Monarch Watch Blog

Tracking Individual Monarchs with Radio Tags as Part of the Project Monarch Collaboration

17 November 2025 | Author: Kristen Baum

With today’s New York Times article (We Can Now Track Individual Monarch Butterflies. It’s a Revelation. 17 November 2025) and press release from Cellular Tracking Technologies (CTT) and the Cape May Point Arts & Science Center (CMPASC), we want to share more information about our participation in the Project Monarch Collaboration.

BlūMorpho Radio Tags

BlūMorpho solar-powered radio transmitters (also referred to as “tags”) provide an amazing opportunity to track the paths of individual monarch butterflies. In particular, the ultralight tags can use Bluetooth crowd-sourced location networks to increase the number of detections. Visit the CTT/CMPASC Project Monarch website to learn more about how the project started and how BlūMorpho tags work. In contrast to these radio tags, our Monarch Watch Tagging Program uses sticker tags and relies on people to observe and report or recover tags with unique letter and number codes. Both tagging approaches provide unique and complementary information about the monarch’s fall migration, as well as different ways for people to engage with monarchs. We are excited about the research questions that can be asked with the new technology and look forward to continuing to study the monarch’s fall migration with both the BlūMorpho tags and Monarch Watch sticker tags. We hope you will share our excitement!

Monarch Watch deployed a total of 30 BlūMorpho tags towards the end of September. Of the 30 monarchs that we tagged, 30% (9) have been detected in Mexico, 63% (19) in Texas, and 70% (21) in Oklahoma. Previous estimates (see Monarch Population Dynamics: Issues of scale) have suggested that 20% (or 1 out of 5) or fewer of monarchs that start the migration across the breeding range make it to the overwintering sanctuaries in central Mexico. While we do not know the origins of the wild-caught monarchs that we tagged with BlūMorpho tags in Kansas, we do know that they had many fewer miles left to fly (1370 miles) by the time we tagged them than those tagged by many of our colleagues and collaborators on this project. For example, those tagged in Long Point, Ontario, had to fly at least 1960 miles to reach the overwintering sanctuaries, while those tagged in Harrisonburg, Virginia, flew at least 1830 miles. Based on the preliminary results from this year and expected mortality during the migration, the success of the BlūMorpho tagged monarchs is very good.

Monarch Tracking Data Visualization

Using the free Project Monarch Science app (download via your device’s app store), you can view lots of information about many of the tagged individuals. You can find the monarchs tagged by Monarch Watch in the Data tab by selecting the monarch icon at the top of the screen then searching for “MW”. When you look at the map view, make sure to zoom in as far as you can so that you are not missing any monarchs.

We had some excitement on Nov. 9 when JMU004 was the first monarch to be detected at a known overwintering site (El Rosario), but MW026 was detected in the same location a couple of hours later, obscuring the view of JMU004, as you can see in the images captured from the app, below.

MW026_appMonarch MW026 obscuring the view of monarch JMU004.

I mentioned in a previous blog post (Radio-tagged monarch MW001 arrives at the MBBR) that monarch movement was slow due to winds from the south. The BlūMorpho tags capture this in a way that was not possible before. Using MW026 as an example, some graphics below illustrate that point. Keep in mind that winds are reported based on the direction they are coming from. That means that North winds (those blowing north to south) help the monarchs move south when they are starting in Kansas, but South winds (those blowing south to north) make the migration more difficult.

MW026_track1

MW026_track2

MW026_track3

MW026_track4Full tracking of monarch MW026 through 16 November 2025.

If you are looking for some monarchs to check out in the app, a good starting point might be MW026, XOKC006, NOK015, LPM093, and JMU004, which are grouped together (at least at the time I am writing this!) in the Monarch Butterfly Biosphere Reserve. There are also lots of other monarchs doing interesting and even unexpected things, so look around!

You could also check out the nine monarchs that we tagged that made it to Mexico: MW001, MW002, MW003, MW008, MW020, MW021, MW023, MW024, M026. Their tracks appear below.

9inMexico_tracksTracks of nine monarchs in Mexico, tagged and released by Monarch Watch.

Below are the tracks of all 30 monarchs that we tagged.

all30_tracksTracks of 30 monarchs tagged and released by Monarch Watch.

Project Monarch Collaboration 2025

More than 25 research organizations make up the Project Monarch Collaboration this year (see logos below). Not only is this project an amazing contribution to science, but it has also been a lot of fun, in particular sharing the experience (including lots of ideas, information, questions, answers, etc.) with so many other dedicated scientists.

project_partnersLogos of 2025 Project Monarch Partners.

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Radio-tagged monarch MW001 arrives at the MBBR

7 November 2025 | Author: Monarch Watch

Monarch Watch is participating in the Project Monarch Collaboration to deploy BlūMorpho radio tags on monarchs during the fall migration this year. The Project Monarch Collaboration was founded through a partnership between Cellular Tracking Technologies and the Cape May Point Arts and Science Center and involves lots of conservation organizations and scientists and an amazing group effort. BlūMorpho tags are extremely lightweight, solar-powered radio tracking tags that can be attached to the thorax of monarchs.

For our part of the project, we received 30 BlūMorpho tags. On September 26th and 27th, we attached each tag to a monarch butterfly and released them. The tagged monarchs can be tracked through the Project Monarch Science app, which you can download to follow along. The monarchs that we tagged are named MW001 through MW030, and you can search for them in the app by searching for “MW” to bring up all of our tagged monarchs.

Our monarchs were slow to move due to winds out of the South. They finally reached Oklahoma on October 7 and Texas on October 21. That is really slow movement! Our first BlūMorpho tagged monarchs reached Mexico on October 29. MW001 reached the Monarch Butterfly Biosphere Reserve (MBBR) yesterday afternoon! MW001 is a male that weighed 0.6 grams when we first caught him in Lawrence, Kansas on September 25, and he had a wing length of 53mm. Several of the other ones that we tagged are close to the MBBR, including two more males and two females.

MW001_path
The path (1360 miles!) of monarch MW001 from Lawrence, KS to the MBBR.

MW001_current
A close-up view of the current location of monarch MW001.

latest_locations
A view of the many BlūMorpho tagged monarchs that are approaching the MBBR. Those labeled MW were released by Monarch Watch in Lawrence, Kansas, PP were released at Point Pelee in Ontario, Canada (1800 miles away!), BCA were released in coastal Alabama, JMU were released in Virgina, LPM were released at Long Point in Ontario, Canada, and XSTI, NOK, and XOKC were all released in Oklahoma.

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A Remarkable Recovery

31 October 2025 | Author: Monarch Watch

Thank you to everyone who’s been participating in our tagging program this year! This program relies on the participation of many people to tag monarchs and send their data to us, helping us study the monarch fall migration. One of our goals for this tagging season was to increase the number of “domestic” tag recoveries. “Domestic” recoveries are tagged monarchs that are observed during the fall migration in the United States, Canada, and northern Mexico. Following each migration season, we post tag recoveries on our website, and ahead of recoveries being posted next year, we want to share a story about one of these “domestic” tag recoveries. The monarch that was observed made quite the journey.

