莱州明波水产有限公司海洋牧场建设项目环境影响报告表

I/r/n /r/n/r/n /r/n/r/n /r/n/r/n /r/n/r/n /r/n/r/n /r/n/r/n /r/n/r/n /r/n/r/n /r/n/r/n /r/n/r/n /r/n/r/n /r/n/r/n /r/n/r/n /r/n/r/n /r/n/r/n /r/n/r/n /r/n/r/n /r/n/r/n /r/n/r/n /r/n/r/n /r/n/r/n /r/n/r/n /r/n/r/n /r/n/r/n /r/n/r/n /r/n/r/n /r/n/r/n /r/n/r/n /r/n/r/n /r/n/r/n1/r/n/r/n牧场建设项目/r/n无/r/n/r/n山东省(自/r/n治/r/n区)/r/n烟台/r/n市/r/n莱州市/r/n石虎嘴海域/r/n/r/n用/r/n地(用海)面积/r/n/r/n(/r/nm/r/n2/r/n)/r/n//r/n长度(/r/nkm/r/n)/r/n97933m/r/n2/r/n团/r/n/r/n新建(迁建)/r/n(核准/r/n//r/n备/r/n案)部门/r/n(选填)/r/n项/r/n目审批(核准/r/n//r/n/r/n备/r/n案)文号(选填)/r/n/r/n(万元)/r/n环保投资(万元/r/n)/r/n环保投/r/n资/r/n/r/n占/r/n比(/r/n%/r/n)/r/n/r/n否/r/n/r/n《莱州市养/r/n殖水域滩涂规划(/r/n2018-2030/r/n年)》，烟台市人民政府，烟/r/n析/r/n1/r/n/r/n与《莱州市养殖水域滩涂规划(/r/n2018-2030/r/n/r/n年)》的符合性分/r/n析/r/n根据/r/n《/r/n莱州市养殖水域滩涂规划(/r/n2018-2030/r/n年)》，项目位于莱州/r/n-/r/n/r/n招远农渔业区养殖区的金城北人工鱼礁区(/r/nR/r/n4/r/n)。规划指出：“养殖区/r/n内/r/n/r/n/r/n2/r/n/r/n/r/n的/r/n自身污染，保护海洋环境。”/r/n/r/n/r/n养/r/n殖产品质量，降低养殖生产的自身污染，保护海洋环境”的要求。/r/n/r/n/r/n因此，本项目建设符合《莱州市养殖水域滩涂规划(/r/n2018-2030/r/n年)》。/r/n》叠置图/r/n/r/n2/r/n/r/n产业政策符合性/r/n根据《国家发展改革/r/n委关于修改/r/n</r/n产业结构调整指导目录/r/n(2019/r/n年本/r/n)>/r/n/r/n/r/n3/r/n/r/n规/r/n划区划符合性分析/r/n(/r/n1/r/n)《山东省海洋功能区划(/r/n2011-2020/r/n/r/n年)/r/n》/r/n3/r/n渔/r/n业区(/r/nA/r/n1-8/r/n)内。/r/n图/r/n1-/r/n2/r/n项目与《山东省海洋功能区划(/r/n2011-2020/r/n年)》叠置图/r/nA/r/n1/r/n-8/r/n渔业功能，兼容矿产与能源等功能。在船/r/n锚地、航道及两侧缓冲区水域禁止养/r/n/r/n求/r/n监测。渔业设施建设区海水水质不劣于二/r/n类(/r/n渔港区执行不劣于现状海水水质标准)，海洋沉积物质量/r/n/r/n和海洋生物质量均不劣于二类标准。其它海域海水/r/n水质不劣于/r/n1/r/n)用途管制要求符合性分析/r/n/r/n/r/n2/r/n)用海方式符合性分析/r/n项目在原来的开放式养殖用海的基础/r/n上进行人工鱼礁建设，人工鱼礁区/r/n/r/n4/r/n/r/n3/r/n)/r/n生态保护目标符合性分析/r/n/r/n/r/n/r/n/r/n4/r/n)环境保护要求符合性分析/r/n本/r/n项/r/n目施工期产生的噪声、废气、悬浮泥沙扩散范围较小，生活污水、/r/n/r/n含油污水和生活垃圾均统一收集后送有陆上处理，/r/n不在海域内排放。在施工/r/n过程中开展跟踪监测，确保项目实施不会对海洋/r/n环境影响严重影响。项目运/r/n营期产生的噪声、废气影响范围小、持续时间短，/r/n基本不会产生悬浮泥沙扩/r/n/r/n排放/r/n。/r/n项目建设符合该功能区的环境保护要求。/r/n综上所述，本工程用海符合《山东省海洋功能区划(/r/n2011-2020/r/n年)/r/n》/r/n(/r/n2/r/n)《烟台市海洋功能区划(/r/n2013-2020/r/n/r/n年)》/r/n)》，项目位于莱州湾莱州/r/n海/r/n域农渔业区(/r/nA/r/n1-8-2/r/n)内。/r/n5/r/n图/r/n1-/r/n3/r/n项目与《烟台市海洋功能区划(/r/n2013-2020/r/n年)》叠置图/r/nA/r/n-2/r/n依法设置的锚地、航道及两侧缓冲/r/n/r/n属性，允许小规模透水构筑物/r/n/r/n本项目为/r/n人/r/n工鱼礁项目，共投放/r/n20/r/n个方形人工鱼礁，人工鱼礁的建设/r/n/r/n/r/n该功能区/r/n的/r/n用途管制要求。项目在原来的开放式养殖用海的基础上进行人工/r/n/r/n鱼礁建设/r/n，/r/n人工鱼礁区为透水构筑物用海，面积为/r/n2.4500/r/nhm/r/n2/r/n，规模较小，/r/n/r/n/r/n未/r/n新占用海域，项目建设符合该功能区用海方式要求。/r/n/r/n/r/n本项目施工期产生的噪声、废气、悬浮/r/n泥沙扩散范围较小，生活污水、含油/r/n6/r/n污水和生活垃圾均统一收集后送/r/n有陆上处理，不在海域内排放。在施工过程/r/n中开展跟踪监测，确保项目实施不/r/n会对海洋环境影响严重影响。项目运营期/r/n产生的噪/r/n声/r/n、废气影响范围小、持续时间短，基本不会产生悬浮泥沙扩散，/r/n/r/n/r/n因/r/n此/r/n，项目用海符合该功能区的环境保护要求。/r/n因/r/n此/r/n，项目用海符合《烟台市海洋功能区划(/r/n2013~2020/r/n年)》。/r/n(/r/n3/r/n)与《山东省“十四五”海洋生态环境保护规划》符合/r/n性/r/n/r/n/r/n/r/n/r/n本项目人工/r/n鱼礁的建设能够改善海洋环境，营造动、植物良好的生存环/r/n境，为鱼类及各种浮游动物提供繁殖、生长发育、索饵等的生息场所项目/r/n，/r/n/r/n有利/r/n于/r/n形成良好的海洋生态系统。同时，本项目施工期产生的噪声、废气、/r/n/r/n悬浮泥沙扩散范围较小，生活污水、含油污水和生/r/n活垃圾均统一收集后送有/r/n陆上处理，不在海域内排放。在施工前、施工阶段/r/n以及项目运营期开展跟踪/r/n监测，确保项目建设不会对海洋环境造成影响。项/r/n目运营期看护和捕捞船舶/r/n产生噪声、废气影响范围小，生活污水、含油污水/r/n和生活垃圾均统一收集后/r/n送陆/r/n上处理，不在海域内排放。/r/n4/r/n/r/n与相关规划的符合性分析/r/n/r/n1/r/n)/r/n与《山东省海洋主体功能区规划》的符合性/r/n/r/n/r/n/r/n/r/n/r/n7/r/n/r/n/r/n/r/n根据该规划，/r/n莱州市海域规划为海洋渔业保障区，即“发展滨海/r/n/r/n旅游产业，海上/r/n休/r/n闲度假游，做好莱州浅滩生态环境的保护工作。