The monarch decline: when did it begin?

Monarch Watch began with a simple tagging program in 1992 followed, in the early years of our program, by attempts to educate the public about monarch biology and research. More recently, our emphasis has been on monarch conservation. The conservation outreach began to increase in importance during the scramble to understand the consequences of the introduction of corn genetically modified to express the endotoxins of Bt strains* in corn tissues, one of which was airborne pollen. Corn pollen containing Bt toxins, when concentrated on milkweed leaves, had been shown to have the potential to kill developing monarch larvae**. During studies (1999-2001) to establish the seriousness of this problem, surveys of monarch production revealed that corn and soybean fields containing milkweeds produced MORE monarchs per acre than other common habitats containing milkweeds. At the same time, soy and corn genetic lines were being introduced, and progressively adopted, that were resistant to the broad spectrum herbicide known as Roundup (glyphosate). These genetically modified crop lines allowed farmers to spray their crops with Roundup to control weeds without damaging the crops. I began to write about this development with some concern in 2001, but the full impact of this technology became apparent when I received an email from a farmer in Nebraska in 2004. My response to this email has been buried among our archived monthly updates. We’ve reprinted this text below for those interested in how this new technology shifted our focus and outreach at Monarch Watch. The realization that the adoption of these genetically modified crops was likely to have an impact on monarch numbers led to the development of the Monarch Waystation program in 2005 and later the Bring Back the Monarchs program in 2010.

Adoption rates of Roundup Ready corn and soybeans increased rapid and milkweeds all but disappeared from these row crops in the Upper Midwest by 2006 (Fig 1). Monarchs numbers, as measured at the overwintering sites in Mexico, began to decline noticeably around the same time. If the decline in milkweeds in the Upper Midwest was the cause of the decline, we might expect to see that reflected in the tagging data in two ways 1) a decline in the success of taggers in the affected areas and 2) a shift in the proportion of tags applied each year within non-affected areas to the east. Data establishing whether either or both of these expectations/signals are present in the 1.5 million tagging records for the last 20 years will be presented at a later date.

Figure 1. Adoption of herbicide tolerant crops vs decline in monarch overwintering population

*Bacillus thuringiensis – https://en.wikipedia.org/wiki/Bacillus_thuringiensis
**Due to the subsequent adoption of corn lines that did not express the Bt endotoxins strongly in pollen and the dynamics of the shedding and concentration of pollen on milkweed leaves within and adjacent to corn fields, none of the Bt corn/monarch studies demonstrated that significant numbers of monarch larvae were exposed to and died from lethal does of Bt containing pollen.

The links in the original June 2004 article are broken but the links included here cover the same issues raised in the original text.

Roundup resistant weeds:

http://weedscience.org/summary/moa.aspx?MOAID=12
https://www.ars.usda.gov/ARSUserFiles/64022000/Publications/Reddy/Nandula-GRW12.pdf

Milkweed in corn and soybean fields.

Effects of Transgenic Crops on Milkweeds – by Chip Taylor, June 2004

How do transgenic crops affect the distribution and abundance of milkweeds?

In the 2001 Monarch Watch Season Summary (p59) I addressed the possibility that the widespread planting of Roundup Ready corn and soybeans could lead to the decline of the common milkweeds in much of the northern breeding area for monarchs:

“Almost unnoticed in this controversy has been the rapid adoption of herbicide resistant (transgenic) corn and soybeans by farmers throughout the Midwest. These crops are extolled for their value in weed control. Growers can plant these crops and then apply herbicides (principally Roundup) to control weeds without concern that the corn will be stunted or killed by the toxin. Cost of weed control is reduced but the potential downside for monarchs is the loss of milkweeds in these fields. One of the outcomes of the Bt corn study was the realization that 90% of the monarchs originate in the agricultural landscape (Taylor and Shields 2000). Further, the studies of habitat use by monarchs showed that although milkweed densities were low in row crops such as corn and soybeans, survival of monarchs in these habitats appeared to be higher than in non-crop areas. Thus, the milkweeds in corn and soybeans are important and their loss due to the adoption of herbicide resistant corn and soybeans could have an impact on the size of the monarch population. Studies of the distribution and abundance of milkweed in GMO and non-GMO crops lands are still needed.

The GMO technologies are here to stay and so are the controversies. The negative consequences associated with these crop varieties are potentially significant and it is unclear whether such effects can be anticipated or controlled.”

To my knowledge, no one has taken up the challenge of assessing the impact of transgenic corn and soybeans on the abundance of milkweeds.

My motivation for revisiting this topic was the following email from a grain farmer in Nebraska.

Sirs:

I am a grain farmer in Northeast Nebraska. I recently, purely by accident, came across your website. I was struck by the information that the common milkweed is the ONLY food of the Monarch larva.

I am concerned that the recent large use of Roundup ready crops (which I use), and the subsequent widespread use of Roundup herbicide (which I also use), had led to the virtual elimination of milkweed in fields and crops. As someone who has raised crops, I can personally attest to scarcity of the milkweed plant today compared to, for example, 20 years ago. Milkweed used to be a common weed in this part of Nebraska. Roundup is particularly effective in eliminating milkweed, since it works on the rootstock of milkweed.

Although I have always considered milkweed a rather troublesome “weed”, and have appreciated how modern herbicides have controlled it, I am concerned about the effect this might have on the monarch butterfly population. I consider the monarch a very beautiful insect, and have noticed that they appear to be scarcer than in years past.

Is there some advice I can get, as a grain farmer with economic considerations, to balance both my needs and that of the monarch? Has anyone ever done any research on this? I appreciate any advice you may have to give me.

Thank you.

David A. Wurdeman
Leigh, Nebraska

I have two reactions to this inquiry. First, growers should carefully examine the short term and long-term pluses and minuses associated with the use of Roundup and second we need to establish what can be done to restore milkweeds under a variety of conditions.

Living in Kansas (and knowing a number of farmers) I know that making a living at farming is difficult and often impossible. Were I a farmer, I would probably be using Roundup Ready corn and soybeans but then again, I might follow the lead of several local farmers who are not using GMO seed lines. As an outsider to this enterprise I can sit back and wonder if the long-term costs of the utilization of this GMO technology and herbicide combination is going to offset the shot term gains that have induced the majority of growers to adopt this system. What are these long-term costs? The most prominent issue is the evolution of herbicide resistant weeds. If you do a web search for herbicide/Roundup resistant weeds you will find a substantial number of references on this topic. In Argentina, an area with a temperate climate, at least 15 weed species have shown resistance to Roundup, including the common bindweed (Convulvulus arvensis) and dandelion (Taraxacum officinale), both abundant in North America

An argument offered by Monsanto is that such resistance is local and can be dealt with on a local basis because most weeds don’t spread that fast. While this might be true for some species, it probably doesn’t apply to these two and this interpretation underestimates how weeds are distributed on farm equipment. These are weeds we are talking about and they do get around the world. The similarity of the species composition of the crop field weeds in both the north and south temperate regions of the world is astounding. A further perusal of web sites on this topic reveals that experts suggest not using Roundup more than once a year on a field, a practice that is frequently violated, and that it should not be used in the same field for more than two years in a row. Again, this is a practice that is often ignored. Roundup resistant weeds seem to be in our future and no other “benign” herbicides seem to be on the horizon.

