الاتحاد الأوروبي نظام تداول الانبعاثات

المرحلتان 1 و 2 (2005-2018)
وقد اختلفت القواعد في الفترتين التجاريتين الأوليين من نظام التداول في الانبعاثات في الاتحاد الأوروبي (إتس) في جوانب هامة عن تلك المتعلقة بالفترة الثالثة الحالية (2018-2020).
الخطوات الأولى.
وقد حدد بروتوكول كيوتو لعام 1997 لأول مرة أهدافا ملزمة قانونيا لخفض الانبعاثات أو قبعات ل 37 بلدا صناعيا. وأدى ذلك إلى الحاجة إلى أدوات سياسية لتحقيق هذه الأهداف.
في مارس 2000، قدمت المفوضية الأوروبية ورقة خضراء مع بعض الأفكار الأولى حول تصميم إتس الاتحاد الأوروبي. وقد كانت بمثابة أساس لمناقشات أصحاب المصلحة العديدة التي ساعدت في تشكيل النظام.
وقد اعتمد توجيه الاتحاد الأوروبي في عام 2003 وبدأ العمل بهذا النظام في عام 2005.
وحدد الحد الأقصى للبدلات على المستوى الوطني من خلال خطط التخصيص الوطنية (نابس).
المرحلة 1 (2005-2007)
وكان هذا البرنامج التجريبي لمدة 3 سنوات من "التعلم بالممارسة" للتحضير للمرحلة 2، عندما تحتاج إتس الاتحاد الأوروبي إلى العمل بفعالية لمساعدة الاتحاد الأوروبي على تحقيق أهدافها كيوتو.
الملامح الرئيسية للمرحلة 1:
تغطي فقط انبعاثات ثاني أآسيد الكربون من مولدات الطاقة والصناعات كثيفة الاستخدام للطاقة آانت جميع البدلات تقريبا تمنح للشركات مجانا. وبلغت عقوبة عدم الامتثال 40 يورو للطن.
وقد نجحت المرحلة الأولى في تأسيسها.
وهو سعر لتداول الكربون الحر في بدلات الانبعاثات في جميع أنحاء الاتحاد الأوروبي البنية التحتية اللازمة لرصد الانبعاثات والتحقق منها من الشركات المشمولة.
وفي حالة عدم وجود بيانات موثوقة للانبعاثات، وضعت قبعات المرحلة 1 على أساس التقديرات. ونتيجة لذلك، انخفض مجموع البدلات المصدرة للانبعاثات، وتجاوز سعر العلاوات في عام 2007 إلى حد كبير، مع تجاوز العرض إلى حد كبير الطلب (صفر) (لم يكن بالإمكان مصارف المرحلة الأولى لاستخدامها في المرحلة 2).
المرحلة 2 (2008-2018)
وتزامنت المرحلة 2 مع فترة الالتزام الأولى لبروتوكول كيوتو، حيث كان لدى البلدان في إتس الاتحاد الأوروبي أهداف ملموسة لخفض الانبعاثات للوفاء بها.
الملامح الرئيسية للمرحلة 2:
(أقل من 6.5٪ مقارنة بعام 2005) انضمت 3 دول جديدة - أيسلندا وليختنشتاين والنرويج انبعاثات أكسيد النيتروز من إنتاج حامض النيتريك التي شملها عدد من البلدان انخفضت نسبة التخصيص المجاني قليلا إلى حوالي 90٪ عدة البلدان المزادات تمت زيادة عقوبة عدم الامتثال إلى 100 يورو للطن تم السماح للشركات بشراء ائتمانات دولية بلغ مجموعها نحو 1.4 مليار طن من سجل الاتحاد المكافئ لثاني أكسيد الكربون محل السجلات الوطنية وسجل معاملات الاتحاد الأوروبي (يوتل) محل الجماعة المستقلة سجل المعاملات (سيتل) تم إحضار قطاع الطيران إلى إتس الاتحاد الأوروبي في 1 يناير 2018 (ولكن تم تعليق طلب الرحلات الجوية من وإلى البلدان غير الأوروبية لعام 2018)
ونظرا لأن بيانات الانبعاثات السنوية المؤكدة من المرحلة التجريبية أصبحت متاحة الآن، فقد خفض الحد الأقصى للبدلات في المرحلة 2، استنادا إلى الانبعاثات الفعلية. ومع ذلك، أدت الأزمة الاقتصادية لعام 2008 إلى تخفيضات في الانبعاثات كانت أكبر مما كان متوقعا. وأدى ذلك إلى فائض كبير من البدلات والائتمانات التي أثرت بشدة على سعر الكربون طوال المرحلة 2.
تطور سوق الكربون الأوروبي.
وقد تطورت السوق في بدلات الانبعاثات بقوة منذ البداية.
في المرحلة الأولى، ارتفعت أحجام التداول من 321 مليون بدل في عام 2005 إلى 1.1 مليار في عام 2006 و 2.1 مليار في عام 2007، وفقا لتقارير السوق الكربون السنوية للبنك الدولي.
وظل االتحاد األورويب لالنتخابات هو املحرك الرئييس لسوق الكربون الدويل خالل املرحلة الثانية. ويف عام 2018، على سبيل املثال، شكلت بدالت االتحاد األورويب 84٪ من قيمة سوق الكربون العاملي اإلمجايل. وارتفعت أحجام التداول من 3.1 مليار في 2008 إلى 6.3 مليار في 2009. وفي عام 2018، تم تداول 7.9 مليار بدل (بقيمة 56 مليار يورو).
تجاوز حجم التداول اليومي 70 مليون في منتصف عام 2018، البيانات التي جمعتها بلومبرج الطاقة الجديدة التمويل وجمعية لوسطاء الطاقة لندن تظهر.
حجم التداول في بدلات الانبعاثات في الاتحاد الأوروبي (بالملايين)
المصدر: بلومبرغ تمويل الطاقة الجديدة. أرقام مأخوذة من بلومبرغ، أيس، بلوينكست، إيكس، غرينكس، كليمكس، كسكس، غرينماركيت، نوردبول. وتشمل المصادر الأخرى تقديرات اتفاقية الأمم المتحدة الإطارية بشأن تغير المناخ وتقديرات بلومبرج لتمويل الطاقة الجديدة.
الرصد والإبلاغ والتحقق من انبعاثات الاتحاد الأوروبي لانبعاثات غازات الدفيئة.
التشريع.
18/08/2018 - قرار اللجنة بشأن تعديل القرار 2007/589 / إيك فيما يتعلق بإدراج مبادئ توجيهية للرصد والإبلاغ لانبعاثات غازات الدفيئة من الأنشطة والغازات الجديدة 08/06/2018 - قرار اللجنة 2018/345 المعدل للمقرر 2007/589 / إيك فيما يتعلق بإدراج مبادئ توجيهية للرصد والإبلاغ لانبعاثات غازات الدفيئة من احتجاز ثاني أكسيد الكربون ونقله وتخزينه الجيولوجي 16/04/2009 - قرار اللجنة 2009/339 / إيك المؤرخ 16 أبريل 2009 المعدل للمقرر 2007/589 / إيك فيما يتعلق بإدراج مبادئ توجيهية للرصد والإبلاغ للانبعاثات وبيانات الكيلومتر من أنشطة الطيران 17/12/2008 - قرار اللجنة 2009/73 / إيك المؤرخ 17 كانون الأول / ديسمبر 2008 المعدل للمقرر 2007/589 / إيك بشأن إدراج الرصد والتقييم المبادئ التوجيهية لانبعاثات أكسيد النيتروز 18/07/2007 - مقرر اللجنة 2007/589 / إيك الذي يضع مبادئ توجيهية لرصد انبعاثات غازات الدفيئة والإبلاغ عنها عملا بالتوجيه 2003/87 / ه البرلمان الأوروبي والمجلس (مرغ 2007) 29/01/2004 - مقرر اللجنة 2004/156 / إيك الذي يضع مبادئ توجيهية لرصد انبعاثات غازات الدفيئة والإبلاغ عنها عملا بالتوجيه 2003/87 / إيك للبرلمان الأوروبي و المجلس (المبادئ التوجيهية الأصلية للرصد والإبلاغ)
القوالب الإلكترونية للإبلاغ عن الانبعاثات من مشغلي الطائرات.
صيغ تبادل البيانات للمرحلة الثانية من إتس للاتحاد الأوروبي.
1-تمثيل عرض الشجرة ل ييتسركست: في. pdf و. png 1b - تمثيل عرض شجرة يوتسبريبورت: في. pdf و. ينغ 2-الكيان-العلاقة المخططات (إرد's) ييتسركست: إن. pdf و. vsd 2b - إنتيتي-ريلاتيونشيب الرسوم البيانية (إرد's) ييتسريبورت: في. pdf و. فسد 3. عناصر البيانات هيكل ووصف سيمانتيكال.

نظام الاتحاد الأوروبي لتجارة الانبعاثات (الاتحاد الأوروبي إتس)
وأوضح نظام الاتحاد الأوروبي لتجارة الانبعاثات.
ويعتبر نظام االتحاد األوروبي لتداول االنبعاثات) إيتس (حجر الزاوية في سياسة االتحاد األوروبي لمكافحة تغير المناخ وأداة رئيسية للحد من انبعاثات غازات الدفيئة من حيث التكلفة. هذا هو أول سوق الكربون الرئيسي في العالم ولا يزال أكبر واحد.
تعمل في 31 دولة (جميع دول الاتحاد الأوروبي البالغ عددها 28 دولة بالإضافة إلى أيسلندا وليختنشتاين والنرويج) تحد من الانبعاثات من أكثر من 11،000 منشأة تستخدم الطاقة الثقيلة (محطات توليد الكهرباء والمنشآت الصناعية) وتغطي شركات الطيران العاملة بين هذه البلدان حوالي 45٪ من غازات الدفيئة في الاتحاد الأوروبي الانبعاثات.
للحصول على نظرة عامة مفصلة، ​​انظر:
A 'كاب والتجارة' النظام.
تعمل إتس الاتحاد الأوروبي على مبدأ "الحد والتجارة".
يتم تحديد سقف على إجمالي كمية غازات الدفيئة معينة التي يمكن أن تنبعث من المنشآت التي يغطيها النظام. ويتم تخفيض الحد الأقصى بمرور الوقت بحيث ينخفض ​​إجمالي الانبعاثات.
وفي إطار الحد الأقصى، تتلقى الشركات أو تشتري بدلات الانبعاثات التي يمكن أن تتاجر بها مع بعضها البعض حسب الحاجة. ويمكنهم أيضا شراء كميات محدودة من القروض الدولية من مشاريع إنقاذ الانبعاثات في جميع أنحاء العالم. ويضمن الحد الأقصى لعدد البدلات المتاحة أن يكون لها قيمة.
وبعد كل سنة، يجب على الشركة أن تسلم ما يكفي من البدلات لتغطية جميع انبعاثاتها، وإلا فرضت غرامات كبيرة. وإذا خفضت الشركة انبعاثاتها، فإنها يمكن أن تحتفظ بدلات احتياطية لتغطية احتياجاتها المستقبلية أو أن تبيعها إلى شركة أخرى تقل عن المخصصات.
فالتجارة تجلب المرونة التي تضمن خفض الانبعاثات حيث تكلف أقل من ذلك. كما يعزز سعر الكربون القوي الاستثمار في التكنولوجيات النظيفة والمنخفضة الكربون.
الملامح الرئيسية للمرحلة 3 (2018-2020)
وقد أصبح الاتحاد الأوروبي للاتصالات الأوروبية الآن في مرحلته الثالثة - يختلف كثيرا عن المرحلتين 1 و 2.
التغييرات الرئيسية هي:
يتم تطبيق سقف واحد على مستوى الاتحاد الأوروبي على الانبعاثات بدلا من النظام السابق للقبعات الوطنية يعتبر المزاد هو الطريقة الافتراضية لتخصيص البدلات (بدلا من التخصيص المجاني)، وتنطبق قواعد التوزيع المنسقة على البدلات التي لا تزال تمنح مجانا. تضمنت الغازات 300 مليون بدلات خصصت في احتياطي المشردين الجدد لتمويل نشر تكنولوجيات مبتكرة للطاقة المتجددة واحتجاز الكربون وتخزينه من خلال برنامج 300 نر.
القطاعات والغازات المشمولة.
ويغطي النظام القطاعات والغازات التالية مع التركيز على الانبعاثات التي يمكن قياسها والإبلاغ عنها والتحقق منها بمستوى عال من الدقة:
من ثاني أكسيد الكربون (CO2) من قطاعات توليد الطاقة والطاقة الحرارية كثيفة الاستخدام للطاقة بما في ذلك مصافي النفط والأعمال الحديدية وإنتاج الحديد والألمنيوم والمعادن والاسمنت والجير والزجاج والسيراميك ولب الورق والورق والكرتون والأحماض والمواد الكيميائية العضوية السائبة أكسيد النيتروز التجاري (N 2 O) من إنتاج أحماض النيتريك والأديبيك والجليوكسيليك ومركبات الكربون الهيدروكلورية فلورية غليوكسال (بكس) من إنتاج الألومنيوم.