One Monarch’s Migration

On October 15, 2025, someone reported a tagged monarch south of Perryton, Texas, a female with the tag code ALNT377. After looking through our records and contacting the tagger, we discovered that this monarch had been tagged in Biddeford, Maine, on August 28. Plotting these two locations on a map (below), we can estimate that this monarch traveled close to 1,700 miles in about six weeks. We won’t ever know exactly what this butterfly’s route was, but to see the distance between Biddeford and Perryton on a map really puts into perspective how far these insects can travel during the migration.

ALNT377_tag_recovery_map

We plotted the great circle distance between Biddeford, Maine, and Perryton, Texas, which is just shy of 1,700 miles.

When spotted in Texas, this butterfly was roosting with several others in a tree (see images below). Who knows where she is now, but hopefully she’ll make it to Mexico’s overwintering grounds. This story is a reminder of the monarchs’ incredibly long journey.

We have an important role to play if monarchs are going to continue their spectacular migration. This butterfly wouldn’t have made it to Texas without nectar plants to fuel her flight, and she wouldn’t have become a butterfly without milkweed, the host plant on which female monarchs lay their eggs and monarch caterpillars exclusively feed. For the migration to continue, we need to keep planting milkweed and nectar plants so monarchs have resources to support their life cycle and migration.

ALNT377_monarch_photo_credit_MD

This tagged female monarch had made it all the way to Texas from her original tagging location in Maine, traveling almost 1,700 miles. This person who observed this monarch in Texas included these photos as part of their recovery report. Photo credit: M.D.

How the Tagging Program Works

Monarch Watch’s tagging program is a mark-and-recapture program. Monarch butterflies are tagged with a weatherproof sticker that has a unique letter and number code, and the location, date, and sex of the butterfly is recorded. Tagged monarchs are reported all along their migration route and recovered every year from the overwintering grounds in central Mexico, providing us important data about the monarch migration. This data has revealed new information about the timing and pace of the migration, where migrating monarchs come from, how weather can affect the migration, and more.

Once all the data has been verified and processed, we’ll post domestic tag recoveries from Canada, the United States, and northern Mexico around March 2026 and recoveries from the overwintering sites in central Mexico around April/May of 2026.

If you haven’t submitted your tagging data yet, go to our Tagging Program page and follow the instructions under the “Submitting Your Tagging Data” section to share your tagging data with us. Additionally, if you have any “domestic” recoveries of tagged monarchs this season and haven’t reported them yet, use our online form to report your recovery – and if you have any photos to go along with your observation, we’d love to see them in the report as well!

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Does tagging harm monarchs?

18 July 2025 | Author: Kristen Baum

We receive lots of inquiries about monarchs every year, and this is the time of year when we start receiving questions about tagging, including if tagging can harm monarchs. We conducted an experiment last summer to compare survival of tagged and untagged monarchs, and we found no difference in survival for males or females. A detailed summary of that project can be found below. We also wanted to take this opportunity to answer other frequently asked questions about monarchs and the tagging process.

Catching and Tagging Monarchs
We receive questions from people who are concerned about potentially injuring a monarch when catching it for tagging. Monarch Watch has hosted public tagging events for more than 20 years, and my research lab has tagged over 6,000 monarchs since 2015. Injuring a monarch while catching it is a rare occurrence, especially with the sweep/swoop-and-flip (also referred to as the swish/flick) method. If you use the flop-and-lift method, be careful not to pull the butterfly through vegetation when removing it from the net. If you catch a monarch that you are concerned about (e.g., damaged wings, small size), let it go without tagging it.

Transferring Ophryocystis elektroscirrha Spores when Tagging
We also get asked about the spore-forming protist Ophryocystis elektroscirrha and, in particular, the possibility of transferring spores during the tagging process. While it’s certainly possible that spores can be transferred between butterflies by handling an infected individual and then handling an uninfected one, monarchs can’t acquire an infection at the adult stage. Spores are the most heavily concentrated on the abdomen, but they’re also present on the wings and on other parts of the body.

Spores acquired during the tagging process would primarily be transferred from wings to wings, where spores are less concentrated. Furthermore, spores transferred during tagging would need to remain on the adults for the remainder of their fall migration to the overwintering sites in Central Mexico, through the winter, and through the return migration to Texas in the spring, and then come in contact with milkweed leaves (or the outside of monarch eggs, since newly hatched caterpillars typically eat their eggshells) that are then consumed by monarch caterpillars. Spring migrants are typically pale and tattered and have lost many scales, which would also likely result in the loss of spores.

While it seems unlikely that many infections would occur this way, it is possible, and this is a challenging question to address experimentally. Given the extremely small proportion of the monarch butterfly population that is tagged each year, it seems unlikely this would negatively impact the population.

The Value of Tagging Monarchs
We typically distribute approximately 300,000 tags each fall to thousands of participants who tag more than 100,000 monarchs during the migration. If one considers the monarch overwintering population size was 1.79 hectares this past winter, or 37,769,000 monarchs (assuming 21.1 million monarchs per hectare), and that a majority of monarchs that start the migration don’t make it to the overwintering sites, then the number tagged is likely much less than one-tenth of 1 percent. Thus, we think the value of tagging outweighs any potential negative impacts and that those negative impacts are likely to be minimal. Tagging has revealed new information about where the overwintering monarchs come from, the timing and pace of the migration, the differences among regions, the impact of weather on the migration, and many other factors.

There’s still much to learn about monarchs and their migration, especially as monarchs respond to shifting conditions related to climate change and habitat loss. We need more research to support monarch conservation and identify approaches for addressing current and future issues, and tagging is an important piece of that puzzle.

Tag Monarchs This Fall
As the 2025 tagging season approaches, consider joining us in tagging monarchs this year. A tagging kit, net, and other monarch supplies are available in the Monarch Watch Shop, and we’ll begin shipping tagging kits in late July.

You can also report tag recoveries. “Domestic” recoveries are tagged monarchs that are observed during the fall migration in the United States, Canada, and northern Mexico. We receive pictures and tag codes to document these “domestic” recoveries, and this gives us information on how long monarchs are staying in an area or how far they travel during different time windows of the fall migration. Sightings of tagged monarchs may be submitted via the Monarch Watch mobile app or Tagging Program page. Sightings may include monarchs tagged by others as well as monarchs you tagged that are still around the next day or days later.

Every chance you get, share your passion for monarchs and their incredible fall migration with others!


Tagging Survival Experiment

Monarch Watch’s tagging program began in 1992, with the circular tags that we currently use adopted in 1997. Each circular tag contains a unique letter-and-number code printed with permanent ink on all-weather stickers. We ran out of combinations of our three-letter-and-three-number codes, so we added a fourth letter in 2019, at which time we also reduced the amount of text on the tag. Each tag is approximately 8.95 mm in diameter and weighs about 0.008 g. A monarch weighs approximately 0.5 g, so the tag is about 1.6% of its body weight. We occasionally receive questions about whether the tags affect monarch survival, so we conducted an experiment last summer to evaluate if survival differs between tagged and untagged monarchs.