Soil quality is another issue. The long-term impact of the use of Roundup on soil quality is not yet clear. In the short run, the use of Roundup appears to be beneficial by reducing tillage, erosion, and carbon loss through carbon dioxide. However, there are concerns that the long-term effect of Roundup will be to reduce the number of soil microbes needed to either breakdown organic matter or to promote plant growth (mycorrhizal fungi). One also has to ask the question whether, at some level, weeds are beneficial. Although we all learn that weeds reduce crop production, and there are certainly plenty of studies to show this, low level contamination with weeds, if tilled under at some point, provide green manure and maintain texture and contribute to the organic matter in the soils. In the long run, a few weeds may be better for soil conservation than Roundup. Whatever the case, the practices adopted by most growers will be driven by short-term economics or perceived benefits rather than long-term considerations.

Cost of production is another factor to consider. If I were a farmer, I would want to know at least three things about a new seed line, performance (yield), cost of production (field preparation, seed cost, per-harvest inputs such as herbicides, and harvest issues such as lodging) and convenience/time -inputs. The performance data for conventional and transgenic soybeans available on several web sites indicate that yields per acre are similar for both types.

The differences, if there are any, are too small to justify adoption of the herbicide resistant lines. Cost of production may be an issue. These costs seem to vary sharply among locations and I haven’t been able to locate data from independent investigators on this point. Seed cost is higher for GMOs, but is coming down and may be offset by lower inputs. My guess is that much of the adoption of GMOs comes down to convenience and time. Spraying with Roundup requires less time, equipment, and equipment maintenance, and lower fuel costs than tillage, leaving more time for other tasks. This would probably make a difference to me. I’d tell myself I’d have more time for fishing but then I’d spend my Sundays writing these updates 😉

When I took ecology in graduate school 40 years ago, we learned that an average of 5,000 acres of “habitat” was lost to development each day. I was astounded by this figure but it made sense as I began to track the developments taking place in areas I knew well. The rate of loss is probably even greater today. Many species are declining due to a progressive loss of habitat and those species confined to special habitats, that are limited geographically, constitute a high proportion of the threatened and endangered species in this country. Monarchs are unique in that they are one of a relatively small group of insect species that breed in a large portion of the North American continent. Much of this breeding capacity is due to the ability of the common milkweed to invade disturbed areas, such as roadsides, railroad right of ways, power-line and gas-line cuts, pastures, and croplands. This plant is essential for the development of monarch larvae and the distribution and abundance of this single milkweed species, even though monarchs utilize 30 or more species of milkweeds over their entire range, accounts for about 90% of the butterflies that join the fall migration each year. An analysis of the distribution of milkweed containing habitats conducted at the time of the concerns about the impact of Bt corn on monarchs suggested that the majority of monarchs, perhaps 90%, originated from areas with intensive agriculture. This observation, together with formal and informal surveys of milkweeds in conventional corn and soybeans, lead to my concern that the rapid adoption of Roundup Ready corn and soybeans could eliminate much of the milkweed in the most productive breeding habitat for monarchs.

I’ve never been impressed by common milkweed as a competitor in crop situations. Although there are claims that the presence of milkweed depresses crop yields, and this may be true in the Red River Valley in Minnesota and Ontario and a few other situations, the densities of the common milkweed are usually too low (20-60 stems per acre) to be of much significance in this regard. Nevertheless, milkweed at these densities is of great value to monarchs. Larvae reared on milkweeds within fields appear to survive at a higher rate than in the field margins and roadsides perhaps due to the lower abundance of predators in these habitats.

Even if we are unable to persuade growers that it is in their interests to adopt non-Roundup Ready crops, to tolerate milkweed or to utilize management practices that are more milkweed friendly, we still need to find ways for growers to restore milkweeds in their field margins, roadsides, conservation set aside lands and wetlands. Here is a preliminary list of the some of the practices that could be adopted:

1) seed marginal lands, fallow lands, or set aside areas with common milkweed and butterfly weed (A. syriaca and A. tuberosa);

2) seed low areas and true wetlands with both common and swamp milkweeds (A. syriaca and A. incarnata);

3) grow milkweeds in gardens- if not common milkweeds because of a prejudice due to their reputation as weeds, then other milkweed species, such as the swamp milkweed, butterfly weed and tropical milkweed;

4) urge local (county) road crews to cut road margins once a year, either in late June or preferably toward the end of the season after the milkweed plants have seeded;

Milkweeds can be established by scattering seeds over areas that have been mowed and lightly disked or tilled as early in the spring as possible. To minimize competition with other species that will invade the seeded area, the sown area should be mowed close to the ground the next spring before growth starts. This practice will favor grasses and milkweeds and will minimize competition for light and nutrients.

Monarch Population Status

A message to all taggers

Hear ye! Hear ye! Taggers take note! What you have contributed to monarch science over the years has been incredible! Collectively, you have tagged well over 1.5 million monarchs in the last 26 years, from the front range in Colorado to the Maritime Provinces in Canada. Further, you have tagged from the beginning of the migration in the vicinity of Winnipeg in early August until the last monarchs cross the border into Mexico in November. It is an amazing record that continues to provide new insights about the dynamics of the monarch migration. Congratulations and thank you.

We are often asked why we keep tagging. We know where monarchs come from that reach Mexico, right? The answer is yes, we do, but tagging and recovery of tagged monarchs is about more than origins. It’s about patterns that tell us what areas of the country contribute most to the overwintering numbers. It’s about the flow of the migrations, that is, how the migration progresses from its start in Canada to its end at the overwintering sites in Mexico. It’s about the influence of weather on migrations and the impact of habitat loss. It’s about the sex ratios and mortality during the migration and it’s even about events that happened 7-8 months before the migration. We are in the process of analyzing over 1.3 million tagging records and more than 13,000 recoveries and, I can tell you, the tagging results have things to say about all these points and more. The amount of monarch habitat is changing along with the climate and it turns out that tagging is one way of monitoring these changes. So please keep tagging from the start to the end of each migration. Your data are of great value.

Some things are worth repeating

My pre-migration message this year leans heavily on the text from last year.