المشاركة في إتس الاتحاد الأوروبي إلزامية للشركات في هذه القطاعات، ولكن.
في بعض القطاعات فقط النباتات فوق حجم معين يتم تضمين بعض المنشآت الصغيرة يمكن استبعادها إذا وضعت الحكومات تدابير مالية أو غيرها من شأنها أن خفض انبعاثاتها من قبل ما يعادلها في قطاع الطيران، حتى عام 2018 ينطبق إتس الاتحاد الأوروبي فقط على الرحلات الجوية بين المطارات الواقعة في المنطقة الاقتصادية الأوروبية (إيا).
تقديم تخفيضات في الانبعاثات.
وقد أثبتت إتس الاتحاد الأوروبي أن وضع سعر على الكربون والتداول في ذلك يمكن أن تعمل. وتنخفض الانبعاثات من المنشآت في المخطط حسب الغرض - بنحو 5٪ مقارنة مع بداية المرحلة 3 (2018) (انظر أرقام 2018).
وفي عام 2020، ستكون الانبعاثات من القطاعات التي يغطيها النظام أقل بنسبة 21 في المائة عما كانت عليه في عام 2005.
تطوير سوق الكربون.
أنشئت في عام 2005، والاتحاد الأوروبي إتس هو أول وأكبر نظام دولي للانبعاثات الانبعاثات في العالم، وهو ما يمثل أكثر من ثلاثة أرباع التجارة الدولية للكربون.
كما تلهم إتس الاتحاد الأوروبي تطوير تجارة الانبعاثات في بلدان ومناطق أخرى. ويهدف الاتحاد الأوروبي إلى ربط إتس الاتحاد الأوروبي مع أنظمة أخرى متوافقة.
التشريعات الرئيسية للاتحاد الأوروبي بشأن التجارة الإلكترونية.
30/04/2018 - نسخة موحدة من التوجيه 2003/87 / إيك للبرلمان الأوروبي والمجلس الذي ينشئ خطة لتداول بدل انبعاث غازات الدفيئة داخل الجماعة وتعديل توجيه المجلس رقم 96/61 / إيك 23/04/2009 - التوجيه رقم 2009/29 / إيك الصادر عن البرلمان الأوروبي والمجلس الأوروبي المعدل للتوجيه 2003/87 / إيك من أجل تحسين وتوسيع نطاق خطة تداول بدل غازات الدفيئة في الجماعة 19/11/2008 - التوجيه 2008/101 / إيك والبرلمان الأوروبي والمجلس الذي يعدل التوجيه 2003/87 / إيك بحيث يشمل أنشطة الطيران في مخطط تداول بدل غازات الدفيئة داخل الجماعة 27/10/2004 - الأمر التوجيهي 2004/101 / إيك الصادر عن البرلمان الأوروبي و المجلس الذي يعدل التوجيه 2003/87 / إيك الذي ينشئ خطة لتداول بدل انبعاث غازات الدفيئة داخل الجماعة فيما يتعلق بآليات مشروع بروتوكول كيوتو 13/10/2003 - الأمر التوجيهي 2003/87 / إيك الصادر عن البرلمان الأوروبي والاتحاد الأوروبي نيل التي تضع مخططا لتداول بدل انبعاث غازات الدفيئة داخل الجماعة وتعديل توجيه المجلس 96/61 / إيك.
تقارير سوق الكربون.
23/11/2017 - كوم (2017) 693 - تقرير عن سير عمل سوق الكربون الأوروبي 01/02/2017 - كوم (2017) 48 - تقرير عن سير عمل سوق الكربون الأوروبي 18/11/2018 - كوم 2018) 576 - تقرير عن أداء سوق الكربون الأوروبي 14/11/2018 - كوم (2018) 652 - حالة سوق الكربون الأوروبي في عام 2018.
تنقيح إتس للاتحاد الأوروبي للمرحلة 3.
04/02/2018 - استنتاجات المجلس الأوروبي المؤرخة 4 شباط / فبراير 2018 (انظر الاستنتاجين 23 و 24) 18/03/2018 - إرشادات بشأن تفسير المرفق الأول لتوجيه الاتحاد الأوروبي بشأن التجارة الإلكترونية (باستثناء أنشطة الطيران) 18/03/2018 - إرشادات ورقة تعريفية لمولدات الكهرباء 06/04/2009 - بيان صحفي صادر عن المجلس حول اعتماد مجموعة المناخ والطاقة 12/12/2008 - استنتاجات رئاسة المجلس الأوروبي (11 و 12 ديسمبر 2008) 12/12/2008 - المجلس الأوروبي بيان بشأن استخدام عائدات المزادات 23/01/2008 - اقتراح بتوجيه من البرلمان الأوروبي والمجلس بتعديل التوجيه 2003/87 / إيك من أجل تحسين وتوسيع نظام تداول بدل غازات الدفيئة في المجتمع 23 / 01/2008 - وثيقة عمل موظفي اللجنة - وثيقة مصاحبة للاقتراح الخاص بتوجيه للبرلمان الأوروبي والمجلس المعدل للتوجيه 2003/87 / إيك من أجل تحسين وتوسيع نطاق نظام تداول بدل انبعاثات غازات الدفيئة في الاتحاد الأوروبي - تقييم الأثر.
التنفيذ.
04/07/2018 - مشروع لائحة تنظيمية بشأن تحديد الاستحقاقات الائتمانية الدولية 05/06/2018 - مشروع لائحة بشأن تحديد استحقاقات الائتمان الدولي 05/05/2018 لائحة المفوضية رقم الاتحاد الأوروبي رقم 389/2018 بتاريخ 2 مايو 2018 بشأن إنشاء السجل الاتحادي إلى التوجيه رقم 2003/87 / إيك الصادر عن البرلمان الأوروبي والمجلس الأوروبي، والمرسومين رقم 280/2004 / إيك رقم 406/2009 / إيك للبرلمان الأوروبي والمجلس الأوروبي، وإلغاء لائحة المفوضية الأوروبية رقم 920/2018 و لا 1193/2018 نص ذو صلة بالمنطقة الاقتصادية الأوروبية 18/11/2018 - لائحة اللجنة التي تنشئ سجل الاتحاد لفترة التداول التي تبدأ في 1 يناير 2018 وفترات التداول اللاحقة من مخطط الإتجار في الانبعاثات بالاتحاد وفقا للتوجيه 2003/87 / إيك والبرلمان الأوروبي والمجلس، والمقرر 280/2004 / إيك الصادر عن البرلمان الأوروبي والمجلس الأوروبي، وتعديل اللائحة التنفيذية رقم 2216/2004 والاتحاد الأوروبي رقم 920/2018 - لم تنشر بعد في الجريدة الرسمية 07 / 10/2018 - كوميسيون ريجول (الاتحاد الأوروبي) رقم 920/2018 لنظام موحد ومضمون للسجلات عملا بالتوجيه 2003/87 / إيك الصادر عن البرلمان الأوروبي والمجلس الأوروبي والقرار رقم 280/2004 / إيك الصادر عن البرلمان الأوروبي والمجلس - بما في ذلك التغييرات التي أدخلتها لائحة 18 نوفمبر 2018 08/10/2008 - لائحة المفوضية (إيك) رقم 994/2008 لنظام موحد ومضمون من السجلات وفقا للتوجيه 2003/87 / إيك للبرلمان الأوروبي والمجلس الأوروبي - القرار رقم 280/2004 / إيك الصادر عن البرلمان الأوروبي والمجلس - الإصدار الساري حتى 31 ديسمبر 2018 26/10/2007 - قرار اللجنة المشتركة للمنطقة الاقتصادية الأوروبية رقم 146/2007 الذي يربط الاتحاد الأوروبي بالإنكليزية إتس مع النرويج وأيسلندا وليختنشتاين 13/11 / 2006 - قرار اللجنة 2006/780 / إيك بشأن تجنب الازدواجية المزدوجة لانبعاثات غازات الدفيئة في إطار خطة الجماعة المعنية بتداول الانبعاثات لأنشطة المشاريع بموجب بروتوكول كيوتو عملا بالتوجيه 2003/87 / إيك الصادر عن البرلمان الأوروبي والمجلس (ن) (2006) 5362) 21/12/2004 - نسخة موحدة من لائحة المفوضية (إيك) رقم 2216/2004 بشأن نظام موحد ومضمون للسجلات معدلة بموجب لائحة المفوضية رقم 916/2007 المؤرخة 31 يوليو / تموز 2007، لائحة المفوضية (إيك) رقم 994/2008 المؤرخة 8 أكتوبر 2008 ولائحة المفوضية (يو) رقم 920/2018 المؤرخة 7 أكتوبر 2018 - نسخة لا تشمل التغييرات التي أدخلتها لائحة 18 نوفمبر 2018.
تطبيق ضريبة القيمة المضافة.
التاريخ التشريعي للتوجيه 2003/87 / إيك.
العمل قبل اقتراح اللجنة.
08/02/2000 - كوم (2000) 87 - ورقة خضراء بشأن الاتجار بانبعاثات غازات الدفيئة في إطار الاتحاد الأوروبي ولاية ونتائج الفريق العامل الأول التابع للجنة إكب: الآليات المرنة 04/09/2001 - المحضر الموجز لاجتماع التشاور مع أصحاب المصلحة (مع الصناعة والمنظمات غير الحكومية البيئية) 19/05/1999 - كوم (1999) 230 - التحضير لتنفيذ بروتوكول كيوتو 03/06/1998 - كوم (1998) 353 - تغير المناخ - نحو استراتيجية ما بعد كيوتو للاتحاد الأوروبي نطاق إتس للاتحاد الأوروبي : 07/2007 - المنشآت الصغيرة داخل الاتحاد الأوروبي نظام تداول الانبعاثات 10/2006 - إدراج أنشطة إضافية والغازات في الاتحاد الأوروبي نظام تداول الانبعاثات مزيد من المواءمة وزيادة القدرة على التنبؤ: 12/2006 - النهج إلى الداخلين الجدد والإغلاق 10/2006 - مزاد بدائل انبعاث ثاني أآسيد الكربون في الاتحاد الأوروبي إتس 10/2006 - مواءمة منهجيات التخصيص 12/2006 - تقرير عن القدرة التنافسية الدولية فريق عمل إكب المعني بتداول الانبعاثات في استعراض إتس للاتحاد الأوروبي 15/06/2007 - التقرير النهائي للمي 4 بشأن الربط مع أنظمة تجارة الانبعاثات في الدول الثالثة 22/05/2007 - التقرير النهائي للاجتماع الثالث حول مزيد من المواءمة وزيادة القدرة على التنبؤ 26/04/2007 - التقرير النهائي للاجتماع الثاني حول الامتثال الصارم وإنفاذ القانون 09/03/2007 - التقرير النهائي للاجتماع الأول بشأن نطاق التوجيه.
أكتوبر 2001.
22/01/2002 - ورقة غير رسمية عن أوجه التآزر بين اقتراح المفوضية الأوروبية بشأن الاتجار بالانبعاثات (كوم (2001) 581) وتوجيه الاتفاقية الدولية لوقاية النباتات 23/10/2001 - كوم (2001) 581 - اقتراح بشأن توجيه إطاري لتداول انبعاثات غازات الدفيئة داخل الجماعة الأوروبية.
رد فعل اللجنة على قراءة الاقتراح في المجلس والبرلمان (بما في ذلك الموقف المشترك للمجلس)
18/07/2003 - كوم (2003) 463 - رأي اللجنة بشأن تعديلات البرلمان الأوروبي على الموقف المشترك للمجلس بشأن اقتراح توجيه البرلمان الأوروبي والمجلس الأوروبي 20/06/2003 - كوم (2003) 364 - الاتصال باللجنة إلى البرلمان الأوروبي بشأن الموقف المشترك للمجلس بشأن اعتماد توجيه يضع مخططا لتداول بدل انبعاثات غازات الدفيئة داخل الجماعة وتعديل توجيه المجلس 96/61 / إيك 18/03/2003 - الموقف المشترك (إيك ) لا 28/2003 - الموقف المشترك للمجلس بشأن اعتماد توجيه يضع مخططا لتداول بدل انبعاثات غازات الدفيئة داخل الجماعة وتعديل توجيه المجلس 96/61 / إيك 27/11/2002 - كوم (2002) 680 - اقتراح معدل لتوجيه من البرلمان الأوروبي والمجلس يضع مخططا لتداول بدل انبعاث غازات الدفيئة داخل الجماعة وتعديل توجيه المجلس 96/61 / إيك فاق.
افتح جميع الأسئلة.
