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Showing posts with label offshore wind. Show all posts
Showing posts with label offshore wind. Show all posts

May 21, 2025

Paradigm for understanding whole ecosystem effects of offshore wind farms in shelf seas. 2025 study

A paradigm for understanding whole ecosystem effects of offshore wind farms in shelf seas

From: IICES Journal of Marine Science, Volume 82, Issue 3, March 2025,  Link to article  https://doi.org/10.1093/icesjms/fsad194 

Abstract With the rapid expansion of offshore windfarms (OWFs) globally, there is an urgent need to assess and predict effects on marine species, habitats, and ecosystem functioning

Doing so at shelf-wide scale while simultaneously accounting for the concurrent influence of climate change will require dynamic, multitrophic, multiscalar, ecosystem-centric approaches. 

However, as such studies and the study system itself (shelf seas) are complex, we propose to structure future environmental research according to the investigative cycle framework. 

This will allow the formulation and testing of specific hypotheses built on ecological theory, thereby streamlining the process, and allowing adaptability in the face of technological advancements (e.g. floating offshore wind) and shifting socio-economic and political climates. 

We outline a strategy by which to accelerate our understanding of environmental effects of OWF development on shelf seas, which is illustrated throughout by a North Sea case study. 

Priorities for future studies include ascertaining the extent to which OWFs may change levels of primary production; whether wind energy extraction will have knock-on effects on biophysical ecosystem drivers; whether pelagic fishes mediate changes in top predator distributions over space and time; and how any effects observed at localized levels will scale and interact with climate change and fisheries displacement effects. 

Keywords: marine renewable energy; bio-physical indicators; predator–prey interactions; scaling; multitrophic; autonomous platforms; dynamic Bayesian network modelling; cumulative impact assessme

Feb 26, 2025

Maine Fishermen's Forum's Ocean Wind Exploitation meetings 2009 - 2024

Fishermen's Forum Offshore wind seminar  audio links and/or pdf files - (only partial as of yet)


2009 - 2013 AUDIO MP3s 

2009 Fishermen's Forum Ocean windpower meeting    ** 2009  Ocean Energy Forum 

2010 Fishermens Forum Ocean windpower meeting 

2011 Fishermens Forum Ocean windpower meeting


2013

ff2013_022813_boem2.MP3  22M


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2018?  2019? 2020? 2021? 2022?
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2023  Wind Seminar Presentations  (PDF files, archived)

Fisheries and Offshore Wind Synthesis of the Science

Integrated Ecosystem Assessments Fisheries and Offshore Wind Development

Gulf of Maine Integrated Ecosystem Assessment Conceptual Model

Influence and Participate in Offshore Wind Research and Monitoring

The Importance of Fishery Engagement in Informing Offshore Wind Development

Wind Seminar Informational Links

Bureau of Ocean Energy Management

Commercial Fisheries Research Foundation

Maine Offshore Wind Research Consortium

Maine State Offshore Wind Roadmap

NOAA Integrated Resource Assessment

NOAA Socioeconomic Impacts of Atlantic Offshore Wind Development

NOAA State of the Northeast Ecosystem reports

NOAA Wind Farms and the Bottom Trawl Survey

Northeast Regional Ocean Council Ocean Use Maps

Responsible Offshore Development Alliance

Responsible Offshore Science Alliance

TETHYS Environmental Effects of Wind and Marine Renewable Energy

Maine Fishermen’s Forum 2020 Wind Seminar Page

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2024 Maine Fishermens Forum 

Seminars on Wind  Energy    (PDF files)
The following PDF presentations were shared in Forum Seminars on February 29, March 1, & 2, 2024

Feb 13, 2025

Hydrodynamic Impacts of Offshore Wind Energy on Nantucket Shoals Regional Ecology 202

From: National Academies of Sciences, Engineering, and Medicine. 2023

Potential Hydrodynamic Impacts of Offshore Wind Energy on Nantucket Shoals Regional Ecology: An Evaluation from Wind to Whales (2023)   Full document pdf


PG 43 Potential Hydrodynamic Impacts of Offshore Wind Energy on Nantucket Shoals Regional Ecology PREPUBLICATION COPY 

CONCLUSIONS AND RECOMMENDATION

Conclusion: Knowledge of the effects of offshore wind turbine structures on hydrodynamics is limited and primarily based on modeling studies. At the turbine scale, there are few observations that can be used to verify turbine-scale wake behavior, and coverage of parameter space is limited in modeling studies. 