The Set Up
We reared 266 monarchs using standard protocols for rearing individuals to maintain our monarch colonies at Monarch Watch. Monarchs eclosed (emerged from their chrysalises) between July 14 and July 21, 2024. The date that each individual eclosed was marked on the discal cell of the left hind wing with an ultra-fine felt-tip marker. One-half of each sex also received a Monarch Watch tag on the discal cell of the right hind wing, while the other half didn’t receive a tag. All tags were applied by me (K. Baum), with light pressure applied to the tag for a few seconds to ensure it adhered to the wing.

Monarchs were placed in one of two large walk-in cages (1.8 x 1.8 x 1.8 meters; Figure 1). One cage contained females and one cage contained males, with the sexes separated to reduce the impacts of mating activity on survival, although males will attempt to mate with other males. The cages were located in the Monarch Watch “bio house” on the University of Kansas’ West Campus in Lawrence, Kansas. The “bio house” is an open-air hoop house covered with 63% shade cloth.

Monarchs were misted with water once daily, except on days when there was already moisture in the cages from rain. Monarchs were provided with a 15% sucrose solution and allowed to feed as needed (Figure 1). Nectar was located in 10 dishes in each cage, which were elevated to increase use by monarchs. Each dish contained a plastic scrubber to allow the monarchs to easily feed. Nectar was replenished daily, as needed, and replaced every 10 to 14 days. Following rain events, the concentration of the sugar solution was checked to ensure it was at 15% or above and replaced if needed. Blooming potted plants (lantanas and pentas) were placed in each corner of the cages and watered as needed. Dead monarchs were collected daily between 8 a.m. and 10 a.m. CDT and the date of collection recorded. By the conclusion of the experiment, three tags were recovered from the male cage, and all other tags were accounted for on dead butterflies

tagging_fig1

Figure 1. A view of one of the walk-in cages, with a close-up view of the nectar dishes. The dish in the center with the white plastic scrubber was used to assess rainfall and didn’t contain nectar.

tagging_fig2

Figure 2. Pictures of monarchs from the experiment, including one of the three males that lost a tag (left), an older tagged male with extensive loss of wing scales (middle), and the oldest surviving female (untagged; right).

The Analyses and Results
Survival was calculated as the number of days between when a butterfly was placed in the cage and when it was collected as dead. We conducted two sets of analyses. For the first set, we only used monarchs where the number of days could be calculated based on the date written on the left hind wing (i.e., individuals where the date was no longer legible were excluded from the analysis). Forty-four individuals were excluded, including 27 females (14 tagged and 13 untagged) and 17 males (13 tagged and four untagged). For the second set, we included tagged individuals where the date could be calculated based on the tag, even if the date was no longer legible on the left hind wing. Seventeen individuals were excluded, including 13 females and four males.

We used t-tests to compare survival between tagged and untagged monarchs. For the first set of analyses, there was no difference in survival between tagged (27.64 ± 1.07; mean ± SE) and untagged (27.75 ± 1.48) female monarchs (t = 0.0581, df = 87, p-value = 0.95) or between tagged (26.40 ± 1.42) and untagged (25.89 ± 1.28) male monarchs (t = 0.2626, df = 131, p-value = 0.79). There was also no difference for the second set of analyses (females: t = 0.1164, df = 101, p-value = 0.91; males: t = 0.3902, df = 144, p-value = 0.70).

tagging_fig3

Figure 3. Survival (# days; mean ± SE) of tagged and untagged female and male monarchs, with individuals excluded if the date on the left hind wing was no longer legible.

We found no difference in survival between tagged and untagged monarchs held in outdoor cages, indicating that tags don’t affect survival under these conditions. This study was conducted during the breeding season, and results could differ for monarchs during the fall migration or those held under different conditions.

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Monarch Population Status

6 March 2025 | Author: Jim Lovett

The WWF-Telmex Telcel Foundation Alliance, in collaboration with the National Commission of Natural Protected Areas (CONANP), the National Autonomous University of Mexico (UNAM), and the Monarch Butterfly Biosphere Reserve (MBBR), announced the total forest area occupied by overwintering monarch colonies today. Eight (8) colonies were located this winter season with a total area of 1.79 hectares, a 99% increase from the previous season (0.90 ha).

monarch-population-figure-monarchwatch-2024-season
Figure 1. Total Area Occupied by Monarch Colonies at Overwintering Sites in Mexico.

Report: 2024 Monitoreo Mariposa Monarca en México 2024-2025

WWF story: Eastern monarch butterfly population nearly doubles in 2025

Note: The WWF-TELMEX Telcel Foundation Alliance collaborates with CONANP to systematically monitor the hibernation of the Monarch since 2004, and they join the Institute of Biology of the National Autonomous University of Mexico (UNAM) to analyze changes in forest cover in the area core of the Monarch Butterfly Biosphere Reserve in order to have scientific bases that support the implementation of conservation strategies for the benefit of the species, ecosystems and human beings.


Monarch overwintering numbers in Mexico for the 2024 season

by Chip Taylor, Founding Director of Monarch Watch

The monarch numbers are in, and they are of interest again, but this time not for the fact that the population declined but for the rate of increase. Last year the overwintering population was extremely low, occupying only 0.90 hectares when all colonies were counted. That number was second only to 2013 when the total was 0.67 hectares. The number this year is 1.79* hectares and that is remarkable. It’s a doubling of the population. How many vertebrate species can double their numbers in one year? Surely few, except for some fishes and a few birds that brood large clutches.

Out of curiosity, I went through all of the records for increases to see whether there are other years with remarkable recoveries and there are 7, including this year. The rate of increase data, represented by the number for the following year divided by the previous year, are as follows:

Years Increase
2000-2001 3.3
2004-2005 2.7
2009-2010 2.1
2013-2014 1.7
2014-2015 3.5
2017-2018 2.4
2023-2024 2.0

As you can see, the 2.0 increase from 2023 to 2024 is in line with increases (1.7-2.7) that have occurred 5 times in the past.

Following that, I checked the spreadsheet I maintain of all the weather and other conditions that might moderate population growth. That revealed there were negative growth indicators for all the low years (droughts, low summer temperatures, etc.) and various degrees of positive growth conditions (near average temperatures and precipitation) in all the following years. In fact, the temperatures and precipitation were close to the long-term averages for the entire growing season for 5 of the years in which the populations increased. Negative years do follow negative years and that has been more common since 2010 than earlier in the record (none prior to 2010 and 5 since 2010). That may say something about greater instability in weather patterns during the growing season since 2010. However, for now, we should put that idea on the watch list.

A takeaway here is that monarchs demonstrate resilience over and over again. Weather knocks them down, but spectacular recoveries are the rule if negative conditions during one year are followed by favorable conditions for population growth. As some of you may recall, I wrote a text for the Monarch Watch Blog that summarized the data that speaks to the three r’s (resilience, redundancy and representation) that are at the core of the Species Status Assessment (SSA). That document is prepared and used as the basis for determining whether a species should be regarded as threatened or endangered. My comments were in reference to the SSA prepared in 2020 but seem relevant now that we are dealing with a new SSA.