أسئلة وأجوبة بشأن نظام الاتحاد الأوروبي المنقح لتداول الانبعاثات (كانون الأول / ديسمبر 2008)
ما هو الهدف من تداول الانبعاثات؟
والهدف من نظام االتحاد األوروبي لتداول االنبعاثات هو مساعدة الدول األعضاء في االتحاد األوروبي على تحقيق التزاماتها للحد من انبعاثات غازات الدفيئة أو الحد منها بطريقة فعالة من حيث التكلفة. والسماح للشركات المشاركة بشراء أو بيع بدلات الانبعاثات يعني أن التخفيضات في الانبعاثات يمكن تحقيقها بأقل تكلفة.
إن إتس الاتحاد الأوروبي هو حجر الزاوية في استراتيجية الاتحاد الأوروبي لمكافحة تغير المناخ. وهو أول نظام تجاري دولي لانبعاثات ثاني أكسيد الكربون في العالم، وهو يعمل منذ عام 2005. واعتبارا من الأول من كانون الثاني / يناير 2008، لا ينطبق هذا النظام على الدول الأعضاء في الاتحاد الأوروبي البالغ عددها 27 دولة فحسب، بل ينطبق أيضا على الأعضاء الثلاثة الآخرين في المنطقة الاقتصادية الأوروبية - النرويج وأيسلندا وليختنشتاين. وهي تغطي حاليا أكثر من 000 10 منشأة في قطاعي الطاقة والصناعة وهما مسؤولان جماعيا عن ما يقرب من نصف انبعاثات الاتحاد الأوروبي من ثاني أكسيد الكربون و 40 في المائة من مجموع انبعاثات غازات الدفيئة. ومن شأن إدخال تعديل على توجيه الاتحاد الأوروبي بشأن التجارة الإلكترونية المتفق عليه في تموز / يوليه 2008 أن يجلب قطاع الطيران إلى النظام اعتبارا من عام 2018.
كيف يعمل تداول الانبعاثات؟
و إتس الاتحاد الأوروبي هو نظام "سقف والتجارة"، وهذا يعني أنه يحد من المستوى العام للانبعاثات المسموح بها ولكن، في حدود هذا، يسمح للمشاركين في النظام لشراء وبيع البدلات كما تتطلب. هذه البدلات هي "عملة" التداول المشتركة في قلب النظام. يمنح أحد البدلات لصاحب الحق الحق في انبعاث طن واحد من ثاني أكسيد الكربون أو ما يعادله من غازات الدفيئة الأخرى. ويؤدي الحد الأقصى لعدد البدلات إلى نشوء ندرة في السوق.
وفي فترة التداول الأولى والثانية في إطار هذا المخطط، كان على الدول الأعضاء أن تضع خططا وطنية للتخصيص تحدد المستوى الكلي لانبعاثاتها، وكم عدد البدلات التي تصدرها كل منشأة في بلدها. وفي نهاية كل سنة يجب أن تسلم المنشآت بدلات تعادل انبعاثاتها. ويمكن للشركات التي تبقي انبعاثاتها دون مستوى بدلاتها أن تبيع بدلاتها الزائدة. ويواجه أولئك الذين يواجهون صعوبة في الحفاظ على انبعاثاتهم وفقا لبدلاتهم خيارا بين اتخاذ تدابير للحد من انبعاثاتهم الخاصة - مثل الاستثمار في تكنولوجيا أكثر كفاءة أو استخدام مصادر طاقة أقل كثافة من الكربون - أو شراء البدلات الإضافية التي يحتاجونها في السوق ، أو مزيج من الاثنين. ومن المرجح أن تحدد هذه الخيارات بتكاليف نسبية. وبهذه الطريقة، تخفض الانبعاثات حيثما يكون ذلك أكثر فعالية من حيث التكلفة.
كم من الوقت كان الاتحاد الأوروبي إتس تعمل؟
تم إطلاق إتس الاتحاد الأوروبي في 1 يناير 2005. استمرت فترة التداول الأولى لمدة ثلاث سنوات حتى نهاية عام 2007 وكانت مرحلة "التعلم بالممارسة" للتحضير لفترة التداول الثانية الحاسمة. وبدأت فترة التداول الثانية في 1 يناير 2008 وتستمر لمدة خمس سنوات حتى نهاية عام 2018. وتأتي أهمية فترة التداول الثانية من كونها تتزامن مع فترة الالتزام الأولى لبروتوكول كيوتو، يجب على البلدان الصناعية أن تحقق أهدافها للحد من انبعاثات غازات الدفيئة أو الحد منها. وبالنسبة لفترة التداول الثانية، تم تحديد انبعاثات الاتحاد الأوروبي لانبعاثات غازات الدفيئة بنحو 6.5٪ عن مستويات عام 2005 للمساعدة على ضمان أن الاتحاد الأوروبي ككل، والدول الأعضاء على حدة، يفي بالتزامات كيوتو.
ما هي الدروس الرئيسية المستفادة من التجربة حتى الآن؟
وقد وضعت إتس الاتحاد الأوروبي سعرا على الكربون وأثبتت أن الاتجار في انبعاثات غازات الدفيئة يعمل. وقد أنشأت فترة التداول الأولى بنجاح التداول الحر لبدلات الانبعاث في جميع أنحاء الاتحاد الأوروبي، ووضعت البنية التحتية اللازمة ووضعت سوقا ديناميكية للكربون. وقد تكون الفائدة البيئية للمرحلة الأولى محدودة بسبب التوزيع المفرط للبدلات في بعض الدول الأعضاء وبعض القطاعات، ويرجع ذلك أساسا إلى الاعتماد على إسقاطات الانبعاثات قبل أن تصبح بيانات الانبعاثات التي تم التحقق منها متاحة في إطار إتس للاتحاد الأوروبي. وعندما أبرز نشر بيانات الانبعاثات المؤكدة لعام 2005 هذا "الإفراط في تخصيص"، كان رد فعل السوق كما هو متوقع من خلال خفض سعر السوق للبدلات. وقد أتاح توافر بيانات الانبعاثات المؤكدة للجنة أن تكفل تحديد الحد الأقصى للمخصصات الوطنية في إطار المرحلة الثانية على مستوى يؤدي إلى تخفيضات حقيقية في الانبعاثات.
وإلى جانب التأكيد على الحاجة إلى بيانات تم التحقق منها، أثبتت التجربة حتى الآن أن زيادة المواءمة داخل إتس الاتحاد الأوروبي أمر حتمي لضمان أن يحقق الاتحاد الأوروبي أهدافه في خفض الانبعاثات على الأقل بتكلفة وبحد أدنى من التشوهات التنافسية. والحاجة إلى مزيد من المواءمة أوضح فيما يتعلق بكيفية تحديد الحد الأقصى لبدلات الانبعاثات الإجمالية.
وتبين الفترتان التجاريتان الأوليان أيضا أن الطرق الوطنية المختلفة على نطاق واسع لتخصيص البدلات للمنشآت تهدد المنافسة العادلة في السوق الداخلية. وعلاوة على ذلك، هناك حاجة إلى قدر أكبر من المواءمة والتوضيح والتنقيح فيما يتعلق بنطاق النظام، وإمكانية الحصول على ائتمانات من مشاريع خفض الانبعاثات خارج الاتحاد الأوروبي، وشروط ربط النظام الأوروبي لتكنولوجيا الاتصالات بالأنظمة التجارية للانبعاثات في أماكن أخرى، متطلبات تقديم التقارير.
ما هي التغييرات الرئيسية في إتس الاتحاد الأوروبي، ومتى سيتم تطبيقها؟
وستطبق التغييرات المتفق عليها للتصميم اعتبارا من فترة التداول الثالثة، أي يناير / كانون الثاني 2018. وبينما ستبدأ الأعمال التحضيرية فورا، لن تتغير القواعد السارية حتى يناير 2018 لضمان الحفاظ على الاستقرار التنظيمي.
وستكون معاهدة التجارة الأوروبية للاتحاد الأوروبي في الفترة الثالثة نظاما أكثر كفاءة وأكثر اتساقا وعدلا.
وتتحقق زيادة الكفاءة من خالل فرتة تداول أطول) 8 سنوات بدال من 5 سنوات (، وخفض انبعاثات قوي ومتراجع سنويا) انخفاض بنسبة 21٪ يف عام 2020 مقارنة بعام 2005 (وزيادة كبرية يف كمية املزادات) من أقل من 4٪ في المرحلة 2 إلى أكثر من النصف في المرحلة 3).
وتم الاتفاق على مزيد من المواءمة في العديد من المجالات، بما في ذلك فيما يتعلق بتحديد الحد الأقصى (وهو سقف على نطاق الاتحاد الأوروبي بدلا من الحدود الوطنية في المرحلتين 1 و 2) والقواعد المتعلقة بالتخصيص الحر الانتقالي.
وازدادت عدالة النظام زيادة كبيرة من خلال التحرك نحو قواعد التخصيص المجاني على نطاق الاتحاد الأوروبي للمنشآت الصناعية وبإدخال آلية لإعادة التوزيع تخول للدول الأعضاء الجديدة في المزاد المزيد من البدلات.
كيف يقارن النص النهائي مع اقتراح اللجنة الأولي؟
وقد تم الحفاظ على أهداف المناخ والطاقة التي وافق عليها مجلس الربيع الأوروبي لعام 2007، ولا يزال الهيكل العام لاقتراح اللجنة بشأن إتس للاتحاد الأوروبي سليما. بمعنى أنه سيكون هناك سقف واحد على مستوى الاتحاد الأوروبي على عدد بدلات الانبعاثات، وسوف ينخفض ​​هذا الحد سنويا على طول خط اتجاه خطى، والذي سيستمر بعد نهاية فترة التداول الثالثة (2018-2020). والفرق الرئيسي مقارنة بالمقترح هو أن مزاد العلاوات سيتم تدريجيا على نحو أبطأ.
