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Nov 25, 2024

Destabilizing Atlantis? Offshore wind energy diversion's impacts on currents & water column stratification. 2008-2024

Below are scientific and govt  links (pdf files)  stretching from 2008 to 2024. They illuminate an  evolution of  understanding of the marine environmental impacts of  ocean wind energy diversion ashore as electricity.

It is observed by many of the below papers and articles  that  the speed and integrity of  oceanic water currents and of seasonal water stratification are  weakened and disorganized by these energy-diverting devices. 

2008 Pioneering paper on topic

2019


2021

New Study Unveils the Unique Seasonality in the Deep Basins of Gulf of Maine NOAA 12/02/2021


2023


Offshore Wind Wake Effects Are Real: We Should Plan for Them. NASA  2023

   

Nov 23, 2024

Chasing the offshore wind farm wind-wake-induced upwelling/downwelling dipole. 2022



From: Frontiers in Marine Science 27 July 2022 Public document
Chasing the offshore wind farm wind-wake-induced upwelling/downwelling dipole. Authors:Jens Floeter*Jens Floeter1*Thomas PohlmannThomas Pohlmann2Andr HarmerAndré Harmer1Christian MllmannChristian Möllmann

A.  Abstract: 

The operational principle of offshore wind farms (OWF) is to extract kinetic energy from the atmosphere and convert it into electricity.

Consequently, a region of reduced wind speed in the shadow zone of an OWF, the so-called wind-wake, is generated. 

As there is a horizontal wind speed deficit between the wind-wake and the undisturbed neighboring regions, the locally reduced surface stress results in an adjusted Ekman transport. 

Subsequently, the creation of a dipole pattern in sea surface elevation induces corresponding anomalies in the vertical water velocities. 

The dynamics of these OWF windwake induced upwelling/downwelling dipoles have been analyzed in earlier model studies, and strong impacts on stratified pelagic ecosystems have been predicted. 

Here we provide for the first time empirical evidence of the existence of such upwelling/downwelling dipoles. 

The data were obtained by towing a remotely operated vehicle (TRIAXUS ROTV) through leeward regions of operational OWFs in the summer stratified North Sea. 

The undulating transects provided high-resolution CTD data which enabled the characterization of three different phases of the ephemeral life cycle of a wind-wake-induced upwelling/downwelling dipole: 

Development, operation, and erosion. 

We identified two characteristic hydrographic signatures of OWF-induced dipoles: distinct changes in mixed layer depth and potential energy anomaly over a distance < 5 km and a diagonal excursion of the thermocline of ~10–14 m over a dipole dimension of ~10–12 km. 

Whether these anthropogenically induced abrupt changes are significantly different from the corridor of natural variability awaits further investigations.

======================

B. From:Introduction

Offshore wind farms (OWFs) convert kinetic wind energy into electricity, creating regions of reduced wind speed and high atmospheric turbulence intensity downstream of wind turbine arrays. 

Christiansen and Hasager (2005)Christiansen and Hasager (2006) were the first to describe these wind-wakes by synthetic aperture radar (SAR)-derived wind speed images and well-known wind farm wake photographs (Hasager et al., 2013). 

Numerical analyses by Broström (2008) triggered a series of modeling studies (Paskyabi and Fer, 2012Paskyabi, 2015Ludewig, 2015), which all predicted that a wind speed of 5–10 m s-1 generates so-called upwelling/downwelling dipoles in a stratified ocean with vertical velocities exceeding 1 m day-1

The generated oceanic response is predicted to extend several kilometers around the OWFs and to be strong enough to influence the local pelagic ecosystem, especially the surface mixed layer (SML).

 These studies formulated prerequisite conditions for the generation of an OWF wind-wake-induced upwelling/downwelling dipole: the characteristic width of the wind-wake has to be at least the internal radius of deformation (Broström, 2008), which is fulfilled for OWFs in the German Bight of the North Sea, as both are ~10 km (Chelton et al., 1998Platis et al., 2018).

 An almost constant wind direction for at least ~8–10 h with moderate speeds (5–10 m s-1) is the second condition which needs to be met (Ludewig, 2015).