*There is one more thing to tell you about the 1.79hectare measurement. It is close to the three- and five-year running averages, which are 1.98hectares and 2.18hectares respectively.

Reference

Taylor, O. R., 2023. The species status assessment (SSA) and the three r’s. Monarch Watch Blog.
monarchwatch.org/blog/2023/10/13/species-status-assessment-and-the-three-rs

Addendum

If you go through the updates I wrote for the Monarch Watch Blog from March through June, you will see that I was really high on the possibility that the recovery this year could be the best ever. It wasn’t. Something happened during late May and early June that limited the reproductive success of the first generation in the Upper Midwest and therefore the size of the second generation that reached maturity in July. That, in turn, limited the size of the third/migratory generation and ultimately the size of the overwintering population.

So, what happened? Probably too much rain and too many days with unfavorable conditions for egg laying in the Upper Midwest, the region that produces the majority of the monarchs that arrive at the overwintering sites. The foundation for this interpretation was outlined by Myron Zalucki and Wayne Rochester in a chapter in The Monarch Butterfly: Biology and Conservation (2004). These authors pointed out that weather which limits egg laying results in a reduction of the total number of eggs laid during a lifetime. In other words, female monarchs don’t fulfill their full reproductive potential if egg laying is significantly delayed and that limits the number of offspring and the size of the next generation. This interpretation deserves a follow up, but the outcome is similar to a reduction in population growth that occurred following a long rainy period I tracked in Ontario a number of years ago. Demography isn’t easy and it becomes really difficult when events that occur over a few days, or a week or more, have a big impact on mortality or reproductive success.

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USFWS Proposed Rule: Thoughts and Implications

22 January 2025 | Author: Kristen Baum

monarch

We have been receiving questions about our thoughts related to the U.S. Fish and Wildlife Service (USFWS) proposed rule to list the monarch butterfly as threatened 4(d) under the Endangered Species Act, as well as what the implications are for Monarch Watch programs. We provide our responses to both questions below, as well as an overview of the listing process and proposed rule.

Thoughts about the Proposed Rule
One topic we have been thinking about is the limit of 250 or fewer butterflies placed on scientific research and educational activities. Monarch Watch has several programs to support our education, conservation, and research mission that mean we currently go above that limit, and that would likely apply to other organizations and individuals as well. For example, we have supported a community-science tagging program since 1992, and some of our taggers regularly tag more than 250 monarchs per year, including some organizations and groups that host tagging events. We also provide educational resources and programs that emphasize the monarch life cycle through the inclusion of monarchs in classrooms and other educational settings, and at in-person events. The research programs of individual researchers, including my own, would also typically exceed that limit, especially if the research requires maintaining a colony of monarchs. At the public hearings on Jan. 14 and 15, the USFWS emphasized that it is possible these activities could continue, but a permit would be needed. An alternative approach to permits would be to increase the number of monarchs included in the exemption for specific activities or to completely exempt certain activities. These alternative approaches would be more likely to ensure these activities continue without additional regulatory constraints.

Another consideration is the section about vegetation-management activities when monarchs are not present. This section of the proposed rule presumably applies to activities not already provided with an exemption. Exemptions are included for “habitat restoration and management activities, livestock grazing and routine ranching activities, routine agricultural activities and conservation practices, fire management, silviculture and forest management, [and] management of habitat on residential and other developed properties.” This section of the proposal might influence milkweed and nectar plant recommendations for settings where management of milkweed and nectar plants may be needed during the growing season when monarchs are likely present. Some of our favorite nectar plants can be on the weedy side and require some work to keep them in their place in garden settings. Many of our milkweed species, including common milkweed, spread via underground rhizomes, so we often recommend planting them in locations where one can limit spread beyond the intended location, especially in urban areas, such as by mowing around the perimeter of the milkweed’s designated planting area.

It is also important to think about what is included or could be included in the proposed 4(d) rule that will make a positive difference by adding more to monarch-conservation efforts than what is already being done.

For example, our Monarch Waystation Program is approaching 50,000 registered habitats after almost 20 years. We also distributed 100,000 free milkweed plants last year. However, we are still losing more monarch habitat each year than we are gaining through these efforts and others. We need to register 50,000 Monarch Waystations every year (or every few months!) instead of every 20 years, and we need to distribute 1 million or more milkweed plants each year. [For anyone who is interested, we are currently accepting applications for our two free milkweed programs, including one program for schools and educational non-profits and another for restoration sites.] We need to figure out how to do more.

We also need to figure out how to get more people involved in monarch-conservation efforts. There are many people dedicated to this mission already, from creating habitat, to participating in community science projects, to raising awareness about monarch-conservation concerns with friends and family. The exciting thing about monarchs is there is something that everyone can do to help them; we just need to figure out how to get everyone involved.

Implications of the Proposed Rule for Monarch Watch Programs
None of the actions included in the proposed rule will take effect until after the USFWS decides whether to list the monarch butterfly. The 90-day comment period is open until March 12, 2025, after which the USFWS will evaluate the comments received and any other relevant new information. The final rule will be posted within a year (by December 12, 2025), and rules typically become effective 30 days after posting. That means that there are no implications for Monarch Watch programs at the present time. However, depending on what exemptions are included in a final rule, it is possible that Monarch Watch may need to modify some of our programs or obtain permits to continue some of our activities, including our education, conservation, and research programs, with some specifics described in the previous section. It is also possible that people and organizations that host events or activities associated with these programs may need permits, such as those that host tagging events or that regularly tag more than 250 monarchs. Some of these possibilities will depend on the wording used in the final rule and the interpretation of that wording, such as what the phrase “one location or facility” means as it relates to the 250-monarch limit.

Overview of Listing Process and Proposed Rule
The USFWS announced a proposed rule on Dec. 10, 2024, to list the monarch butterfly as threatened under the Endangered Species Act, including a 4(d) rule.

“Threatened” is defined as “likely to become endangered in the foreseeable future throughout a significant portion of its range,” and “endangered” is defined as “in danger of extinction throughout all or a significant portion of its range.”

If the proposed rule had been an endangered listing, there would have been an automatic set of prohibitions. A threatened proposed ruling with an accompanying 4(d) rule allows the USFWS to modify or exempt some prohibitions based on conservation and management needs identified specifically for the monarch. It is also important to note that this is a proposed rule. There is a 90-day comment period that will end on March 12, 2025. A final rule won’t be posted until up to a year later (by Dec. 12, 2025, unless there is an extension), and then rules typically become effective 30 days after posting.

The USFWS reached its decision based on a Species Status Assessment (SSA) for the monarch. An SSA is a risk assessment based on available information and considers both the current status of the species as well as expected future status based on possible scenarios. An SSA is based on the “3 Rs,” which are resiliency, redundancy, and representation, or collectively the likelihood a species can maintain wild populations.