ما هي التغييرات الرئيسية مقارنة باقتراح اللجنة؟
وباختصار، فإن التغييرات الرئيسية التي أدخلت على المقترح هي كما يلي:
ويسمح لبعض الدول الأعضاء بانتقاص اختياري ومؤقت من القاعدة التي تنص على عدم تخصيص أي بدلات مجانا لمولدات الكهرباء اعتبارا من عام 2018. ويتاح هذا الخيار للتقييد للدول الأعضاء التي تستوفي شروطا معينة تتعلق بالترابط بين الكهرباء وحصة وقود أحفوري واحد في إنتاج الكهرباء، ونصيب الفرد من الناتج المحلي الإجمالي بالنسبة لمتوسط ​​الاتحاد الأوروبي 27. وبالإضافة إلى ذلك، فإن مقدار البدلات المجانية التي يمكن أن تخصصها دولة عضو لمحطات توليد الطاقة يقتصر على 70 في المائة من انبعاثات ثاني أكسيد الكربون من المصانع ذات الصلة في المرحلة 1 والتراجع في السنوات التالية. وعلاوة على ذلك، لا يمكن تخصيص التخصيص المجاني في المرحلة 3 إلا لمحطات توليد الطاقة التي تعمل أو قيد الإنشاء في موعد لا يتجاوز نهاية عام 2008. انظر الرد على السؤال 15 أدناه. وسيكون هناك مزيد من التفاصيل في التوجيه بشأن المعايير التي ستستخدم لتحديد القطاعات أو القطاعات الفرعية التي تعتبر معرضة لخطر كبير من تسرب الكربون، وتاريخ سابق لنشر قائمة اللجنة لهذه القطاعات (31 كانون الأول / ديسمبر) 2009). وعلاوة على ذلك، تخضع المنشآت في جميع الصناعات المعرضة لبدلات مجانية بنسبة 100 في المائة إلى الحد الذي تستخدم فيه التكنولوجيا الأكثر كفاءة، رهنا بالاستعراض عند التوصل إلى اتفاق دولي مرض. ويقتصر التوزيع الحر للصناعة على حصة انبعاثات هذه الصناعات في إجمالي الانبعاثات في الفترة من عام 2005 إلى عام 2007. وسوف ينخفض ​​مجموع البدلات المخصصة مجانا للمنشآت في قطاعات الصناعة سنويا بما يتماشى مع انخفاض سقف الانبعاثات. كما يجوز للدول الأعضاء أن تعوض منشآت معينة عن تكاليف ثاني أكسيد الكربون التي تم تمريرها في أسعار الكهرباء إذا كانت تكاليف ثاني أكسيد الكربون قد تعرضها لخطر تسرب الكربون. وتعهدت اللجنة بتعديل المبادئ التوجيهية للجماعة بشأن المعونة الحكومية لحماية البيئة في هذا الصدد. انظر الرد على السؤال 15 أدناه. وسيزداد مستوى المزاد العلني للبدلات للصناعات غير المعرضة بطريقة خطية على النحو الذي اقترحته اللجنة، ولكن بدلا من الوصول إلى 100٪ بحلول عام 2020 سيصل إلى 70٪، بهدف الوصول إلى 100٪ بحلول عام 2027. وكما هو متوقع في فإن اقتراح اللجنة، سيعاد توزيع 10 في المائة من البدلات المخصصة للمزاد العلني من الدول الأعضاء ذات الدخل الفردي المرتفع إلى ذوي الدخل الفردي المنخفض من أجل تعزيز القدرة المالية لهذه البلدان على الاستثمار في التكنولوجيات الصديقة للبيئة. وقد أضيفت مخصصات لآلية إعادة توزيع أخرى بنسبة 2 في المائة من البدلات المزاد بالمزاد العلني لتأخذ في الاعتبار الدول الأعضاء التي حققت في عام 2005 انخفاضا بنسبة 20 في المائة على الأقل في انبعاثات غازات الدفيئة مقارنة بالسنة المرجعية التي حددها بروتوكول كيوتو. وتزداد حصة إيرادات المزادات التي توصي الدول الأعضاء باستخدامها لمكافحة تغير المناخ والتكيف معه بشكل رئيسي داخل الاتحاد الأوروبي، ولكن أيضا في البلدان النامية، من 20٪ إلى 50٪. وينص النص على زيادة المستوى المقترح لاستخدام اعتمادات الجماعة الإسلامية / آلية التنمية النظيفة في سيناريو بنسبة 20 في المائة بالنسبة للمشغلين الحاليين الذين حصلوا على أقل الميزانيات لاستيراد واستخدام هذه الائتمانات فيما يتعلق بالمخصصات والوصول إلى الائتمانات في الفترة 2008-2018. وستكون القطاعات الجديدة والداخلين الجدد في الفترتين 2018-2020 و 2008-2018 قادرين أيضا على استخدام الائتمانات. ومع ذلك، فإن المبلغ الإجمالي للائتمانات التي يمكن استخدامها لن يتجاوز 50 في المائة من التخفيض بين عامي 2008 و 2020. واستنادا إلى تخفيض أكثر صرامة للانبعاثات في سياق اتفاق دولي مرض، يمكن للجنة أن تسمح بالوصول الإضافي إلى وحدات خفض الانبعاثات المعتمدة ووحدات خفض الانبعاثات للمشغلين في مخطط الجماعة. انظر الرد على السؤال 20 أدناه. وستستخدم العائدات من مزاد 300 مليون بدالة من احتياطي الوافدين الجدد لدعم ما يصل إلى 12 مشروعا ومشروعا إيضاحيا بشأن احتجاز وتخزين الكربون تبين تكنولوجيات مبتكرة للطاقة المتجددة. وهناك عدد من الشروط المرفقة بآلية التمويل هذه. انظر الرد على السؤال 30 أدناه. وقد تم توسيع إمكانية اختيار منشآت الاحتراق الصغيرة بشرط خضوعها لتدابير مماثلة لتغطي جميع المنشآت الصغيرة بغض النظر عن النشاط، فقد تم رفع عتبة الانبعاثات من 10،000 إلى 25،000 طن من ثاني أكسيد الكربون سنويا، وعتبة القدرة التي منشآت الاحتراق يجب أن تفي بالإضافة قد أثيرت من 25MW إلى 35MW. ومع هذه العتبات المتزايدة، تصبح حصة الانبعاثات المغطاة التي يحتمل استبعادها من نظام الاتجار بالانبعاثات هامة، وبالتالي أضيف حكم يسمح بإجراء تخفيض مناظر في الحد الأقصى للبدلات على نطاق الاتحاد الأوروبي.
هل ستظل هناك خطط وطنية للتخصيص (نابس)؟
لا، حددت الدول الأعضاء في خطط عملها الوطنية للفترة الأولى (2005-2007) والفترة التجارية الثانية (2008-2018) الكمية الإجمالية للبدلات التي ستصدر - الحد الأقصى - وكيفية تخصيصها للمنشآت المعنية. وقد ولد هذا النهج اختلافات كبيرة في قواعد التخصيص، مما يخلق حافزا لكل دولة عضو على تفضيل صناعتها الخاصة، وأدى إلى تعقيد كبير.
واعتبارا من فترة التداول الثالثة، سيكون هناك سقف واحد على نطاق الاتحاد الأوروبي وسيتم تخصيص البدلات على أساس القواعد المنسقة. ولذلك لن تكون هناك حاجة إلى خطط تخصيص وطنية.
كيف سيتم تحديد الحد الأقصى للانبعاثات في المرحلة 3؟
وفيما يلي قواعد حساب سقف الاتحاد الأوروبي:
واعتبارا من عام 2018، سينخفض ​​العدد الإجمالي للبدلات سنويا بطريقة خطية. ونقطة البداية في هذا الخط هي متوسط ​​الكمية الإجمالية للبدلات (سقف المرحلة الثانية) الذي ستصدره الدول الأعضاء للفترة 2008-12، وتعديله ليعكس النطاق الواسع للنظام اعتبارا من عام 2018، وكذلك أي منشآت صغيرة عضو وقد اختارت الدول استبعادها. والعامل الخطي الذي ينخفض ​​به المبلغ السنوي هو 1.74٪ بالنسبة إلى غطاء المرحلة 2.
ونقطة الانطلاق لتحديد العامل الخطي 1.74٪ هي التخفيض العام بنسبة 20٪ لغازات الدفيئة مقارنة بعام 1990، وهو ما يعادل انخفاضا بنسبة 14٪ مقارنة بعام 2005. ومع ذلك، يلزم تخفيض أكبر في إتس للاتحاد الأوروبي لأنه cheaper to reduce emissions in the ETS sectors. The division that minimises overall reduction cost amounts to:
a 21% reduction in EU ETS sector emissions compared to 2005 by 2020; a reduction of around 10% compared to 2005 for the sectors that are not covered by the EU ETS.
The 21% reduction in 2020 results in an ETS cap in 2020 of a maximum of 1720 million allowances and implies an average phase 3 cap (2018 to 2020) of some 1846 million allowances and a reduction of 11% compared to the phase 2 cap.
All absolute figures indicated correspond to the coverage at the start of the second trading period and therefore don't take account of aviation, which will be added in 2018, and other sectors that will be added in phase 3.
The final figures for the annual emission caps in phase 3 will be determined and published by the Commission by 30 September 2018.
How will the emission cap beyond phase 3 be determined?
The linear factor of 1.74% used to determine the phase 3 cap will continue to apply beyond the end of the trading period in 2020 and will determine the cap for the fourth trading period (2021 to 2028) and beyond. It may be revised by 2025 at the latest. In fact, significant emission reductions of 60%-80% compared to 1990 will be necessary by 2050 to reach the strategic objective of limiting the global average temperature increase to not more than 2°C above pre-industrial levels.
An EU-wide cap on emission allowances will be determined for each individual year. Will this reduce flexibility for the installations concerned?
No, flexibility for installations will not be reduced at all. In any year, the allowances to be auctioned and distributed have to be issued by the competent authorities by 28 February. The last date for operators to surrender allowances is 30 April of the year following the year in which the emissions took place. So operators receive allowances for the current year before they have to surrender allowances to cover their emissions for the previous year. Allowances remain valid throughout the trading period and any surplus allowances can now be "banked" for use in subsequent trading periods. In this respect nothing will change.
The system will remain based on trading periods, but the third trading period will last eight years, from 2018 to 2020, as opposed to five years for the second phase from 2008 to 2018.
For the second trading period Member States generally decided to allocate equal total quantities of allowances for each year. The linear decrease each year from 2018 will correspond better to expected emissions trends over the period.
What are the tentative annual ETS cap figures for the period 2018 to 2020?
The tentative annual cap figures are as follows:
These figures are based on the scope of the ETS as applicable in phase 2 (2008 to 2018), and the Commission's decisions on the national allocation plans for phase 2, amounting to 2083 million tonnes. These figures will be adjusted for several reasons. Firstly, adjustment will be made to take into account the extensions of the scope in phase 2, provided that Member States substantiate and verify their emissions accruing from these extensions. Secondly, adjustment will be made with respect to further extensions of the scope of the ETS in the third trading period. Thirdly, any opt-out of small installations will lead to a corresponding reduction of the cap. Fourthly, the figures do not take account of the inclusion of aviation, nor of emissions from Norway, Iceland and Liechtenstein.
Will allowances still be allocated for free?
نعم فعلا. Industrial installations will receive transitional free allocation. And in those Member States that are eligible for the optional derogation, power plants may, if the Member State so decides, also receive free allowances. It is estimated that at least half of the available allowances as of 2018 will be auctioned.
While the great majority of allowances has been allocated free of charge to installations in the first and second trading periods, the Commission proposed that auctioning of allowances should become the basic principle for allocation. This is because auctioning best ensures the efficiency, transparency and simplicity of the system and creates the greatest incentive for investments in a low-carbon economy. It best complies with the “polluter pays principle” and avoids giving windfall profits to certain sectors that have passed on the notional cost of allowances to their customers despite receiving them for free.
How will allowances be handed out for free?
By 31 December 2018, the Commission will adopt EU-wide rules, which will be developed under a committee procedure (“Comitology”). These rules will fully harmonise allocations and thus all firms across the EU with the same or similar activities will be subject to the same rules. The rules will ensure as far as possible that the allocation promotes carbon-efficient technologies. The adopted rules provide that to the extent feasible, allocations are to be based on so-called benchmarks, e. g. a number of allowances per quantity of historical output. Such rules reward operators that have taken early action to reduce greenhouse gases, better reflect the polluter pays principle and give stronger incentives to reduce emissions, as allocations would no longer depend on historical emissions. All allocations are to be determined before the start of the third trading period and no ex-post adjustments will be allowed.
Which installations will receive free allocations and which will not? How will negative impacts on competitiveness be avoided?
Taking into account their ability to pass on the increased cost of emission allowances, full auctioning is the rule from 2018 onwards for electricity generators. However, Member States who fulfil certain conditions relating to their interconnectivity or their share of fossil fuels in electricity production and GDP per capita in relation to the EU-27 average, have the option to temporarily deviate from this rule with respect to existing power plants. The auctioning rate in 2018 is to be at least 30% in relation to emissions in the first period and has to increase progressively to 100% no later than 2020. If the option is applied, the Member State has to undertake to invest in improving and upgrading of the infrastructure, in clean technologies and in diversification of their energy mix and sources of supply for an amount to the extent possible equal to the market value of the free allocation.
In other sectors, allocations for free will be phased out progressively from 2018, with Member States agreeing to start at 20% auctioning in 2018, increasing to 70% auctioning in 2020 with a view to reaching 100% in 2027. However, an exception will be made for installations in sectors that are found to be exposed to a significant risk of 'carbon leakage'. This risk could occur if the EU ETS increased production costs so much that companies decided to relocate production to areas outside the EU that are not subject to comparable emission constraints. The Commission will determine the sectors concerned by 31 December 2009. To do this, the Commission will assess inter alia whether the direct and indirect additional production costs induced by the implementation of the ETS Directive as a proportion of gross value added exceed 5% and whether the total value of its exports and imports divided by the total value of its turnover and imports exceeds 10%. If the result for either of these criteria exceeds 30%, the sector would also be considered to be exposed to a significant risk of carbon leakage. Installations in these sectors would receive 100% of their share in the annually declining total quantity of allowances for free. The share of these industries' emissions is determined in relation to total ETS emissions in 2005 to 2007.
CO 2 costs passed on in electricity prices could also expose certain installations to the risk of carbon leakage. In order to avoid such risk, Member States may grant a compensation with respect to such costs. In the absence of an international agreement on climate change, the Commission has undertaken to modify the Community guidelines on state aid for environmental protection in this respect.
Under an international agreement which ensures that competitors in other parts of the world bear a comparable cost, the risk of carbon leakage may well be negligible. Therefore, by 30 June 2018, the Commission will carry out an in-depth assessment of the situation of energy-intensive industry and the risk of carbon leakage, in the light of the outcome of the international negotiations and also taking into account any binding sectoral agreements that may have been concluded. The report will be accompanied by any proposals considered appropriate. These could potentially include maintaining or adjusting the proportion of allowances received free of charge to industrial installations that are particularly exposed to global competition or including importers of the products concerned in the ETS.
Who will organise the auctions and how will they be carried out?
Member States will be responsible for ensuring that the allowances given to them are auctioned. Each Member State has to decide whether it wants to develop its own auctioning infrastructure and platform or whether it wants to cooperate with other Member States to develop regional or EU-wide solutions. The distribution of the auctioning rights to Member States is largely based on emissions in phase 1 of the EU ETS, but a part of the rights will be redistributed from richer Member States to poorer ones to take account of the lower GDP per head and higher prospects for growth and emissions among the latter. It is still the case that 10% of the rights to auction allowances will be redistributed from Member States with high per capita income to those with low per capita income in order to strengthen the financial capacity of the latter to invest in climate friendly technologies. However, a provision has been added for another redistributive mechanism of 2% to take into account Member States which in 2005 had achieved a reduction of at least 20% in greenhouse gas emissions compared with the reference year set by the Kyoto Protocol. Nine Member States benefit from this provision.