 Other theoretically derived factors likely to influence the vertical velocities in OWF wind-wake-induced upwelling/downwelling dipoles are the size of the wind farm (Broström, 2008), surface waves and tidal advection (Paskyabi and Fer, 2012), and atmospheric stability (Platis et al., 2018).
...
In June 2016, we deployed a high-speed remotely operated towed vehicle (ROTV) to investigate the offshore wind farm wind-wake-induced upwelling/downwelling dipole.

C. Discussion
Our working hypotheses of observing three different phases of an upwelling/downwelling dipole life cycle, i.e., early development, established and eroding phases, were generally confirmed. The coexistence of a tidal mixing front on June 29–30 in our investigation area prevented the observation of an undisturbed OWF wind-wake-induced development and decay of dipoles.

* Wind-wakes

In situ wind and turbulence measurements of far-field OWF wakes (Platis et al., 2018) confirmed previous model- (Dörenkämper et al., 2015) and SAR-derived results (Li and Lehner, 2013Djath et al., 2018Djath and Schulz-Stellenfleth, 2019) that higher atmospheric stability, i.e., the absence of thermally produced turbulence, increases wake dimensions. However, we do not know the atmospheric stability during our survey.

SAR images quantifying wind-wake dimensions in a specific situation are rare, as the repeat cycle of the satellite is about 11–12 days (Platis et al., 2018), but promising (Elyouncha et al., 2021). 

Airborne observational data showed that in the German Bight stable atmospheric situations are most probable for southwesterly wind directions, as in our survey period, from which Platis et al. (2018) inferred that this is the most likely direction producing long wakes. 

However, even in unstable and neutral atmospheric situations, Platis et al. (2018)Platis et al. (2020)Platis et al. (2021) frequently observed wind-wakes with lengths between 5 and at least 35 km in our study area. 

Therefore, we deduced that the southwesterly wind with speeds >4 m s-1 which prevailed during our study generated wind-wakes at the leeward regions of BARD and GTI, with lengths between 5 and ~35 km. 

Observations of absolute (Figure 10) and normalized (Supplementary Figure 9) wind speeds recorded at FS Heincke revealed for June 27 a clear wind deficit leeward of BARD only for T1 and T2—the transects with identified upwelling/downwelling dipoles. The wind speed deficit was ~3 m s-1 or 30%, which is well in the range reported by Platis et al. (2018) for a similar-sized neighboring OWF. 

On June 29, wind-wakes with a deficit ~25% were detected at FS Heincke vessel height on transects T1, T2, T3, and T4 (Supplementary Figures 10, 11), supporting our analysis of the developing dipole. 

Hence, the June 27 onboard wind measurements suggest that the wind-wake had a length of ~14 km, and >20 km on June 29. On June 30, the wind-wake deficits were relatively larger (~46%) on T1 and T2 but on a lower absolute level (Supplementary Figures 12, 13)...

* Water Currents
During the survey, maximum ambient currents in a depth of 15 m were in the order of 0.6 m s-1, which is about one (Ludewig, 2015) to two (Christiansen et al., 2022) magnitudes higher than the mean wind-wake-induced changes in the horizontal surface water velocity field. 

Therefore, the spatial orientation of the tidal ellipse in relation to the direction of the wind-wake can be expected to enhance or weaken the development of an upwelling/downwelling dipole. Tidal excursions in this region have a magnitude of ~6–9 km in an east–west direction (Floeter et al., 2017), which was at an ~45° angle to the average wind-wake-induced Ekman transport during our study. 

Subsequently, the tidal phase can be expected to have an effect on the vertical velocities and the spatial locations of the dipoles. The BSHcmod-derived wind- and tide-driven ambient currents were similar during the comparative measurements of T1 on June 27 and 29, exhibiting a westward water movement with velocities around 0.2–0.3 m s-1 (Figure 11). 

However, the tidal phase was different as on June 27 the 280° westward currents persisted for 12 h before we surveyed T1, whereas the ambient current was eastward (100°) during the 12-h period prior to the TRIAXUS measurements of T1 on June 29. 

A hydrodynamic modeling analysis would be needed to assess how the different tidal histories contributed to the observed dipole shapes and dynamics.
....