When it comes to estimating the size of the migration, each year is a series of experiments, with numerous hypotheses, during which I try to match what I know about monarchs with the progression of the seasonal conditions that influence both monarch behavior and plant growth. To make projections for each fall migration and overwintering population, I start with the numbers of monarchs measured at the overwintering sites in Mexico. Next, I focus on overwintering mortality, followed by the spring conditions as monarchs move northward from the overwintering sites to the milkweed areas in south and central Texas, and then the conditions in the South Region (TX, OK, LA, AR, KS) during the growth of the first generation in March and April. That is followed by attention to the conditions during the period from 1 May-9 June that allow, or don’t allow, first generation monarchs to reach the northern breeding grounds. Summer temperatures along with the seasonal distribution and amounts of rainfall are also in focus when estimating the fall and winter numbers. These stage and time specific assessments provide the context for a number of hypotheses or projections concerning the coming migration and the opportunities to tag monarchs each season. Sometimes I’m on the mark and sometimes I’m wrong. The point is to not only give those interested an idea of what to expect but to learn from my mistakes and few successes. Last year, I predicted a large population in the Northeast in general and for Cape May in particular. I was right on the money. However, I underestimated the impact of the drought that ranged from the eastern Dakotas through western Minnesota down through western Iowa. I also overestimated the production of monarchs in the rest of the Upper Midwest with the overall result that the overwintering population of 2.48 hectares was lower than the near 4 hectares I was expecting. These differences were reflected in the number of overnight roosts reported to Journey North through the migration and the relative success of taggers in the East and Midwest. Still, it was a great tagging season.

So, let’s see if I can do better this year. With respect to the Northeast, this should be another good season, although not as good as last year. In Canada, eastern Quebec will be down, but most of Ontario is on track to produce a substantial number of fall monarchs. The counts of monarchs per hour at Cape May will be lower this year, but will still be well above the long-term average. On the positive side, in the Upper Midwest, unless I’ve misjudged the situation once again, the migration should be the strongest since 2008 (a 5-hectare year) with the real possibility that the overwintering population could hit 5 hectares once again. Let’s see if I’m correct.

Good luck with your tagging and thanks to all of you for participating in our program. Please visit our Blog for updates as the season progresses.

If you plan on tagging this fall, please order your tags soon as they are going fast. Tagging Kits (item 121239) are available via the Monarch Watch Shop at shop.monarchwatch.org

Monarch Population Status 2/2

For monarchs every year is the same and yet every year is different. There are similar factors that affect the growth of the population every year, but the combinations differ. The average March temperature in Texas this year was 5.3ºF above normal. This high temperature continues a pattern. March temperatures in Texas have been 2ºF above normal for 11/18 years. Higher than normal temperatures in Texas have usually been associated with rapid movement of the returning monarchs beyond the borders of Texas with 2012 and 2017 being the extreme examples of movement northward. That didn’t happen this year due to a multitude of factors from a split in the polar vortex, sudden stratospheric warming in mid-winter and a persistent blocking high centered over Greenland in March and April, all of which had the effect of sending a series of cold air masses over the mid-continental region as far south as North Texas. It was simply too cold for monarchs to move northward during late March and much of April with the result that egg laying by returning monarchs was confined to Texas in the central corridor – and that’s a good thing.

In most ‘normal’ years, the returning monarchs are near the end of life in mid-April with few surviving to 1 May. That’s likely to be the case this year given the warmer than usual temperatures in Texas. While warmer than normal temperatures probably shorten the lives of returning adults, they have the effect of speeding up development of larvae and pupae and that is better than having females lay eggs further north where temperatures are lower and development of the immatures takes longer. The bottom line for this year is that what is normally a negative, when in combination with weather conditions that confined monarchs to Texas, has actually been beneficial. So, this year the high March temperatures are likely to lead to a growth in the population rather than a decline. That expectation is based on several assumptions. First, that the returning monarchs laid a lot of eggs in Texas and that many of the new larvae will mature to the adult stage and begin moving north in late April and through May and early June. That may be the case. There have been a number of reports both to Monarch Watch and Journey North of large numbers of eggs and larvae on milkweeds from Houston to North Texas and many other locations.

The next assumption deals with the conditions first generation monarchs will encounter as they move north. Because the movement northward is temperature sensitive, I checked the expected temperatures for a number of locations in the northern breeding area from 1 May to mid-June. An additional assumption is that temperatures in the high 60s and low 70s favor movement northward. With that in mind, conditions will be mostly favorable for northward movement through the 20th of May followed by about 10 days of lower than normal temperatures that should slow down the advance. Temperatures will again be favorable during the first half of June. Overall, even though there is some uncertainty in the forecasts and about the size of the first generation moving north from Texas, I’m still expecting the population to increase this year.

My self-interruption while trying to finish the text started on the 10th of March (see Monarch Population Status 1/2) concerned my quest to understand and trace the movement of monarchs north from the overwintering colonies. Based on some guesswork, a small amount of prior knowledge from working on neo-tropical African bees (Africanized bees) in northern Mexico and inference as to the temperatures preferred by migratory monarchs, I traced out two prospective pathways returning monarchs might use to reach the milkweed-rich areas of Texas. The target areas are north and east of the counties in South Texas in which milkweed diversity and abundance is low as shown in Figure 1. There is surprisingly little milkweed in South Texas with most areas having only scattered populations of one species – Asclepias oenotheroides (Zizotes milkweed).

Figure 1. Counties in South Texas with limited diversity and abundance of milkweeds.

After laying out the prospective pathways on a Google Earth image of northern Mexico (Figure 2), I consulted the records posted to Journey North for Mexico for this year to see if they approximated my imagined pathways.

Figure 2. Prospective monarch pathways.

There is a modestly good fit for much of the interior pathway and that appears to correlate to some extent with the distribution of human population centers. The coastal pathway is not supported by sightings and that is likely due to the lack of population centers along that route. The pathways are represented by narrow lines in this image, but the real pathways, as suggested by some of the outlying observations, are likely to be rather broad. Both routes are crudely drawn. The interior pathways probably range in elevation from 800′ to 3500′, with most monarchs flying at elevations from 1200-2400′ in the mountains. As to distances, I measured the pathways and came up with the following minimal distances from the colonies to areas with abundant milkweeds in Texas (Figure 1).

Coastal pathway – from Angangueo to the vicinity of Corpus Christi, TX = at least 635 miles.

Interior pathway – from Angangueo to an area between Del Rio and Eagle Pass and then to just SW of San Antonio = at least 800 miles. If monarchs were to take the western interior path, the distances would be even greater.

