglers have suggested that the very fact that it was not included is proof that it is the prime reason. Trout fishermen are always traditionally so suspicious of any bureaucracy. When the trout fishery regulations are composed by a Government Department then their conspiracy antennae are even more activated.
To a Government Department like DOC (Department of Conservation are the fishery managers) the continued close cooperation of Genesis Energy may have been more important politically and may have outweighed the fishing results… Genesis controls the flow from several sources into Lake Taupo via the Tokaanu Power Station. Another power company controls the outlet into the Waikato River chain of eight more hydropower stations. The requirements to provide power for electric cars in Auckland or air conditioning far outweigh any considerations of Lake O anglers.
This is the crunch! During the last two seasons, when dead trout were sighted floating in the lake, the inlet canal was not flowing. Excessive water temperature is the killer.
Without the flow of cooler snow-melt from the Whakapapa River, the shallow lake heated up much more than the usual February temperatures. All Lake O anglers understand that whenever the lake heated up during previous seasons the resident trout moved up the inlet canal to refresh and re-oxygenate from the cooler frothy invigorating waterfall flowing into the Te Whaiau canal and through the tiny Lake Te Whaiau.
The uncontrolled upper Wanganui River alone – which joins the inlet canal and is used for the fish trap data – has insufficient volume to maintain the lake water temperature at a cooler survivable level. For a view of the fish trap operation on the Wanganui River, have a squiz at the brief educational video below produced by TRM – starring Didymo Dave no less!
The photos illustrate the physical nature of the canal geography better than I can describe it.
But as the closure of the inlet canal and lack of any flow was not referred to in DOC’s analysis of the reasons which forced them to close Lake O in February, it must have been just a coincidence…
Trout anglers are such suspicious characters.
What do you think?
Lake Otamangakau: Research update 2021
Lake Otamangakau: Research update 2021
Archived content: This media release was accurate on the date of publication.
Introduction
This report by Taupō fishery scientist Dr Michel Dedual summarises a body of research and sets out potential management options for the future of this iconic trout fishery.
Date: 01 December 2021
Report title: Management of Lake Otamangakau fishery in the face of various anglers’ aspirations, changing climate and evolving societal perception of recreational fishing.
Introduction
The main objective of this study is to apply a decision making process to support possible changes to fishing regulations during extreme environmental conditions. Twenty-seven years of research and monitoring provides us with a very good understanding of trout populations at Lake Otamangakau (Lake O), but we must also consider the following elements:
- Angler surveys indicate the fishing community is split between two distinct groups of anglers; those who want to catch less but larger fish and those who want to catch as many fish as they can. This dichotomy can create a substantial difficulty for managers as any decision may affect one group more than the other.
- The number of trophy fish (herein >650 mm) has declined steadily between 1994 and 2014 and it is now very low, probably no more than 100 specimens.
- Trophy fish at Lake O are large not because they grow fast but because they live a long time. To reach a trophy size they must be at least 5 to 6 years old, meaning that they grew and survived fishing pressure over a longer period.
- The fishing mortality includes fish that are killed voluntarily (harvested) and those that are killed involuntarily by releasing them after capture (catch-and-release).
- Fishing pressure is “the elephant in the room” affecting mortality. Even in the absence of harvest, mortality caused by catch-and-release may be sufficient to eradicate trophy fish if fishing pressure is sufficient. Fishing pressure (visits/year/hectare) estimated in Lake O is amongst the highest in New Zealand.
- Mortality associated with catch-and-release has been well studied worldwide but results are difficult to extrapolate as they are sometimes contradictory and/or specific to a geographic location. However, the major consistent driver of mortality is water temperature within which fish are played – the higher the temperature the higher the mortality. In Lake O catch and release mortality ranges from 0 to 30 % at water temperatures of <11 and >22 ˚C respectively. Furthermore, these estimations of catch-and-release mortality can be underestimated for several reasons. The number of times an individual trout was hooked and released wasn’t considered but with the current level of pressure in the lake, it is reasonable to expect that some fish that survived the first release may not survive an additional catch-and-release event. No data are available on the impact of repeat capture, but some studies suggest that if a trout had a 30 % chance of mortality after one capture event, the total probability of mortality after 2 hooking events could increase to 50 %. We don’t have any data on the number of times the same trout can be captured during its life. Mortality beyond 66 % cannot be ruled out, as several studies have shown that fish vulnerability to predation or susceptibility to disease can increase following catch-and-release.
- Elevated trout mortality at high water temperatures has pushed some fishery managers to close waters to recreational fishing when temperatures climb above a certain threshold. In most cases at 18 to 20 ˚C.