* Wind-wake-induced changes in potential energy anomaly of water column

Earlier model studies have demonstrated that OWF-induced disturbances to the wind field modulate tidal mixing front-related upwelling processes (Paskyabi, 2015) and change the upper ocean stratification pattern (Ludewig, 2015). 

To differentiate natural and anthropogenic effects, we calculated the potential energy anomaly of the 5–20-m envelope of the water column following the approach of Simpson (1981) by considering changes in the potential energy relative to the mixed condition [Eq. 2 in Simpson (1981)]. 

The calculation was based on the potential density anomalies [kg m-3] of the transects, gridded with ODV-DIVA (Schlitzer, 2021Troupin et al., 2012) applying a horizontal and vertical resolution of 250 m and 0.1 m.

All transects surveyed on June 27 and 29 revealed an overall north–south decrease in the potential energy anomaly, following the stratification trend from offshore to the coast (Figure 12). 

The trajectories of the transects with established OWF-induced upwelling/downwelling dipoles (June 27 T1, T2, and June 29 T3) were distinct from all others by showing abrupt changes in potential energy anomaly of ~4 kJ m-3 over a short distance of ~2–4 km (Figure 12).

* Characteristic signatures of the observed upwelling/downwelling dipoles

We identified two characteristic hydrographic signatures of OWF-induced dipoles:

a. Distinct changes in mixed layer depth and potential energy anomaly of the 5–20-m water column envelope over a distance <5 km

b. Diagonal excursion of the thermocline of ~10–14 m over a dipole dimension of ~10–12 km

Whether these anthropogenically induced changes in potential energy anomaly and mixed layer depth are significantly different from the corridor of natural variability awaits further investigations. The same applies to the representativity of the observed signatures

* Potential ecological consequences

In a modeling study, Christiansen et al. (2022) identified reduced vertical mixing of the upper water column due to the wind speed deficit in the OWF wake as the predominant process impacting on the pelagic environment of the German Bight. 

When the wind direction changes, the enhancement of stratification and shallowing of the SML is affecting varying areas. 

By analyzing monthly mean hydrodynamic results, Christiansen et al. (2022) concluded that OWF wind-wake-induced convergence and divergence of water masses lead to the formation of large-scale sea surface elevation dipoles, which generate structural changes in the stratification strength in the German Bight. 

However, because of almost constantly changing wind directions, the magnitude of the monthly averages is so low that it can hardly be distinguished from the interannual variability (Christiansen et al., 2022).

A shallowing of the nutrient-depleted summer SML (Topcu et al., 2011) brings the lower regions of the thermocline, and with it high concentrations of nutrients and phytoplankton cells (Richardson et al., 2000Zhao et al., 2019) upward into more illuminated water depth levels.

 As some light for net primary production is available below the thermocline (Floeter et al., 2017), it can be expected that these phytoplankton organisms are viable and immediately increase their production.

Thus, when in a specific situation the wind direction is stable over at least ~10 h, like the ones we encountered on 2016 June 27 and 29, the shallowing of the mixed layer depth by distinct OWF wind-wakes has the potential to generate significant anthropogenic pulses of enhanced primary production at the lower spatial mesoscale (i.e., ~10–35 km). 

While Christiansen et al. (2022) confirmed the correlations between the sea-level dipole anomalies and changes in the vertical density and temperature distributions derived by Ludewig (2015), associated changes in the mean vertical velocity field, i.e. upwelling/downwelling dipoles were not detectable.

The cause can be found in the different nature of the two main effects of OWF wind-wakes on the water column:

1) Wherever a wind-wake leads to reduced vertical mixing, the subsequent enhancement of the stratification is not reversed when the wake direction changes because the wind deficit prevails within the entire wake. Hence, the effects of this first process remain detectable in monthly average flow fields.

2) When a wind-wake directionally persists for some time, it generates an upwelling/downwelling dipole. When the wind direction changes, negative and positive vertical water velocities wipe out each other as the downwelling cell is shifted over the upwelling cell or vice versa. Hence, the effects of this second process are vanishing in monthly average flow fields.

The excursions of the thermocline due to this second wind-wake effect of upwelling/downwelling dipoles are substantially larger (~10–14 m, Figures 47) than the shallowing of the mixed layer depth caused by reduced vertical mixing. 