Throughout March I monitored the temperatures along the routes of this northern exodus with the use of Windy.com. Looking at these images, I quickly formed the opinion that one or both pathways could be ‘shut down’ by high temperatures. This idea became a preoccupation when I learned of reports of 30 trees still covered with monarchs at El Rosario as of the morning of the 3rd of April. This was a very late date for monarchs to still be at El Rosario and the prospect that it could become too hot for them to successfully reach breeding areas in Texas seemed likely. On the 7th of April I learned that most of these monarchs had left on the afternoon of the 3rd. That set me on a path to create a record of the temperatures along the pathways from the 7th through the 20th of April. Under favorable spring conditions, monarchs appear to be able to advance about 50 miles per day, so by stopping the observations on the 20th, that gave them about 16.5 days to reach milkweed areas in Texas by taking the interior pathway ( +/- 800 miles).

As far as I have been able to determine, directional flight (i.e. migration) shuts down completely once temperatures exceed the low 80s. The preferred temperatures for sustained directional flight are in the low 70s. In contrast to the fall, during which monarchs deploy a great deal of gliding and soaring, in the spring, most of the migration involves powered flight. Powered flight generates high thoracic and head temperatures requiring monarchs to slow down or even stop flight to avoid overheating. Hence, the idea that the pathways could be blocked during periods when the temperatures reached the 80s or higher. To document these conditions, I took screen shots of the temperatures along the pathway areas represented at Windy.com for 10AM, 1PM and 4PM each day. Each set of images is accompanied with my assessment as to the likelihood that the conditions favored migratory flight. These images are provided in Figures 3-16.

Figure 3. Saturday 7 April 2018 10AM, 1PM, 4PM High temperatures block coastal route.

Figure 4. Sunday 8 April 2018 10AM, 1PM, 4PM Temperatures favorable.

Figure 5. Monday 9 April 2018 10AM, 1 PM, 4 PM High temperatures block coastal route.

Figure 6. Tuesday 10 April 2018 10 AM, 1PM, 4 PM Unfavorably low temperatures.

Figure 7. Wednesday 11 April 2018 10AM, 1PM, 4PM Temperatures and winds favorable.

Figure 8. Thursday 12 April 2018 10AM, 1PM, 4PM Temperatures unfavorable.

Figure 9. Friday 13 April 2018 10AM, 1PM, 4PM Temperatures unfavorable.

Figure 10. Saturday 14 April 2018 10AM, 1PM, 4PM Temperatures favorable, headwinds.

Figure 11. Sunday 15 April 2018 10AM, 1PM, 4PM Temperatures and winds favorable.

Figure 12. Monday 16 April 2018 10AM, 1PM, 4PM Temperatures mostly favorable.

Figure 13. Tuesday 17 April 2018 10AM, 1PM, 4PM Temperatures unfavorable.

Figure 14. Wednesday 18 April 2018 10AM, 1PM, 4PM Temperatures unfavorable.

Figure 15. Thursday 19 April 2018 10AM, 1PM, 4PM Temperatures favorable.

Figure 16. Friday 20 April 2018 10AM, 1PM, 4PM Temperatures favorable.

The bottom line here is that I don’t know whether the monarchs that left El Rosario on the afternoon of 3 April made it to the milkweed area in Texas or not. There were no reports of late monarchs moving through Mexico in mid-April and only one late report from Texas (Beeville, 15 April near the north end of the coastal pathway) in an area through which these monarchs might have passed. What is clear in these images is that moving north from the colonies late in the season is not easy and could result in considerable attrition among the migrants due to high temperatures and perhaps the lack of nectar in times of drought.

Monarch Population Status 1/2

The following text was written on 10 March 2018.

Predicting the trends in the monarch population in 2018

If you have been following a number of my posts to the Blog over the years, you have surely noticed that I have a tendency to make predictions. This is all part of my process of trying to learn from my mistakes, and my few successes, as to what contributes to the increases and decreases in the population. The long-term goal is to develop a predictive model based on physical (weather) and biological factors that will provide a better understanding of the inter-annual variation as well as the dynamics of the population within each year. If successful, such a model should allow us to develop effective approaches to monarch conservation.

Most of my predictions have been made in late June or July with iterations as the seasons have progressed. I’m moving it up a notch this year by declaring that “the population will increase this year” – an increase from the recently-reported 2.48 hectares that overwintered in 2017-2018 (see Monarch Population Status). Ok, I’ve said it. If I’m wrong, we should be able to figure out why. At this juncture, I can’t tell you how large the population will be, but it should be 3 hectares or larger. I can’t explain all of my reasoning at this point, but let’s be clear, this declaration is based on a number of assumptions with respect to the numbers of returning monarchs, the conditions in the South for March and April, the conditions as the monarchs move north, the summer temperatures, and the conditions during the migration. Yes, it’s all conditional and the only justification for my approach is that the long-range forecasts are generally accurate and we now have over 20 years of data on how the population responds to a variety of weather patterns. I’ve looked at the weather records from 1895 to the present and it’s clear that monarchs have experienced much greater extremes in the past than the population has experienced since the colonies were brought to the outside world’s attention by Ken and Catalina (now Trail) Brugger in 1975. In saying this, I’m pointing out that our knowledge of how monarchs respond to weather conditions is limited to that of the relatively stable climate conditions that have occurred since the majority of the overwintering colonies were first measured (1993). That said, there is nothing in the long-range forecasts to suggest that weather events during the coming breeding season will have a negative impact on population growth. Rather, given past weather patterns associated with increases in monarch numbers, 2018 looks to be a year in which the population will increase due to favorable temperatures in the South Region in March and April, together with good recolonization numbers, May and June temperatures that will allow for recolonization of the northern breeding areas, and normal summer temperatures.

There are still a lot of gaps in our knowledge of how the monarch population functions. We don’t have a detailed understanding of when the monarchs leave the colonies, what the weather conditions are during their passage to the north, how fast they move from day to day, the paths or routes taken, the impacts of drought conditions on nectar availability, how long the journey takes and the amount of mortality experienced before monarchs reach areas in Texas with significant numbers of milkweeds. It will take some time to acquire these details, but I decided to see what I could learn about these issues from my desk and computer in Lawrence, Kansas.

Accordingly, on the 25th of February, I announced in an email to a number of colleagues that I was going to try to remotely follow the migration northward from the colonies. I’ve done just that and have accumulated numerous observation that will be summarized at a later date.

Milkweed Restoration in Oklahoma

Monarch Watch is engaged in a number of projects that focus on habitat restoration designed to benefit monarchs and pollinators. One of these efforts involves a collaborative project with seven tribal nations in Oklahoma. The goals of the project involve the planting of 5,000 milkweed plugs and 4,000 native forbs on the lands of each tribe. In total, 32,000 milkweed plugs have been planted to date. Production of the forbs (mostly native nectar plants) has involved training to identify beneficial native species, seed collection and processing and all the steps from seed storage to propagation and planting. This collaborative effort is known as the “Tribal Environmental Action for Monarchs” (TEAM). The images below make up a presentation prepared by Andrew Gourd, Land Use Coordinator Eastern Shawnee Tribe of Oklahoma. This presentation is now on display at the National Museum of the American Indian (part of the Smithsonian Institution).