适度发/r/n/r/n展临港产业、盐/r/n及/r/n盐化工业和海洋生物产业。加强莱州市三山岛渔业资源/r/n/r/n保护区/r/n和/r/n莱州梭子蟹种质资源保护区建设和管理。”/r/n/r/n/r/n/r/n/r/n响/r/n/r/n/r/n/r/n2/r/n)与《山东省人工鱼礁建设规划(/r/n2014-2020/r/n/r/n年)》的符合性/r/n据《山东省人工鱼礁建设规划(/r/n2014-2020/r/n年)》，根据山东省沿海/r/n区/r/n/r/n位/r/n优势、海域生态类型、渔业资源特点和渔区社会经济发展现状，根据“兼/r/n/r/n洋捕捞业和海洋生态建设的协调发展，/r/n统/r/n筹/r/n人工鱼礁、渔业保护区建设和渔业资源增殖放流等渔业资源养护手段，/r/n/r/n提/r/n高渔业资源修复效益，实现海洋生态系统和渔业生物资源养护”的建设思/r/n/r/n路，因地制宜，突出/r/n特/r/n色，规划建设/r/n9/r/n大人工鱼礁带，/r/n40/r/n个人工鱼礁群，/r/n/r/n海/r/n近海/r/n4/r/n个、荣成近海/r/n6/r/n个、文登/r/n-/r/n海阳近海/r/n5/r/n个、青岛近海/r/n4/r/n个、/r/n日/r/n照近海/r/n的人工鱼礁建设格局，构成集人/r/n工鱼礁建/r/n设/r/n、休闲海钓、生态环境修复和资源合理利用等多功能于一体的生/r/n/r/n态/r/n工/r/n程建设框架。/r/n8/r/n/r/n/r/n/r/n/r/n管理。项/r/n目/r/n所在海域所有沉积物调查项目均符合国家一类海洋沉积物标准，/r/n/r/n域整/r/nB/r/n/r/n本项目所在海域浮游植物、浮游动物、底栖生物丰度指数、均匀度指数、/r/n多/r/n/r/n样性指数/r/n较/r/n为正常、调查期间海域环境质量状况良好。渔业资源种类丰富，/r/n/r/n/r/n公顷的四边/r/n形/r/n海域内，选择/r/n2.4500/r/n公顷海域用方形钢混整体构件共建设/r/n20/r/n/r/n个方形人工鱼礁，规划投礁规模/r/n13500/r/nm/r/n3/r/n·空。项目拟建设良性循环/r/n的海/r/n物资/r/n/r/n鱼礁建设、休闲海钓、生态环境修复和资源合理利用等多功能于一体的生/r/n态/r/n/r/n工/r/n程建设框架有着积极作用。/r/n因/r/n此/r/n，项目符合《山东省人工鱼礁建设规划(/r/n2014-2020/r/n年)》。/r/n图/r/n1-4/r/n项目与《/r/n山东省人工鱼礁建设规划(/r/n2014-2020/r/n年)》叠置图/r/n9/r/n3/r/n)/r/n与《烟台市“十四五”海洋经济发展规划(/r/n2021-2025/r/n)》符合性/r/n/r/n/r/n/r/n/r/n/r/n/r/n/r/n聚/r/n。”/r/n/r/n/r/n/r/n/r/n洋经济发展规划(/r/n2021-2025/r/n)》。/r/n4/r/n)与《莱州市海域使用规划(/r/n2013-2020/r/n/r/n年)》的符合性/r/n根据《莱/r/n州/r/n市海域使用规划(/r/n2013-2020/r/n年)》，项目位于金城北人工/r/n/r/n鱼/r/n礁区(/r/n1.4-5/r/n)。金城北人工鱼礁区(/r/n1.4-5/r/n)的用途与开发利用方向为：/r/n/r/n/r/n养殖，兼容风电。在船舶习惯航路和依法设置的锚地、航道及两侧缓冲/r/n区水/r/n/r/n格保护砂/r/n质/r/n自然岸线。”用海方式要求为：“开放式筏式养殖、底播养殖、/r/n/r/n/r/n近岸砂质海岸。保持海水水质现状，海洋沉积物质量和海洋生物质量均/r/n不劣/r/n于/r/n一类标准。”/r/n/r/n/r/n/r/n/r/n/r/n/r/n/r/n因此/r/n，/r/n本项目建设符合《莱州市海域使用规划(/r/n2013-2020/r/n)》。/r/n图/r/n1-/r/n5/r/n项目与《莱州市海域使用规划(/r/n2013-2020/r/n年)》叠置图/r/n(/r/n1/r/n)生态保护红线符合性/r/n1/r/n)/r/n《山东省生态保护红线规划(/r/n2016-2020/r/n/r/n年)》/r/n根/r/n据《山东省生态保护红线规划(/r/n2016-2020/r/n年)》，工程建设不占用/r/n/r/n态红线区为/r/nSW/r/n侧/r/n8.8km/r/n的烟台莱州、招远北/r/n部沿/r/n海/r/n防风固沙生态保护红线区(/r/nSD/r/n-06-/r/nB/r/n3-01/r/n)。/r/n图/r/n1-6/r/n项目与《/r/n山东省生态保护红线规划(/r/n2016-2020/r/n年)》叠置图/r/n2/r/n)/r/n《山东省渤海海洋生态红线划定方案(/r/n2016—2020/r/n/r/n年)》/r/n山/r/n东/r/n省渤海海洋生态红线划定的具体范围为沿海岸线西起漳卫新河河/r/n/r/n/r/n。/r/n/r/n侧/r/n/r/n7.60/r/nkm/r/n/r/n的莱州湾半滑舌鳎口虾蛄梭子蟹渔业海域限制区(/r/nXZ/r/n5-9/r/n)，/r/nE/r/n侧/r/n8.59/r/nkm/r/n/r/n的招远砂质黄金海岸国家级海洋公园(海域部分)(/r/nXZ/r/n2-8/r/n)/r/n，/r/n/r/n/r/n远/r/n渔业海域(/r/nXZ/r/n5-11/r/n)。/r/n工程施工/r/n期间产生的悬浮泥沙不会扩散至周边红线区内，不会对其产生/r/n/r/n污水/r/n、/r/n含油污水和生活垃圾均统一收集后送有陆上处理，不在海域内排放。/r/n/r/n在施/r/n工/r/n过程中开展跟踪监测，确保项目实施不会对海洋环境影响严重影响。/r/n/r/n项目运营期产生的噪声、废气影响范围小、持续时/r/n间短，基本不会产生悬浮/r/n/r/n海/r/n域/r/n内排放，项目建设不会对周边红线区的生态环境造成不利影响。/r/n/r/n年/r/n)》管控要求。/r/n图/r/n1-7/r/n项目与《山/r/n东省渤海海洋生态红线区划定方案(/r/n2013~2020/r/n年)》叠置图/r/n3/r/n)/r/n《/r/n烟台市“三线一单”生态环境分区管控方案》/r/n/r/n/r/n/r/n本项/r/n目/r/n为人工鱼礁项目，共投放/r/n20/r/n个方形人工礁体；本项目不在船舶/r/n/r/n习惯航路和依法设置的锚地、航道及两侧缓冲区水/r/n域投石，符合合理控制开/r/n发强度的要求。人工鱼礁的建设能够改善海洋环境/r/n，营造动、植物良好的生/r/n存环/r/n境/r/n，为鱼类及各种浮游动物提供繁殖、生长发育、索饵等的生息场所。/r/n/r/n本项目施工期产生的噪声、废气、悬浮泥沙扩散范/r/n围较小，生活污水、含油/r/n污水和生活垃圾均统一收集后送有陆上处理，不/r/n在海域内排放。项目运营期/r/n不会产生噪声、废气，基本不会产生悬浮泥沙扩散/r/n。/r/n(/r/n2/r/n)环境质量底线符合性/r/n/r/n/r/n准/r/n，空气质量优良率达到/r/n80%/r/n以上，基本消除重污染天气。