Any auctioning must respect the rules of the internal market and must therefore be open to any potential buyer under non-discriminatory conditions. By 30 June 2018, the Commission will adopt a Regulation (through the comitology procedure) that will provide the appropriate rules and conditions for ensuring efficient, coordinated auctions without disturbing the allowance market.
How many allowances will each Member State auction and how is this amount determined?
All allowances which are not allocated free of charge will be auctioned. A total of 88% of allowances to be auctioned by each Member State is distributed on the basis of the Member State's share of historic emissions under the EU ETS. For purposes of solidarity and growth, 12% of the total quantity is distributed in a way that takes into account GDP per capita and the achievements under the Kyoto-Protocol.
Which sectors and gases are covered as of 2018?
The ETS covers installations performing specified activities. Since the start it has covered, above certain capacity thresholds, power stations and other combustion plants, oil refineries, coke ovens, iron and steel plants and factories making cement, glass, lime, bricks, ceramics, pulp, paper and board. As for greenhouse gases, it currently only covers carbon dioxide emissions, with the exception of the Netherlands, which has opted in emissions from nitrous oxide.
As from 2018, the scope of the ETS will be extended to also include other sectors and greenhouse gases. CO 2 emissions from petrochemicals, ammonia and aluminium will be included, as will N2O emissions from the production of nitric, adipic and glyocalic acid production and perfluorocarbons from the aluminium sector. The capture, transport and geological storage of all greenhouse gas emissions will also be covered. These sectors will receive allowances free of charge according to EU-wide rules, in the same way as other industrial sectors already covered.
As of 2018, aviation will also be included in the EU ETS.
Will small installations be excluded from the scope?
A large number of installations emitting relatively low amounts of CO 2 are currently covered by the ETS and concerns have been raised over the cost-effectiveness of their inclusion. As from 2018, Member States will be allowed to remove these installations from the ETS under certain conditions. The installations concerned are those whose reported emissions were lower than 25 000 tonnes of CO 2 equivalent in each of the 3 years preceding the year of application. For combustion installations, an additional capacity threshold of 35MW applies. In addition Member States are given the possibility to exclude installations operated by hospitals. The installations may be excluded from the ETS only if they will be covered by measures that will achieve an equivalent contribution to emission reductions.
How many emission credits from third countries will be allowed?
For the second trading period, Member States allowed their operators to use significant quantities of credits generated by emission-saving projects undertaken in third countries to cover part of their emissions in the same way as they use ETS allowances. The revised Directive extends the rights to use these credits for the third trading period and allows a limited additional quantity to be used in such a way that the overall use of credits is limited to 50% of the EU-wide reductions over the period 2008-2020. For existing installations, and excluding new sectors within the scope, this will represent a total level of access of approximately 1.6 billion credits over the period 2008-2020. In practice, this means that existing operators will be able to use credits up to a minimum of 11% of their allocation during the period 2008-2018, while a top-up is foreseen for operators with the lowest sum of free allocation and allowed use of credits in the 2008-2018 period. New sectors and new entrants in the third trading period will have a guaranteed minimum access of 4.5% of their verified emissions during the period 2018-2020. For the aviation sector, the minimum access will be 1.5%. The precise percentages will be determined through comitology.
These projects must be officially recognised under the Kyoto Protocol’s Joint Implementation (JI) mechanism (covering projects carried out in countries with an emissions reduction target under the Protocol) or Clean Development Mechanism (CDM) (for projects undertaken in developing countries). Credits from JI projects are known as Emission Reduction Units (ERUs) while those from CDM projects are called Certified Emission Reductions (CERs).
On the quality side only credits from project types eligible for use in the EU trading scheme during the period 2008-2018 will be accepted in the period 2018-2020. Furthermore, from 1 January 2018 measures may be applied to restrict the use of specific credits from project types. Such a quality control mechanism is needed to assure the environmental and economic integrity of future project types.
To create greater flexibility, and in the absence of an international agreement being concluded by 31 December 2009, credits could be used in accordance with agreements concluded with third countries. The use of these credits should however not increase the overall number beyond 50% of the required reductions. Such agreements would not be required for new projects that started from 2018 onwards in Least Developed Countries.
Based on a stricter emissions reduction in the context of a satisfactory international agreement , additional access to credits could be allowed, as well as the use of additional types of project credits or other mechanisms created under the international agreement. However, once an international agreement has been reached, from January 2018 onwards only credits from projects in third countries that have ratified the agreement or from additional types of project approved by the Commission will be eligible for use in the Community scheme.
Will it be possible to use credits from carbon ‘sinks’ like forests?
No. Before making its proposal, the Commission analysed the possibility of allowing credits from certain types of land use, land-use change and forestry (‘LULUCF’) projects which absorb carbon from the atmosphere. It concluded that doing so could undermine the environmental integrity of the EU ETS, for the following reasons:
LULUCF projects cannot physically deliver permanent emissions reductions. Insufficient solutions have been developed to deal with the uncertainties, non-permanence of carbon storage and potential emissions 'leakage' problems arising from such projects. The temporary and reversible nature of such activities would pose considerable risks in a company-based trading system and impose great liability risks on Member States. The inclusion of LULUCF projects in the ETS would require a quality of monitoring and reporting comparable to the monitoring and reporting of emissions from installations currently covered by the system. This is not available at present and is likely to incur costs which would substantially reduce the attractiveness of including such projects. The simplicity, transparency and predictability of the ETS would be considerably reduced. Moreover, the sheer quantity of potential credits entering the system could undermine the functioning of the carbon market unless their role were limited, in which case their potential benefits would become marginal.
The Commission, the Council and the European Parliament believe that global deforestation can be better addressed through other instruments. For example, using part of the proceeds from auctioning allowances in the EU ETS could generate additional means to invest in LULUCF activities both inside and outside the EU, and may provide a model for future expansion. In this respect the Commission has proposed to set up the Global Forest Carbon Mechanism that would be a performance-based system for financing reductions in deforestation levels in developing countries.
Besides those already mentioned, are there other credits that could be used in the revised ETS?
نعم فعلا. Projects in EU Member States which reduce greenhouse gas emissions not covered by the ETS could issue credits. These Community projects would need to be managed according to common EU provisions set up by the Commission in order to be tradable throughout the system. Such provisions would be adopted only for projects that cannot be realised through inclusion in the ETS. The provisions will seek to ensure that credits from Community projects do not result in double-counting of emission reductions nor impede other policy measures to reduce emissions not covered by the ETS, and that they are based on simple, easily administered rules.
Are there measures in place to ensure that the price of allowances won't fall sharply during the third trading period?
A stable and predictable regulatory framework is vital for market stability. The revised Directive makes the regulatory framework as predictable as possible in order to boost stability and rule out policy-induced volatility. Important elements in this respect are the determination of the cap on emissions in the Directive well in advance of the start of the trading period, a linear reduction factor for the cap on emissions which continues to apply also beyond 2020 and the extension of the trading period from 5 to 8 years. The sharp fall in the allowance price during the first trading period was due to over-allocation of allowances which could not be “banked” for use in the second trading period. For the second and subsequent trading periods, Member States are obliged to allow the banking of allowances from one period to the next and therefore the end of one trading period is not expected to have any impact on the price.
A new provision will apply as of 2018 in case of excessive price fluctuations in the allowance market. If, for more than six consecutive months, the allowance price is more than three times the average price of allowances during the two preceding years on the European market, the Commission will convene a meeting with Member States. If it is found that the price evolution does not correspond to market fundamentals, the Commission may either allow Member States to bring forward the auctioning of a part of the quantity to be auctioned, or allow them to auction up to 25% of the remaining allowances in the new entrant reserve.
The price of allowances is determined by supply and demand and reflects fundamental factors like economic growth, fuel prices, rainfall and wind (availability of renewable energy) and temperature (demand for heating and cooling) etc. A degree of uncertainty is inevitable for such factors. The markets, however, allow participants to hedge the risks that may result from changes in allowances prices.
Are there any provisions for linking the EU ETS to other emissions trading systems?
نعم فعلا. One of the key means to reduce emissions more cost-effectively is to enhance and further develop the global carbon market. The Commission sees the EU ETS as an important building block for the development of a global network of emission trading systems. Linking other national or regional cap-and-trade emissions trading systems to the EU ETS can create a bigger market, potentially lowering the aggregate cost of reducing greenhouse gas emissions. The increased liquidity and reduced price volatility that this would entail would improve the functioning of markets for emission allowances. This may lead to a global network of trading systems in which participants, including legal entities, can buy emission allowances to fulfil their respective reduction commitments.
The EU is keen to work with the new US Administration to build a transatlantic and indeed global carbon market to act as the motor of a concerted international push to combat climate change.
While the original Directive allows for linking the EU ETS with other industrialised countries that have ratified the Kyoto Protocol, the new rules allow for linking with any country or administrative entity (such as a state or group of states under a federal system) which has established a compatible mandatory cap-and-trade system whose design elements would not undermine the environmental integrity of the EU ETS. Where such systems cap absolute emissions, there would be mutual recognition of allowances issued by them and the EU ETS.
What is a Community registry and how does it work?
Registries are standardised electronic databases ensuring the accurate accounting of the issuance, holding, transfer and cancellation of emission allowances. As a signatory to the Kyoto Protocol in its own right, the Community is also obliged to maintain a registry. This is the Community Registry, which is distinct from the registries of Member States. Allowances issued from 1 January 2018 onwards will be held in the Community registry instead of in national registries.
Will there be any changes to monitoring, reporting and verification requirements?
The Commission will adopt a new Regulation (through the comitology procedure) by 31 December 2018 governing the monitoring and reporting of emissions from the activities listed in Annex I of the Directive. A separate Regulation on the verification of emission reports and the accreditation of verifiers should specify conditions for accreditation, mutual recognition and cancellation of accreditation for verifiers, and for supervision and peer review as appropriate.
What provision will be made for new entrants into the market?
Five percent of the total quantity of allowances will be put into a reserve for new installations or airlines that enter the system after 2018 (“new entrants”). The allocations from this reserve should mirror the allocations to corresponding existing installations.
A part of the new entrant reserve, amounting to 300 million allowances, will be made available to support the investments in up to 12 demonstration projects using the carbon capture and storage technology and demonstration projects using innovative renewable energy technologies. There should be a fair geographical distribution of the projects.
In principle, any allowances remaining in the reserve shall be distributed to Member States for auctioning. The distribution key shall take into account the level to which installations in Member States have benefited from this reserve.
What has been agreed with respect to the financing of the 12 carbon capture and storage demonstration projects requested by a previous European Council?
The European Parliament's Environment Committee tabled an amendment to the EU ETS Directive requiring allowances in the new entrant reserve to be set aside in order to co-finance up to 12 demonstration projects as requested by the European Council in spring 2007. This amendment has later been extended to include also innovative renewable energy technologies that are not commercially viable yet. Projects shall be selected on the basis of objective and transparent criteria that include requirements for knowledge sharing. Support shall be given from the proceeds of these allowances via Member States and shall be complementary to substantial co-financing by the operator of the installation. No project shall receive support via this mechanism that exceeds 15% of the total number of allowances (i. e. 45 million allowances) available for this purpose. The Member State may choose to co-finance the project as well, but will in any case transfer the market value of the attributed allowances to the operator, who will not receive any allowances.
A total of 300 million allowances will therefore be set aside until 2018 for this purpose.
What is the role of an international agreement and its potential impact on EU ETS?
When an international agreement is reached, the Commission shall submit a report to the European Parliament and the Council assessing the nature of the measures agreed upon in the international agreement and their implications, in particular with respect to the risk of carbon leakage. On the basis of this report, the Commission shall then adopt a legislative proposal amending the present Directive as appropriate.
For the effects on the use of credits from Joint Implementation and Clean Development Mechanism projects, please see the reply to question 20.
ما هي الخطوات التالية؟
Member States have to bring into force the legal instruments necessary to comply with certain provisions of the revised Directive by 31 December 2009. This concerns the collection of duly substantiated and verified emissions data from installations that will only be covered by the EU ETS as from 2018, and the national lists of installations and the allocation to each one. For the remaining provisions, the national laws, regulations and administrative provisions only have to be ready by 31 December 2018.
The Commission has already started the work on implementation. For example, the collection and analysis of data for use in relation to carbon leakage is ongoing (list of sectors due end 2009). Work is also ongoing to prepare the Regulation on timing, administration and other aspects of auctioning (due by June 2018), the harmonised allocation rules (due end 2018) and the two Regulations on monitoring and reporting of emissions and verification of emissions and accreditation of verifiers (due end 2018).

Eu emission trading system directive

نحن نستخدم ملفات تعريف الارتباط للتأكد من أننا نقدم لك أفضل تجربة على موقعنا. إذا تابعت دون تغيير إعداداتك، فسنفترض أنك توافق على استلام جميع ملفات تعريف الارتباط في هذا الموقع. مزيد من المعلومات والرجوع إلى سياسة الخصوصية. اقرأ أكثر.