There are two main monarch populations in the U.S., including the eastern migratory population and the western migratory population. The eastern migratory population occurs east of the continental divide and migrates from as far north as southern Canada to overwintering sites in central Mexico each year. The western population occurs west of the continental divide and overwinters along the coast of California. Estimates of population size for the eastern migratory population are based on estimates of the area of trees covered by monarchs, whereas estimates of population size for the western population are based on counts of individual monarchs at overwintering sites located along hundreds of miles of California coastline. For example, the eastern migratory population size was recorded as 0.9 hectares last overwintering season, which was the second-lowest population size on record. To put that in perspective, the highest population size based on current methods was recorded in 1996 at more than 18 hectares. Previous research has suggested there are approximately 21.1 million monarchs per hectare, so there were less than 19 million monarchs last year compared with more than 380 million in 1996. The western migratory population size is much smaller, with counts ranging from less than 2,000 to more than 1.2 million. Based on the SSA, the USFWS estimates that the eastern migratory population has declined by approximately 80%, with an extinction probability of 56% to 74% by 2080. The USFWS estimates the western population has declined by more than 95% since the 1980s, with an extinction probability of more than 99% by 2080.

When the proposed rule was announced, the 4(d) section was what many of us read first. In it, the USFWS identifies the need to increase the availability of milkweed and nectar plants, to protect and enhance overwintering habitat, to reduce the negative impacts of pesticides, and to maintain public support for monarch conservation. The USFWS also emphasizes the importance of people in shaping current conservation efforts and indicated its intent with the proposed 4(d) rule is to incentivize voluntary efforts.

The way that can be seen in the proposed 4(d) rule is that activities may continue that do not result in conversion of native or naturalized grassland, shrubland, or forested habitat, and that includes allowing for the removal of milkweed and nectar plants. The USFWS includes exemptions for “habitat restoration and management activities, livestock grazing and routine ranching activities, routine agricultural activities and conservation practices, fire management, silviculture and forest management, management of habitat on residential and other developed properties, and vegetation management activities when monarchs are not present.” The explanation for this approach is that the USFWS expects any localized removal of milkweed and nectar plants would be outweighed by the overall addition of milkweed and nectar plants at larger scales. The USFWS also mentions this is meant to reduce the fear of regulation by private landowners who could remove milkweed from their land now, prior to the final rule, fearing potential future regulatory constraints. The focus is on incentivizing voluntary efforts, especially given how extensive and successful voluntary efforts have been since the petition to list the monarch was submitted in 2014.

The USFWS also indicates it wants to maintain people’s interactions with monarchs. Where this can be seen in the proposed 4(d) rule is the exemption of small-scale collection, possession, captive-rearing, and release of monarchs. “Small-scale” is defined as 250 or fewer butterflies. That same 250-or-fewer number is applied to scientific research, educational activities, and the sale of captively reared monarchs.

The USFWS also provides an exemption for the possession of dead monarchs and monarch mortality due to vehicle strikes.

Critical habitat is also designated as part of the proposed 4(d) rule. The critical habitat designation identifies specific areas that are critical for the conservation of the species and may need special management or protection. There is some confusion over what that designation means. Critical habitat only affects federal agency actions, including activities funded by federal agencies or that require authorization by federal agencies, such as permits or licenses. Activities by private landowners are not affected unless federal funding or permitting is involved. In the proposed rule, critical habitat is focused on overwintering areas used by the western monarch population.

Another area of interest is potential limits on the use of pesticides. The USFWS includes specific areas where it seeks additional information and input, and that includes an extensive section seeking public comment on how to address pesticide use in the 4(d) rule.

We are in the 90-day comment period, which ends on March 12, 2025. For people or organizations thinking about providing comments, it is important to remember that the USFWS is required to base decisions on the best scientific and commercial data available, so consider how to provide an effective comment that can be used to inform the 4(d) rule.

Additional Reading from Monarch Watch
Monarch Listing Announcement Expected Next Week
Species Status Assessment and the three r’s
The pending decision: Will monarchs be designated as threatened or endangered?
Why there will always be monarchs
Monarchs now ranked as ‘endangered’ in Canada


Photo by Damien Campbell on Unsplash

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Monarch Listing Announcement Expected Next Week

26 November 2024 | Author: Kristen Baum

monarch

The monarch butterfly was petitioned for listing under the Endangered Species Act in August 2014. The United States Fish and Wildlife Service (USFWS) issued a “warranted, but precluded” decision in December 2020, which designated the monarch as a candidate species until a final decision is made. The USFWS is expected to announce that decision, likely as a proposed rule, by Dec. 4, 2024. There are three possible outcomes, including not warranted for listing, threatened, or endangered. An endangered proposed ruling would involve an automatic set of prohibitions, whereas a threatened proposed ruling would likely include a proposed 4(d) rule to modify or exempt some prohibitions based on monarch-specific conservation needs. A public comment period, typically 60 days, will follow the proposed ruling. The USFWS will issue a final rule within twelve months after the end of the comment period.

A recent example of a proposed rule is for the regal fritillary, which includes a proposed endangered listing for the eastern regal fritillary (the eastern subspecies) and proposed threatened listing for the western regal fritillary (the western subspecies), including a 4(d) rule for the western regal fritillary. The comment period closed on Oct. 7, 2024, and you can view the comments that were submitted. You will notice that the proposed 4(d) rule for the western regal fritillary allows for routine livestock operations and other activities, but specifies blade heights for brush control, return intervals for prescribed fire, etc. Many of the submitted comments focus on the implications of these specifications for geographic locations and contexts, including best management practices.

Reviewing the comments for the regal fritillary proposed rule may be helpful for those who plan to provide comments about a proposed ruling for the monarch. There is also a document on “Tips for Submitting Effective Comments” posted by the Forest Service on Regulations.gov. Some important points from that document are 1) state the issue(s) within the rule that you are commenting on, 2) provide clear and concise comments including, 3) include pros, cons, trade-offs, examples, explanations, alternatives, etc., when relevant, 4) include a description of your background and qualifications to provide context for your comment(s), and 5) a well-written comment may be more effective than many form letters. Examples of how comments are addressed by the USFWS in final rulings can be found on the Federal Register, such as the final rule for the silverspot butterfly.

Regardless of the outcome of the listing process, we know that there continues to be cause for concern about the monarch population even with numerous ongoing voluntary conservation efforts. We need to do more to support monarchs. That means increasing the amount of monarch habitat we are creating each year, enhancing existing habitats to increase their value for monarchs, and decreasing the amount of monarch habitat that is lost each year. There are many groups and organizations supporting current efforts, but we need to expand that network to include even more people.

Join Monarch Watch in creating habitat to support monarchs and their spectacular fall migration. Please share information within your communities about creating Monarch Waystations. Encourage people, schools, and other organizations to apply to our Free Milkweeds for Schools & Educational Non-Profits and Free Milkweeds for Restoration Projects programs. If you are interested in sponsoring free milkweeds to increase the number we can give away, please reach out to let us know as we are currently in the process of working with our partner nurseries to set grow goals for 2025. The Milkweed Market will open in January 2025 for ordering milkweeds for spring planting.