水环境质量持/r/n/r/n/r/n.6%/r/n；入海河流消除劣/r/nV/r/n类；近岸海域水/r/n/r/n控/r/n，全市受污染耕地安全利用率达到/r/n96%/r/n以上，污染地块安全利用率达到/r/n/r/n/r/n/r/n/r/n/r/n/r/n/r/n/r/n(/r/n3/r/n)资源利用上线符合性/r/n根据《烟台市“三线一单”生态环境分区管/r/n控方案》，资源利用上线主/r/n/r/n指标/r/n完成省下达任务。实行最严格的水资源管理制度，实现总量及强度“双/r/n/r/n/r/n亿立方米以内，万元国内生产总值用/r/n水/r/n量、万元工业增加值用水量控制目标完成省下达任务；浅层地下水超采区/r/n/r/n/r/n控制国土空间开发强度，土地资源开发利用总量及强度指标达到省下达/r/n目/r/n/r/n/r/n建设/r/n用/r/n地总规模和城市开发强度，落实城镇开发边界控制线。/r/n/r/n/r/n(/r/n4/r/n)环境准入负面清单符合性/r/n未制定环境准入负面清单。根据市场准入负面清单(/r/n2020/r/n/r/n构调/r/n整指导目录/r/n(2019/r/n年本/r/n)>/r/n的决定》，本项目属于鼓励类“第一类、农林/r/n/r/n/r/n。/r/n6/r/n/r/n与政策文件要求符合性/r/n/r/n水(船舶机器处所油污水和油船含货油残余物的油污水)、生活/r/n本项目涉及船舶主要为施工船、运营期养殖看护船及采捕船。含油污/r/n水/r/n/r/n水/r/n体/r/n造成明显影响。项目的建设符合《船舶水污染防治技术政策》的要求。/r/n7/r/n/r/n与《山东省近岸海域环境功能区划(/r/n2016-2020/r/n/r/n年)》的符合性/r/n20/r/n年)》，本项目所在/r/n/r/n人/r/n工/r/n鱼礁施工期间产生的污染物均经妥善处理，不直接向海域内排放。/r/n/r/n鱼礁周围海域采用开放式的养殖方式，对区域/r/n水文动力、冲淤环境等均不会/r/n保护目标的实/r/n现。/r/n图/r/n1-9/r/n《山东省近/r/n岸海域环境功能区划(/r/n2016-2020/r/n年)》/r/n/r/n44.790/r/n″~/r/n37/r/n°/r/n30/r/n′/r/n10.110/r/n″/r/nN/r/n/r/n，/r/n120/r/n°/r/n02/r/n′/r/n54.811/r/n″~/r/n120/r/n°/r/n03/r/n′/r/n25.889/r/n″/r/nE/r/n，项目/r/n为更好的发展生态渔业，实现海洋渔业的可持续发展，莱州明波水产/r/n有限公/r/n司拟在莱州湾东侧、石虎嘴海域、原确权的莱州明波水产有限公司网箱养/r/n殖/r/n项目/r/n /r/n产/r/n有限公司网箱养殖项目变更为莱州明波水产有限公司网箱养殖项目和莱州/r/n明/r/n波水/r/n产有限公司海洋牧场建设项目，用海方式由原来的开放式养殖用海分别变/r/n更/r/n为开/r/n。/r/n/r/n主体工程/r/n/r/n/r/n/r/n/r/n目总投资/r/n950/r/n万元，其中环保投资/r/n16.06/r/n万元，环保投资占项目总投资的/r/n3/r/n/r/n辅助工程/r/n(/r/n1/r/n)材料来源/r/n。/r/n(/r/n2/r/n)辅助设施/r/n/r/n环保工程/r/n(/r/n1/r/n)施工期/r/n施工期生活污水统一收集，送套子湾污水处理厂处理；产生的含油污水委/r/n托/r/n(/r/n2/r/n)运营期/r/n施工期生活污水统一收集，送套子湾污水处理厂处理；产生的油污水委托/r/n含/r/n依托工程/r/n本项目施工期鱼礁体堆放场地及装运码需要依托陆域设施，礁体构件装/r/n运需/r/n/r/n在三山岛习惯性渔船停泊点，采捕季节捕获养殖产品会利用周边习惯性航道/r/n进行/r/n/r/n项目总平面布置/r/n本项目为人工鱼礁建设工程，依据莱州市莱州湾海域的水动力、底质、/r/n生物/r/n资源状况，考虑到项目区形态大小和水深等条件，拟定鱼礁区布置设计方案/r/n，/r/n现/r/n(/r/n1/r/n)人工鱼礁区平面布/r/n置/r/n在礁区平面布置设计上本着节约用海、增殖面积最大化的原则，使项目的/r/n实/r/n/r/n地理位置特点，在用海/r/n面积/r/n34.4007/r/n公顷的四边形海域内，选择适宜区域，建设/r/n/r/n域面积/r/n2.4500/r/nhm/r/n2/r/n，/r/n25/r/n个方形钢混整体构件组成/r/n1/r/n个单位鱼礁(/r/n675m/r/n3/r/n·空)，/r/n(/r/n2/r/n)投礁方案/r/nm/r/n/r/n工方案/r/n项目部设项目经理、技术负责人、材料员、测量工程师、财务主管/r/n、/r/n安全员/r/n各一名及船运负责人两名。技术负责人全面负责现场施工，协调各作业面、/r/n各工/r/n序施工，负责各资源的合理配备；材料员负责材料供应，联系各材料供应点/r/n材料/r/n正常供应，及各种材料陆上、水上运输的协调工作，确保各材料供应满足施/r/n工生/r/n(/r/n1/r/n)预制混凝土构件/r/n严格按照设计标准进行构件礁的成型预制。公司选调经验丰富的技术骨/r/n干和/r/n/r/n由材料员对钢筋质量、水泥标号、砂规格等严格把关。制定专门人员对模具/r/n的定/r/n/r/n程进行质量检查与跟踪，确保预制钢筋混凝土人工礁体达到设计的成型要求/r/n和强/r/n混凝土浇筑用模具按设计要求选择专业模具制作单位进行定制加工。/r/n选用的/r/n钢筋使用前要检查是否合格产品。在钢筋加工过程中如发现脆断、焊接性能/r/n不/r/n正/r/n常时，应进行化学成分检验并停止使用。钢筋下料前必须进行表面除锈。钢/r/n筋/r/n在/r/n弯曲成型时，必须保证尺寸和形状正确，弯点处不能有裂缝。接头焊接和绑/r/n扎/r/n均/r/n/r/n以防/r/n漏浆。要备足足够数量，以满足混凝土连续浇筑的需要。浇筑混凝土应连续/r/n/r/n/r/n混凝土浇筑完毕。浇筑混凝土时应经常观察模板、钢筋、预留孔洞等有无/r/n移动、/r/n(/r/n2/r/n)陆上运输及装卸/r/n/r/n和吊车、铲车，用于将预制礁体从礁体预制场地到专用码头的装载、运输。/r/n所有/r/n码头装卸有专人负责，按/r/n设计要求将不同规格人工预制礁体分类理选堆放，/r/n。/r/n(/r/n3/r/n)海运及投/r/n放/r/n海上运输航行由具有船运资格的船员操作。船员应严格按照海上航行的有/r/n关/r/n规程。海上抛投施工由船上挖掘机操作人员与船员共同完成。