To explore what type of management action could be the most effective at maintaining anglers’ satisfaction levels and fish population perennity, we first used the biological aspects of trout runs collected over 20 years of trapping to build a dynamics model. We then submit this population to various degrees of fishing pressure, water temperature, changes caused by global warming and the corresponding catch-and-release mortality, into the model. The impacts of global warming were considered using 23 management regulation scenarios. We estimate these impacts on the catch rate of all fish, trophy fish and the duration of a fishing season. The outcomes of each scenario are presented in the table below.
Table 1. Outcomes and impacts of various fishing regulations for Lake Otamangakau on CPUE (fish/visit) of all sizes and trophy fish (>650 mm) and implications on the duration of the fishing season. | View larger (JPEG, 200K)
Results and discussion
The highest Catch Per Unit Effort (CPUE) would be expected with regulations allowing only catch-and-release combined with a closure of the fishery when the water temperature reaches 11 ˚C. This temperature threshold represents the condition when we observed no mortality caused by catch-and-release (commonly called “no kill”). However, such a regulation would dramatically reduce the fishing season restricting it to just over a month (4.7 weeks). The lake surface water temperature remains below 11 ˚C from April to November although this period will diminish with global warming.
Some anglers may suggest extending the fishing season to include the entire duration with water <11 ˚C. I think this would add another unnecessary stress on fish migrating to spawn and during the early phase of their recovery.
Note: For clarity and conciseness, I didn’t put the impact values of the increases in water temperature caused by global warming but considered scenarios with different rates of temperature increase per year. The results indicate that the rate of temperature change will negatively affect both the CPUE and the duration of the fishing season.
At the other end of the spectrum maintaining the status quo (doing nothing) or having a compulsory harvest of fish >350 mm in February would generate the lowest CPUE but would maximise the duration of the fishing season.
We believe that neither of these two options are desirable nor justified. We know that the number of fish in Lake Otamangakau has a negative impact on their average size, so aiming at no mortality (catch-and-release only and closure at 11 ˚C) could lead to an overpopulation of fish that would prevent the production of trophy fish and hence negate the benefit of a change in fishing regulation. On the other hand, not changing anything or relaxing harvest further could potentially reduce the fish population to levels where no trophy fish are available.
As we said earlier, there are several types of anglers fishing Lake O, with some who want to harvest fish for the table. We have analysed the length class distribution of the fish kept by anglers and we can see that the number of fish kept is small and that the average size is less than 550 mm indicating that anglers are not selecting trophy fish to harvest (Graph 1).
Graph 1. Length class distribution of the fish kept (n=269) by anglers recorded during angling survey (n=2343) carried out at Lake Otamangakau between 1997 and 2020. | View larger (JPEG, 121K)
Therefore, we are confident that allowing some harvest will not have a significant detrimental effect on the availability of trophy fish and that a catch-and-release only regulation is not warranted. However, even though the surveys indicate that virtually no angler seeks to harvest the allowed daily bag, I would suggest that reducing the daily bag to 2 fish would send the right message.
In fact, the outcomes of catch-and-release only without any temperature threshold closure will have a less positive impact on CPUE than allowing some harvest of fish with some size regulation and water temperature restriction.
Setting the threshold temperature at 20 ˚C for closing the fishery would have the best outcome but it presents some logistic problems and can have an unfair impact on anglers. The temperature in the lake can change quickly from one day to the next so it would be difficult to put in place and enforce such a rule. Furthermore, it would be unfair to those anglers who plan trips to Lake O at great expense, only to arrive and be prevented from fishing because the water temperature is over the threshold.
The continuous temperature monitoring indicates that the lake surface water temperature is highest from mid-January to mid-March. So having a fixed closure period covering February would be simpler to understand and easier to enforce.
Considering all the limitations and constraints of the various scenarios, I believe that having a maximum size of 550 mm combined with a February closure constitutes the best compromise to address the angler’s satisfaction and maintaining and protecting the trout population.
Even though the differences in CPUE outcomes between the different scenarios seem very small we must remember that the total fish mortality will be multiplied by the fishing pressure. The Lake O fishery is open access; therefore, the long-term effectiveness of the above regulation will be dependent on the unknown and unpredictable fishing pressure exerted.
Restrictions on angler effort may represent an important management option for maintaining the trout population. However, policies that seek to reduce fishing effort are often unacceptable and hence have rarely been implemented in recreational fisheries. In addition, reducing fishing effort will also mean less revenue from licence sales – the only source of income. Therefore, before reducing fishing pressure managers need to have a clear understanding of the financial impact, particularly when angling participation is in decline and managers need to retain current angler participation as well as recruit new anglers.