At the wind farm scale, the potential impacts include reduction in ocean current speeds, reduction in the stratification, reduction in ocean surface wind speed, and deflection of the pycnocline. At the regional scale, perturbations due to turbines are difficult to quantify because of the natural processes that drive significant environmental variability across the region. 

Understanding Hydrodynamic Effects 

Conclusion: There are significant uncertainties in the hydrodynamic response of the wind and ocean wakes and of hydrodynamic effects of turbines. 

Conclusion: Impacts of offshore wind development in the Nantucket Shoals region on the regional hydrodynamics are uncertain and will be difficult to isolate from the much larger magnitude of variability introduced by natural and anthropogenic sources (including climate change) in this dynamic and evolving oceanographic system. 

Conclusion: More hydrodynamic observations are available at the regional scale than at the wind farm and turbine scales. Existing oceanographic monitoring programs historically have, and should continue to provide, important baseline data at the regional scale; new smaller-scale observational studies are encouraged and are a priority. 

Recommendation: The Bureau of Ocean Energy Management, National Oceanic Atmospheric Administration, and others should promote, and where possible, require observational studies within wind farms during all phases of wind energy development:

PG 44 Potential Hydrodynamic Impacts of Offshore Wind Energy on Nantucket Shoals Regional Ecology PREPUBLICATION COPY 

surveying, construction, operation, and decommissioning—that target processes at the relevant turbine to wind farm scales to isolate, quantify, and characterize the hydrodynamic effects. 

Studies at Block Island, Dominion, Vineyard Wind I, and South Fork should be considered as case study sites given their varying numbers of turbines, types of foundation, and sizes of spacing of turbines.  









Jan 21, 2025

Executive Order on offshore wind exploitation January 20, 2025

 White house link to the Executive order

January 20, 2025

MEMORANDUM for the Secretary Of the Treasury,  the Attorney General, the Secretary Of The Interior, the Secretary Of Agriculture, the Secretary Of Energy, The Administrator Of The Environmental Protection Agency

SUBJECT: Temporary Withdrawal of All Areas on the Outer Continental Shelf from Offshore Wind Leasing and Review of the Federal Government’s Leasing and Permitting Practices for Wind Projects

Section 1.  Temporary Withdrawal of Areas.  Consistent with the principles of responsible public stewardship that are entrusted to this office, with due consideration for a variety of relevant factors, including the need to foster an energy economy capable of meeting the country’s growing demand for reliable energy, the importance of marine life, impacts on ocean currents and wind patterns, effects on energy costs for Americans –- especially those who can least afford it –- and to ensure that the United States is able to maintain a robust fishing industry for future generations and provide low cost energy to its citizens, I hereby direct as follows:

Under the authority granted to me in section 12(a) of the Outer Continental Shelf Lands Act, 43 U.S.C. 1341(a), I hereby withdraw from disposition for wind energy leasing all areas within the Offshore Continental Shelf (OCS) as defined in section 2 of the Outer Continental Shelf Lands Act, 43 U.S.C. 1331.  This withdrawal shall go into effect beginning on January 21, 2025, and shall remain in effect until this Presidential Memorandum is revoked.

To the extent that an area is already withdrawn from disposition for wind energy leasing, the area’s withdrawal is extended for a time period beginning on January 21, 2025, until this Presidential Memorandum is revoked.