船员负责海/r/n上寻找/r/n施工进度安排/r/n工程海域的风、浪等环境因素对海上施工有一定影响，施工中应充分/r/n利用现/r/n施工中必须充分吸纳和使/r/n用先进技术和施工工艺，围绕施工计划关键线路，/r/n除按照常规执行各项海上施工作业的/r/n安全技术规程外，施工现场水域拟设置/r/n/r/n案/r/n合同/r/n放和构件礁体的制作及投放/r/n养殖方案/r/n根据人工鱼礁的养殖方案，在鱼礁周边海/r/n域中，通过自育或外购，选择斑石/r/n/r/n/r/n绍/r/n莱州明波水产有限公司是以优质海水鱼类、贝类育苗养成为主的高新/r/n技术企/r/n/r/n/r/n/r/n/r/n苗、养成、加工到销售、技术/r/n服务的全产业链，产品获得著名商标，列山东农产/r/n/r/n准/r/n状/r/n根据《山东省海洋主体功能区规划》，项目用海位于烟台莱州市海域，/r/n为海洋/r/n/r/n/r/n2/r/n/r/n生态环境现状/r/n/r/n/r/n.506″/r/n.521″/r/n.073″/r/n.816″/r/n.334″/r/n.962″/r/n.408″/r/n.626″/r/n.039″/r/n.988″/r/n.572″/r/n.983″/r/n.167″/r/n.541″/r/n.454″/r/n.973″/r/n.542″/r/n.688″/r/n.026″/r/n.903″/r/n1/r/n2/r/n3/r/n(/r/n1/r/n)海水水质环境/r/n1/r/n)/r/n调查分析项目/r/n/r/n2/r/n)调查分析方法/r/n/r/n《海洋/r/n调/r/n查规范》(/r/nGB/r/n12763-2007/r/n)中的相关规定执行。/r/n检出限/r/n/r/n /r/n(/r/nmg/r/n//r/nL/r/n)/r/npH/r/n/r/n值/r/npH/r/n/r/n计法/r/nGB/r/n法/r/nGB/r/nGB/r/n3/r/nGB/r/n3/r/nGB/r/n3/r/nGB/r/n-3/r/nGB/r/nGB/r/nGB/r/n汞/r/n0/r/n-3/r/nGB/r/n砷/r/n0/r/n.06(μ/r/ng/r/n//r/nL/r/n)/r/nB/r/n铜/r/n3/r/nGB/r/n铅/r/n-3/r/nGB/r/n锌/r/nGB/r/n镉/r/n-3/r/nGB/r/nGB/r/nT/r/n2/r/n测深仪/r/nGB/r/nT/r/n2/r/nGB/r/n安替比林分光光度法/r/nGB/r/ng/r/nL)/r/nGB/r/n3/r/n)评价标准/r/n根据《山东省海洋功能区划(/r/n2011-202/r/n0/r/n)》的海洋环境保护要求以及《海水水/r/n/r/n/r/n业区和/r/n保留区水质评价执行第二类标准，港口航运区(航道、锚地)和工业与城镇/r/n/r/n用海区/r/n水质评价执行第三类标准，港口航运区(港口区)水质评价执行第四类水质/r/n/r/n/r/n/r/n表/r/n/r/n3-4/r/n海水水质标准(/r/nGB/r/n3907-1997/r/n)/r/n(/r/n单位：/r/nmg/r/n//r/nL/r/n，除/r/npH/r/n/r/n值外)/r/npH/r/n铜/r/n铅/r/n7.8/r/n~/r/n8.5/r/n≤/r/n2/r/n≤0.20/r/n≤/r/n0.015/r/n≤0.05/r/n≤/r/n0.005/r/n≤/r/n0.001/r/n7.8/r/n~/r/n8.5/r/n≤/r/n3/r/n≤0.30/r/n≤/r/n0.030/r/n≤0.05/r/n≤/r/n0.010/r/n≤/r/n0.005/r/n6.8/r/n~/r/n8./r/n8/r/n≤/r/n4/r/n≤0.40/r/n≤/r/n0.030/r/n≤0.30/r/n≤/r/n0.050/r/n≤/r/n0.010/r/n6.8/r/n~/r/n8./r/n8/r/n≤/r/n5/r/n≤0.50/r/n≤/r/n0.045/r/n≤0.50/r/n≤/r/n0.050/r/n≤/r/n0.050/r/n锌/r/n镉/r/n砷/r/n≤/r/n0.020/r/n≤/r/n0.001/r/n≤0.05/r/n≤/r/n0.00005/r/n≤/r/n0.020/r/n≤/r/n0.005/r/n≤/r/n0.020/r/n≤/r/n0.050/r/n≤/r/n0.005/r/n≤0.10/r/n≤/r/n0.0002/r/n≤/r/n0.030/r/n≤/r/n0.005/r/n≤/r/n0.050/r/n≤0.10/r/n≤/r/n0.010/r/n≤0.20/r/n≤/r/n0.0002/r/n≤/r/n0.050/r/n≤/r/n0.010/r/n≤/r/n0.100/r/n≤0.50/r/n≤/r/n0.010/r/n≤0.50/r/n≤/r/n0.0005/r/n≤/r/n0.050/r/n≤/r/n0.050/r/n≤/r/n0.250/r/n4/r/n)评价方/r/n法/r/nI/r/ni/r/n=/r/nC/r/ni/r/n//r/nS/r/ni/r/n②/r/n溶解氧(/r/nDO/r/n)采用下式计算：/r/nO/r/nDO/r/nf/r/nDO/r/nDO/r/nf/r/nDO/r/ns/r/nDO/r/nDOs/r/nI/r/ni/r/n/r/n(/r/nDO/r/n)/r/n=10-9/r/nDO/r/n//r/nDO/r/ns/r/n/r/n/r/nDO<DOs/r/nDO/r/nf/r/n/r/n=468/(3/r/n1.6+/r/nt/r/n)/r/nDO/r/nf/r/n—/r/n—/r/n现场水温及氯度条件下，水样中氧饱和浓度(/r/nmg/r/n//r/nL/r/n)；/r/n/r/nDO/r/ns/r/n—/r/n—溶解氧标准值(/r/nmg/r/n//r/nL/r/n)；/r/npH/r/n——/r/npH/r/n调查实测值/r/n*/r/n；/r/n5/r/n)海水水质监测与评价结果/r/n石油类超第二类水质标准，符合第三类水质标准外，其余站位各监测因/r/n子均符合二/r/n(/r/n2/r/n)海洋沉积物环境/r/n1/r/n)/r/n调查分析项目/r/n积物调查项目主要包括：有机碳、硫化物、石油类、锌、铅、铜、砷、/r/n2/r/n)调查分析方法/r/n/r/n《/r/n海/r/n洋调查规范》(/r/nGB/r/n12763-2007/r/n)中的相关规定执行(表/r/n3-5/r/n)。/r/n法/r/n容量法/r/n0/r/n-6/r/n铜/r/n度法/r/n-6/r/n铅/r/n度法/r/n锌/r/n度法/r/n镉/r/n度法/r/n-6/r/n汞/r/n0/r/n-6/r/n铬/r/n度法/r/n-6/r/n砷/r/n-6/r/n3/r/n)评价标准/r/n根据《山东省海洋功能区划(/r/n201/r/n1-2020/r/n)》的海洋环境保护要求和《海洋沉积/r/n/r/n/r/n/r/n石油类(/r/n×10/r/n-6/r/n)/r/n≤/r/n500.0/r/n硫化/r/n物(/r/n×10/r/n-6/r/n)/r/n≤/r/n300.0/r/n≤/r/n500.0/r/n≤/r/n600.0/r/n有机碳(/r/n×10/r/n-2/r/n)/r/n≤2.0/r/n≤3.0/r/n≤4.0/r/n铜/r/n(/r/n×10/r/n-6/r/n)/r/n≤35.0/r/n≤/r/n200.0/r/n铅/r/n(/r/n×10/r/n-6/r/n)/r/n≤60.0/r/n≤/r/n250.0/r/n锌/r/n(/r/n×10/r/n-6/r/n)/r/n≤/r/n350.0/r/n≤/r/n600.0/r/n镉/r/n(/r/n×10/r/n-6/r/n)/r/n≤0.50/r/n≤5.00/r/n汞/r/n(/r/n×10/r/n-6/r/n)/r/n≤0.20/r/n≤0.50/r/n铬/r/n(×10/r/n-6/r/n)/r/n≤/r/n270.0/r/n砷/r/n(×10/r/n-6/r/n)/r/n≤20.0/r/n≤65.0/r/n≤93.0/r/n4/r/n)评价方/r/n法/r/nI/r/ni/r/n/r/n=/r/nC/r/ni/r/n/r/n//r/nS/r/ni/r/ni/r/ni/r/n/r/n/r/n5/r/n)海洋沉积物环境质量监测与评价结果/r/n2021/r/n年/r/n10/r/n月调查工程周边及附近海域沉积物各调查站位各监测因子均/r/n符合所/r/n(/r/n3/r/n)海洋生态环境质量现状/r/n1/r/n)调查方/r/n法/r/n/r/n/r/n样品用浅水Ⅲ型浮游生物网自底至表垂直拖曳获得，经碘液固定、/r/n/r/n海水溶液固定、保存，显微镜下进行种类鉴定，个体记数，挑去杂质，称其/r/n湿重并/r/n底/r/n栖生物：样品的采集、保存和运输按《海洋调查规范》(/r/nGB/r/n12763-2007/r/n)和/r/n/r/n《海洋监测规范》(/r/nGB/r/n17378-2007/r/n)中的规定进行。