Having established the TEAM project as a base, and by learning from both both our successes and failures, we decided to use this project as a stepping stone for a new and larger project we call TAP (Tribal Alliance for Pollinators). This outreach and training program is just getting started, but has great promise for engaging many tens of the 566 federally-recognized tribes throughout the United States.

Our partner in the TEAM and TAP projects is Jane Breckinridge, Citizen of Muscogee Creek Nation of Oklahoma and Director of the Euchee Butterfly Farm. Jane is the “boots on the ground” in Oklahoma where she has the task of coordinating and assisting the seven tribes which are widely scattered over the eastern part of the state. The distances are considerable since every tribe seems to be an hour to two hours driving time from one another. One of the rewarding, and we are told unique, aspects of the TEAM effort is that the project is bringing the tribes together. They are sharing their successes and failures and are helping each other succeed.

This presentation is also available as a PDF file.

2018 Monarch Calendar Project

NOTE: We will send an email with a link to the actual submission form after each period comes to a close (June 20th for period 1 and September 25th for period 2). Please hang onto any data sheets you have completed until those times. Thank you!

Monarch Watch is seeking the immediate assistance of hundreds of monarch enthusiasts (citizen scientists) in collecting observations of monarchs in their area during the spring and fall. This project is an attempt to assemble quantitative data on monarch numbers at critical times during the breeding season. The data from these observations will be used to assess their value in predicting trends in the population.

We are excited about the data we received for 2017 and are in the process of analyzing it. It looks like it is going to help explain some aspects of the monarch migration and “pre-migration”. We will share a summary of the results as soon as we have everything worked out.

BACKGROUND

Why do we need a “monarch calendar” and your help recording monarch numbers?

The decline in monarch numbers over the last 15 years has inspired numerous attempts to define critical factors that explain the inter-annual variation in monarch numbers. The data sets used for these analyses have had a variety of limitations which have either been ignored or underappreciated by the authors of a number of publications. The truth is that much of the data that is available is too general and does not adequately represent important aspects of the biology that underlies the development of the population each reproductive season.

There are numerous gaps in our knowledge and some of these gaps can be addressed if we can convince a large number of monarch enthusiasts (citizen scientists) to record the number of monarchs they see each day and what the monarchs are doing, along with general information about the physical conditions associated with each observation.

At this time we are not asking participants to record behavior or physical conditions (temperatures and wind speed and direction) but a few observations and notes along those lines might be useful in targeting conditions most favorable for monarch activity. The pivotal latitude is 35N (e.g., Oklahoma City) and we have provided some links below to help you determine your latitude. If the observer is located at a latitude less than 35N (i.e., “South”), we need the number of monarchs seen each day during the following two periods: 15 Mar-30 Apr and 1 Aug-25 Sep – 47 days & 56 days = 103 days total. If the observer is located at a latitude greater than 35N (i.e., “North”) the observation periods are 1 Apr-20 Jun and 15 Jul-20 Aug – 81 days & 37 days = 118 days total.

The first period in the south covers the interval during which the overwintering monarchs arrive in Texas and Oklahoma and points to the east. We need to capture a better estimate of the number of monarchs in this region that arrive from Mexico each year. This starting number has not been captured effectively. The second interval in the south captures the arrival of pre-migration monarchs from the north as well as potential local reproduction during this time. In the north, the first interval will capture some of the returning monarchs early in that period but is more likely to chronicle the arrival of first generation monarchs migrating north to the summer breeding grounds. The second period in the north should capture the relative intensity of the reproductive activities of monarchs during the period in which most of the eggs are laid that become the adults that populate the migratory generation later in August and September.

To provide meaningful data, we need to recruit hundreds of volunteers to record what they see.

INSTRUCTIONS FOR CITIZEN SCIENTISTS

Here is what we need you, as citizen scientists, to do:

1. Register as a participant in this 2018 project (even if you registered previously) by providing your name, location (including latitude and longitude), and email address via the form at

To determine your geographic coordinates, please use any of the following sites (or others) to enter your city, state/province, and zip/postal code and retrieve your latitude and longitude in decimal form (e.g., latitude: 38.95 longitude: -95.27 for Lawrence, KS 66045).

2. Record every monarch seen in your location for specific periods depending on your latitude. To keep these records all one has to do is to list the number of monarchs seen each day in which seeing a monarch was a possibility. If you were outdoors and saw none, record a zero (0). On the other hand, if there was no opportunity to make any observation due to work or vacation, etc., leave that date record blank. There will often be days when monarchs can’t be active due to weather conditions (e.g., low temperatures, extreme overcast, heavy rainfall). These intervals, if long enough, can also impact population growth. A “W” (for weather) should be entered for each of these days.

We have provided some sample files below that you can use to log your observations but exactly how you do it is up to you. Here are some suggestions: spreadsheets (Excel, Numbers, Google Sheets, etc.), printed calendar sheets (or just a calendar), calendar applications on your computer or phone, notebooks, notes or other text files on your computer or phone. Please feel free to use whatever is easiest and most comfortable for you to log your daily observations of monarch numbers – you will then use this log to complete a simple online form at the end of the observation period.

Please note: The records for each time period should only reflect the numbers of monarchs seen on any specified day within 50 miles of your home location. If you wish to report monarchs seen at a location other than your home location (specifically, at a different latitude) please use another datasheet as this should be submitted separately.

3. Submit your data to us at the end of the observation period via an online form. We will provide a link to the submission form at a later date via the email address you give us when you register. The form will be very simple; all you will need to do is enter your name and location (including coordinates as you do when you register) then you will be presented with the appropriate time period form to enter your data for each day.

We will assemble the calendar records for each period and region then provide summaries online once we have a chance to analyze the data.

Please register for this project and start logging your observations today! Thank you in advance for your assistance – if you have any questions or comments about this project, please contact us at monarch@ku.edu

SAMPLE FILES (for logging observations)

Spreadsheets (Excel format; can be imported into other applications)
2018-spring-south.xls
2018-spring-north.xls
2018-fall-south.xls
2018-fall-north.xls
sample-data.xls (partially completed sheet for reference)

Blank Calendar Sheets (to print)
2018-spring-south.pdf (Mar-Apr 2018)
2018-spring-north.pdf (Apr-Jun 2018)
2018-fall-south.pdf (Aug-Sep 2018)
2018-fall-north.pdf (Jul-Aug 2018)
You can also create custom calendars via www.timeanddate.com

FREQUENTLY ASKED QUESTIONS

Preamble

We’ve received a number of questions about our Monarch Calendar Project. We’ve tried to summarize these questions and, through the answers, clarify how we’d like you to record the data.

