Newsletter > Detecting species presence: RES benchmarks eDNA vs. conventional seining

Detecting species presence: RES benchmarks eDNA vs. conventional seining

February 20, 2024

Species habitat mitigation is a primary focus for RES in California. Within the Livermore Valley, RES is currently working on multiple mitigation projects requiring conservation of land, in perpetuity, that contains aquatic and dispersal habitat for two hard-to-detect species: California tiger salamander (Ambystoma californiense) and California red-legged frog (Rana draytonii).

It can be challenging to provide sufficient evidence to regulatory agencies that these species-of-concern are present and are completing their lifecycles on the property. Agencies such as the California Department of Fish & Wildlife (CDFW) and the United States Fish & Wildlife Service (USFWS) rely on biological data for the mitigation approval process. Acquiring it can be costly, time-consuming, and labor-intensive.

RES has found a creative approach to proving the presence of a particular species with a high level of confidence, while also reducing the resources and level of effort required: Environmental DNA (eDNA).

eDNA is the isolation of genetic material from soil, water, or air, and the amplification of target sequences to detect species presence. This pioneering method has been shown to be a cost-effective, non-invasive, and effective tool for monitoring the distribution of aquatic species across large and small geographic ranges.

RES benchmarked eDNA vs. seining over several mitigation project sites in the Livermore Valley. The results show the promise of eDNA to accelerate the mitigation approval process and the development of habitat management plans in many types of projects – such as the Klamath River restoration, where RES is using eDNA extensively.

Unlike many traditional methods of surveying for aquatic species such as the California tiger salamander and California red-legged frog, eDNA….

  • does not require a Recovery Permit,
  • is not dependent on surveyor skill,
  • is highly repeatable,
  • has no risk of hurting animals,
  • is archivable for future analysis of additional species, and
  • is not subject to misidentification of target species.

Last fall, RES ecologists Dylan Keel, Amanda Casby, Sarah Wood, and Daniel Chase led a study that paired repeated eDNA surveys and conventional seining and dip netting to detect California tiger salamander and California red-legged frog at several sites in the Livermore Valley. Being able to compare 89 eDNA samples and 66 seine hauls helped answer the following questions:

  • Where are California tiger salamanders and California red-legged frogs?
  • If we did not detect them, how can we be sure they were not there?
  • And, how many eDNA samples and seine hauls are necessary to be sure?

After data collection, RES ecologists used multimethod occupancy models to conduct a statistical analysis. The results: both seining and eDNA had an approximately equal probability of detecting California tiger salamander and California red-legged frog.

The analyses showed that at a typical pond, California red-legged frogs were more easily detectable, requiring only two seine hauls or two eDNA samples to be 95% sure that the pond was either occupied or not occupied.

The California tiger salamanders were more difficult to detect, requiring eight eDNA samples or eight seine hauls to be 95% sure that the pond was or was not occupied.

Although RES ecologists found equal detection probability between the methods, the environment affected how well each method worked. The models showed that the more complex cover the pond had (e.g. algae, rooted aquatic vegetation, etc.) the better eDNA performed at detecting California tiger salamander relative to seining. Inversely, the clearer the water, the better eDNA performed at detecting California red-legged frogs relative to seining.

This kind of analysis is extremely useful to RES as we move forward with species habitat mitigation. Not only is eDNA a proven, helpful tool for conducting due diligence on properties, but applying statistical analysis to the data creates useful comparisons for presentation to the Interagency Review Team (IRT). If we can continue to document that eDNA is equally, or more, sensitive than traditional surveys and quantify the amount of effort necessary to detect species, we can better plan field efforts, save time and money, and provide statistical justification for the probability that species occur on mitigation properties.

This research study in the Livermore Valley, conducted on custom turnkey mitigation sites, is a great example of the power of custom sites with unique locations to test new methods. The RES team is excited about applying eDNA for species mitigation projects across our portfolio and hopes to present additional applications of the technology in 2024.