采用/r/n0.05/r/nm/r/n2/r/n的曙光型采泥器/r/n/r/n/r/n再/r/n用/r/n/r/n75%/r/n的酒精固定。样品运回实验室后，在显微镜下进行种类鉴定并用感量为/r/n2/r/n)评价方法/r/n根据各站位的生物密度，分别计算底栖生物的多样性指数、均匀度指数/r/n和丰富/r/n①/r/n香农/r/n-/r/n威纳(/r/nShannon/r/n-/r/nWiener/r/n)多样性指数/r/ns/r/nH/r/n'/r/n=/r/n/r/n/r/nP/r/ni/r/n/r/n/r/nlog/r/n2/r/nP/r/ni/r/ns/r/n=/r/n1/r/nD/r/nD/r/nJ/r/n/r/n=/r/n=/r/nN/r/n1/r/n/r/n+/r/nN/r/n2/r/n=/r/nT/r/nN/r/nT/r/nlog/r/n2/r/nN/r/n /r/nlog/r/n2/r/nN/r/nd/r/n/r/n=/r/n3/r/n)叶绿素/r/n/r/na/r/n4/r/n)浮游植物/r/n组/r/n海域内浮游植物平均细胞数为/r/n1.88/r/n×/r/n10/r/n7/r/n个/r/n//r/nm/r/n3/r/n个，其变化范围在/r/n4.68/r/n×/r/n10/r/n5/r/n个/r/n//r/nm/r/n3/r/n~/r/n8.18/r/n×/r/n10/r/n7/r/n个/r/n//r/nm/r/n3/r/n之间，出现细/r/n胞数/r/n20/r/n21/r/n年/r/n10/r/n月浮游植物优势种为劳氏角毛藻(/r/nChaetoceros/r/n/r/nlorenzianus/r/n/r/nGrunow/r/n)/r/n/r/n和/r/n角毛藻(/r/nChaetoceros/r/n/r/nspp/r/n./r/n)。/r/n202/r/n1/r/n年/r/n10/r/n月浮游植物调查结果显示，多样性指数/r/n1.45/r/n~/r/n4.08/r/n之间，均匀度指/r/n/r/n数在/r/n0.32/r/n~/r/n0/r/n./r/n82/r/n之间，丰度指数在/r/n0.64/r/n~/r/n1.39/r/n之间。/r/n5/r/n)浮游动物/r/n/r/n/r/n/r/nmg/r/n//r/nm/r/n3/r/n，各站位生物量的波动范围在/r/n/r/n126.9/r/nmg/r/n//r/nm/r/n3/r/n~/r/n9339.8/r/nmg/r/n//r/nm/r/n3/r/n之间，最高生物量/r/n/r/n/r/n/r/n20/r/n21/r/n年/r/n10/r/n月浮游动物调查结果表明，调查海区内浮游动物优势种为夜光虫、/r/n2021/r/n年/r/n10/r/n月浮游动物调查结果表明，调查海域内浮游动物种类多样性/r/n指数值/r/n6/r/n)底栖生物/r/n/r/n布/r/n海区底栖生物的生物量平均为/r/n89.4g/r/n//r/nm/r/n2/r/n/r/n，各站位生物量的波动范围介于/r/n0.235g/m/r/n2/r/n~/r/n151.7g/m/r/n2/r/n之间，以/r/n54/r/n站位最高，/r/n。/r/n202/r/n1/r/n年/r/n10/r/n月调查海域内底栖生物多样性指数在/r/n1.55/r/n~/r/n3.45/r/n之间；均匀度指数/r/n/r/n在/r/n0.73/r/n~/r/n0.925/r/n/r/n之间；丰度指数在/r/n0.39/r/n~/r/n1.6/r/n之间。/r/n(/r/n4/r/n)渔业资源/r/n1/r/n)种类组成/r/n/r/n2/r/n)优势种/r/n葛氏长臂虾；重要/r/n日本蟳、短吻红舌鳎；其他/r/n/r/n3/r/n)资源密度/r/n/r/n/r/n4)幼/r/n体/r/n/r/n/r/n×/r/n10/r/n3/r/nind/r/n//r/nkm/r/n2/r/n。/r/nkg/r/nkm/r/nkg/r/nkm/r/n.84/r/nd/r/nkm/r/n甲壳类幼体平/r/n均资源密度为/r/n1.19/r/nkg/r/n//r/nkm/r/n2/r/n，最小为/r/n0.00/r/nkg/r/n//r/nkm/r/n2/r/n，最大为/r/n3.24/r/n/r/n/r/n4./r/n67/r/n×/r/n10/r/n3/r/nind/r/n//r/nkm/r/n2/r/n。/r/n头足类幼体平均资源密度为/r/n1.96/r/nkg/r/n//r/nkm/r/n2/r/n，最小为/r/n0.00/r/nkg/r/n//r/nkm/r/n2/r/n，最大为/r/n7.19/r/n/r/n/r/n3./r/n70/r/n×/r/n10/r/n3/r/nind/r/n//r/nkm/r/n2/r/n。/r/n5)多样性/r/n/r/n指数平均为/r/n1.807/r/n，分布于/r/n0.4/r/n82/r/n~/r/n2.420/r/n之间；均匀度指数平均为/r/n0.679/r/n，分布于/r/n/r/n0/r/n.299/r/n~/r/n0.861/r/n之间。/r/n(/r/n5/r/n)生物体质量/r/n1/r/n)采样及分析方法/r/n样品制备：鱼、虾类用现场海水冲洗干净，冰冻保存；贝类选择大小相近/r/n的个/r/n/r/n确保样品在冷藏条件下运输，样品由专人负责送回实验室保存。用于生物/r/n质量检测/r/n分析方法：监测项目包括铜、铅、锌、镉、铬、汞、砷、石油烃/r/n等，样品的分/r/n析依据《海洋监测规范第/r/n6/r/n部分：生物体分析》(/r/nGB/r/n17378.6-2007/r/n)的相关规/r/n定/r/n执/r/n铜/r/n度法/r/nAA/r/n000/r/n原子吸收分光光度计/r/n6/r/n铅/r/n度法/r/n-6/r/n锌/r/n度法/r/n6/r/n镉/r/n度法/r/n0/r/n-6/r/n铬/r/n度法/r/n-6/r/n汞/r/nMercur/r/n汞仪/r/n0/r/n-6/r/n砷/r/nPF/r/n2/r/n原子荧光光度计/r/nRF/r/n/r/n荧光分光光度计/r/n2/r/n)评价标准/r/n评价方法与水质评价方法相同，均采用标准指数法和超标统计法。