We need a better way of predicting the fall migration and the size of the overwintering population. This project is an attempt to capture three aspects of the seasonal dynamics of the monarch population that will help us understand how the population develops through the breeding season. Specifically, we are trying to obtain data (with your help) that will provide information on the relative numbers of monarchs seen after first sightings in most areas of the country. In addition, we are seeking data on the number of monarchs seen during the last egg laying periods in the north and south. Lastly, records of the weather-related events, as indicated by the Ws on the data sheets, may indicate times and regions during which weather had a negative impact on the population.

Thanks for your willingness to participate in this project. We appreciate your help. As you can see, from the scope of the project, the only way to obtain these data is through the cooperation and commitment of a large number of citizen scientists such as yourself. Again, we appreciate your help and we are looking forward to receiving your data.

Questions and Answers

1. When should I start my calendar?

The idea is to keep the record keeping as simple and as accurate as possible. Here are some suggestions:
• Start with your first sighting
• Start when you find the first eggs
• Start when monarchs and/or eggs have been sighted in your area
• Start only when sightings are reasonable given your latitude.

2. How do I make counts? Suppose I see a monarch six times in my garden during a day do I count that as six butterflies or one?

The rule here has to be to use common sense and be conservative. Egg laying females in the morning and patrolling males in the afternoon will often return to the same patch over and over on a given day. If during the sightings, the observed butterfly appears to be the same color, size and condition, count it as a single butterfly. Females are darker than males and male/female behavior is different. Careful observations should help you distinguish one butterfly from another. However, if you are uncertain, be conservative and record the lower number.

3. What if I am in an area in the northern part of the range where monarchs are seldom seen before 20 June?

Actually, we want to confirm that monarchs aren’t seen above certain latitudes until after the 20th of June. Please indicate that to be the case, if true, and only record data for the critical egg laying period from 15 July to 20 August. This directive is likely only to apply to a few of you who report sightings from 46N or further north.

4. What if I work during the week and can’t make observations? Or, do I have to observe for a certain length of time on a given day to record a number seen or a zero?

We expect the opportunity to observe will vary greatly for each observer over the calendar period and that some observers will, by virtue of opportunity, activity or lifestyle, see more monarchs than others. That’s fine. We want to capture relative numbers over large areas and long time periods for multiple years. Don’t worry if you don’t see monarchs or don’t spend a lot of time looking for them. Just record what you see and, if you think there was a good opportunity to have seen a monarch and didn’t, just record that day as a zero. If you had no opportunity to observe, that’s a blank. We expect more blanks and 0s with some Ws (for “weather” – see #7 below) than actual numbers sighted on nearly all the data sheets.

5. If I raise and release monarchs, do I count those?

The short answer is no. We are trying to record the dynamics of the wild population.

6. What about species that are easily confused with monarchs?

Yes, there are species that are sometimes confused with monarchs, most commonly the viceroy and the queen. In flight, the viceroy flies closer to the ground than monarchs and frequently lands on the ground. It is also less likely to visit flowers. However, when on flowers, viceroys and queens can be easily mistaken for monarchs. Monarchs are larger than both of these species. All we can tell you here is to learn your butterflies, observe closely and do your best.

7. When should I record a W for weather? What weather conditions limit monarchs?

Low temperatures (mid 60s and lower), extremely high temperatures (95 and higher), extreme overcast, rain, and high winds can completely stop monarch activity. When that happens, please record a W for weather. The Ws are important. There is no reproduction during a W – no mating, no egg laying and, if the temperatures are low, larval development slows down as well. Monarchs can get off to a good start and then be slammed by weather that shuts down reproduction. We need to capture that. Five consecutive days of low temperatures and rain can have a strong negative impact on a population that can easily be missed if projections are based on mean monthly temperatures. We aren’t really concerned about the weather before monarchs arrive. If necessary, we can capture weather data from “Weather Underground” for the periods prior to the arrival of monarch in any region.

8. Does this project apply to Hawaii, Southern California or Florida or other continuously breeding populations?

No, it doesn’t. Continuously breeding populations are found in Florida, some regions along the Gulf Coast, Southern California, Hawaii and numerous Pacific Islands. It’s probable that some or all of these populations cycle with the seasons and this should be captured. However, that will require a different protocol.

9. Why aren’t you asking us to record eggs, larvae and migrating monarchs?

The reason is simple; there are other programs that provide data on these aspects of the life history. Please see the following links if you wish to participate in any of these programs.

First eggs – these sightings can be reported via Journey North (learner.org/jnorth/tm/monarch/SpringWatch.html)

The Monarch Larval Monitoring Project (MLMP) at the University of Minnesota tracks both larvae and eggs (mlmp.org)

Migratory monarchs are tracked by Journey North through sightings of overnight roosts (https://www.learner.org/jnorth/tm/monarch/FallWatch.html)

Monarch Watch’s tagging program captures data related to the size and dynamics of the migratory population (monarchwatch.org/tagging)

Monarch Population Status

World Wildlife Fund Mexico in collaboration with CONANP and the Monarch Butterfly Biosphere Reserve (MBBR) announced the total forest area occupied by overwintering monarch colonies this week. Nine (9) colonies were located this winter season with a total area of 2.48 hectares, a 14.77% decrease from the previous season:

Figure 1. Total Area Occupied by Monarch Colonies at Overwintering Sites in Mexico

We will provide additional details as we receive and process them.

WWF release (in spanish): Superficie forestal ocupada por las colonias de hibernación de la mariposa monarca en México durante Diciembre de 2017.

Forgotten Victims of Harvey – the Pollinators

We recently received the following account of the hurricane and the alarmingly low number of pollinators post-Harvey. ~Monarch Watch

I am writing from Sugar Land, Fort Bend County, Texas where my home is located approximately 2 miles from the Brazos River, which is scheduled to crest at 59 feet above sea level, the highest level ever recorded. Over the course of three days, we’ve received a record-breaking 51.5” of rain from the category 4 hurricane Harvey and are under a voluntary evacuation order. Hospitals, grocery stores, pharmacies and restaurants are all closed. Some people in my subdivision are using kayaks and canoes to navigate their street. Coast Guard helicopters fly overhead on a regular basis. Our latest social media communication from the city stated “If you can’t flush toilets, no cause for alarm – just give it time, the system will catch up as water recedes.” And after watching 3 days of hurricane coverage showing others more badly affected, I was grateful for that communication. You really can’t imagine the number of things we take for granted until faced with disaster. Now imagine that disaster is a 1000 year flood resulting from a hurricane going on outside while you have 389 Monarch caterpillars to feed inside…

Pre-Harvey

As I rushed to complete pre-hurricane Harvey preparations, one more task was added to my list that was different from previous storm preparations, picking up monarch caterpillars. My first call came from the leader of a partnering organization. I met to accept my first box of caterpillars in the parking lot of Gallery Furniture, which one day later would become a temporary shelter for local evacuees and an overnight hostel for the activated National Guard. I accepted my final container of monarch caterpillars at the HEB parking lot where I expected to make a quick grocery run and instead found a 50 minute wait in the pouring rain outside locked grocery store doors manned by the store manager to prevent uncontrolled crowds fighting for necessities like water, eggs and milk. People deliver caterpillars in all manner of open boxes, and so my normal 10 minute drive home became a much longer drive through traffic, high waters, windshield wipers unable to keep up with falling rain, and moving caterpillars trying to escape their box.