This withdrawal temporarily prevents consideration of any area in the OCS for any new or renewed wind energy leasing for the purposes of generation of electricity or any other such use derived from the use of wind.  This withdrawal does not apply to leasing related to any other purposes such as, but not limited to, oil, gas, minerals, and environmental conservation.

Nothing in this withdrawal affects rights under existing leases in the withdrawn areas.  With respect to such existing leases, the Secretary of the Interior, in consultation with the Attorney General as needed, shall conduct a comprehensive review of the ecological, economic, and environmental necessity of terminating or amending any existing wind energy leases, identifying any legal bases for such removal, and submit a report with recommendations to the President, through the Assistant to the President for Economic Policy.

Section 2.  Temporary Cessation and Immediate Review of Federal Wind Leasing and Permitting Practices.  

(a)  In light of various alleged legal deficiencies underlying the Federal Government’s leasing and permitting of onshore and offshore wind projects, the consequences of which may lead to grave harm — including negative impacts on navigational safety interests, transportation interests, national security interests, commercial interests, and marine mammals — and in light of potential inadequacies in various environmental reviews required by the National Environmental Policy Act to lease or permit wind projects, the Secretary of the Interior, the Secretary of Agriculture, the Secretary of Energy, the Administrator of the Environmental Protection Agency, and the heads of all other relevant agencies, shall not issue new or renewed approvals, rights of way, permits, leases, or loans for onshore or offshore wind projects pending the completion of a comprehensive assessment and review of Federal wind leasing and permitting practices.  

The Secretary of the Interior shall lead that assessment and review in consultation with the Secretary of the Treasury, the Secretary of Agriculture, the Secretary of Commerce, through the National Oceanic and Atmospheric Administration, the Secretary of Energy, and the Administrator of the Environmental Protection Agency.  

The assessment shall consider the environmental impact of onshore and offshore wind projects upon wildlife, including, but not limited to, birds and marine mammals.  The assessment shall also consider the economic costs associated with the intermittent generation of electricity and the effect of subsidies on the viability of the wind industry.

(b)  In light of criticism that the Record of Decision (ROD) issued by the Bureau of Land Management on December 5, 2024, with respect to the Lava Ridge Wind Project Final Environmental Impact Statement (EIS), as approved by the Department of the Interior, is allegedly contrary to the public interest and suffers from legal deficiencies, the Secretary of the Interior shall, as appropriate, place a temporary moratorium on all activities and rights of Magic Valley Energy, LLC, or any other party under the ROD, including, but not limited to, any rights-of-way or rights of development or operation of any projects contemplated in the ROD.  

The Secretary of the Interior shall review the ROD and, as appropriate, conduct a new, comprehensive analysis of the various interests implicated by the Lava Ridge Wind Project and the potential environmental impacts.

(c)  The Secretary of the Interior, the Secretary of Energy, and the Administrator of the Environmental Protection Agency shall assess the environmental impact and cost to surrounding communities of defunct and idle windmills and deliver a report to the President, through the Assistant to the President for Economic Policy, with their findings and recommended authorities to require the removal of such windmills.

(d)  The Attorney General may, as appropriate and consistent with applicable law, provide notice of this order to any court with jurisdiction over pending litigation related to any aspect of the Federal leasing or permitting of onshore or offshore wind projects or the Lava Ridge Wind Project, and may, in the Attorney General’s discretion, request that the court stay the litigation or otherwise delay further litigation, or seek other appropriate relief consistent with this order, pending the completion of the actions described in subsection (a) or subsection (b) of this section, as applicable.

This memorandum shall be implemented consistent with applicable law and subject to the availability of appropriations. 

This memorandum is not intended to, and does not, create any right or benefit, substantive or procedural, enforceable at law or in equity by any party against the United States, its departments, agencies, or entities, its officers, employees, or agents, or any other person. You are authorized and directed to publish this memorandum in the Federal Register.

END



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