其中单/r/n因子/r/nI/r/ni/r/n/r/n=/r/nC/r/ni/r/n/r/n//r/n/r/nS/r/ni/r/n/r/n3/r/n)评价方/r/n法/r/n贝/r/n类生物质量评价采用《海洋生物质量》(/r/nGB/r/n1842-2001/r/n)中规定的标准值，/r/n/r/n/r/n港/r/n口航运区(航道、锚地)执行第二类生物质量标准，港口航运区(港口区)执行/r/n/r/n/r/n鱼类和甲壳类的生物质量评价采用《全国/r/n海岸和海涂资源综合调查简明规程》/r/n中规定的海洋生物质量/r/n标准，石油烃含量的评价标准采用《第二次全国海洋污染基/r/n线/r/n调/r/n查技术规程》(第二分册)中规定的生物质量标准，见表/r/n3-9/r/n。/r/n表/r/n/r/n3-8/r/n海洋生物质量(/r/nGB/r/n1842-2001/r/n)评价标准标准(单位：/r/nmg/r/n//r/nkg/r/n)/r/n镉/r/n≤/r/n铬/r/n≤/r/n砷/r/n≤/r/n铜/r/n≤/r/n锌/r/n≤/r/n总汞/r/n≤/r/n石/r/n油烃/r/n≤/r/n表/r/n/r/n3-9/r/n生物质量评价项目及其评价标准(单位：/r/nmg/r/n//r/nkg/r/n)/r/n铜/r/n≤/r/n锌/r/n≤/r/n铅/r/n≤/r/n镉/r/n≤/r/n铬/r/n≤/r/n砷/r/n≤/r/n汞/r/n≤/r/n石/r/n油烃/r/n4/r/n)调查结/r/n果/r/n调查/r/n海/r/n域鱼类/r/n2/r/n号站位镉超《全国海岸带和海涂资源综合调查简明规程》中的/r/n/r/n质量标准，超标倍数为/r/n1.233/r/n；贝类/r/n5/r/n号站位镉超《海洋生物质量》(/r/nGB/r/n1842-2001/r/n)/r/n/r/n/r/n(/r/n6/r/n)水动力环境/r/n439″/r/n818″/r/n937″/r/n454″/r/n746″/r/n750″/r/n578″/r/n628″/r/n489″/r/n1/r/n)潮流/r/n/r/n底层最大流速为/r/n37/r/n./r/n1/r/ncm/r/n//r/ns/r/n/r/n；/r/nC/r/n2/r/n站位表层最大流速为/r/n62.5/r/ncm/r/n//r/ns/r/n，中层最大流速为/r/n/r/n/r/n/r/n中层最大流速为/r/n64.1/r/ncm/r/n//r/ns/r/n，底层最大流速为/r/n34.4/r/ncm/r/n//r/ns/r/n/r/n；/r/nC/r/n6/r/n站位表层最大流速/r/n为/r/ncm/r/ns/r/nC/r/n/r/n/r/n/r/n/r/n/r/n/r/nWNW/r/nESE/r/n落/r/n；/r/n垂向上，各站位表层最大流速和平均流速均大于底层，流速基本呈现/r/n自表层至/r/n图/r/n3-5/r/na/r/n/r/n各/r/n站位大潮海流矢量图(表层)/r/n图/r/n3-5/r/nb/r/n/r/n各站位大潮海流矢量图(中层)/r/n图/r/n3-5/r/nc/r/n/r/n各/r/n站位大潮海流矢量图(底层)/r/n2/r/n)余流/r/nC/r/n/r/nC/r/n0/r/n0/r/n0/r/n20/r/n0/r/n20/r/n00/r/n(/r/n7/r/n)水深地形/r/n根据青岛中海基业海洋科技有限公司水下地形测量技术报告，本项目所/r/n在海域/r/n水深介于/r/n12.5~13.5/r/nm/r/n/r/n之间(基于/r/n1985/r/n国家高程标准)。北侧水深相对较大，/r/n介/r/n于/r/n(/r/n8/r/n)工程地/r/n质/r/n受莱州明波水产有限公司委托，烟台大地岩土工程有限公司根/r/n据《岩土工程勘/r/n察/r/n规范》/r/n(GB50021-2001)/r/n(/r/n2009/r/n年版)相关规定，对人工鱼礁项目建设海域进行了/r/n岩土工程勘察，并出具了《莱州明波水产有限公司海洋牧场建设项目岩土工程/r/n勘察/r/n/r/n1/r/n)岩土层分布特/r/n征/r/n含较多淤泥及贝壳碎片，颗粒形状为次圆状，磨圆度一般，颗粒级配不良/r/n。该层分/r/n/r/n②层为粉砂(/r/nQ/r/n4/r/nm/r/n/r/n)：灰/r/n-/r/n灰黄色，饱和，中密，主要颗粒成分为长石、石英/r/n,/r/n含/r/n少量贝壳碎片，颗粒形状为次圆状，磨圆度一般，颗粒级配不良。该层分布/r/n于整个/r/n/r/n/r/n配不良，颗粒形状为次圆，磨圆度一般，粘粒含量较低。该层分布于整个/r/n场区，本/r/n/r/n高/r/n-23.08/r/n米。/r/n根据周围建筑地质资料可知，拟建场地内第③层粗砂以下为粉质黏土层/r/n，其下/r/n2/r/n)地基土的物理力学性质/r/n统计方法及结果：/r/n按《岩土工程勘察规范》(/r/nGB/r/n50021-2001/r/n)(/r/n2009/r/n年版)的/r/n/r/n规定，对各岩土层的标准贯入试验结果进行了分层统计，其平均值、标/r/n准差、变异/r/n。/r/nn/r/nФ/r/nФ/r/nФ/r/nmin/r/nФ/r/nm/r/nФ/r/nσ/r/n6/r/nΦ/r/nk/r/nN/r/n5/r/nN/r/n’/r/n5/r/n表/r/n3-1/r/n2/r/nb/r/n/r/n②层粉砂标准贯入试验结果/r/nn/r/nФ/r/nФ/r/nФ/r/nmin/r/nФ/r/nm/r/nФ/r/nσ/r/n6/r/nΦ/r/nk/r/nN/r/n6/r/nN/r/n’/r/n6/r/nn/r/nФ/r/nФ/r/nФ/r/nmin/r/nФ/r/nm/r/nФ/r/nσ/r/n6/r/nΦ/r/nk/r/nN/r/n6/r/nN/r/n’/r/n6/r/n3/r/n)岩土工程分析评/r/n价/r/n根/r/n据《中国地震动参数区划图》(/r/nGB/r/n18306-2015/r/n)及《建筑抗震设计规范》/r/n/r/n(/r/nGB/r/n50/r/n0/r/n11-2010/r/n)(/r/n2016/r/n年版)可知，本工程场地的抗震设防烈度/r/n7/r/n度，/r/nⅡ/r/n类场地/r/n根据《建/r/n筑/r/n抗震设计规范》(/r/nGB/r/n50011-2010/r/n)(/r/n2016/r/n年版)，场区饱和砂土在/r/n/r/n/r/n第②层粉砂及第③层粗砂均为不液化土层，综合判定拟建场地地基的液化等级为不/r/n/r/n液化(液化指数详见附表—标准贯入试验液化判别及液化指数计算成果表)/r/n。/r/n根据勘察结果，结合场地地面标高及基础底面地层情况，拟建建筑物以/r/n第②层/r/n粉砂作为地基基础持力层时，第②层粉砂及其以下各岩土层层面起伏变化不/r/n大，层/r/n根据野外特征、原位测试结果及室内试验数据资料，对各岩土层进行分/r/n析评定/r/n各岩土层的压缩模量(/r/nEs/r/n1-2/r/n)及地基承载力特征值(ƒ/r/nak/r/n)见表/r/n3-13/r/n。