Additional Reading about the Upcoming Proposed Rule Announcement
Monarch Joint Venture: United States Endangered Species Act Status
Iowa Monarch Conservation Consortium: What if the monarch butterfly is listed as threatened? Understanding options with 4(d) rules
Farmers for Monarchs: ESA Listing Decision Toolkit


Photo by Ryan Balter on Unsplash

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Join the 29th annual Symbolic Monarch Migration!

4 September 2024 | Author: Monarch Watch

Symbolic Monarch Migration logoEvery year, thousands of paper monarchs fly south to Mexico alongside the real monarchs, though with a slightly different pathway. Monarch butterflies only weigh about 0.5 grams, and these paper ones are just as light. The paper butterflies are part of the Symbolic Monarch Migration, which connects students in Canada, the U.S., and Mexico to teach them about monarch butterflies and their annual migration. Students from Canada and the U.S. send paper butterflies to students in Mexico in the fall and learn all about the migration. The monarchs are brought to students in Mexico, along with letters from other students and lessons on monarch conservation. The monarchs are sent back north in the spring, ending up in different locations like the real monarch migration. Students learn not just about monarchs, but cooperation across countries, and it is a great opportunity to make new connections. Since the program took flight in 1996, more than 13,000 groups have participated, and more than half a million paper butterflies have followed the monarchs on their amazing long-distance migration. Just last year there were over 25,000 participating youth from the U.S. and Canada.

The Symbolic Monarch Migration has been coordinated by Ms. Susan Meyers since 2018. Ms. Meyers is one of our long-time Monarch Conservation Specialists. She is supported by a team of volunteers with Monarchs Across Georgia (MAG) which is a committee of the Environmental Education Alliance of Georgia. Ms. Meyers has been an advocate for monarchs ever since she visited the Mexican overwintering sites in 2003. Now, she uses her experience to facilitate educator workshops using the Monarchs & More curriculum, as well as incorporating community science projects like the Monarch Larva Monitoring Project, Journey North Tracking, Project Monarch Health, and the Monarch Watch tagging and Waystation programs. She has organized visits to the overwintering colonies since 2004 and initiated the Mexico Book Project to bring books written in Spanish to schools near the sanctuaries. She is currently a Georgia Master Gardener, Master Naturalist, and a certified Pollinator Steward with the Pollinator Partnership. Ms. Meyers was awarded the Conservation Partner Award for her work with monarchs at the 2015-16 Southeast Regional Director’s Honor Awards Ceremony, and she continues to play a big part today.

Ms. Estela Romero is another critical member of the Symbolic Monarch Migration team. As a certified English teacher living in Mexico, she acts as a key link for many collaborative programs. The Symbolic Monarch Migration was at first just an exchange of paper butterflies between students, but when Ms. Romero began delivering the butterflies to students in Mexico, she started teaching environmental lessons at the same time. Many of these students live in remote areas without good internet access. Ms. Romero brings together students in Mexico with those in the United States and Canada through her blog posts and school visits and expands her lessons beyond just monarchs. In total she visits over a thousand students in Mexico every year. She also has submitted countless reports to Journey North on the activity of monarchs at the overwintering colonies, documenting significant colony activity, weather events, and more through her writing and photos. Her contributions to monarch conservation have been invaluable.

Here’s how to get involved with the Symbolic Monarch Migration:

Purchase a Passenger Ticket

Passenger Tickets help cover the cost of the program, including school visits to Mexico to deliver the butterflies and provide conservation education. There should be one Passenger Ticket per Ambassador Folder, which is intended for roughly 30 participants. If you sign up as an Early Migrant, the fee is reduced from $20 to $15. Early Migrants must purchase their passenger ticket and mail their Ambassador Folder and life-sized butterflies by September 30th to receive the discount. You can purchase passenger tickets online at the EE Alliance’s Website. Be sure to visit the Symbolic Migration webpage for the full details and read through the Team Leader Packet for the 2024-25 season.

Supporting Activities

Check out the educational activities listed on the Journey North webpage! You can use the activities as a tool to help teach students about not just monarch butterflies, but also about ambassadorship and cooperation across countries. The list is not meant to be exhaustive, but to provide ideas on how best to approach the topic with students. Journey North also has tracking maps for monarchs and links to many other great resources.

Create an Ambassador Folder

Use one of the templates provided in the leader packet to create an Ambassador Folder or create a completely original design! Ambassador folders will hold the paper butterflies and letter sheet. Each Ambassador Folder should be personalized with decorations or a message to the students in Mexico. These folders will stay with the students in Mexico.

Make Life-Size Butterflies

You have access to a template in the leader packet to create paper butterflies for all the participants in your group. You may want to fill in information digitally and leave just the name blank for students to fill in. Please do not laminate them. These butterflies will travel to Mexico, but when they are sent north in the spring, they may not return to the same students, just as monarch butterflies may not fly the same path in the fall and spring. Leaders of each participating group should use the information on each butterfly to inform team leaders from other groups about where their butterflies ended up.

Fill out the Letter Sheet

Fill out the blanks in the letter sheet provided in the leader packet. Mark where you live and draw an arrow to show your monarchs’ migration path. You can also choose to add an extra group photo, postcard, or letter (letters should be written in Spanish).

Mail the Monarchs!

Put everything into the Ambassador Folder and mail your monarchs to the address below. Don’t forget to include a copy of your Passenger Ticket. Do not mail payments to this address. Payments can be made via credit card online or mailed to the address included on the online form.

Send a Monarch to Mexico!
c/o Symbolic Migration
1497 Candleberry Court SW
Lilburn, GA 30047 USA

Learn more about monarchs using the provided resources once you’ve sent your paper monarchs! They will be delivered to students in Mexico from November to March. You can check if your butterflies have arrived, as well as see the blog posts by Ms. Romero at the Symbolic Migration’s school visit webpage. Butterflies will return to the U.S. and Canada from April to May. These butterflies will not be the same ones you sent. Please contact the team leaders listed on each paper butterfly, as their students will be waiting to hear where their monarchs ended up.

Summarized Timeline

September 30th: Deadline for Early Migrants, including reduced fee.

October 18th: Final postmark deadline for mailing folders.

November-March: Butterflies are delivered to Mexico. See the website for updates and more monarch news.

April-May: Butterflies are sent back north to students. Please contact other team leaders directly to share news on where their butterflies landed.

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Monarch Population Status

20 August 2024 | Author: Chip Taylor

Tagging will tell

As you may recall, I posted three reports on the development of this years’ monarch population from 1March to 10 June to the Monarch Watch Blog (see below). I stopped reporting in early June due to the lack of meaningful monarch observations that can be used to track how the population is developing. There is weather data to work with, but the temperatures seemed ok so I ignored the rainfall which had already been excessive. That was a mistake. Rainfall, if it persists for days – and it did over wide areas – can make a difference by limiting the number of hours and days during which females can lay eggs. In other words, it can reduce realized fecundity because there are only so many days in a female’s life and there is no way to fully recover from time lost. This idea is covered in a paper by Zalucki and Rochester (2004). The overall effect of delayed and reduced oviposition in June would be a reduction in the number of second-generation adults that emerge in July, and that, in turn, could result in a reduction of the number of offspring that become third and fourth generation migrants in August and September.