Therefore, it can be expected that they generate more intense but ephemeral pulses of primary production with spatial dimensions at the lower meso-/upper submesoscale. 

Whether the magnitude of this anthropogenic primary production enhancement is similar to that of tidal mixing fronts awaits further investigations. 

At the current developmental stage of OWFs in the German Bight, their cumulative wind-wake-induced upwelling area is smaller than the tidal front region, but the potential of submesoscale features as drivers of biophysical coupling in the German Bight was already highlighted by North et al. (2016) and their location in stratified regions may make a difference.

The further fate of the manmade additional primary production, which fraction is cascading up the trophic chain (Lévy et al., 2018; Wang et al., 2018; Slavik et al., 2019; Twigg et al., 2020; Kaiser et al., 2021), how much will contribute to oxygen minimum zones (Topcu and Brockmann, 2015; Große et al., 2016; Queste et al., 2016), or the impact on fisheries resources (Methratta and Dardick, 2019; Methratta, 2020; van Berkel et al., 2020); add another level of complexity.

END










Penobscot Bay Report, 11/23/24, Juniper Ridge Expansion short and long audio/video

 

JRL's official website 

Juniper Ridge expansion plan meeting Nov 21, 2024   32 minutes (meeting in progress)

https://penbay.org/wrfr/2024/112324/wrfr_2024_112124_juniper_ridge_mtg_pt1_32min.mp3 

Nicky S's written  observations:  " I noticed that Casella's lawyer and state house lobbyist was in the room. I know him because he also represents Poland Spring and has been working hard to prevent more protective regulations from towns where they export water from. Irony, because the landfill is where most of the plastic ends up, while people nearby the landfill have to rely on bottled water because the water is not safe. An ugly cycle. You might see him at future meetings. His name is Brian Rayback and he is a partner at Pierce Atwood law firm in Portland. 


Link to full 90 minute Audio video by sunlight media collective  

https://www.facebook.com/WabanakiSovereignty/videos/1092444685699297/


JIMI Stereo 

Nov 14, 2024

 KEY FINDINGS FROM EACH DOCUMENT:

A. "climatic_effects_windpower_2018.txt" (Miller & Keith)

  • Wind power generation creates measurable warming effects
  • Surface temperatures affected by turbine mixing of boundary layer
  • Wind impacts approximately equivalent to reduced warming from decarbonizing electricity
  • Solar impacts about 10 times smaller than wind for same generation

B. "impacts_accelerating_deployment103122.txt" (Akhtar et al.)

  • Wind farm wakes extend 35-40 km downstream
  • Wind speed deficits reach 2-2.5 m/s within farms
  • Seasonal variations in impact (strongest spring, weakest winter)
  • Capacity factor reductions of 20% or more in downstream farms
  • Identifies wind energy as potentially limited resource in North Sea

C. "wind_sci_2022_offshorewind_diversion.txt" Article 1 (Christiansen et al.):

  • Shows emergence of large-scale hydrodynamic structures
  • Documents changes in stratification strength
  • Identifies dipole formation in sea surface elevation
  • Notes effects on temperature and salinity distribution

Article 2 (Akhtar et al.):

  • Confirms wake effects up to 70 km under stable conditions
  • Shows impacts on neighboring wind farms
  • Identifies seasonal patterns in wind speed deficits
  • Notes potential ecosystem impacts

D. "pbw_boem_072224.txt"

  • Calculates energy diversion from air-sea interface
  • Links energy extraction to current weakening
  • Calls for HAPC designation for Eastern Maine Coastal Current
  • Advocates precautionary approach

E. "gom_deep_basin-currents.txt"

  • Reveals unique seasonal temperature patterns in deep basins
  • Documents 3-month transit time for slope water intrusion
  • Shows importance of Nova Scotia Current in stratification
  • Links Gulf Stream position to deep water properties
  1. COMMON THEMES:

A. Scale of Impact

  • Consistent findings of extensive wake effects
  • Far-reaching hydrodynamic changes
  • Cumulative effects of multiple farms

B. Ecosystem Concerns

  • All sources note potential ecological impacts
  • Emphasis on stratification changes
  • Recognition of complex system interactions