/r/n压/r/n缩模量(/r/nE/r/ns/r/n1-2/r/n)(/r/nMPa/r/n)/r/n承/r/n载力特征值(/r/nkPa/r/n)/r/n①/r/n(/r/n6.50/r/n)/r/n②/r/n(/r/n19.20/r/n)/r/n③/r/n(/r/n31.60/r/n)/r/n根据场地工程地质条件及水文地质条件，结合拟建建筑物类型、荷载要/r/n求、变/r/n形要求及地基条件和场地环境条件综合考虑，本工程拟建建筑物可/r/n考虑采用天然地/r/n图/r/n3-9/r/nb/r/n/r/n工程地质剖/r/n面图(/r/n2-2/r/n’)/r/n图/r/n3-9/r/nc/r/n/r/n工程地质剖面/r/n图(/r/n3-3/r/n’)/r/n图/r/n3-9/r/nd/r/n/r/n工程地质剖/r/n面图(/r/n4-4/r/n’)/r/n(/r/n9/r/n)其/r/n他/r/n/r/n项目属于《环境影响评价技术导则土壤环境(试行)》(/r/nHJ/r/n964-2018/r/n)附录/r/n/r/nA/r/n中土壤环境影响/r/nⅣ/r/n类项目，本项目可不开展/r/n环境影响评价工作。根据《环境影响评/r/nHJ/r/n6/r/n)附录/r/nA/r/n，属于/r/nⅣ/r/n类项目，可不开展地下水/r/n与项/r/n目/r/n有关的原有环境污染和生态破坏问/r/n题/r/n标/r/n标/r/n护目/r/n3/r/n/r/n生/r/n态环境保护目标/r/n标/r/n与项目最/r/n近/r/n/r/n距离/r/n(/r/nkm/r/n)/r/n1/r/n箱养/r/nN/r/n海/r/n水水质不劣于二类(渔港区/r/n执行不劣于现状海水水质/r/n标/r/n/r/n/r/n2/r/n增养殖/r/nN/r/n3/r/n司筏/r/nN/r/nm/r/n4/r/n筏式/r/nW/r/n5/r/n筏式/r/nW/r/n6/r/n7/r/n8/r/n海底/r/nW/r/n9/r/n底底/r/n式养/r/n筏式/r/nS/r/n目/r/nS/r/n司筏式/r/nS/r/n养殖项目/r/nS/r/nE/r/nE/r/n箱养/r/nE/r/nE/r/n筏式/r/nNW/r/nNW/r/n司筏/r/n增养殖项目/r/nkm/r/n增养殖项目/r/n项目/r/n别保护区/r/n/r/n洋沉积物质量和海洋生物/r/n质/r/n/r/n级海洋/r/nS/r/n//r/n(/r/n1/r/n)海洋保护区/r/n项目周边保护区有招远砂质海岸海洋特别保护区和招远砂质黄/r/n金海岸国家级海/r/n主要保护对象为海岸带生态系统和海洋生物资源。招远砂质黄金海/r/n岸国家级海/r/n洋公园所在海域海底平坦，淡水注入多，水质肥沃，邻近莱州湾渔场，是多/r/n种鱼虾/r/n的主要产卵场，也是多种鱼类的索饵场及洄游通道。招远砂质黄金海岸国家/r/n级海洋/r/n公园以沿岸独特的砂质黄金海岸、河口湿地景观为特色，以保护海岸带生态/r/n系统和/r/n(/r/n2/r/n)海水养殖区/r/n项目周边的有较多的人工养殖区，本项目占用莱州明波水产有/r/n限公司网箱养殖/r/n(/r/n3/r/n)旅游/r/n区/r/n/r/n“荧阳郑文公碑”被誉为“魏/r/n碑鼻祖”、“隶楷之极”。南有“群之甲胜”之誉的/r/n/r/n大基山道士谷；北有百里金海/r/n岸，砂质良好，海水洁净，依次建有职工疗养院、西/r/nkm/r/n，总/r/n/r/n闲娱乐和海洋民俗风情为基本内容，以山、海、湖、林、岛为景观背景，建/r/n成的集/r/n/r/n(/r/n4/r/n)村庄/r/n/r/n址、曲松龄旧居、石虎嘴商会分事物所旧址、大基山森林公园、莱州云/r/n峰山旅游景/r/n(/r/n5/r/n)海洋红线区/r/n根据《山/r/n东/r/n省渤海海洋生态红线划定方案(/r/n2016-2020/r/n年)》，工程不占用红线/r/n/r/n环境质量标准/r/n本项目为人工鱼礁项目，在原有的开放式养殖海域内投放海参圈，仅/r/n对船舶废/r/n(/r/n1/r/n)环境空气/r/n根据/r/n《/r/n环境空气质量标准》(/r/nGB/r/n3095-2012/r/n)，一类区(自然保护区、风景名/r/n/r/n胜区/r/n和/r/n其他需要特殊保护的区域)执行一级标准，二类区(居住区、商业交通居民/r/n/r/n混合/r/n区、文化区、工业区和农村地区)执行二级标准。根据本项目的特点，本项目/r/n/r/n执行《环境空气质量标准》(/r/nGB/r/n3095-2012/r/n)的二级标准/r/n；/r/n(/r/n2/r/n)海水水质/r/n根据《海/r/n水/r/n水质标准》(/r/nGB/r/n3097-1997/r/n)，按照海域的不同使用功能和保护目/r/n/r/n标，海水水质分为四类：第一类适用于海洋渔业水域，海上自然保护区和珍/r/n稀颜危/r/n海洋生物保护区；第二类适用于水产养殖区，海水浴场，人体直接接触海水/r/n的海上/r/n运动或娱乐区，以及与人类食用直接有关的工业用水区；第三类适用于一般/r/n工业用/r/n本/r/n项/r/n目为人工鱼礁建设，属于水产养殖类活动，根据《海水水质标准》(/r/nGB/r/n309/r/n7/r/n-1997/r/n)，本项目执行《海水水质标准》(/r/nGB/r/n3097-1997/r/n)中的二类标准。/r/n(/r/n3/r/n)海洋沉积物/r/n根据《海洋沉积物质量》/r/n(/r/nGB/r/n18668-2002/r/n)，按照海域的不同使用功能和环境/r/n保护目标，海洋沉积物质量分为三类：第一类适用于海洋渔业水域，海/r/n洋自然保护/r/n区，珍稀与濒危生物自然保护区，海水养殖区，海水浴场，人体直接接触沉/r/n积物的/r/n海上运动或娱乐区，与人类食用直接有关的工业用水区；第二类适用于一般/r/n工业用/r/n本项目为人工鱼礁建设，属于海水养殖区，因此本项目海洋沉积物执/r/n行《海洋/r/n沉/r/n积物质量》(/r/nGB/r/n18668-2002/r/n)第一类标准；/r/n(/r/n4/r/n)海洋生物质/r/n量/r/n执行《海洋生物质量》(/r/nGB/r/n1842-2001/r/n)第二类标准。鱼类、甲壳类和软体/r/n类/r/n/r/n生物(/r/n除/r/n双壳贝类)生物质量评价，目前国家尚未颁布统一的评价标准，铜、锌、/r/n/r/n铅、镉、汞评价本报告采用《全国海岸带和海涂资源综合调查简明规程》/r/n中的“海/r/n洋生物质量评价标准”进行评价；铬、砷、石油烃参考《第二次全国海洋/r/n污染基线/r/n调/r/n查技术规程(第二分册)》中规定的生物质量标准。/r/n/r/n污染物排放标准/r/n(/r/n1/r/n)大气污染物/r/n船舶废/r/n气/r/n执行《船舶发动机排气污染物排放限值及测量方法(中国第一、二阶/r/n/r/n段/r/n)》(/r/nGB/r/n15097-2016/r/n)第一阶段排放限值；/r/n(/r/n2/r/n)水污染物/r/n船舶/r/n污/r/n水执行《船舶水污染物排放控制标准》(/r/nGB/r/n3552-2018/r/n)；/r/n(/r/n3/r/n)固体废物/r/n项目一般工业固体废物储存执行《一般工业固体废物贮存和填/r/n埋污染控制标准/r/n(/r/nGB/r/n18599-2020/r/n)》中的相关规定。