Most of the monarchs in each migration originate from breeding areas north of 40N latitude – imagine a line from St Joseph, Missouri to Philadelphia, Pennsylvania. We have learned from recovered tags that timing of departure and geographic origin of each migrant largely determines whether it will reach the overwintering sites in Mexico. It’s important to be early, or at least on time, relative to the timing of migrations under average weather conditions. This migration could be late. The “tagging will tell”, but to assess lateness, we will need taggers to extend their tagging efforts as late as possible into the migration.

As most of you know, the size of the last generation is a function of the number of eggs laid from about 20 July to 5-10 August as well as the quality of the milkweeds and the weather. The adults from that oviposition typically emerge throughout August into early September. This year the emergence could be delayed due to a cold front that moved into the northern breeding area starting on the 4th of August. Overnight temperatures dipped into the 50s in many areas limiting the number of hours for larval development. It’s possible that development has been pushed back by at least 10 days. This means that monarchs that would normally be on the wing in early to mid-August are still larvae or pupae at this writing (19 August). Hopefully, that’s the case, and we are simply dealing with a late emergence and migration.

This has happened before. The temperatures in August 2004 in Minnesota and the Upper Midwest were the lowest in the 30year record. The migration was extraordinarily late and the number reaching Mexico was lower than expected. Again, tagging will tell if that outcome is duplicated during this migration.

Oh, and there is one more thing. Significantly higher-than-average September temperatures have occurred in 17 of the last 30 years and in 13 of those years, the population has decreased from that of the previous year. These high temperatures also delay migrations. Elevated September temperatures have occurred in 6 of the last 8 years and are becoming the new normal. Should such conditions occur again this September, those could also reduce the number of monarchs arriving at the overwintering sites.

References
Taylor, O. R. 2024. Monarch population development in 2024: Part 1.
monarchwatch.org/blog/2024/04/02/monarch-population-development-in-2024-part-1

Taylor, O. R. 2024. Monarch population development in 2024: Part 2.
monarchwatch.org/blog/2024/05/23/monarch-population-development-in-2024-part-2

Taylor, O. R. 2024. Monarch population development in 2024: Part 3.
monarchwatch.org/blog/2024/06/28/monarch-population-development-in-2024-part-3

Zalucki, M.P. & Rochester, W.A. (2004) Spatial and temporal population dynamics of Monarchs down-under: lessons for North America. The Monarch Butterfly: Biology and Conservation (ed. by K. Oberhauser and M. Solensky), pp. 219–228. Cornell University Press, Ithaca, New York.

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Monarch population development in 2024: Part 3

28 June 2024 | Author: Chip Taylor

The expectations were low at the beginning of this breeding season. The overwintering numbers were the second lowest in the record (0.9ha), and it was reasonable to expect low numbers of monarchs to return from Mexico in March. It was easy to envision that, like in 2013 (the lowest population recorded at 0.67ha), it would take several years for the population to recover. As expected, the early numbers of returnees were low, but they were early and that was a positive sign that the population might recover. That was followed by more positive sign of recovery in Part 2 and even more in the text that follows. At this date in the middle of June, it seems safe to say that the numbers indicate that the growth of the population this year is comparable to that of most populations since 2015. The recovery to this point is nothing short of extraordinary and is a testament to the monarch’s resilience. The question now is – what’s ahead?

We are 3.5 months into the breeding season at this writing (15 June). By my calendar, the breeding season starts on the first of March, the date the first monarchs returning from overwintering in Mexico cross the border into Texas. The breeding ends progressively southward in the fall as the declining angle of the sun at solar noon approaches and drops below 57 degrees. That means that reproduction all but ceases in the vicinity of Winnipeg (50N) in the first week of August but not until the first week of October at the latitude of San Antonio, TX. Since most of the monarchs that overwinter in Mexico originate from north of 40N, for the purpose of analysis, I use the first week of September as the end of the breeding season. So, in total, the breeding season is effectively 6 months in duration (7 months if we want to be more inclusive) and the monarchs are more than halfway through it with 2.5 months to go. This report is therefore all about the development of the population to this point as well as what we might expect in the next 2.5 months. In addition, because the migration begins at 50N in early August, and overlaps the breeding season until the first week of October, I will say a few words about what to expect during the migration.

Directional/migratory flight for this season has stopped based on our analysis of the link between day length and directional flight. That means colonization has stopped, it’s over and all sightings from here on are of monarchs that have already reached their northernmost latitude and easternmost longitude. So, how effective has this recolonization been and how does this year compare with others? There are several ways to judge these recolonizations. The spatial distribution is one feature, the numbers of sightings are another and the timings of the recolonizations are another. We might also look at the longitudinal distribution of all sighting through the colonization period. To all of those considerations, we can ask whether temperatures or other weather conditions influenced colonization. Let’s start with mapping.

Mapping

First sightings recorded by Journey North 11 June 2024.

map1

First sightings recorded by Journey North 13 June 2018.

map2

These two maps look similar. In 2018, there were more sightings in Manitoba but fewer in the Maritimes than in 2024. The more important comparison is the Upper Midwest where there appear to have been more first sightings in 2024. But, it’s hard to tell. We have to dig deeper. I’ve used 2018 to compare with 2024 since the population in Mexico in that winter was 6.05 hectares, the largest population since 2006. So, the similarity is promising indeed. However, if one scans through all the maps of past years, they all look very similar – until you get back to the maps for 2013, 2014 and 2015 all of which show poor recolonization. This was the time of the previous low mark in the population with only 0.67ha measured in 2013.

First sightings recorded by Journey North 13 June 2013.

map3

The recolonization in 2013 was numerically the lowest and latest in the first sighting record and it foretold the overwintering number. One point to make here is that the first sightings map and numbers for 2024 are far better than those of 2013-2015.

Numbers of sightings from 1 March through 9 June

The numbers that follow are rough. The number of people reporting first sighting has increased in recent years and I did not scan the records to eliminate duplicates or records west of the Rockies. Nevertheless, the numbers are of interest since they show the low recolonization in 2013 (552) and a rough similarity between 2018 (1739) and 2024 (1397). If we add one more year, for example 2021 with 2429 sightings and 2.83 hectares at the end of the season, it becomes clear that the number of sightings is only part of the story.

If we refine the numbers a bit by limiting the counts to the total sightings in the summer breeding regions north of 40N, we get the numbers summarized in Table 1. Again, we can see some similarities and differences of interest.

The number for 2013 (107) is low as expected and 2024 is similar to a number of years when we just consider the total through 9 June (2019, 2018, 2017). If we compare all sightings north of 40N, 2024 is similar to both 2022 and 2018.

table1

There are two points that can be made here. First, the first sightings in 2024 are comparable in number to those of other years with relatively good overwintering numbers and second, they are far better than expected for a population with the second lowest number of wintering monarchs in the 30year record – and much better than from 2013-2015.