European Union Emissions Trading System (EU ETS) is the cornerstone of the European Union's policy to tackle climate change and its key tool for cost-effective reduction of emissions of carbon dioxide (CO2) and other greenhouse gases (GHG) in the power, aviation and industrial sectors.
The EU ETS was launched in 2005 and is t he first - and still by far the largest - international system for trading greenhouse gas emission allowances covering over three-quarters of the allowances traded on the international carbon market.
The EU ETS operates in the 31 countries of the European Economic Area (EEA).
It limits emissions from nearly 11,000 power plants and manufacturing installations as well as slightly over 500 aircraft operators flying between EEA's airports (Report from the Commission to the European Parliament and to the Council, Report on the functioning of the European carbon market, 23 November 2017 (COM(2017) 693 final, p. 7).
From the start of phase 3 (2018 - 2020), the system covers around 45% of the EU's GHG emissions.
EU Member States may add more sectors and greenhouse gas emissions to the EU ETS (opt-in procedure).
The EU ETS works on the 'cap and trade' principle and is a market-based measure where participants are required to monitor and report their emissions and surrender sufficient emission allowances to cover their reported emissions in each year.
Emission allowances can be traded to enable abatement to occur where it is most cost effective to do, thereby lowering the overall cost of tackling climate change.
A 'cap' is an absolute quantity of greenhouse gases which can be emitted by the factories, power plants and other installations in the system, to ensure the emission reduction target is met.
The cap corresponds to number of allowances put in circulation over a trading phase.
In phases 1 and 2 (2005 - 2018) the EU-wide cap was determined in a bottom-up manner from the aggregated total quantity of allowances laid down by Member States in their National Allocation Plans (NAPs).
As from the start of the phase 3, an EU-wide cap is determined by the EU ETS Directive.
The 2018 cap for emissions from stationary installations was set at 2 084 301 856 allowances.
This cap decreases each year by a linear reduction factor of 1.74% of the average total quantity of allowances issued annually in 2008-2018, thus ensuring that the number of allowances that can be used by stationary installations will be 21% lower in 2020 than in 2005.
The inherent assumptions are that in 2020, emissions from sectors covered by the EU ETS will be 21% lower than in 2005 and by 2030 the decrease will reach the level of 43%.
Improvements of the EU ETS in the third phase.
A major revision of the EU ETS system was agreed in 2009, for the implementation in the third trading phase to run from 2018 until 2020.
The overall driver for the 2009 EU ETS reform was to streamline its operating rules through increased harmonisation of its pre-existing parts fragmented by national borders of the EU Member States.
This tendency has been expressed, in particular, in the following EU ETS features in the period 2018-2020:
- For the purposes of enhanced predictability and stability, a single, EU-wide cap on has been imposed na the allowances' volume, the cap is decreasing by 1.74% annually (in line with the Linear Reduction Factor - LRF), and replaces the previous system of the EU Member States' national caps;
- Open, transparent, harmonised and non-discriminatory auctioning has replaced the free allocation as the default method for allocating emission allowances (the detailed rules are stipulated in the EU ETS Auctioning Regulation;
- The procedures for the free allocation of emission allowances have also been harmonised across the EU and ambitious EU-wide ex-ante performance benchmarks have been introduced (Benchmarking Decision);
- Stricter rules and conditions for the use of international carbon credits in the EU ETS with harmonised limits for their use by operators (for details see here);
- Central electronic Union Registry has replaced the emissions allowances registries run previously individually by the EU Member States. The Central Union Emissions Allowances Registry is governed by a Registry Regulation applying directly in all EU Member States.
Another reform under implementation is to change the emission allowances legal status into financial instruments and subject them (along with being already in scope derivative financial instruments or auctioned products based on them) to financial market supervisory system, mainly to the Markets in Financial Instruments Directive and Regulation under the MiFID II package and the Market Abuse Regulation.
The European Commission in November 2018 proposed a short-term measure to postpone (back-load) auctioning of 900 million emission allowances until 2019 and 2020. The European Parliament and the Council agreed on the proposal in December 2018 and the implementation of back-loading started in March 2018 (more on the EU ETS allowances backloading read here).
On 15 July 2018 the Commission presented a legislative proposal to revise the EU Emissions Trading System in line with the 2030 framework.
Coverage of activities, installations and aircraft operators.
In terms of greenhouse gases EU ETS scope was firstly defined in the Directive 2003/87/EC and has been amended by the Directive 2009/29/EC, including some new activities (such as production and processing of non-ferrous metals, some chemicals etc.) and new greenhouse gases (nitrous oxide (N2O) and perfluorocarbons (PFCs)).
The EU ETS currently covers carbon dioxide (CO2) emissions, nitrous oxide (N2O) emissions from all nitric, adipic, glyoxal and glyoxylic acid production and perfluorocarbons (PFC) emissions from aluminium production ( see Annex I of the Directive which lists the categories of activities to which the ETS currently applies).
As from the start of the phase 3 of the EU ETS (i. e. 1 January 2018), the sectors with stationary installations covered by the EU ETS are energy intensive industries, including power stations and other combustion plants, with ≥20MW thermal rated input (except hazardous or municipal waste installations), oil refineries, coke ovens, iron and steel, cement clinker, glass, lime, bricks, ceramics, pulp, paper and board, aluminium, petrochemicals, ammonia, nitric, adipic, glyoxal and glyoxylic acid production, CO2 capture, transport in pipelines and geological storage of CO2.
Even though participation in the EU ETS is mandatory, in some sectors only installations above a certain size are included.
Moreover, participating countries can exclude small installations from the system if measures are in place that will cut their emissions by an amount equivalent to the amount of emissions which would have been cut had the installations been included in the EU ETS.
Participating countries may also add more sectors and GHGs to the EU ETS.
The EU ETS covers about 11 000 power plants and manufacturing installations in all EU Member States, Iceland, Norway and Liechtenstein (Report on the functioning of the European carbon market, accompanying the document Report from the Commission to the European Parliament and to the Council, Climate action progress report, including the report on the functioning of the European carbon market and the report on the review of Directive 2009/31/EC on the geological storage of carbon dioxide of 18 November 2018 (COM(2018) 576 final), p. 5).
The aviation scope of the EU ETS is limited to flights within the EEA until 2018.
The aviation activities within the initial scope of the EU ETS included all flights from or to an aerodrome situated in the territory of a Member State to which the Treaty applies, with some exceptions as listed in Annex I of the EU ETS Directive.
However, in the light of the negotiations within ICAO looking to propose a global market based mechanism for reduction of aviation emissions, this scope has been temporarily reduced and only flights within the EEA are covered.
Table: Key features of the EU ETS across trading phases.
EU27 + Norway, Iceland, Liechtenstein.
Croatia from 1.1.2018.
(aviation from 1.1.2018)
Power stations and other.
combustion plants ≥20MW.
Iron and steel plants.
Paper and board.
Same as phase 1 plus Aviation (from 2018)
Same as phase 1 plus.
Aviation from 1.1.2018.
Nitric, adipic and glyoxylic.
transport in pipelines and geological storage of CO2.
N2O emissions via opt-in.
CO2, N2O, PFC from aluminium production.
2084 million tCO2 in 2018,
decreasing in a linear way by 38 million tCO2 per year.
Not eligible: Credits from forestry, and large hydropower projects.
CERs and ERUs from forestry, HFC, N2O or large hydropower projects.
Note: CERs from projects registered after 2018 must be from Least Developed Countries.
Source of the Table: EU ETS Handbook, p. 18, 19.
There are four types of tradable credits under the EU ETS:
- EU Aviation Allowances (EUAAs),
- Certified Emission Reduction (CERs),
- Emission Reduction Units (ERUs).
EUAs are most common units, EUAAs entitle the holder to emit one tonne of carbon dioxide within the valid period, has been created specifically for the compliance of aircraft operators and can be surrendered only by aviation operators and enjoy considerably smaller tradable demand.
Qualifying credits for emission reductions accomplished outside the European Union, which can be also, within certain limits, submitted for compliance under EU ETS are CERs and ERUs (however, they need to be translated into EUAs in order to count for compliance purposes).
CERs are obtained through the Clean Development Mechanism (CDM), which allows emission reductions achieved in less developed country to be credited in a developed country.
ERUs are produced through the Joint Implementation (JI) mechanism, which promotes technology transfer between Kyoto Protocol Annex 1 countries.
EU ETS carbon market.
The EU ETS carbon market is dominated by derivatives - it is assessed around 85% of trade in allowances involves the use of derivatives: futures, forwards, options, which are subject to EU financial markets regulations.
In 2018, the EU ETS total volume traded was 8.33 billion tonnes of CO2 either as spot allowances or derivatives of allowances (total value of EUR 47 billion), where only around 900 million allowances were traded on the spot market (value of about EUR 5.2 billion).
EU ETS covers more than 11 000 power stations and industrial plants in 31 countries, around 2 000 intermediaries, traders, organisations and individuals voluntarily participate in the EU ETS.

Participating in the EU Emissions Trading System (EU ETS)
Introduction to the EU Emissions Trading System including how the cap-and-trade System works, how free allowances are allocated, details on complying, the inclusion of aviation in the System and the UK’s opt-out scheme for small emitters and hospitals.
نظرة عامة.
The EU ETS is the largest multi-country, multi-sector greenhouse gas emissions trading system in the world.
It includes more than 11,000 power stations and industrial plants across the EU with around 1,000 of these in the UK. These include power stations, oil refineries, offshore platforms and industries that produce iron and steel, cement and lime, paper, glass, ceramics and chemicals.
Other organisations, including universities and hospitals, may also be covered by the EU ETS depending upon the combustion capacity of equipment at their sites. Aviation operators flying into or from a European airport are also covered by the EU ETS .
This guidance explains the EU ’s cap and trade system, including details of the phases of delivery of the System. It provides information on the UK’s application for Phase III free allowances via its National Implementation Measures (NIMs ), as well as details of compliance and verification. There are also sections on emissions regulation for the aviation industry and the UK’s Small Emitters and Hospitals Opt-out Scheme.
Cap and trade.
The EU ETS works on a ‘cap and trade’ basis, so there is a ‘cap’ or limit set on the total greenhouse gas emissions allowed by all participants covered by the System and this cap is converted into tradable emission allowances.
Tradable emission allowances are allocated to participants in the market; in the EU ETS this is done via a mixture of free allocation and auctions. One allowance gives the holder the right to emit 1 tonne of CO2 (or its equivalent). Participants covered by the EU ETS must monitor and report their emissions each year and surrender enough emission allowances to cover their annual emissions.
Participants who are likely to emit more than their allocation have a choice between taking measures to reduce their emissions or buying additional allowances; either from the secondary market – eg companies who hold allowances they do not need – or from Member State held auctions. More information is available on the EU ETS : carbon markets webpage.
It does not matter where (in terms of physical location) emission reductions are made because emissions savings have the same environmental effect wherever they are made.
The rationale behind emissions trading is that it enables emission reductions to take place where the cost of the reduction is lowest, lessening the overall cost of tackling climate change.
How trading works: a simplified hypothetical example.
Historically installation A and installation B both emit 210 tonnes of CO2 per year. Under the EU ’s allocation process they are given 200 allowances each. At the end of the first year, emissions of 180Mt were recorded for installation A as it installed an energy efficient boiler at the beginning of the year which reduced its CO2 emissions. It is now free to sell its surplus allowances on the carbon market.
Installation B however emitted 220Mt CO2 because it needed to increase its production capacity and it was too expensive for it to invest in energy efficiency technology.
Therefore, installation B bought allowances from the market, which had been made available because installation A has been able to sell its additional allowances.
The net effect is that the investment in carbon reduction occurs in the cheapest place, and CO2 emissions are limited to the 400 allowances issued to both installations.
Delivery phases of the Emissions Trading System.
To date, 3 operational phases of the EU ETS have been delivered or agreed although it is envisaged the scheme will continue beyond 2020:
Phase I (1 January 2005 to 31 December 2007)
This phase is complete. Further details around this phase can be viewed on the National Archives version of the DECC: EU ETS Phase I web page.
Phase II (1 January 2008 to 31 December 2018)
Phase II of the EU ETS coincided with the first Kyoto Commitment Period. Phase II built on the lessons from the first phase, and was broadened to cover CO2 emissions from glass, mineral wool, gypsum, flaring from offshore oil and gas production, petrochemicals, carbon black and integrated steelworks.
In Phase II, each Member State developed a National Allocation Plan (NAP ), which set out the total quantity of allowances that the Member State intended to issue during that phase and how it proposed to distribute those allowances to each of its operators covered by the System. Each NAP had to be approved by the European Commission. The approved UK Phase II NAP was published on 16 March 2007.
Further details around this phase can be viewed on the National Archives version of the National Archives version of the DECC: EU ETS Phase 2 web page.