/r/n总量控制对象/r/n捕捞船舶等尾气的排放，/r/n尾气能满足《大气污染物综合排放标准(/r/nGB/r/n16297-1996/r/n)》无组织排放监控/r/n浓度限/r/n其/r/n/r/n/r/n施工和运营过程中产生的固废均得到有效处理，不外排；/r/n他/r/n本项目生活污水经集中收集至市政污水管道排入套子湾污水处理厂处/r/n理达标后/r/n态环境影响分析/r/n/r/n(/r/n1/r/n)水环境/r/n1/r/n)生活污水/r/n/r/n/r/n/r/n/r/n2/r/n)船舶机舱含油污水/r/n船舶机舱油/r/n污/r/n水是机舱内各闸阀和管路中漏出的水与机器在运转时漏/r/n/r/n/r/n计规范》(/r/nJTS/r/n149-2018/r/n)，船舶油污水不允许直接排海。/r/n/r/nd/r/n/r/n/r/n(/r/n2/r/n)固体废弃物/r/n/r/n(/r/n3/r/n)噪声/r/n/r/n/r/n最/r/n大声级(/r/ndB/r/n)/r/n测/r/n点与声源距离(/r/nm/r/n/r/n)/r/n5/r/n/r/n/r/nr/r/nm/r/nm/r/n5/r/n0824/r/n72/r/n988/r/n30/r/n工/r/n程施工场界噪声满足《建筑施工场界环境噪声排放标准》(/r/nGB/r/n12523-201/r/n1/r/n)的噪声排放限值，对周边村庄等声环境敏感目标基本无影响。/r/n(/r/n4/r/n)废气/r/nkw/r/n计，一艘船舶/r/n换算成马力(/r/n0.735/r/nkw/r/n=1/r/n马/r/n力)：/r/n1000/r/nkw/r/n/0.735=1360.5/r/n马力/r/n/r/nB/r/n0=150×/r/n1360.5×10/r/n-3/r/n=204.08kg/r/nGs/r/n=2/r/nB/r/n0/r/nS/r/n0/r/n(/r/n1-/r/nn/r/n/r/n)/r/n式中：/r/nGs/r/n—/r/nSO/r/n2/r/n排放量(/r/nkg/r/n)；/r/nB/r/n0/r/n——燃油量(/r/nkg/r/n)；/r/nS/r/n0/r/n——油中硫/r/n的/r/n/r/n含/r/n量(/r/n%/r/n)；/r/nn/r/n—/r/nSO/r/n2/r/n的脱除效率(/r/n%/r/n)。/r/n/r/nGs/r/n=2/r/nB/r/n0/r/nS/r/n0/r/n/r/n(/r/n1-/r/nn/r/n/r/n)/r/n=2/r/n×/r/n204.08/r/n×/r/n0.75%/r/n×(/r/n1-0/r/n)/r/n=3.06/r/nkg/r/n//r/nh/r/n式中：/r/nGc/r/n—/r/n—/r/nCO/r/n/r/n排放量(/r/nkg/r/n)；/r/nB/r/n0/r/n——燃油量(/r/nkg/r/n)；/r/nq/r/n/r/n——燃料的/r/n/r/n燃/r/n烧不完全值(/r/n%/r/n)，取/r/n2%/r/n；/r/n/r/n/r/n2/r/n/r/n运营期主要污/r/n染源和污染物影响分析/r/n/r/n(/r/n1/r/n)废气/r/n/r/n/r/nd/r/n4/r/n×/r/nkg/r/n。/r/n/r/n2kg/r/n。/r/na/r/n./r/nSO/r/n2/r/n源强/r/nGs/r/n=2/r/nB/r/n0/r/nS/r/n0/r/n/r/n(/r/n1-/r/nn/r/n/r/n)/r/n式中：/r/nGs/r/n—/r/nSO/r/n2/r/n排放量(/r/nkg/r/n)；/r/nB/r/n0/r/n——燃油量(/r/nkg/r/n)；/r/nS/r/n0/r/n——油中硫/r/n的/r/n/r/n含/r/n量(/r/n%/r/n)；—/r/nSO/r/n2/r/n的脱除效率(/r/n%/r/n)。/r/n/r/nb/r/n./r/nNO/r/nx/r/n/r/n源强/r/n/r/n/r/nc/r/nCO/r/n式中：/r/n/r/nGc/r/n——/r/nCO/r/n/r/n排放量(/r/nkg/r/n)；/r/nB/r/n0/r/n——燃油量(/r/nkg/r/n)；/r/nq/r/n——燃料的/r/n/r/n燃烧不完全值(/r/n%/r/n)，取/r/n2%/r/n；/r/nC/r/n——燃/r/n料含碳量，/r/n85%~90%/r/n。/r/n/r/n/r/n/r/nO/r/n/r/n/r/n(/r/n2/r/n)噪声/r/n船舶噪声污/r/n染/r/n源主要为看护船和捕捞船产生的噪声。主要噪声源强在/r/n/r/n55/r/n~/r/n85/r/ndB/r/n/r/n之间。项目区距离声敏感目标较远，项目运营不会对周边敏感/r/n目/r/n/r/n(/r/n3/r/n)废水/r/n/r/n1/r/n)生活污水/r/n/r/n/r/n/r/n/r/n/r/n/r/n2/r/n)舱底油污/r/n水/r/n/r/n/r/n/r/n/r/n3/r/n)悬浮泥沙/r/n/r/n(/r/n4/r/n)固体废弃物/r/n/r/n/r/n/r/n(/r/n5/r/n)养殖污染物/r/n/r/n3/r/n/r/n项目各阶段非/r/n污染环境影响分析/r/n/r/n/r/n/r/n/r/n环境影响分析/r/n(/r/n1/r/n)大气环境影响分析/r/n/r/n/r/n(/r/n2/r/n)声环境影响分析/r/n/r/n/r/n(/r/n3/r/n)水环境影响分析/r/n/r/n。/r/n(/r/n1/r/n)入海悬浮泥沙发生点位置/r/n(/r/n2/r/n)入海悬浮泥沙源强/r/n/r/n/r/ns/r/n/r/nS/r/n0/r/n×/r/n0.45/r/n×/r/n0.0075=2.80kg/s/r/n(/r/n3/r/n)悬浮泥沙浓度增量分布/r/n根/r/n据/r/n数值模拟结果(图/r/n4-2/r/n)，礁体抛填施工期间，悬浮泥沙超二类水/r/n/r/n质标准范围(/r/n10/r/nmg/r/n//r/nL/r/n/r/n浓度悬浮泥沙扩散范围)面积为/r/n309.41/r/nhm/r/n2/r/n，/r/n50/r/nmg/r/n//r/nL/r/n浓度/r/n悬浮泥沙扩散范围面积为/r/n205.20hm/r/n2/r/n，悬浮泥沙超三类水质标准范围/r/n /r/n/r/n/r/n(/r/n4/r/n)水动力、地形地貌与冲淤环境的影响分析/r/n1/r/n)水文动力环境影响分/r/n析/r/n/r/n/r/n/r/n算法可靠、计算稳定、界面友好、前后处理功能强大等优点，已在全球/r/n/r/n70/r/n多个国家得到/r/n应/r/n用，有上百例成功算例，计算结果可靠，为国际所公认。/r/n/r/nMIKE/r/nFM/r/nGalerkin/r/n采/r/nEQ\*jc3\*hps20\o\al(\s\up6(/r/n),/r/n?/r/nt/r/n)/r/n /r/nu/r/nv/r/n_/r/n/r/n/r/nc/r/nx/r/n/r/n))|/r/n_/r/n/r/n/r/nc/r/nx/r/n/r/n))||/r/n_/r/nfv/r/n/r/n+/r/n=/r/n_/r/ng/r/n/r/nEQ\*jc3\*hps17\o\al(\s\up5(/r/n),/r/n?/r/n)/r/n匕/r/nx/r/n/r/nEQ\*jc3