C. Energy Flow Disruption

  • Quantifiable energy extraction
  • Effects on natural mixing processes
  • Impacts on current systems
  1. GAPS NEEDING DOCUMENTATION:

A. Biological Response

  • Specific impacts on marine species
  • Changes in migration patterns
  • Effects on larval transport

B. Long-term Effects

  • Cumulative impacts over decades
  • Ecosystem adaptation capabilities
  • Recovery potential

C. Regional Specifics

  • Gulf of Maine-specific modeling
  • Local current system responses
  • Seasonal variation patterns

D. Economic Impacts

  • Fisheries effects quantification
  • Tourism implications
  • Cost-benefit analyses
  1. ACCESSIBILITY CONSIDERATIONS:

Need versions for: A. Technical Audience

  • Full scientific detail
  • Mathematical models
  • Technical terminology

B. Policy Makers

  • Executive summaries
  • Clear impact statements
  • Policy implications

C. General Public

  • Plain language explanations
  • Visual aids
  • Relatable examples

D. Industry Stakeholders

  • Fisheries-specific impacts
  • Operational implications
  • Economic considerations

Ocean windfarms and natural fisheries don't mix

What we've learned about the Gulf of Maine's natural patterns, and their vulnerability to disruption, combining the 2021 NOAA study  "Variability of Deep Water in Jordan Basin of the Gulf of Maine: Influence of Gulf Stream Warm Core Rings and the Nova Scotia Current."

Jiabi Du, Weifeng G. Zhang, Yizhen Li

Published on: 12/02/2021

Primary Contact(s): yizhen.li@noaa.govinsights with our earlier analyses:

Vulnerable Natural Patterns:

  1. Deep Water Exchange System
  • The newly discovered 3-month transit time for slope water is critical
  • This timing evolved to match seasonal biological cycles
  • Wind farm-induced mixing could:
    • Speed up or slow down this transit time
    • Create "short circuits" in the natural flow
    • Disrupt the temperature inversion pattern (warmer winter/colder summer deep water)
  1. Energy Transfer Disruption
  • Our earlier calculations showed ~6 gigawatts of wind energy could be diverted
  • This energy normally helps drive:
    • Surface mixing
    • Current maintenance
    • Seasonal turnover patterns
  • Removing this energy could weaken these processes
  1. Stratification Effects
  • The NOAA study shows how Nova Scotia Current's fresh water creates important stratification
  • Wind farm wakes could:
    • Break down natural stratification barriers
    • Create artificial mixing zones
    • Interfere with the natural preservation of deep water properties
  1. Nutrient Cycling Impacts
  • The 30% nutrient contribution from slope water is crucial
  • Disrupted patterns could affect:
    • Timing of nutrient delivery
    • Distribution patterns
    • Concentration levels in different water layers
  1. Biological Timeline Disruption
  • Natural systems depend on predictable patterns
  • Species affected could include:
    • Plankton bloom timing
    • Fish spawning cycles
    • Larval transport
    • Feeding migrations
  1. Cumulative Effects
  • Multiple wind farms could create:
    • Overlapping zones of disruption
    • Cascading effects on currents
    • Complex interactions with natural processes
    • Year-round rather than seasonal impacts
  1. Ecosystem Timing Mismatches
  • Could create "ecological disconnect" where:
    • Food isn't available when needed
    • Spawning doesn't match optimal conditions
    • Migration patterns become less effective

This vulnerability is particularly concerning because:

  1. The Gulf of Maine is already experiencing rapid climate change
  2. Many commercial species depend on these precise patterns
  3. Once disrupted, these patterns may be difficult or impossible to restore
  4. Effects could extend far beyond wind farm boundaries

For fisheries and ecosystem managers, this means:

  • Greater uncertainty in predicting stock behavior
  • Possible changes in traditional fishing grounds
  • Need for more intensive monitoring
  • Potential for unexpected ecosystem shifts

Would you like me to elaborate on any of these points or explore specific implications for particular species or fishing operations?