Phase III (1 January 2018 to 31 December 2020)
The current phase of the EU ETS builds upon the previous two phases and is significantly revised to make a greater contribution to tackling climate change including: an EU - wide cap on the number of available allowances and an increase in auctioning of those allowances, as well as the UK’s scheme to lower compliance costs for small emitters and hospitals.
The EU cap will reduce the number of available allowances by 1.74% each year, delivering an overall reduction of 21% below 2005 verified emissions by 2020. The trajectory will be calculated from a departure point of the mid-point of Phase II and will describe a declining cap from 2018 onwards.
Free allocation of allowances.
All sectors covered by the EU ETS , with the exception of most of the EU power sector, are provided with a free allocation of allowances in order to assist with their transition towards a low carbon economy.
In addition, industrial sectors at significant risk of competition from countries without similar carbon costs (see section on carbon leakage in the EU ETS for more information) are eligible to receive a higher proportion of allowances for free.
In 2018, Member States were required to submit to the European Commission a list of the preliminary number of free allowances to be issued to each industrial installation in Phase III, referred to as ‘National Implementation Measures’ or ‘NIMs ’. The UK submitted its NIMs to the European Commission on 12 December 2018, and subsequently submitted modified NIMs in April 2018.
On 5 September 2018 the European Commission announced completion of the process to check and confirm the free allocation of EU ETS allowances in each Member States’ NIMs . It also announced that a cross sectoral correction factor was required to ensure that free allocation across the EU remains within the cap set in the ETS Directive. The factor reduced the preliminary allocation for each EU ETS installation by 5.73% in 2018, rising to 17.56% in 2020. The average reduction of allocation is therefore 11.58% over the period 2018-2020.
The first list below shows free allocation figures in Phase III for each industrial installation in the UK, as approved by the European Commission on 18 December 2018. The second list shows updated free allocation figures for Phase III, taking into account any changes to the allocation agreed in the UK’s NIMs for individual installations as of 30 April 2018, for instance due to partial cessations, significant capacity reductions or where installations have entered the EU ETS (new entrants). This list will be updated on an annual basis to take into account further changes to allocation over the course of the phase.
Phase III free allocation as approved in the UK National Implementation Measures.
PDF , 635KB , 14 pages.
قد لا يكون هذا الملف مناسبا لمستخدمي التكنولوجيا المساعدة. طلب نسق يسهل الوصول إليه.
إذا كنت تستخدم التكنولوجيا المساعدة (مثل قارئ الشاشة) وتحتاج إلى إصدار من هذا المستند بتنسيق أكثر سهولة، يرجى مراسلتنا على البريد الإلكتروني: communicationence@decc. gsi. gov. uk. من فضلك قل لنا ما الشكل الذي تحتاجه. وسوف يساعدنا إذا كنت تقول ما التكنولوجيا المساعدة التي تستخدمها.
UK National Allocation Table: Phase III free allocation including changes to allocation: June 2018.
PDF , 727KB , 31 pages.
قد لا يكون هذا الملف مناسبا لمستخدمي التكنولوجيا المساعدة. طلب نسق يسهل الوصول إليه.
إذا كنت تستخدم التكنولوجيا المساعدة (مثل قارئ الشاشة) وتحتاج إلى إصدار من هذا المستند بتنسيق أكثر سهولة، يرجى مراسلتنا على البريد الإلكتروني: communicationence@decc. gsi. gov. uk. من فضلك قل لنا ما الشكل الذي تحتاجه. وسوف يساعدنا إذا كنت تقول ما التكنولوجيا المساعدة التي تستخدمها.
UK National Allocation Table: Phase III National Allocation including changes: April 2018.
PDF , 397KB , 32 pages.
قد لا يكون هذا الملف مناسبا لمستخدمي التكنولوجيا المساعدة. طلب نسق يسهل الوصول إليه.
إذا كنت تستخدم التكنولوجيا المساعدة (مثل قارئ الشاشة) وتحتاج إلى إصدار من هذا المستند بتنسيق أكثر سهولة، يرجى مراسلتنا على البريد الإلكتروني: communicationence@decc. gsi. gov. uk. من فضلك قل لنا ما الشكل الذي تحتاجه. وسوف يساعدنا إذا كنت تقول ما التكنولوجيا المساعدة التي تستخدمها.
UK National Allocation Table: Phase III National Allocation including changes: April 2018.
MS Excel Spreadsheet , 73.2KB.
قد لا يكون هذا الملف مناسبا لمستخدمي التكنولوجيا المساعدة. طلب نسق يسهل الوصول إليه.
إذا كنت تستخدم التكنولوجيا المساعدة (مثل قارئ الشاشة) وتحتاج إلى إصدار من هذا المستند بتنسيق أكثر سهولة، يرجى مراسلتنا على البريد الإلكتروني: communicationence@decc. gsi. gov. uk. من فضلك قل لنا ما الشكل الذي تحتاجه. وسوف يساعدنا إذا كنت تقول ما التكنولوجيا المساعدة التي تستخدمها.
UK National Allocation Table: Phase III National Allocation including changes: April 2017.
PDF , 407KB , 24 pages.
قد لا يكون هذا الملف مناسبا لمستخدمي التكنولوجيا المساعدة. طلب نسق يسهل الوصول إليه.
إذا كنت تستخدم التكنولوجيا المساعدة (مثل قارئ الشاشة) وتحتاج إلى إصدار من هذا المستند بتنسيق أكثر سهولة، يرجى مراسلتنا على البريد الإلكتروني: communicationence@decc. gsi. gov. uk. من فضلك قل لنا ما الشكل الذي تحتاجه. وسوف يساعدنا إذا كنت تقول ما التكنولوجيا المساعدة التي تستخدمها.
Carbon leakage and the EU ETS.
Carbon leakage is a term used to describe the prospect of an increase in global greenhouse gas emissions when a company shifts production or investment outside the EU because - in the absence of an legally binding international climate agreement - they are unable to pass on the cost increases induced by the EU ETS to their customers without significant loss of market share.
The best way to address carbon leakage would be a legally binding international climate agreement. This would create a level playing field for industry inside and outside the EU with respect to accounting for the costs of carbon.
In the meantime, the EU ETS provides 2 mechanisms to mitigate the risk of carbon leakage. First, sectors deemed to be at significant risk of carbon leakage are eligible to receive 100% free allocation of allowances up to the sector’s benchmark. This is a significant source of relief, as sectors not deemed at risk will receive 80% of their allocation for free in 2018, declining annually to 30% in 2020 with a view to reaching 0% (ie full auctioning) in 2027.
The second mechanism allows Member States to compensate sectors at significant risk of carbon leakage as a result of indirect EU ETS costs (ie through EU ETS - related increases in electricity prices), provided that schemes are designed within the framework set by the European Commission (see section on indirect carbon leakage compensation scheme for more information).
The UK government strongly supports the principle of free allocation in the absence of an international climate agreement. We believe that the proportionate free allocation of allowances gives relief to sectors at significant risk of carbon leakage, without raising barriers to international trade. We are concerned however that those most at risk may not be compensated sufficiently in the future if current EU ETS rules are not reformed for Phase IV of the EU ETS .
The UK government recognises industry concerns around competitiveness and carbon leakage and is committed to ensuring that sectors genuinely at significant risk of carbon leakage are protected from this risk. In June 2018, we published a research project commissioned by the Department of Energy and Climate Change and undertaken by Vivid Economics and Ecofys, which investigates the occurrence of carbon leakage so far and the fundamental drivers of carbon leakage for a selection of industrial sectors and assesses the measures in place for its mitigation.
The report models the risk of carbon leakage for 24 industrial sectors, and was produced in consultation with industry stakeholders. Modelling analysis shows that in the absence of any mitigating policy measures (such as free allocation of allowances), no allowance for carbon abatement potential, and no increase in carbon regulation outside of the European Union, a number of sectors are at risk of leakage. Given these assumptions, the modelling analysis shows higher rates of carbon leakage than would be expected to occur in reality. The views expressed in the report are those of its writers, and do not represent an official position of the UK government.
The final report, case studies and associated peer review are available:
Assessment of carbon leakage status for the free allocation of allowances.
Sectors at risk of carbon leakage are assessed against a set of criteria and thresholds set out in the EU ETS Directive. The list of sectors deemed at risk of leakage for the period 2018-2018 were agreed through the EU comitology procedure in December 2009, with additions to the list made in subsequent European Commission Decisions.
The EU ETS Directive allows for a review of sectors at risk every five years, with the possibility of adding sectors to the list on annual, ad hoc basis. On 5 May 2018, the European Commission published its draft list of sectors for the period 2018-19, based on the quantitative and qualitative criteria set out in the ETS Directive. The draft carbon leakage list will be presented to the EU Climate Change Committee for vote shortly, after which it must be sent to the European Parliament and the Council for three months scrutiny before adoption.
On 31 August 2018, the UK responded to the European Commission’s consultation on the methodology for determination of the carbon leakage list for 2018 to 2019.
Indirect carbon leakage compensation scheme.
In the 2018 Autumn Statement, the Chancellor announced that the government intended to implement measures to reduce the impact of policy on the costs of electricity for the most electricity-intensive industries, beginning in 2018 and worth around £250 million over the Spending Review period.
As part of this, the government has committed to compensate the most electricity-intensive businesses to help offset the indirect cost of the Carbon Price Floor and the EU ETS , subject to state aid guidelines. In the 2018 Budget, the Chancellor announced that compensation for the indirect costs of the Carbon Price Floor and the EU ETS would be extended to 2019 to 2020.
The European Commission adopted revised State Aid guidelines on compensation for the indirect costs of the EU ETS in June 2018. These guidelines list the sectors deemed to be exposed to a significant risk of carbon leakage due to indirect emissions costs, and provide details of the maximum levels of compensation that can be made available to them. Any Member State compensation scheme must be designed within the framework set by the European Commission.
In October 2018, DECC and BIS launched the energy intensive industries compensation scheme consultation, which set out our proposals for the eligibility and design of the compensation package.
The consultation, which closed in December 2018, provided an opportunity for all those interested in the package to comment on the proposals, helping us ensure that compensation is targeted at those companies who are most at risk of carbon leakage as a result of energy and climate change policies.
Following detailed consideration of the responses and state aid clearance for the EU ETS compensation package, in May 2018 we published the government’s response to the consultation and the final compensation scheme design for the EU ETS . The UK started making payments in respect of indirect costs of the EU ETS in 2018.
For Carbon Price Floor compensation, which remains subject to state aid approval from the European Commission, we expect to publish guidance later in the summer and begin payments shortly thereafter.
New Entrants Reserve.
The New Entrants Reserve (NER ) is a set aside of EU allowances, reserved for new operators or existing operators who have significantly increased capacity. The UK’s EU ETS Regulators are responsible for administering and assessing all NER applications.
Further information on allowances can be found on the EU ETS : allowances page.
Complying with the EU ETS.
The EU ETS Regulators are responsible for enforcing compliance with the EU ETS Regulations, including operational functions such as granting and maintaining permits and emissions plans (for aviation), monitoring and reporting (including monitoring plans), assessing verified emission reports (and tonne-kilometre reports), assessing applications to the NER , determining reductions in allocations as a result of changes in capacity or cessation of activities, exchanging of information with UKAS on verifier activities.
For the purpose of calculating civil penalties, BEIS determine the value of the EU ETS carbon price used by the regulator. The determination is published in November each year:
On 7 August 2018, we launched a consultation on a number of technical amendments to the Greenhouse Gas Emissions Trading Scheme Regulations 2018 so as to simplify and harmonize EU ETS penalties in the transition to Phase III, improve clarity and reduce the burden for businesses. The consultation closed on 19 September 2018.
For more information on how to comply with EU ETS please visit:
Monitoring, reporting, verification and accreditation.
The European Commission’s Guidance on the Accreditation and Verification Regulation aims to help operators of all stationary installations, aviation operators, verification bodies and regulators perform verifications consistently throughout the EU . It provides practical information and advice on the process and requirements for annual verification required by the EU ETS Directive, the European Commission’s Monitoring and Reporting Regulation and Greenhouse Gas permits/monitoring plans/tonne-kilometre plans.
Finding an accredited EU ETS verifier in the UK.
The UKAS list does not include verifiers accredited by other national accreditation bodies and under Phase III rules there is no ‘registration’ or acceptance procedure for non-UK verifiers. All verifiers are required to demonstrate that they are either accredited (or certified) in accordance with the Accreditation and Verification Regulation. Operators are responsible for ensuring that their verifier is accredited for the relevant scope of work. Details of a verifier’s scope of accreditation can be found on the verifier’s accreditation certificate.
Include the following information in your email:
name of verifier organisation country accreditation identification number a copy of your accreditation certificate full name and email address of the main point of contact (this user will have the responsibility for managing other users for this verifier)
Once the ETSWAP administrator has approved your request for access, ETSWAP will send you an email with the login details for your individual user account.
To apply for a verifier Registry account, email etregistryhelp@environment-agency. gov. uk for an application pack.
