My 1.5 acre pond is still settling, with more suspended particles than I'd prefer. This is due to currently inadequate vegetation on the shoreline, with current efforts to remedy this that aren't complete yet unfortunately.
A little background on the pond:In November 2024, relatively small numbers of YP and SMB were introduced after a forage base of FHM and Eastern Silvery Minnows were established and supplemented by naturally occurring crayfish (at least a few different species), frogs and their tadpoles (tree frogs and a species called green frog, which looks like a somewhat smaller bullfrog) as well as GSH. My hope is to add brook trout when the turbidity settles out to a level that I'm confident they can tolerate.
Based on my water temps, the YP should be finishing their first spawn. The fish that were introduced were large enough that they should be capable of that this year. The SMB that were introduced averaged about 5", so I don't suspect they will be large enough to spawn this year.
I just had a Secchi disk delivered and have yet to get out with the kayak to get a reading. While I was waiting for it to arrive, I did what I could to educate myself on the effects of turbidity on my fishery, and thought I would share a bit of what I found and open the forum to discussion from the experiences of others.
Although a Secchi disk seems to be the preferred method of folks like us, there are more scientific methods of measuring turbidity, most of which use Nephelometric Turbidity Units (NTU) as their unit of measure. Despite my efforts, I couldn't find a correlation between Secchi disk readings and NTUs. Does anyone here happen to know what they are? I think this would be helpful, given that the published literature uses NTUs but mere mortals such as us use a Secchi disk.
Of the published research that I found on the topic of turbidity, here are a few interesting points that I came across. Most studies on freshwater fish tolerance to turbid conditions are done on streams and rivers, with much fewer done on lakes and ponds. A study done on the Great Lakes did sampling of fish via traps or electrofishing in water bodies of varying turbidity, with the assumption that species that were "present and abundant" in more turbid conditions equated to that species being tolerant to turbidity. Surprisingly, YP were listed in the category of the most tolerant to turbid conditions. Equally surprising, FHM were considered "moderately tolerant", less so than YP. Also in the "moderately tolerant" category were LMB, SMB, and GSH. They were in the same category as black and brown bullheads, which I have always thought to be one of the most resilient freshwater fish. Based on this study, YP exceeded bullheads in their tolerance for turbidity. Here is the study for anyone interested:
https://www.researchgate.net/public...es_of_Great_Lakes_Coastal_Wetland_FishesSpecifically for YP, I found a study that compared turbidity from sediment vs turbidity from algal blooms on survival and growth of YP up to one year old. Interestingly, higher turbidity from
sediment during the youngest stages of life led to faster growth than either low turbidity or turbidity from algal blooms. They hypothesized that this was an effect of the focal length of the fish's eyes changing at varying stages of growth, with younger fish having increased visual contrast of prey items when sediment turbidity is present. Because YP fry were able to be more effective hunters in waters with sediment turbidity, they matured faster (underwent ontogenetic shift) than YP fry in clear waters or in turbid waters caused by algal blooms. This was not the case when they reached the "juvenile stage".
In this same study, turbidity caused by algal blooms led to decreased growth because "algal turbidity both scatters incoming light and selectively absorbs photosynthetically active radiation, thus reducing light levels more than sediment turbidity of the same intensity (Gallegos et al. 1990)," therefore YP fry were less able to see prey. Less successful hunting led to slower growth, longer times to reach ontogenetic shift, and more starvation leading to death. Even low levels of algal growth led to worse conditions in all stages of development studied (age-0). This seems counter to the common practice of fertilizing ponds to cause blooms. I'm curious to hear the feedback of the professionals as it relates to this. Here is the link to the publication of you'd like to read it.
https://www.researchgate.net/public...es_of_Great_Lakes_Coastal_Wetland_FishesAnother study found BCP, BG, GSH and pumpkinseeds among the most tolerant of turbidity, with LMB, bullheads and YP considered "moderately tolerant". Moderately intolerant were SMB, BNM, CSH, BT and dace species. FHM were listed in the least tolerant category, which surprised me again.
https://academic.oup.com/najfm/article/18/2/236/7862980Since I'm hoping to add BT to the pond when it is clear enough that I'm comfortable doing so, I looked deeper into their tolerance of turbid water. A Canadian study I found assessed daily food consumption and growth rates at varying levels of turbidity. They found that trout ate the same despite water clarity levels, but those living in greater turbidity grew less. They hypothesized that the needed to actively hunt more to get the same amount of food, therefore they burned more calories from energy expenditure and put on less weight.
https://cdnsciencepub.com/doi/10.1139/f00-260I thought someone else may have some of the same questions that I had, so I thought I would share what I've learned.
Some questions that I wasn't able to answer are:
How does turbidity effect egg viability?
What is the conversion from Secchi disk readings to NTUs?
How does color staining by tannins impact turbidity readings? Waters around me are clear and brown, like ice tea.
How do the above studies in lakes and streams correlate to smaller impoundments such as ours?
I welcome your thoughts and experiences.