Data assimilative hindcast of the Gulf of Maine coastal circulation. 2005

 From Journal of Geophysical Research: OceansVolume 110, Issue C10 Oct 2005

Link to 2005 article Data assimilative hindcast of the Gulf of Maine coastal circulation

From Intro

"A data assimilative model hindcast of the Gulf of Maine (GOM) coastal circulationduring an 11 day field survey in early summer 2003 is presented. "

"In situ observations include surface winds, coastal sea levels, and shelf hydrography, as well as moored and shipboard acoustic Doppler D current profiler (ADCP) currents."

...

"A mean drifter divergence rate(1.78 km d1 ) is found, demonstrating the utility of the inverse data assimilation modeling system in the coastal ocean setting. "

"Model hindcast also reveals complicated hydrodynamic structures and synoptic variability in the GOM coastal circulation and their influences on coastal water material property transport. "

The complex bottom bathymetric setting offshore of Penobscot and Casco bays is shown to be able to generate local upwelling and downwelling that may be important in local plankton dynamics.

Nov 10, 2024

Penobscot Bay dredging/mercury resuspension could cost lobster industry millions

Friends of Penobscot Bay update for 7/16/13 
 
Maine' has issued a two lobsters/per week mercury consumption advisory.

Searsport dredge plan could cost Bay lobster industry millions in lost sales if state's 2-per-week mercury safety limit drops to 1/week for Penobscot Bay lobsters.

According to Pamela Wadman, an environmental toxicologist  at Maine Ctr for Disease Control and Prevention, Maine presently  has a coastwide two lobsters/week safety limit advisory for pregnant women & other sensitive people.  This is based on the "Maine Fish Tissue Action Level for Methylmercury"  which is 0.2 mg/kg  per week.

However, the  two-per-week coastwide lobster advisory is based on those two lobsters each having 0.1mg/kg  methylmercury or less in their meat.  If she can confirm information supplied us by a Belfast lobsterman that mercury levels in a significant percent of lobsters in that area are  double that, around the 0.2 mg/kg level or higher, she will have to issue a "Spot Advisory"  restricting safe lobster consumption of lobsters captured in that area to one lobster meal per week.  

Where is that area? Belfast lobsterman  gathered lobsters from an upper bay area for mercury testing under a special license from DMR for several years. See attached map (map also here) of the area.  Lobsters were collected inside the red triangle.

This triangle's corners are the II Buoy northeast of Marshall Point on Islesboro, the Gong 1 buoy south of Sears Island, and the DMP Buoy in the middle of the upper bay waters shared by Islesboro, Belfast and Searsport.

There is a " pretty heavy concentration of mercury" along the line between the II Buoy and the Gong 1 Buoy. This is the area beginning north of the old disposal site, then going northeast along the edge of the shipping channel  to the Gong 1 Buoy.  

But the very hottest  reach is the shoal edge above  the deeper water east of  the DMP buoy, (the shoal edge is the wiggly line inside the red triangle)

The lobsterman said that while he did not take sample lobsters from the exact bay floor the army Corps of engineers wants to dredge, which is  northeast of the DMP buoy, he is confident that the same elevated mercury would be found in that area if they do test for it. 

If so they've got a problem.  Having a "spot advisory"  for a small part of the upper bay would be economically disrupting enough for people that fish in that area. But if dredging and dumping tainted sediment resuspends a significant amount of methyl mercury in the waters from Searsport to Vinalhaven, the state might be required to issue a Penobscot Baywide lobster methylmercury advisory.   

If that happens, the drop in sales of live and processed lobsters sourced from Penobscot Bay could easily be in the million dollar-plus range. The heightened advisory would also throw a monkeywrench into the state's brand new Maine lobster sales global promotion strategy.  Eeek! No expansion dredging please!

LINKS NOVEMBER 10. 2024

 https://tethys.pnnl.gov/marine-energy-adventure-game

https://www.boem.gov/newsroom/press-releases/boem-issues-offshore-wind-research-lease-state-maine

https://blogs.helmholtz.de/kuestenforschung/2022/03/08/offshore-wind-farms-have-an-impact-on-ocean-dynamics/

https://finance.yahoo.com/news/trump-vowed-kill-offshore-wind-050127376.html






Nov 9, 2024

The Living Currents of the Gulf of Maine"


"The Living Currents of the Gulf of Maine"

Consider the Gulf of Maine:  a vast, living tapestry, woven from countless threads of energy and DNA life. Every wave that rolls, every current that flows, carries kinetic energy that started as wind pushing across the water's surface. This moving water powers life's  marine conveyor belts in  and around the Gulf of Maine.