Over the course of two days I collected caterpillars, farming some out to local enthusiasts until I ran out of available enthusiasts. I already had 80 caterpillars of my own I was raising for our 2017 annual Monarch Madness Festival. Some of the people asking me to adopt their cats were evacuating. Others couldn’t slosh through wet yards to collect milkweed. Still others expressed fear the caterpillars would die in the rain and some were simply running out of milkweed, having misjudged the number of plants it would take to feed the quantity of caterpillars on their plants. Surprisingly, nobody feared losing their caterpillars to flood which turned out to be the greatest threat.

I thought long and hard before accepting the caterpillars. Unlike some of the donors, I knew exactly how many plants it would take to feed 389 caterpillars. I also knew that many of the caterpillars I was accepting were likely born of butterflies infected with OE, a dormant protozoan carried by the monarch that is then deposited onto the egg sack and consumed by the caterpillar. Still others were likely preyed upon by tachinid flies, as it is the height of their season.

The value of saving these caterpillars was about much more than the cats themselves. These caterpillars represented Houston and Sugar Land monarch enthusiasts I had a part in growing. The reality of monarch conservation is that children and adults grow to love the butterflies produced from THEIR school, park and backyard gardens that I asked them to create and that love will help this species recover. Now those monarch enthusiasts trusted me to keep the product of their work and love alive. I said yes.

Last May, at the Texans By Nature Milkweed Symposium, Dr. Chip Taylor of University of Kansas’s Monarch Watch proposed that monarch butterflies are a metaphor for ourselves and our ability to save them speaks to our ability to sustain our own species. If that is true, I reasoned, then my ability to save these 389 caterpillars could be said to represent Houstonians’ and my own ability to survive hurricane Harvey. So I committed to become the surrogate guardian of more caterpillars than I ever raised in the middle of the worst hurricane in US history. I set up an indoor operation which included mesh butterfly cages and little cup nurseries. I sloshed through ankle deep water, hail, sleet and stinging rain blowing sideways twice a day to collect my own and my neighbors’ fresh milkweed.

On day one a tree fell on our fence and in the dark of night two, I stepped into the kitchen to feel water on my feet. Sleet, an unusual occurrence in Houston was clinging to shingles, brick and overflow pipes damaging our roof. Water was dripping from the roof into our kitchen cabinets, filling all the dishes before dripping into the controls of our electric stove below and across our kitchen. One of our hoop house type greenhouse roofs left the premise on high winds never to be found again. But all-in-all we are good and our damage was minor. I feel survivor guilt even voicing our damage when others are being evacuated from roof tops and had lost everything.

In some ways we are nearing the end of this storm and in others we haven’t yet seen the worst conditions. When the Brazos River crests, it has the ability to impact Monarch Gateway’s signature event, the annual fall Monarch Madness Festival, a family friendly, monarch butterfly and pollinator conservation festival. During this event Monarch Gateway awards the annual Catalina Aguado Trail Young Naturalist Award and scholarship to a young person contributing to monarch conservation. If Brazos Bend State Park is flooded when the river crests, as happened last year during the Memorial Day floods, the park will close for cleanup, impacting our September 24th festival.

Post Harvey, Pre-Brazos River Cresting

Texas Parks and Wildlife Department announced the closure of Brazos Bend State Park which is already flooded and expects to sustain additional flooding when the river crests.

Figure 1A. 200′ to left is the BBSP Monarch Waystation which is not flooded but the only way to access the park is by canoe. David Heineke, photographer.

Staff at Brazos Bend State Park and George Observatory, a satellite site of the Houston Museum of Natural Science inside the park informed us we would need to find an alternate location for Monarch Madness as both are closed through October and expect a months-long cleanup period.

Figure 2. I live one mile down the road in center of this picture.

I left our home for the first time post-Harvey for an appointment in South Houston and as I drove, I looked for butterflies, which were absent in my yard since Harvey. I returned home aware I saw none, no bees, no butterflies, or even dragonflies, all of which usually return to my yard shortly after any storm. The life of the monarch butterfly is short, sometimes just 2-4 weeks long and it makes sense that many probably perished in hurricane Harvey as did the caterpillars on plants under flood waters.

I was grateful this storm did not occur just a couple of weeks later as monarch butterflies begin their annual migration through Texas to Mexico because Harvey’s heavy rain bands extended into many areas in the I35/migration corridor and its impact could have been great. All but the smallest caterpillars have now become chrysalis and the City of Meadows Place has agreed to host our annual Monarch Madness event if we can plan for the rescheduling of an entire festival in 3 weeks amidst all else.

Epilogue

We now know Harvey was a 40,000 year flood event by some calculations and a 1000 year event by others that delivered 9 trillion gallons of water to Texas with catastrophic results. In the week since hurricane Harvey, I have only seen one tiger swallowtail butterfly. Because my backyard is designed for wildlife and I’m in the business of noticing pollinators as I travel throughout my day, I estimate I normally see between 25 and 100 per day. My awareness of the various pollinators flitting around is a bit like white noise, I’m most aware when it stops. Harvey has presented me a real-life opportunity to view my city with no monarch butterflies or pollinators and it has piqued my determination.

As we all get back to normal life we can’t help but walk among people in various stages of grief and acceptance but in the end, we are all determined to survive, to rebuild our habitat, find the foods that sustain us and have a safe, dry place to rest at night, just like the monarch butterfly. There are many ways to help people after a natural disaster and each organization and person will gravitate toward that topic that speaks to their heart. My heart says go rebuild pollinator habitat so that the forgotten victims of Harvey, the pollinators, in all their life stages from caterpillar to winged adult can once again thrive in our communities. My heart says make as much of that habitat native prairie with its 15 foot deep roots that also help absorb future hurricane and storm runoff. If I can save hundreds of monarch caterpillars in the worst hurricane in U.S. history, increasing the monarch population is doable. I challenge you to stand with me, with Houstonians, with the Texan will to survive and help the monarch butterfly and other pollinator species survive too.