Distribution and timing

The connection between the distribution and timing of first sighting is summarized for 2013, 2014 and 2018 in Table 2. The overall pattern of colonization from west to east is similar for all years. The percentages of the first sightings before 21May were low for both 2013 and 2014 but much higher for 2018 (23%) and even higher for 2014 (55%). Low numbers and percentages in the first 20 days of May are associated with low fall migrations while the opposite hold for high numbers and percentages. This indicates that the timing and number of females starting the second generation has a role in determining the size of the third generation that becomes part of the migration. An early start to the second generation could, under the right conditions, lead to a fourth generation in some locations, and that could happen this year.

Table 2. Distribution of first sighting in 10-day intervals across longitudes quadrants (Q) from west to east for 2013, 2014 and 2018. The fourth quadrant (70W-65W) is not shown due to the low number of sightings. The timing and number of first sightings is critical. Low numbers and percentages in the first 20 days of May are associated with low migrations while high numbers sighted during the first 20 days of May usually signal large numbers of fall migrants. The third quadrant (Q3) tends to be colonized later than the first two quadrants as a result of the general movement of the spring migration to the northeast.

table2

Weather

Monarch population development is largely a function of weather conditions that occur during the breeding season. That said, the upper limits to the size of the population are determined by the abundance, distribution and quality of the milkweed and nectar sources available.

With temperatures and precipitation, it is common to work with deviations from long-term means. However, a 4F deviation can be favorable or unfavorable to monarch development depending on the base. Generally, positive deviations in the spring favor rapid development of eggs, larvae and pupae, but, as I have pointed out elsewhere, high March temperatures can enable monarchs returning from Mexico to migrate too far north too soon. In this case, higher temperatures can have different effects on immatures and adults. However, during the migration northward in May by first generation monarchs, because the seasonal means are low, elevated temperatures during that month benefit the development of immatures and the northward migration by first generation adults. This May the mean temperatures favored growth and migration for the entire breeding range north of 40N (Table 3). These conditions contributed to an earlier colonization of the northern latitudes than seen in many years and an earlier start to the second generation.

table3

Analysis

The dive into the first sightings data to create these reports, has given me a deep appreciation of the value and utility of this 25-year record. I’ve identified two statistically significant trends in these data.

First, May temperatures in Minnesota are correlated with the percent of first sightings that occur in the last 10-day interval in the 40 days from 1 March through 9 June, p<0.0001. In this case, it is clear that low May temperatures delay recolonization while high temperatures enable earlier recolonization. This result has implications for the recolonizations of the highest latitudes and eastern Canada. In years during which the May temperatures in Minnesota or the Upper Midwest are low, it is likely monarch numbers throughout the breeding season will also be low throughout Canada (Taylor, 2023). Second, the total first sighting of monarchs that return from Mexico recorded in March and April in Texas and Oklahoma is correlated with the total first sightings of first-generation migrants recorded north of 40N before 10 June, p<0.0001. This means the number of first sightings of returning monarchs are a reasonably good predictor of the size of the first generation.

Outlook

The weather conditions from June through August strongly influence the development of the second and third generations. In the Upper Midwest, the source of about 70% of the monarchs that reach Mexico (Taylor, et al., in prep), mean temperatures in excess of either +3F or -3F in July or August have a negative impact on population growth. High temperatures, especially if combined with low soil moisture, likely result in a reduction of lifespan, egg laying and larval survival, in effect, a reduction in what is known as realized fecundity. Low temperatures allow females to lay eggs over an extended interval but delayed development can expose immatures to predation for a longer interval and lengthen overall generation length. The overall effect is an older age to first reproduction for the next generation which would also tend smaller. These results are clear in the weather records for the last 30 years. The summers in 2004 and 2009 were too cold and the high mean temperature in July of 2012 (+5.3F) combined with drought conditions reduced the size of the migratory populations in those years.

The temperatures in the Upper Midwest this June have been close to the long-term average. Rainfall has been excessive in some areas of the Dakotas, Iowa and Minnesota which could have a negative impact. Excessive rainfall or intervals of more than three days that are too cold for feeding, mating and egg laying surely have a negative impact on growth but is difficult to assess.

The July forecast for the Upper Midwest is not as favorable and could be a problem since the mean temperature is projected to be +3F above the long-term average. This means the size of the third generation could pivot on the accuracy of this forecast. Temperatures substantially greater than +3F, could reduce the size of the fall migration. The conditions in August are seldom extreme, although there is often a carry-over from the conditions in July. July is crucial. We need to follow the conditions closely.

Once past July, the focus shifts to the temperatures and precipitation in August since they determine both the development of the third generation and start of the migration.

In recent years, high temperatures during the first 6 weeks of the migration from late August through September have slowed the pace of the migrations. These conditions are associated with lower-than-expected numbers of monarchs reaching the overwintering sites and that scenario could develop this year as well.

Droughts in Texas and Oklahoma in late September and October are always a concern. Last fall the extreme drought that extended from Oklahoma through most of Mexico had a strong impact on the number surviving the migration (Hobson et al., 2023). At the moment, drought is not widespread in Texas and whether a drought will develop by October is unclear, but it is something to watch for. Similarly, the conditions in Mexico are a concern since the drought that developed last year still persists along most of the path monarchs take to reach the overwintering sites.

Overall, the outlook is mixed. If the weather conditions in the Upper Midwest remain close to the long-term average through August, the migration could represent a remarkable recovery from a low overwintering population and a relatively small number of monarchs returning from Mexico. Further, if conditions are favorable through the migration, there is the possibility that the numbers this winter could represent the strongest recovery in the record. But, reaching that lofty goal will surely be out of reach if the drought conditions in Mexico persist into October.

References

Hobson, K., O. Taylor, M.I. Ramirez, R. Carrera-Treviño, J. Pleasants, R. Bitzer, K.A. Baum, B.X. Mora Alvarez, J. Kastens, and J.N. McNeil. 2023. Dynamics of stored lipids in fall migratory monarch butterflies (Danaus plexippus): Nectaring in northern Mexico allows recovery from droughts at higher latitudes. Conservation Physiology 11(1): coad087. https://doi.org/10.1093/conphys/coad087

Taylor, O.R, 2023. Monarch Watch Blog. Monarchs: Reaching 50N and beyond.
https://monarchwatch.org/blog/2023/07/09/monarchs-reaching-50n-and-beyond

Taylor O.R. Jr, Pleasants J.M., Grundel R., Pecoraro S.D., Lovett J.P., Ryan A., and C. Stenoien. (In prep) Geographic and temporal variation in monarch butterfly migration success.

Acknowledgements

This report would not have been possible without the long record of first sightings reported to Journey North (University of Wisconsin–Madison Arboretum) under the direction of Elizabeth Howard and later Nancy Sheehan. Janis Lentz assisted with the tabulation of the first sightings and Jim Lovett assisted with the layout and posting of this text.

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