The herring that lobstermen depend on for bait? They follow these living currents. Their eggs and larvae drift in them, their food (tiny plankton) blooms because of them, and the adult fish school within them. Break these currents, weaken them by stealing their wind-driven power, and you're pulling threads from this ancient tapestry.

When massive floating wind turbines extract energy from the wind before it hits the water, they're not generating electricity - they're diverting  away energy  that has, since time immemorial, driven the Gulf's marine ecosystems. 

Our calculations show each large wind farm area could drain over 6 billion watts of power from this system. 

That's energy that would normally:

  • Mix surface waters rich in oxygen with deeper waters
  • Drive plankton blooms that feed everything from herring to whales
  • Keep currents flowing that marine life depends on for transport, feeding, and breeding
  • Maintain the delicate balance of temperature layers that different species need

Think about how a river changes when you put a dam across it. Now imagine doing something similar to the wind that drives our ocean currents. The effects ripple through the entire food web:

  • Plankton blooms shift location or timing
  • Fish migrations disrupted
  • Feeding grounds become less productive
  • Essential nursery areas are altered

For creatures like herring, which time their spawning with specific current patterns and feed on plankton that bloom in predictable places, these changes could be devastating. And what affects herring affects everything that eats them - from groundfish to seabirds to marine mammals.

For those of faith, this is about being good stewards of Creation

For scientists, it's about preserving complex ecosystems we're still working to understand enough to avoid wrecking them.

For fishermen, it's about protecting the marine environment that has sustained generations of coastal communities.

The Gulf of Maine isn't just a place to put wind turbines - it's a living system that's already under stress from climate change. Before we start removing massive amounts of energy from this system, shouldn't we understand what that energy means to the countless creatures that depend on it?

We're not against renewable energy. But we are for protecting the intricate energy systems that nature has perfected over millennia. There might be better places for wind farms, or better technologies that don't disrupt these crucial marine energy flows. What we can't afford to do is treat the Gulf of Maine like a blank canvas for industrial development, ignoring the complex web of life that depends on its natural energy systems.

Remember: Once we start unraveling these ancient patterns of wind, wave, and current, we don't know if we can put them back together again. And it's not just fish and fishermen who depend on getting this right - it's the entire living system of the Gulf of Maine.


Would you like me to expand on any particular aspect of this narrative, or focus more specifically on certain species or ecological relationships?

Estuarine sediments produce toxic methylmercury. A Maine Seagrant Report

Maine SeaGrant: Estuarine sediments produce toxic methylmercury.  
July 2008 / Vol. 5

Sediments can be a source of dissolved mercury and organic matter because of the activity of microorganisms.

As the deposited mercury is buried beneath new layers of sediment, organic matter in the sediment is consumed by certain types of bacteria living a few millimeters below the sediment- water interface, beyond the reach of oxygen. These bacteria get their energy through chemical reactions that involve sulfur and iron, and produce toxic methylmercury as a byproduct.

Figure 3 shows a significant production of pore-water methylmercury at a depth of approximately five centimeters, where a concentration as high as 15 ppt is observed. Methylmercury can travel up or down through the sediment.

Figure 3 13 also shows that pore-water methylmercury rapidly disappears between a depth of one and two centimeters, inhibiting the release of this toxic chemical into the water. The exact reason for this is not known. Some bacteria can actually convert methylmercury back into the less toxic form of inorganic mercury. Or, the methylmercury that is diffusing up may get adsorbed by a relatively high concentration of iron hydroxide close to the sediment-water interface.

The lack of methylmercury release into the overlying water from the studied sediments does not mean that the animals in the mud and water are not exposed to this toxic chemical.

Methylmercury maybe directly taken up by deposit-feeding and burrowing organisms, such as worms and clams, and move up the food chain.

In other experiments, we have found that semi-permanent flooding or ponding, as would happen in a salt marsh panne, can create conditions where methylmercury released to the overlying water is greatly enhanced. With sea level rise, many coastal freshwater wetlands will be flooded with seawater, and may act as "hotspots" for methylmercury release.