HOUSTON, UNITED STATES
08.29.2017

Gallery Furniture. Photo by Sgt. Steve Johnson, 100th Mobile Public Affairs Detachment

Monarch Population Status

I’ve done many things in my career that I’ve enjoyed greatly and among those was teaching a course in honey bee biology. The course incorporated some hands-on lessons in how to manage bees for pleasure and the sweet rewards bees could provide. To manage bees for honey production, you have to know how to manipulate the growth of the colonies in the spring: that is, to bring the numbers of bees in each colony to the maximum number at the time the flowers provide the greatest amounts of nectar. Since colony development is strongly correlated with the seasonal progression of flowering (phenology), which in turn is influenced by temperature and moisture, the goal is to manage each colony in concert with the sequence of flowering to provide the best shot at maximizing honey production. I used to tell the students that each spring is a challenge, in effect a series of experiments, in which beekeepers have to apply their knowledge of bee biology and management skills for each colony with what they can deduce from the temperature and moisture patterns during the spring that determine plant growth and flowering. And so it is with monarchs. Each year is an experiment, or series of experiments, with numerous hypotheses, during which I try to match what I know about monarchs with the progression of the seasonal conditions that influence both monarch behavior and plant growth. As a beekeeper, my hypotheses were often off the mark and I have been off the mark about monarch projections as well, but that’s alright. The idea is to learn from one’s mistakes.

To make projections for each fall migration and overwintering population, I start with the numbers of monarchs measured at the overwintering sites in Mexico. Next, I focus on overwintering mortality, followed by the spring conditions that prevail as monarchs move northward from the overwintering sites to the milkweed areas in south and central Texas, and then the conditions in the South Region (Texas, Oklahoma, Louisiana, Arkansas, Kansas) during the growth of the first generation in March and April. That is followed by attention to the conditions during the period from 1 May-9 June that allow (or don’t allow) first-generation monarchs to reach the northern breeding grounds. Summer temperatures along with the seasonal distribution and amounts of rainfall are also in focus when estimating the fall and winter numbers.

The above provides the context for a number of hypotheses or projections concerning the coming migration and the opportunities to tag monarchs this fall. First, this should be a GREAT tagging season. It will certainly be as good as the 2015 season and probably better. The overwintering numbers should match or exceed the 4.01-hectare population measured in the winter of 2015-2016 (see Monarch Population Status from February). Further, several fall monitoring sites (Peninsula Point, MI; Long Point, ONT and Cape May, NJ) are all likely to record much higher numbers of monarchs than in recent years. Specifically, the migration through Cape May has the potential to be stronger than any migration since 2012. While the numbers at Cape May will probably not be as high as 2012, they are likely to rank within the top ten seasonal averages in the 25 years of that program. Fall monarchs should be abundant in the Upper Midwest from the eastern Dakotas east to Wisconsin and Illinois with good numbers present from Michigan through Ohio as well. Production of monarchs should also be higher than it has been for many years for all of the Northeast from New York and Pennsylvania through Maine. The Mid-Atlantic region hasn’t been heard from in recent months, but the flow south and southwest through that region by monarchs originating further north should present some good opportunities for tagging in that region as well. Taggers located south of the northern breeding areas, particularly those located in Kansas, Oklahoma and Texas, should also have a greater opportunity to tag monarchs than in recent years.

In sum, this looks to be a good year for monarchs – with a stronger migration in most regions and a good prospect that the overwintering population will increase from the 2.91 hectares of last year to 4 hectares or better this coming winter.

Monarch Population Status

Those of us who are educators, and who follow monarchs closely, are being educated by the monarchs themselves this spring. The movement and behavior of monarchs returning from Mexico has been unprecedented. I’ll save the details for a longer Status of the Population that will be posted online at a later date but for the purpose of making the point of how the monarchs are schooling us, I’ll briefly summarize the important points here.

The overwintering population was just 2.91 hectares. That’s a relatively small population. Yet, more returning monarchs have been reported this spring than for any previous overwintering population including many that were much larger.

Monarchs moved into central Texas after the 12th of March in good numbers and advanced at a rapid rate to the north and northeast, reaching Oklahoma a bit earlier and in larger numbers than seen in most years. This advance into Oklahoma continued in late March and early April, resulting in many sightings of egg dumping (multiple eggs on single plants). Evidently, large numbers of monarchs had reached northern Oklahoma before the 4th of April, but no further due to colder weather in Kansas and Missouri. On the 4th of April, we received a report of clustering monarchs on a ridge top near Bixby, OK (see “Spring roosting: A rare event” at monarchwatch.org/blog/2017/04/11/spring-roosting-a-rare-event/). This clustering may have been the result of storms that were moving through the area at the end of the day. Small spring clusters have been reported before, but the observers in this case reported that 1200-2000 monarchs had clustered in a series of pine trees on this hilltop. That was unprecedented. No one has reported seeing that many monarchs in one place that far north in the spring. Some monarchs lingered at this site through the 6th.

The weather changed on the 7th and from 7-9 April strong south and southwesterly winds and favorable temperatures allowed monarchs to expand the leading edge of the returning population from the Kansas/Oklahoma border well into Nebraska, a distance of 300 miles, in three days. I’ve looked at all the first sightings data posted via Journey North and I don’t recall anything comparable to that expansion in those records. While the expansion was impressive, the number of monarchs in this wave was also remarkable.

These monarchs were ahead of the milkweeds in most of Kansas, Missouri, Nebraska and Iowa. Milkweed that had just emerged in burned over grassland sites, in the heat islands of cities and towns, and in some gardens, were quickly found by females who deposited large numbers of eggs on the few plants available. Egg dumping was the rule, allowing the collection of hundreds and hundreds of eggs and larvae – again, unprecedented numbers for these latitudes for this time of year. The eggs and larvae were collected to save both the milkweed plants in gardens and the monarchs from predators. We collected well over 500 eggs and larvae with a minimum of effort. We also monitored a number of sites with large number of eggs and larvae that were not collected. Nearly all of the latter disappeared.

I kept watch on a special cohort of larvae that were relatively protected from predators to monitor their developmental rate. Those larvae were from eggs laid on the 9th and 10th of April. They are 29-30 days old at this writing (9 May) and most will pupate over the next three days. At emergence, most will be 45 days old. That’s a long generation and that’s not good. Shorter generation times are better for a number of reasons.

Monarchs resulting from the premature, ahead of the milkweed push, resulting from the winds of 7-9 April, will arrive late to the northern breeding grounds. In effect, these monarchs will lose a generation.

In 2000, there was a somewhat similar earlier push into Kansas and other northern sites. That didn’t work out well. The overwintering population that year was only 2.83 hectares, down considerably from the 9.05 hectares from the previous overwintering population.

So, what does all of this foretell for this year’s migration and overwintering population? Frankly, it doesn’t look good. We could be looking at another decline such as seen in 2000, but it is really too early to make predictions. We will have to assess the number and timing of first generation monarchs that move into the northern breeding areas later this month and into early June. If those numbers are low, the population is certain to decline. Moderate numbers and summer temperatures that are 1.5F above normal could offset the loss of reproduction associated with the “too far north too soon” scenario that has played out this spring.