Further guidance.
Using UK greenhouse gas inventory data in EU ETS monitoring and reporting: the country-specific factor list.
The European Commission’s Regulation on Monitoring and Reporting allows nationally reported data to be used as default factors in specific circumstances.
Carbon emission factors and calorific values from the UK Greenhouse Gas Inventory (AEA-Ricardo) are available for annual emissions reporting for the EU ETS :
Emission factors and calorific values for 2017.
MS Excel Spreadsheet , 81.7KB.
The national factors are Tier 2 and Tier 2a emission factors and net calorific values for specific fuels used by particular industries.
The data have largely been extracted from the UK Greenhouse Gas Inventory that is presented on an annual basis to the United Nations Framework Convention on Climate Change (UNFCCC ). The Greenhouse Gas Inventory is developed independently to the EU Emissions Trading System. This data means the data referred to in Article 31(1) of the Monitoring and Reporting Regulation.
The factors in these tables should only be used in accordance with the requirements in an installation’s approved monitoring plan, which is part of the Greenhouse Gas permit.
Tables for previous years are available as follows:
EU ETS non-compliance.
The EU ETS Directive requires Member States to put in place a system of penalties which is effective, proportionate and dissuasive but the nature of the penalties is largely left to Member State discretion (with the exception of the penalty for failure to surrender sufficient allowances in certain circumstances).
The Greenhouse Gas Emissions Trading System Regulations 2018 set out the civil penalties to which a person is liable if they do not comply with the EU ETS . DECC has produced the guidance below for the offshore oil and gas industry detailing the Department’s approach to enforcement and sanctions.
The Regulations provide for the right of appeal against decisions of an EU ETS Regulator. In England and Wales appeals for both operators of stationary installations and aircraft operators, as well as offshore installations, are heard by the First-tier Tribunal.
Appeals in Northern Ireland are heard and determined by the Planning Appeals Commission (PAC). In Scotland, the Directorate for Planning and Environmental Appeals (DPEA) in the Scottish Government hears and determines appeals on behalf of the Scottish Ministers.
Different arrangements apply to appeals brought by aviation operators against a penalty notice served under the Aviation Greenhouse Gas Emissions Trading Scheme Regulations 2018 for the 2018 scheme year. The relevant rules under the 2018 Regulations continue to apply in relation to any appeal brought against any decision made or notice served under the 2018 Regulations. These provide that the appeal body is the Secretary of State or an independent person appointed by the Secretary of State.
Appeal Determinations.
2018 scheme year: Six appeals determinations have been made under these Regulations:
Aviation in the EU ETS.
The EU Emissions Trading System requires aircraft operators to monitor and report emissions of CO2 and surrender the equivalent number of allowances. The scheme is designed to be a cost-effective means of tackling the CO2 emissions from aviation, enabling the aviation industry to grow sustainably whilst delivering emission reductions. The scheme applies to all flights between airports in the European Economic Area.
The key changes are:
an Intra-European Economic Area (EEA) scope for the Aviation ETS from 1 January 2018 until 31 December 2018 a deferral of compliance deadlines for 2018 emissions until March and April 2018 an exemption for non-commercial operators emitting less than 1,000 tonnes of CO2 per year until 2020 simplified procedures for operators emitting less than 25,000 tonnes of CO2 per year the number of free allowances issued and allowances auctioned are reduced in proportion to the reduction in scope.
We welcome views from any organisation or individual, and the consultation will be of particular interest to aircraft operators, aerodrome operators, verifiers, other participants in the EU ETS and environmental groups.
Regulation of aircraft operators’ emissions.
Each aircraft operator is administered by a single member state. The European Commission produces an annual list showing which operators are administered by which member state.
You can find out more about what operators need to do to comply with the scheme on the EU ETS : operators and activities affected web page.
Auctioning.
Free allocation to aircraft operators.
The European Commission enacted legislation in April 2018 changing the scope of EUETS with regards to international aviation emissions (Regulation (EU ) No 421/2018 amending Directive 2003/87/EC ). As a result of the change in scope of Aviation EU ETS , the UK is obligated to recalculate the allocation of free allowances due to eligible aircraft operators. This recalculation has been done in accordance with the Commission guidance.
The table includes all operators who were previously due free allowances and indicates their new free allowance allocation under the reduced scope. Operators who ceased operations have been removed from this list.
Operators who are now exempt under the new non-commercial de minimis (under 1,000tCO2 per annum calculated on the basis of full scope) still appear in this table. However owing to their exempt status these operators are not due free allowances and as such their Aircraft Operator Holding Account (AOHA) will be marked as ‘excluded’ in the registry – meaning that no transactions can be carried out and no free allowances will be deposited.
If you believe you are no longer due any allowances as a result of the changes or you wish to seek further clarification as to your new free allowance allocation please contact the Environment Agency aviation helpdesk ETAviationHelp@environment-agency. gov. uk.
Historic information.
Please visit the EU ETS legislation page to see UK legislation and EU Regulations.
Please visit the National Archives version of the Aviation in the EU Emissions Trading System web pages to see information relating to aviation/aviation appeals previously available on the DECC website.
Small Emitter and Hospital Opt-out Scheme.
The UK’s Small Emitter and Hospital Opt-out Scheme allows eligible installations to be excluded from Phase 3 (2018 to 2020) of the EU ETS . The scheme has been approved by the European Commission.
Article 27 of the EU ETS Directive enables small emitters and hospitals to be excluded from the EU ETS , with the primary aim of reducing the administrative burdens on these installations. This acknowledges that the administrative costs faced by smaller emitters under the EU ETS are disproportionately high per tonne of CO2, in comparison to the costs for large emitting installations. The Directive requires that excluded installations are subject to a domestic scheme that will deliver an equivalent contribution to emission reductions as the EU ETS .
The UK’s opt-out scheme was designed in consultation with industry and aims to offer a simple, deregulatory alternative to the EU ETS whilst maintaining the incentives for emission reductions. We estimate that the scheme will offer savings of up to £39 million to industry over Phase III.
The opt-out scheme offers deregulatory savings through:
the replacement of a requirement to surrender allowances with an emissions reduction target simplified monitoring, reporting and verification requirements (MRV), including the removal of the requirement for third party verification no requirement to hold an active registry account less burdensome rules for target adjustment following an increase in installation capacity.
Further details on the scheme are contained in the documents listed below. Please note that these documents will be updated later in 2018. The consultations referred to in the ‘Frequently asked questions’ document are now closed.
Participants in the opt-out scheme.
The application period for the opt-out scheme ran from 23 May to 18 July 2018. Operators of 247 installations were approved to participate in the opt-out scheme by the European Commission as excluded from the EU ETS .
The EU ETS Directive does not provide for further installations to join the opt-out scheme.
Previous information on the development of the scheme including, the application period, policy development and the small emitters workshop held on the 12 June 2018, can be viewed on the National Archives website.
معلومات المستند.
Published: 22 January 2018.
Updated: 31 July 2017.
31 July 2017 Emission factors and calorific values for 2017. 27 April 2017 UK National Allocation Table: Phase III National Allocation including changes: April 2017. 21 September 2018 Determination of 4 appeals under the Aviation EU ETS. 28 July 2018 Emission factors and calorific values for 2018 29 April 2018 UK National Allocation Table: Phase III National Allocation including changes: April 2018 29 April 2018 UK National Allocation Table: Phase III National Allocation including changes: April 2018 23 October 2018 Jet Airways civil penalty appeal determination added 20 October 2018 Addition of EU ETS strategy and reform paper 26 August 2018 Addition of free aviation allowance table 16 July 2018 Added information regarding Phase IV. 15 May 2018 Peer review of Ecofys cap-setting report published. 30 April 2018 Updated EU ETS National Allocation table published. 7 August 2018 Details of consultation added under "Complying with the EU ETS". 13 May 2018 The Government response to the consultation on Implementing the Aviation Emissions Trading System ‘stop the clock’ Decision in UK Regulations has been published today. 4 March 2018 Includes new information about a carbon leakage call for evidence. 31 January 2018 Update to include the recent European Commission announcement on NIMS 22 January 2018 First published.
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EU Emissions Trading Scheme (EU ETS)
Guide to the EU Emissions Trading Scheme (EU ETS) and its impact on business.
Content last updated: November 2018.
The EU ETS - also known as the European Union Emissions Trading Scheme - puts a cap on the carbon dioxide (CO2) emitted by business and creates a market and price for carbon allowances. It covers 45% of EU emissions, including energy intensive sectors and approximately 12,000 installations.
See further details below on:
The EU ETS: Phase II (2008-2018)
Phase II of the EU ETS ran from from 2008-2018 (the commitment period of the Kyoto Protocol). During this phase, every EU member state:
Developed a National Allocation Plan (NAP) Member State proposed a limit ('cap') on total emissions from relevant installations The plans were approved by the European Commission, in many cases after some revision. Distributed Allowances The 'Cap' was converted into allowances, known as EUAs (1 tonne of Carbon Dioxide = 1 EUA) The Member States distributed these allowances to installations in the scheme in their country according to their approved plan. Up to 10% of the allowances could be auctioned instead of being given for free. These auctions were largest in the UK and in Germany. Operated the Scheme Installations were obliged to monitor and report verified carbon emissions At the end of each year, installations were obliged to surrender sufficient allowances to cover their emissions and could buy additional allowances or sell any surplus Joint Implementation (JI) and Clean Development Mechanism (CDM) credits could be used within the scheme, through the 'Linking Directive', agreed in 2004)
How the EU ETS works now (2018-2020)
Phase III started in 2018 and run until 2020. The biggest changes in Phase III are:
The scheme was also meant to be extended to the aviation industry from January 2018, covering all flights taking off and landing in the EU, including those originating from or travelling to non-EU countries. However in November 2018 the European Commission decided to defer the extension of the scheme to extra-EU flights until after the International Civil Aviation Organization (ICAO) General Assembly in Autumn 2018, on the expectation that a global agreement on greenhouse gas mitigation from aviation will be reached. The ETS continues to apply to intra-EU flights from January 2018. Latest information on the EU ETS and aviation can be found on gov. uk. Opt-out.
DECC has introduced an opt-out provision for small emitters and hospitals in the UK, allowing them to move to a more "light-touch" scheme with lower administrative costs (which hit disproportionately smaller companies). The opt-out will deliver an equivalent carbon reduction. Allowances.
At least 50% of allowances will be auctioned from 2018 (rather than given to installations). Use of Clean Development Mechanism (CDM) allowances will be more tightly restricted to no more than 50% of the reductions required.
Carbon Trust EU ETS reports.
Publication date: 2004 - 2008.
Cutting Carbon in Europe: The 2020 plans and the future of the EU ETS (CTC734)
Publication date: 01/06/2008.
This report analyses amendments to the EU emissions trading scheme (EU ETS) proposed by the European Commission on the 23 January 2008 and their implications for business.
It concludes that the proposals are a bold and significant step in the right direction that correct weaknesses in the current scheme and provide the level of certainty that business and investors have been calling for.
EU ETS impacts on profitability and trade (CTC728)
Publication date: 11/01/2008.
This report combines data on how business costs would be affected by carbon costs with analysis of the effect on prices and international trade in order to identify the small group of activities for which competitiveness is an issue for the environment, as well as for business, and to identify potential responses.
EU ETS Phase II allocation: implications and lessons (CTC715)
Publication date: 21/05/2007.
This report analyses the implications for the Phase II carbon market (and the resulting industrial abatement incentives) and the wider lessons to be learned from the allocation process.
Allocation and competitiveness in the EU Emissions Trading System: Options for Phase II and beyond (CTC609)
Publication date: 01/06/2006.
This report, based on collaborative research with Climate Strategies, examines the workings of the EU ETS to date and offers analysis and recommendations on its future development.
The study identifies seven key challenges to overcome for the second phase of the EU ETS and sets out the Carbon Trust's own conclusions and recommendations for the future of the EU ETS as an instrument that can both help business deliver emission reductions as efficiently as possible, and also protect and ultimately enhance business competitiveness in a CO 2 - constrained world.
The European Emissions Trading Scheme: Implications for Industrial Competitiveness (CT-2004-04)
Publication date: 30/06/2004.
This report explores in depth the implications of the EU ETS for industrial competitiveness in the UK and the wider EU. It presents our analysis of combined insights from economic modelling and a stakeholder interview programme.
خلفية.
The EU ETS scheme started in 2005 in order to help the EU meet its targets under the Kyoto Protocol (8% reduction in greenhouse gas emissions from 1990 levels).
The scheme is the world's largest carbon-trading scheme. It provides an incentive for installations to reduce their carbon emissions, because they can then sell their surplus allowances.
Installations are included in the scheme on the basis of their Carbon Dioxide (CO2) emitting activities. Industries that are covered include:
Electricity generation Iron & steel Mineral processing (for example: cement manufacture) Pulp and paper processing.
More information on the EU ETS can be found on the DECC website.
خدمات.
International sites.
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