In mudflats, regular flooding and exposure with changing tides can create conditions that lead to rapid mercury methylation and release into the overlying water. Future research will look at mercury concentrations in marsh plants, sediments, and animals living in the mudflats.

Do mercury levels In the Penobscot Rlver estuary threaten the health of fish, wildlife, or humans?

Mercury in the Penobscot Riyer is currently under a U.S. District Court- ordered investigation by an intemational team of expert scientists.

Phase I of the study was completed and approved bythe court in March 2000. The study team sampled water, sediments, wetlands, benthic invertebrates, fish, shellfish, birds and manmals in the Penobscot Riyerand estuary in 2006 and 2007.The researchers found that mercury concentrations decreased with increasing distance from the Holtrachem site.

The most severe contamination of the Penobscot system is between Brewer on the lower river and about Fort Point or Sears Island in the upper estuary.
They also found that:
* Mercury in the sediments was 20 times more concentrated in the lower river and estuary compared to a reference area in the East Branch Penobscot River.


* Mercury attached to particles suspended in the water was two times higher downstream of the Holtrachem site.

* In some individual lobsters, levels of methymercury in claw and tail muscle exceeded the Maine DEP and U.S. EPA criteria for protection of human health.

* Mercury in mussels was high compared to other sites in Maine and the U.S.

* Mercury levels in songbirds inhabiting wetlands adjacent to the lower Penobscot River in the Frankfort Flats area were very high compared to songbirds in other parts of Maine, and high enough for possible toxic effects on the birds themselves.

* Mercury in cormorant eggs in the upper estuary approached or exceeded levels thought to impair reproduction.

The study's authors concluded,"The Penobscot River and estuary are contaminated with mercury to an extent that poses endangerment to some wildlife species and possibly some limited risk for human consumers of fish and shellfish."

Phase ll of the study will concentrate on understanding where and when mercury is produced in the system and how it is transported and bioaccumulated in the lower river and upper estuary. Data from the study will be used to evaluate the practicalityof possible mitigation measures.

in 2007 (Figures 8,9) showed patterns that were very similar to those found in 2006 

(Figures 10-13). 



The within site core-to-core variation of these data is typical of sediment mercury data, 
and is the reason why we sampled sites repeatedly to adequately characterize mercury 
concentrations. For example, for sample period II (Sept. 2006; Figure 11) both the total 
Hg and methyl Hg concentrations at sites OB 1 and OB 2 were very high. These 
concentrations were not seen for the other five sampling periods at these two stations, 
indicating that 2 “hotspots” of mercury had been sampled during period II. 

The geographic pattern of methyl Hg concentrations was very similar to the geographic 
pattern seen for total Hg concentrations (Figures 8-13). There was a noticeable 
increase from East Branch to Old Town – Veazie reach and a much larger increase in 
the Brewer – Orrington, Orrington – Bucksport reaches. Concentrations then decreased 
with distance into the estuary. This was consistent at all sampling times. Methyl Hg 
concentrations were generally lower in the outer part of the estuary, especially at the 
most southerly five Estuary sites. Methyl Hg concentrations showed similar levels of 
variation at particular sites among sampling times as was evident for total Hg 
concentrations. This is because in the Penobscot system microbial production of 
methyl Hg is primarily controlled by concentrations of inorganic mercury (see 
discussions below). 

Also plotted on Figures 8-13 is the percent of total Hg that is methyl Hg. Several other 
studies have concluded that the percent of total Hg that is methyl Hg is a good indicator 
of the intensity of bacterial methyl Hg production in sediments2
. In the top 3 cm of the 
sediment cores, while some sites were higher than others, there was little overall 
geographic trend trough out the river and upper estuary (Figures 8-13). This lack of 
trend suggests that the efficiency of methylation of inorganic mercury is quite constant, 
per unit of total Hg. Efficiencies were somewhat lower in the outer estuary. This may 
have been because sulfide concentrations were higher in the waters of the outer 
estuary. It is well known that high sulfide concentrations reduce the production of 
methyl Hg by binding the inorganic mercury making it unavailable for the mercury 

methylating bacteria